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{{#Wiki_filter:W9LF CREEK NUCLEAR OPERATING CORPORATION Michael J. Westman Manager Regulatory Affairs April 23, 2014 RA 14-0048 U. S. Nuclear Regulatory Commission ATTN: Document Control Desk Washington, DC 20555  
{{#Wiki_filter:W9LF CREEK   NUCLEAR OPERATING CORPORATION Michael J. Westman Manager Regulatory Affairs April 23, 2014 RA 14-0048 U. S. Nuclear Regulatory Commission ATTN: Document Control Desk Washington, DC 20555


==Subject:==
==Subject:==
Docket No. 50-482: 2013 Annual Radiological Environmental Operating Report Gentlemen:
Docket No. 50-482: 2013 Annual Radiological Environmental Operating Report Gentlemen:
The purpose of this letter is to submit the enclosed Annual Radiological Environmental Operating Report, which is being submitted pursuant to Wolf Creek Generating Station (WCGS) Technical Specification 5.6.2. This report covers radiological environmental monitoring around WCGS for the period of January 1, 2013, through December 31, 2013.This letter contains no commitments.
The purpose of this letter is to submit the enclosed Annual Radiological Environmental Operating Report, which is being submitted pursuant to Wolf Creek Generating Station (WCGS) Technical Specification 5.6.2.                     This report covers radiological environmental monitoring around WCGS for the period of January 1, 2013, through December 31, 2013.
If you have any questions concerning this matter, please contact me at (620) 364-4009, or Mr. William Muilenburg, at (620) 364-4186.Sincerely, Michael J. Westman MJW/rlt  
This letter contains no commitments. If you have any questions concerning this matter, please contact me at (620) 364-4009, or Mr. William Muilenburg, at (620) 364-4186.
Sincerely, Michael J. Westman MJW/rlt


==Enclosure:==
==Enclosure:==
2013 Annual Radiological Environmental Operating Report cc:    M. L. Dapas (NRC), w/e C. F. Lyon (NRC), w/e N. F. O'Keefe (NRC), w/e Senior Resident Inspector (NRC), w/e P.O. Box 411 / Burlington, KS 66839 / Phone: (620) 364-8831 An Equal Opportunity Employer MIFIHCNET                        44-
                                                                                                            /


2013 Annual Radiological Environmental Operating Report cc: M. L. Dapas (NRC), w/e C. F. Lyon (NRC), w/e N. F. O'Keefe (NRC), w/e Senior Resident Inspector (NRC), w/e P.O. Box 411 / Burlington, KS 66839 / Phone: (620) 364-8831 An Equal Opportunity Employer MIFIHCNET 44-/
Enclosure to RA 14-0048 Wolf Creek Nuclear Operating Corporation Wolf Creek Generating Station 2013 Annual Radiological Environmental Operating Report (169 pages)
Enclosure to RA 14-0048 Wolf Creek Nuclear Operating Corporation Wolf Creek Generating Station 2013 Annual Radiological Environmental Operating Report (169 pages)
WOLF CREEK NUCLEAR OPERATING CORPORATION WOLF CREEK GENERATING STATION 2013 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT'F April 15, 2014 TABLE OF CONTENTS List of Tables ii List of Figures ii List of Charts ii Executive Summary 1 Introduction 1 I. Program Description 1 I1. Discussion of Results 4 Ill. Program Revisions/Changes 9 IV. Program Deviations 10 V. Interlaboratory Comparison Program 10 VI. Comparison to the Radioactive Effluent Release Program 11 Tables 12 Figures 21 Charts 26 Appendix A -Interlaboratory Comparison Program Results A-1 Appendix B -Summary Tables B-1 Appendix C -Individual Sample Results C-1 Air Particulate and Charcoal Filters C-1 Quarterly Air Particulate  
 
-Gamma C-13 Surface Water C-25 Ground Water C-33 Drinking Water C-49 Quarterly Drinking Water -Tritium C-57 Shoreline Sediment C-59 Fish C-62 Food/Garden C-67 Feed and Forage C-74 Bottom Sediment C-77 Aquatic Vegetation C-93 Terrestrial Vegetation C-96 Soil C-98 Deer C-100 Appendix D -Land Use Census Report D-1 LIST OF TABLES 1 Radiological Environmental Monitoring Program Description 12 2 Sample Location Identifiers, Distances (Miles) and Directions (Sectors) 17 3 OSL Dosimeter Results 20 LIST OF FIGURES 1 Airborne Pathway Sampling Locations 21 2 Direct Radiation Pathway Sampling Locations 22 3 Waterborne Pathway Sampling Locations 23 4 Ingestion Pathway Sampling Locations 24 5 Distant Sampling Locations 25 LIST OF CHARTS 1 Airborne Gross Beta Weekly Results 26 2 Historical Airborne Smoothed Indicator and Control Gross Beta 27 3 OSL Dosimeters  
WOLF CREEK NUCLEAR OPERATING CORPORATION WOLF CREEK GENERATING STATION 2013 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT
-Indicator and Control Locations 28 4 Historical TLD Nearsite Locations and Control Locations 29 5 Coffey County Lake Surface Water Tritium Data 30 6 Drinking Water Gross Beta (5 years) 31 7 Detected Cs-1 37 Activity in Bottom Sediment 32 ii EXECUTIVE  
                        'F April 15, 2014
 
TABLE OF CONTENTS List of Tables                                                   ii List of Figures                                                 ii List of Charts                                                   ii Executive Summary                                               1 Introduction                                                     1 I. Program Description                                         1 I1. Discussion of Results                                       4 Ill. Program Revisions/Changes                                   9 IV. Program Deviations                                         10 V. Interlaboratory Comparison Program                         10 VI. Comparison to the Radioactive Effluent Release Program     11 Tables                                                         12 Figures                                                         21 Charts                                                         26 Appendix A - Interlaboratory Comparison Program Results   A-1 Appendix B - Summary Tables                               B-1 Appendix C - Individual Sample Results                     C-1 Air Particulate and Charcoal Filters   C-1 Quarterly Air Particulate - Gamma       C-13 Surface Water                           C-25 Ground Water                           C-33 Drinking Water                         C-49 Quarterly Drinking Water - Tritium     C-57 Shoreline Sediment                     C-59 Fish                                   C-62 Food/Garden                             C-67 Feed and Forage                         C-74 Bottom Sediment                         C-77 Aquatic Vegetation                     C-93 Terrestrial Vegetation                 C-96 Soil                                   C-98 Deer                                   C-100 Appendix D - Land Use Census Report                       D-1
 
LIST OF TABLES 1 Radiological Environmental Monitoring Program Description               12 2 Sample Location Identifiers, Distances (Miles) and Directions (Sectors) 17 3 OSL Dosimeter Results                                                   20 LIST OF FIGURES 1 Airborne Pathway Sampling Locations                                     21 2 Direct Radiation Pathway Sampling Locations                             22 3 Waterborne Pathway Sampling Locations                                   23 4 Ingestion Pathway Sampling Locations                                   24 5 Distant Sampling Locations                                             25 LIST OF CHARTS 1 Airborne Gross Beta Weekly Results                                     26 2 Historical Airborne Smoothed Indicator and Control Gross Beta           27 3 OSL Dosimeters - Indicator and Control Locations                       28 4 Historical TLD Nearsite Locations and Control Locations                 29 5 Coffey County Lake Surface Water Tritium Data                           30 6 Drinking Water Gross Beta (5 years)                                     31 7 Detected Cs-1 37 Activity in Bottom Sediment                           32 ii
 
EXECUTIVE  


==SUMMARY==
==SUMMARY==
Plant-related activation, corrosion, or fission products were not detected during 2013 in airborne particulate and radioiodine, filters, drinking water, ground water, broadleaf vegetation, shoreline sediment, crops, aquatic vegetation, terrestrial vegetation, bottom sediment, or soil samples.Activation, corrosion or fission products attributable to plant operation were detected during 2013 in surface water, fish, and deer samples.Nuclides detected in Radiological Environmental Monitoring Program (REMP) samples were below applicable Nuclear Regulatory Commission (NRC) reporting levels.Based upon the radiological environmental monitoring program results, it was concluded station operations had no significant radiological impact on the health and safety of the public or the environment.
 
INTRODUCTION The 2013 Annual Radiological Environmental Operating Report for Wolf Creek Generating Station (WCGS) covers the period from January 1 through December 31, 2013. WCGS is located in Coffey County, Kansas, approximately five miles northeast of Burlington, Kansas.Fuel loading commenced at WCGS on March 12, 1985. The operational phase of the REMP began with initial criticality on May 22, 1985, and the first detectable quantities of radioactivity were reported in plant effluents in June 1985.This report contains a description of the REMP conducted by Wolf Creek Nuclear Operating Corporation (WCNOC), a discussion of monitoring program results, the revisions or changes to the program, program deviations, the Interlaboratory Comparison Program and a comparison to the Radioactive Effluent Release Program. The Interlaboratory Comparison Program results, a summary of results in the NRC Branch Technical Position specified format, the individual sample results, and the Land Use Census Report are included as appendices.
Plant-related activation, corrosion, or fission products were not detected during 2013 in airborne particulate and radioiodine, filters, drinking water, ground water, broadleaf vegetation, shoreline sediment, crops, aquatic vegetation, terrestrial vegetation, bottom sediment, or soil samples.
I. PROGRAM DESCRIPTION Radiological environmental monitoring samples were collected according to the schedule in WCGS procedure AP 07B-004, Offsite Dose Calculation Manual (Radiological Environmental Monitoring Program).
Activation, corrosion or fission products attributable to plant operation were detected during 2013 in surface water, fish, and deer samples.
Radiological environmental monitoring program samples were collected by the WCGS Environmental Management group and were analyzed by Environmental, Inc.Landauer, Inc. processed the environmental optically stimulated luminescence (OSL)dosimeters.
Nuclides detected in Radiological Environmental Monitoring Program (REMP) samples were below applicable Nuclear Regulatory Commission (NRC) reporting levels.
Table 1 identifies the exposure pathway/sample type, number of samples and sample locations, sample collection frequency, and type and frequency of analysis.
Based upon the radiological environmental monitoring program results, it was concluded station operations had no significant radiological impact on the health and safety of the public or the environment.
Table 2 lists the sample location identifiers, distances and directions from the plant. Samples in addition to those required by AP 07B-004 were also obtained and analyzed.The following is a description of the sampling and analysis program by individual pathways.2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 1 of 32 A. Airborne Pathway Low volume air sampling pumps with digital flow meters continuously collected air particulate and radioiodine samples on 47 mm glass fiber filters and charcoal canisters, respectively.
INTRODUCTION The 2013 Annual Radiological Environmental Operating Report for Wolf Creek Generating Station (WCGS) covers the period from January 1 through December 31, 2013. WCGS is located in Coffey County, Kansas, approximately five miles northeast of Burlington, Kansas.
The air particulate filters and charcoal canisters were changed out weekly. Gross beta analysis was performed on the air particulate filters. Air particulate filters were also analyzed quarterly for gamma emitting isotopes.
Fuel loading commenced at WCGS on March 12, 1985. The operational phase of the REMP began with initial criticality on May 22, 1985, and the first detectable quantities of radioactivity were reported in plant effluents in June 1985.
Charcoal canisters were analyzed for 1-131.Air samples were collected from six locations.
This report contains a description of the REMP conducted by Wolf Creek Nuclear Operating Corporation (WCNOC), a discussion of monitoring program results, the revisions or changes to the program, program deviations, the Interlaboratory Comparison Program and a comparison to the Radioactive Effluent Release Program. The Interlaboratory Comparison Program results, a summary of results in the NRC Branch Technical Position specified format, the individual sample results, and the Land Use Census Report are included as appendices.
The five indicator locations sampled included 2, 18, 32, 37 and 49. A control location near the intersection of 20th Road and Yearling Road (location
I. PROGRAM DESCRIPTION Radiological environmental monitoring samples were collected according to the schedule in WCGS procedure AP 07B-004, Offsite Dose Calculation Manual (Radiological Environmental Monitoring Program). Radiological environmental monitoring program samples were collected by the WCGS Environmental Management group and were analyzed by Environmental, Inc.
: 53) was also sampled. Indicator sample locations are shown in Figure 1 and the control sample location is shown in Figure 5.B: Direct Radiation Pathway Optically stimulated luminescence (OSL) dosimeters were used continuously at 43 locations during the sample year to measure direct radiation.
Landauer, Inc. processed the environmental optically stimulated luminescence (OSL) dosimeters. Table 1 identifies the exposure pathway/sample type, number of samples and sample locations, sample collection frequency, and type and frequency of analysis. Table 2 lists the sample location identifiers, distances and directions from the plant. Samples in addition to those required by AP 07B-004 were also obtained and analyzed.
The OSLs were typically positioned roughly 3 to 4 feet above the ground in plastic thermostat boxes. Three OSLs were placed at each designated location.
The following is a description of the sampling and analysis program by individual pathways.
The OSLs were changed out quarterly and analyzed for gamma dose.Transit dose was measured and subtracted from the ambient dose. Indicator OSL sample locations are illustrated in Figure 2 and control sample locations are shown in Figure 5. Control sample locations were 39 (Beto Junction) and 53 (near the intersection of 2 0 th Road and Yearling Road).C. Waterborne Pathway Water samples were analyzed to determine if gamma emitters were present. In addition to gamma isotopic analysis, radiochemical analysis for 1-131 was performed on drinking water and ground water samples. Gross beta analysis was also performed on drinking water samples.Tritium analysis was performed monthly by liquid scintillation for surface water and quarterly for drinking water. Tritium analysis was also performed on ground water samples. Four surface water samples from the Coffey County Lake Spillway (SP) location and four surface water samples from the John Redmond Reservoir (JRR) location were also analyzed for Fe-55. The waterborne pathway sample locations are shown in Figures 3 and 5.Monthly grab samples of surface water were collected from the JRR control location and from the SP indicator location.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                 Page 1 of 32
The SP indicator sample location is located near the spillway of Coffey County Lake, formerly known as Wolf Creek Lake.Quarterly grab samples of ground water were collected from seven wells. Six locations (C-10, C-49, F-1, G-2, J-1 and J-2) located hydrologically down gradient from the site were used as indicator sample locations.
 
Location B-12 located hydrologically up gradient from the site was used as a control sample location.Drinking water was sampled at the water treatment facilities in the towns of Iola (indicator sample location IO-DW) and Burlington (control sample location BW-15). The Iola facility is located downstream of the site and the Burlington facility is located upstream of the confluence of the Coffey County Lake discharge and the Neosho River. Composite samples were obtained monthly from automatic samplers at each location.
A. Airborne Pathway Low volume air sampling pumps with digital flow meters continuously collected air particulate and radioiodine samples on 47 mm glass fiber filters and charcoal canisters, respectively. The air particulate filters and charcoal canisters were changed out weekly. Gross beta analysis was performed on the air particulate filters. Air particulate filters were also analyzed quarterly for gamma emitting isotopes. Charcoal canisters were analyzed for 1-131.
The drinking water automatic samplers collected approximately 27 milliliters of water every two hours.2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 2 of 32 Shoreline sediments were sampled semiannually.
Air samples were collected from six locations. The five indicator locations sampled included 2, 18, 32, 37 and 49. A control location near the intersection of 20th Road and Yearling Road (location 53) was also sampled. Indicator sample locations are shown in Figure 1 and the control sample location is shown in Figure 5.
Gamma isotopic analyses were performed on the shoreline sediment samples. Shoreline sediment sample locations were the Coffey County Lake discharge cove (DC) indicator location and the JRR control location.D. Ingestion Pathway Milk was not collected during the sample year. The Land Use Census did not identify any locations producing milk for human consumption within five miles of the plant.Fish were sampled semiannually from the Coffey County Lake (indicator sample location) and from the tail waters of JRR (control sample location).
B: Direct Radiation Pathway Optically stimulated luminescence (OSL) dosimeters were used continuously at 43 locations during the sample year to measure direct radiation. The OSLs were typically positioned roughly 3 to 4 feet above the ground in plastic thermostat boxes. Three OSLs were placed at each designated location. The OSLs were changed out quarterly and analyzed for gamma dose.
These sample locations are identified in Figure 4. Gamma isotopic analyses were performed on the boneless edible portions of the fish.Several species of game fish and rough fish were sampled. Fish were also analyzed for tritium.Broadleaf vegetation samples were collected monthly when available during the growing season. Three indicator (B-1, H-2 and Q-6) gardens (Figure 4) and one control (D-2) garden (Figure 5) were sampled. Gamma isotopic analyses were performed on these samples.Crop samples were obtained from two indicator sample locations (NR-D1 and NR-D2)downstream of the confluence of Wolf Creek and the Neosho River. Crops were also sampled from control location NR-U1. Gamma isotopic analysis was performed on each sample. Crop sample locations are identified on Figure 5.E. Additional Samples Collected (not required by AP 07B-004)Quarterly, duplicate ground water grab samples were obtained from indicator location C-49 and were labeled L-49. These duplicate samples served as laboratory quality checks. The ground water samples were analyzed for gamma emitters, 1-131, and tritium.Bottom sediment samples were collected from indicator sample locations at the Coffey County Lake discharge cove (DC), Environmental Education Area (EEA), Make-Up Discharge Structure (MUDS), Ultimate Heat Sink (UHS), Essential Service Water (ESW) channel, and the control sample location (JRR). Gamma isotopic analyses were performed on the bottom sediment samples. Samples obtained from DC, ESW and UHS were also analyzed for Fe-55. Some of the bottom sediment samples were collected as part of a cooperative sampling effort with the Kansas Department of Health and Environment (KDHE). The sample locations are identified on Figure 3.Shoreline sediment samples were collected from indicator sample location EEA. Gamma isotopic analyses were performed on the samples. These samples were collected as part of a cooperative sampling effort with the KDHE. This sample location is identified on Figure 3.Aquatic vegetation was collected from indicator sample locations DC ALT, EEA and MUDS.Gamma isotopic analyses were performed on the aquatic vegetation samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 3.Terrestrial vegetation (grass) was sampled from the EEA and MUDS indicator sample locations.
Transit dose was measured and subtracted from the ambient dose. Indicator OSL sample locations are illustrated in Figure 2 and control sample locations are shown in Figure 5. Control sample locations were 39 (Beto Junction) and 53 (near the intersection of 2 0 th Road and Yearling Road).
Gamma isotopic analyses were performed on the grass samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 4.2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 3 of 32 Soil was sampled from the EEA and MUDS indicator sample locations.
C. Waterborne Pathway Water samples were analyzed to determine if gamma emitters were present. In addition to gamma isotopic analysis, radiochemical analysis for 1-131 was performed on drinking water and ground water samples. Gross beta analysis was also performed on drinking water samples.
Gamma isotopic analyses were performed on the soil samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 4.A deer was sampled from indicator sample location R2.7. Gamma isotopic analysis and tritium analysis was performed on the deer sample. This sample was collected as part of a cooperative sampling effort with the KDHE. The sample location is identified on Figure 4.II. DISCUSSION OF RESULTS Analysis results for pathways are summarized in Appendix B using the format described in Radiological Assessment Branch Technical Position, Revision 1, November 1979 (NRC Generic Letter 79-065). Results for individual samples are listed in Appendix C.A. Airborne Pathway Chart 1 graphically illustrates weekly gross beta results for the sample year for all of the airborne sample locations.
Tritium analysis was performed monthly by liquid scintillation for surface water and quarterly for drinking water. Tritium analysis was also performed on ground water samples. Four surface water samples from the Coffey County Lake Spillway (SP) location and four surface water samples from the John Redmond Reservoir (JRR) location were also analyzed for Fe-55. The waterborne pathway sample locations are shown in Figures 3 and 5.
Chart 2 represents the gross beta historical airborne smoothed averages of indicator sample locations and control sample locations.
Monthly grab samples of surface water were collected from the JRR control location and from the SP indicator location. The SP indicator sample location is located near the spillway of Coffey County Lake, formerly known as Wolf Creek Lake.
Charts 1 and 2 demonstrate how closely the indicator and control sample locations tracked together.
Quarterly grab samples of ground water were collected from seven wells. Six locations (C-10, C-49, F-1, G-2, J-1 and J-2) located hydrologically down gradient from the site were used as indicator sample locations. Location B-12 located hydrologically up gradient from the site was used as a control sample location.
Chart 2 reveals a seasonal cyclic trend; the gross beta values peak in the winter months (December or January) and decrease to a low point in the spring months (May or June). This trend is expected and is attributed to seasonal meteorological changes, i.e., changes in prevailing winds and precipitation.
Drinking water was sampled at the water treatment facilities in the towns of Iola (indicator sample location IO-DW) and Burlington (control sample location BW-15). The Iola facility is located downstream of the site and the Burlington facility is located upstream of the confluence of the Coffey County Lake discharge and the Neosho River. Composite samples were obtained monthly from automatic samplers at each location. The drinking water automatic samplers collected approximately 27 milliliters of water every two hours.
The gross beta results of 2013 were compared to pre-operational monitoring results of 1983 and 1984. The weekly gross beta analyses range for 1983 and 1984 was 0.0064 to 0.084 pCi/m 3.The 2013 weekly gross beta analyses range for indicator locations was 0.009 to 0.050 pCi/mi 3.The 2013 weekly gross beta analyses range was lower than the 1983 and 1984 pre-operational range. Additionally, the annual mean for indicator locations for 2013 (0.026 pCi/m 3) was lower than the annual mean for 1983 (0.032 pCi/m 3).The gross beta results for the indicator locations were also compared to the control location.The annual mean for indicator locations for 2013 (0.026 pCi/m 3) was the same as the annual mean of the control location (0.026 pCi/m 3). The indicator location with the highest gross beta annual mean was location 49 (0.027 pCi/m 3) and was slightly higher than the annual mean of the control location (0.026 pCi/m 3).Naturally occurring Be-7 activity was detected, as was the case during pre-operational monitoring.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                 Page 2 of 32
In 1984, the range for Be-7 detected activity was 0.024 to 0.211 pCi/m 3 for indicator locations and the annual mean for indicator locations was 0.069 pCi/m 3.In 2013, the range for Be-7 detected activity was 0.052 to 0.092 pCi/m 3 for indicator locations and the annual mean for indicator locations was 0.076 pCi/m 3.The annual mean of the indicator locations (0.076 pCi/m 3)was the same as the annual mean of the control location (0.076 pCi/m 3).1-131 activity was not detected in the weekly analysis of charcoal filters at any location.The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in airborne particulate and radioiodine filters and no unusual trends were noted.2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 4 of 32 B. Direct Radiation Pathway Quarterly OSL dosimeter results for each location are shown in Table 3. Measured values have been converted to a standardized 90-day quarter.The annual mean of indicator sample locations in 2013 was 18.7 mR per standardized 90-day quarter. The annual mean of the control sample locations in 2013 was 19.5 mR per standardized 90-day quarter.For pre-operational comparison, in 1981, the annual mean of indicator sample locations was 18.9 mR per standardized 90-day quarter and the annual mean for the control sample locations was 17.1 mR per standardized 90-day quarter. It should be noted WCGS changed from thermoluminescence dosimeters (TLD) to optically stimulated luminescence (OSL) dosimeters in 2008.The indicator sample location with the highest annual mean was 47 (24.2 mR per standardized 90-day quarter).
 
The close proximity of location 47 to the Radwaste Building is likely the reason direct radiation levels are higher at this location.Based upon Condition Report 00027489, improvements were made in measuring and subtracting transit dose in 2010. As expected, the OSL results have increased since 2010.Chart 3 visibly displays the increase of the OSL results. Chart 3 also displays how closely the indicator and control location OSL dosimeter results are for 2013.Chart 4 displays the TLD nearsite sample locations (1, 2, 7-9, 11-14, 18, 26, 27, 29, 30, 37 and 38) and the control sample locations (locations 39 and 48) for the preoperational years through 2007.C. Waterborne Pathway (1) Surface Water Tritium, attributable to WCGS operation, was detected in surface water samples collected from the Coffey County Lake Spillway (SP) indicator sample location.
Shoreline sediments were sampled semiannually. Gamma isotopic analyses were performed on the shoreline sediment samples. Shoreline sediment sample locations were the Coffey County Lake discharge cove (DC) indicator location and the JRR control location.
The annual mean for detected tritium activity at the SP location was 11,100 pCi/L and the range was 9,295 to 13,170 pCi/L.The detected tritium activity was below the'30,000 pCi/L AP 07B-004 reporting level. Chart 5 illustrates the yearly averages of surface water tritium data for the spillway (SP) location.
D. Ingestion Pathway Milk was not collected during the sample year. The Land Use Census did not identify any locations producing milk for human consumption within five miles of the plant.
Chart 5 indicates the average tritium concentration of the Coffey County Lake spillway (SP) location has reached equilibrium.
Fish were sampled semiannually from the Coffey County Lake (indicator sample location) and from the tail waters of JRR (control sample location). These sample locations are identified in Figure 4. Gamma isotopic analyses were performed on the boneless edible portions of the fish.
Tritium activity was not detected in samples obtained from the control sample location (JRR).During pre-operational radiological environmental monitoring, measured radiological activity was not detected in surface water samples.The AP 07B-004 required lower limits of detection were met. Radionuclides were not detected by the gamma isotopic analyses or by Fe-55 analyses.Tritium was the only activity detected during 2013 in surface water samples and no unusual trends were noted.2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 5 of 32 (2) Ground Water The AP 07B-004 required lower limits of detection were met for 1-131, tritium and gamma isotopic analyses.
Several species of game fish and rough fish were sampled. Fish were also analyzed for tritium.
Radioactivity was not detected in any ground water samples. No unusual trends were noted. Plant-related activation, corrosion or fission products were not detected during 2013 in ground water samples.(3) Drinking Water Gross beta activity was detected in drinking water samples collected from the indicator sample location and in samples collected from the control sample location.
Broadleaf vegetation samples were collected monthly when available during the growing season. Three indicator (B-1, H-2 and Q-6) gardens (Figure 4) and one control (D-2) garden (Figure 5) were sampled. Gamma isotopic analyses were performed on these samples.
The annual mean of the indicator sample location gross beta activity (2.9 pCi/L) was lower when compared to the annual mean of the control sample location gross beta activity (3.1 pCi/L). The 2013 annual means of gross beta activity for both the indicator and control sample locations were lower than those of the pre-operational monitoring year of 1984. In 1984, the annual mean of the indicator sample location gross beta activity was 7.5 pCi/L and the annual mean of the control sample location gross beta activity was 6.4 pCi/L.Chart 6 illustrates the drinking water gross beta results for the last five years and how closely the gross beta results compared for the indicator and control sample locations.
Crop samples were obtained from two indicator sample locations (NR-D1 and NR-D2) downstream of the confluence of Wolf Creek and the Neosho River. Crops were also sampled from control location NR-U1. Gamma isotopic analysis was performed on each sample. Crop sample locations are identified on Figure 5.
Radionuclides were not detected by the 1-131 or gamma isotopic analyses.The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in drinking water samples and no unusual trends were noted.(4) Shoreline Sediment Naturally occurring K-40 was detected in shoreline sediment samples collected from the DC (indicator sample location) and JRR (control sample location).
E. Additional Samples Collected (not required by AP 07B-004)
K-40 was also detected during pre-operational shoreline sediment monitoring.
Quarterly, duplicate ground water grab samples were obtained from indicator location C-49 and were labeled L-49. These duplicate samples served as laboratory quality checks. The ground water samples were analyzed for gamma emitters, 1-131, and tritium.
No other radionuclides were detected in the DC or JRR shoreline sediment samples during 2013.The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in shoreline sediment samples and no unusual trends were noted.D. Ingestion Pathway (1) Milk Milk was not collected during the sample year since no indicator locations within five miles of the plant were identified during the Land Use Census.2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 6 of 32 (2) Fish Naturally occurring K-40 activity was detected in fish samples obtained from the CCL indicator sample location and in fish samples obtained from the JRR control sample location.
Bottom sediment samples were collected from indicator sample locations at the Coffey County Lake discharge cove (DC), Environmental Education Area (EEA), Make-Up Discharge Structure (MUDS), Ultimate Heat Sink (UHS), Essential Service Water (ESW) channel, and the control sample location (JRR). Gamma isotopic analyses were performed on the bottom sediment samples. Samples obtained from DC, ESW and UHS were also analyzed for Fe-55. Some of the bottom sediment samples were collected as part of a cooperative sampling effort with the Kansas Department of Health and Environment (KDHE). The sample locations are identified on Figure 3.
K-40 activity was also detected during pre-operational fish monitoring.
Shoreline sediment samples were collected from indicator sample location EEA. Gamma isotopic analyses were performed on the samples. These samples were collected as part of a cooperative sampling effort with the KDHE. This sample location is identified on Figure 3.
Fish samples were also analyzed for tritium. Fish samples collected from Coffey County Lake had tritium activity detected (7,743 pCi/kg annual mean). The detected tritium activity was attributable to plant operation.
Aquatic vegetation was collected from indicator sample locations DC ALT, EEA and MUDS.
An adult consuming 21 kilograms of fish, at the maximum measured tritium concentration (8,852 pCi/kg), would receive a committed effective dose equivalent of 0.012 mRem.Tritium activity was not detected in the control location samples collected from JRR.No other radionuclides were detected in fish samples during 2013. The AP 07B-004 required lower limits of detection were met and no unusual trends were noted.(3) Broadleaf Vegetation Gamma analyses of broadleaf vegetation samples obtained from indicator and control sample locations detected naturally occurring gamma emitters Be-7 and K-40. Be-7 and K-40 activity were also detected pre-operationally.
Gamma isotopic analyses were performed on the aquatic vegetation samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 3.
No other radionuclides were detected in broadleaf vegetation samples during the year.The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in broadleaf vegetation samples no unusual trends were noted.(4) Crop Samples Gamma analysis detected naturally occurring K-40 activity to be present in the samples collected from the indicator sample locations and in the samples collected from the control sample location.
Terrestrial vegetation (grass) was sampled from the EEA and MUDS indicator sample locations.
K-40 activity was also detected during pre-operational crop monitoring.
Gamma isotopic analyses were performed on the grass samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 4.
K-40 was the only activity detected in the crop samples.The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in crop samples and no unusual trends were noted.E. Additional Samples Collected (not required by AP 07B-004)(1) Bottom Sediment Gamma analysis detected naturally occurring K-40 activity to be present in the samples collected from the indicator sample locations and in the samples collected from the control sample location.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                               Page 3 of 32
K-40 activity was also detected during pre-operational bottom sediment monitoring.
 
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 7 of 32 Cs-137 activity was detected in twelve samples obtained from indicator locations (range 38 to 108 pCi/kg, dry). Cs-137 activity was also detected in one sample obtained from the control sample location (85 pCi/kg, dry).Cs-137 activity was detected in pre-operational samples. The Cs-137 activity detected in 2013 indicator sample location bottom sediment samples was within the pre-operational range.(Cs-137 activity detected in 1981 and 1982 was in the range of 79 to 953 pCi/kg. The decay corrected range of pre-operational Cs-1 37 activity detected is approximately 38 to 457 pCi/kg.)The detected Cs-137 activity in the samples collected from the indicator sample locations was likely due to fallout since the measured activity is within the decay corrected range of pre-operational Cs-137 detected activity and Cs-137 activity has also been detected in samples collected at the control sample location.Chart 7 plots the Cs-1 37 detected activity from the discharge cove indicator sample location and JRR control sample location bottom sediment samples. The detected Cs-137 activity measured from the discharge cove location reflects a decreasing trend. The Chart 7 trendline indicates Cs-137 activity detected at the JRR control location has also been decreasing.
Soil was sampled from the EEA and MUDS indicator sample locations. Gamma isotopic analyses were performed on the soil samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 4.
Chart 7 also displays that in recent years, the detected Cs-1 37 activity for the JRR and DC sample locations overlap.Fe-55 activity was not detected in the fourteen samples obtained from indicator sample locations.
A deer was sampled from indicator sample location R2.7. Gamma isotopic analysis and tritium analysis was performed on the deer sample. This sample was collected as part of a cooperative sampling effort with the KDHE. The sample location is identified on Figure 4.
No other radionuclides were detected in bottom sediment samples.Plant-related activation, corrosion, or fission products were not detected during 2013 in bottom sediment samples and no unusual trends were noted.(2) Aquatic Vegetation Gamma analyses of aquatic vegetation samples obtained from indicator sample locations detected naturally occurring gamma emitters Be-7 and K-40. Be-7 and K-40 activity were also detected during pre-operational monitoring.
II. DISCUSSION OF RESULTS Analysis results for pathways are summarized in Appendix B using the format described in Radiological Assessment Branch Technical Position, Revision 1, November 1979 (NRC Generic Letter 79-065). Results for individual samples are listed in Appendix C.
No other radionuclides were detected in aquatic vegetation samples. Plant-related activation, corrosion, or fission products were not detected during 2013 in aquatic vegetation samples and no unusual trends were noted.(3) Shoreline Sediment Naturally occurring K-40 activity was detected in the shoreline sediment samples obtained from the EEA indicator sample location.
A. Airborne Pathway Chart 1 graphically illustrates weekly gross beta results for the sample year for all of the airborne sample locations. Chart 2 represents the gross beta historical airborne smoothed averages of indicator sample locations and control sample locations.               Charts 1 and 2 demonstrate how closely the indicator and control sample locations tracked together. Chart 2 reveals a seasonal cyclic trend; the gross beta values peak in the winter months (December or January) and decrease to a low point in the spring months (May or June). This trend is expected and is attributed to seasonal meteorological changes, i.e., changes in prevailing winds and precipitation.
K-40 activity was also detected during pre-operational monitoring.
The gross beta results of 2013 were compared to pre-operational monitoring results of 1983 and 1984. The weekly gross beta analyses range for 1983 and 1984 was 0.0064 to 0.084 pCi/m 3 .
Cs-137 activity (89.2 pCi/kg, dry) was detected in a shoreline sediment sample obtained from the EEA indicator sample location.
The 2013 weekly gross beta analyses range for indicator locations was 0.009 to 0.050 pCi/mi3 .
Cs-137 activity was also detected in pre-operational shoreline sediment samples. Cs-137 activity detected in shoreline sediment samples collected from the DC location from 1982 to 1984 was in the range of 224 to 437 pCi/kg, dry. The decay corrected range of pre-operational Cs-1 37 activity detected is approximately 115 to 218 pCi/kg, dry. The detected Cs-137 activity in the shoreline sediment sample was likely due to fallout since the results are lower than the pre-operational decay corrected range. Additionally, Cs-1 37 activity is routinely detected in soil and sediment samples collected from the control locations.
The 2013 weekly gross beta analyses range was lower than the 1983 and 1984 pre-operational range. Additionally, the annual mean for indicator locations for 2013 (0.026 pCi/m 3) was lower than the annual mean for 1983 (0.032 pCi/m 3).
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 8 of 32 No other radionuclides were detected in the EEA shoreline sediment samples. Plant-related activation, corrosion, or fission products were not detected during 2013 and no unusual trends were noted.(4) Terrestrial Vegetation Naturally occurring Be-7 and K-40 activity were detected in terrestrial vegetation indicator location samples. No other radionuclides were detected in terrestrial vegetation.
The gross beta results for the indicator locations were also compared to the control location.
Plant-related activation, corrosion or fission products were not detected during 2013 in terrestrial vegetation samples and no unusual trends were noted.(5) Soil Naturally occurring K-40 activity was detected in soil samples obtained from the indicator locations.
The annual mean for indicator locations for 2013 (0.026 pCi/m 3 ) was the same as the annual mean of the control location (0.026 pCi/m 3). The indicator location with the highest gross beta annual mean was location 49 (0.027 pCi/m 3) and was slightly higher than the annual mean of the control location (0.026 pCi/m 3).
K-40 activity was also detected during pre-operational soil monitoring.
Naturally occurring Be-7 activity was detected, as was the case during pre-operational monitoring. In 1984, the range for Be-7 detected activity was 0.024 to 0.211 pCi/m 3 for indicator locations and the annual mean for indicator locations was 0.069 pCi/m 3 . In 2013, the range for Be-7 detected activity was 0.052 to 0.092 pCi/m 3 for indicator locations and the annual mean for indicator locations was 0.076 pCi/m 3 . The annual mean of the indicator locations (0.076 pCi/m 3) was the same as the annual mean of the control location (0.076 pCi/m 3).
Cs-137 activity (range 148 to 250 pCi/kg) was detected in soil samples obtained from the indicator locations.
1-131 activity was not detected in the weekly analysis of charcoal filters at any location.
Data was reviewed for soil samples collected pre-operationally.
The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in airborne particulate and radioiodine filters and no unusual trends were noted.
The detected Cs-137 activity range from February of 1985 was 255 to 2,160 pCi/kg. The decay corrected range of pre-operational Cs-137 activity detected in soil is approximately 134 to 1,137 pCi/kg. The detected Cs-137 activity in soil sampled in 2013 is within the decay corrected pre-operational range and is likely due to fallout.Plant-related activation, corrosion, or fission products were not detected during 2013 in soil samples and no unusual trends were noted.(6) Deer Naturally occurring K-40 activity was detected in the deer sample obtained from the indicator location.Tritium activity (251 pCi/kg) was also detected in the deer sample. The detected tritium activity was attributable to plant operation.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                   Page 4 of 32
 
B. Direct Radiation Pathway Quarterly OSL dosimeter results for each location are shown in Table 3. Measured values have been converted to a standardized 90-day quarter.
The annual mean of indicator sample locations in 2013 was 18.7 mR per standardized 90-day quarter. The annual mean of the control sample locations in 2013 was 19.5 mR per standardized 90-day quarter.
For pre-operational comparison, in 1981, the annual mean of indicator sample locations was 18.9 mR per standardized 90-day quarter and the annual mean for the control sample locations was 17.1 mR per standardized 90-day quarter. It should be noted WCGS changed from thermoluminescence dosimeters (TLD) to optically stimulated luminescence (OSL) dosimeters in 2008.
The indicator sample location with the highest annual mean was 47 (24.2 mR per standardized 90-day quarter). The close proximity of location 47 to the Radwaste Building is likely the reason direct radiation levels are higher at this location.
Based upon Condition Report 00027489, improvements were made in measuring and subtracting transit dose in 2010. As expected, the OSL results have increased since 2010.
Chart 3 visibly displays the increase of the OSL results. Chart 3 also displays how closely the indicator and control location OSL dosimeter results are for 2013.
Chart 4 displays the TLD nearsite sample locations (1, 2, 7-9, 11-14, 18, 26, 27, 29, 30, 37 and
: 38) and the control sample locations (locations 39 and 48) for the preoperational years through 2007.
C. Waterborne Pathway (1) Surface Water Tritium, attributable to WCGS operation, was detected in surface water samples collected from the Coffey County Lake Spillway (SP) indicator sample location. The annual mean for detected tritium activity at the SP location was 11,100 pCi/L and the range was 9,295 to 13,170 pCi/L.
The detected tritium activity was below the'30,000 pCi/L AP 07B-004 reporting level. Chart 5 illustrates the yearly averages of surface water tritium data for the spillway (SP) location. Chart 5 indicates the average tritium concentration of the Coffey County Lake spillway (SP) location has reached equilibrium. Tritium activity was not detected in samples obtained from the control sample location (JRR).
During pre-operational radiological environmental monitoring, measured radiological activity was not detected in surface water samples.
The AP 07B-004 required lower limits of detection were met. Radionuclides were not detected by the gamma isotopic analyses or by Fe-55 analyses.
Tritium was the only activity detected during 2013 in surface water samples and no unusual trends were noted.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                 Page 5 of 32
 
(2) Ground Water The AP 07B-004 required lower limits of detection were met for 1-131, tritium and gamma isotopic analyses. Radioactivity was not detected in any ground water samples. No unusual trends were noted. Plant-related activation, corrosion or fission products were not detected during 2013 in ground water samples.
(3) Drinking Water Gross beta activity was detected in drinking water samples collected from the indicator sample location and in samples collected from the control sample location. The annual mean of the indicator sample location gross beta activity (2.9 pCi/L) was lower when compared to the annual mean of the control sample location gross beta activity (3.1 pCi/L). The 2013 annual means of gross beta activity for both the indicator and control sample locations were lower than those of the pre-operational monitoring year of 1984. In 1984, the annual mean of the indicator sample location gross beta activity was 7.5 pCi/L and the annual mean of the control sample location gross beta activity was 6.4 pCi/L.
Chart 6 illustrates the drinking water gross beta results for the last five years and how closely the gross beta results compared for the indicator and control sample locations.
Radionuclides were not detected by the 1-131 or gamma isotopic analyses.
The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in drinking water samples and no unusual trends were noted.
(4) Shoreline Sediment Naturally occurring K-40 was detected in shoreline sediment samples collected from the DC (indicator sample location) and JRR (control sample location). K-40 was also detected during pre-operational shoreline sediment monitoring.
No other radionuclides were detected in the DC or JRR shoreline sediment samples during 2013.
The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in shoreline sediment samples and no unusual trends were noted.
D. Ingestion Pathway (1) Milk Milk was not collected during the sample year since no indicator locations within five miles of the plant were identified during the Land Use Census.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                 Page 6 of 32
 
(2) Fish Naturally occurring K-40 activity was detected in fish samples obtained from the CCL indicator sample location and in fish samples obtained from the JRR control sample location. K-40 activity was also detected during pre-operational fish monitoring.
Fish samples were also analyzed for tritium. Fish samples collected from Coffey County Lake had tritium activity detected (7,743 pCi/kg annual mean). The detected tritium activity was attributable to plant operation. An adult consuming 21 kilograms of fish, at the maximum measured tritium concentration (8,852 pCi/kg), would receive a committed effective dose equivalent of 0.012 mRem.
Tritium activity was not detected in the control location samples collected from JRR.
No other radionuclides were detected in fish samples during 2013. The AP 07B-004 required lower limits of detection were met and no unusual trends were noted.
(3) Broadleaf Vegetation Gamma analyses of broadleaf vegetation samples obtained from indicator and control sample locations detected naturally occurring gamma emitters Be-7 and K-40. Be-7 and K-40 activity were also detected pre-operationally.
No other radionuclides were detected in broadleaf vegetation samples during the year.
The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in broadleaf vegetation samples no unusual trends were noted.
(4) Crop Samples Gamma analysis detected naturally occurring K-40 activity to be present in the samples collected from the indicator sample locations and in the samples collected from the control sample location. K-40 activity was also detected during pre-operational crop monitoring. K-40 was the only activity detected in the crop samples.
The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in crop samples and no unusual trends were noted.
E. Additional Samples Collected (not required by AP 07B-004)
(1) Bottom Sediment Gamma analysis detected naturally occurring K-40 activity to be present in the samples collected from the indicator sample locations and in the samples collected from the control sample location. K-40 activity was also detected during pre-operational bottom sediment monitoring.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                 Page 7 of 32
 
Cs-137 activity was detected in twelve samples obtained from indicator locations (range 38 to 108 pCi/kg, dry). Cs-137 activity was also detected in one sample obtained from the control sample location (85 pCi/kg, dry).
Cs-137 activity was detected in pre-operational samples. The Cs-137 activity detected in 2013 indicator sample location bottom sediment samples was within the pre-operational range.
(Cs-137 activity detected in 1981 and 1982 was in the range of 79 to 953 pCi/kg. The decay corrected range of pre-operational Cs-1 37 activity detected is approximately 38 to 457 pCi/kg.)
The detected Cs-137 activity in the samples collected from the indicator sample locations was likely due to fallout since the measured activity is within the decay corrected range of pre-operational Cs-137 detected activity and Cs-137 activity has also been detected in samples collected at the control sample location.
Chart 7 plots the Cs-1 37 detected activity from the discharge cove indicator sample location and JRR control sample location bottom sediment samples. The detected Cs-137 activity measured from the discharge cove location reflects a decreasing trend. The Chart 7 trendline indicates Cs-137 activity detected at the JRR control location has also been decreasing. Chart 7 also displays that in recent years, the detected Cs-1 37 activity for the JRR and DC sample locations overlap.
Fe-55 activity was not detected in the fourteen samples obtained from indicator sample locations. No other radionuclides were detected in bottom sediment samples.
Plant-related activation, corrosion, or fission products were not detected during 2013 in bottom sediment samples and no unusual trends were noted.
(2) Aquatic Vegetation Gamma analyses of aquatic vegetation samples obtained from indicator sample locations detected naturally occurring gamma emitters Be-7 and K-40. Be-7 and K-40 activity were also detected during pre-operational monitoring.
No other radionuclides were detected in aquatic vegetation samples. Plant-related activation, corrosion, or fission products were not detected during 2013 in aquatic vegetation samples and no unusual trends were noted.
(3) Shoreline Sediment Naturally occurring K-40 activity was detected in the shoreline sediment samples obtained from the EEA indicator sample location. K-40 activity was also detected during pre-operational monitoring.
Cs-137 activity (89.2 pCi/kg, dry) was detected in a shoreline sediment sample obtained from the EEA indicator sample location. Cs-137 activity was also detected in pre-operational shoreline sediment samples. Cs-137 activity detected in shoreline sediment samples collected from the DC location from 1982 to 1984 was in the range of 224 to 437 pCi/kg, dry. The decay corrected range of pre-operational Cs-1 37 activity detected is approximately 115 to 218 pCi/kg, dry. The detected Cs-137 activity in the shoreline sediment sample was likely due to fallout since the results are lower than the pre-operational decay corrected range. Additionally, Cs-1 37 activity is routinely detected in soil and sediment samples collected from the control locations.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                 Page 8 of 32
 
No other radionuclides were detected in the EEA shoreline sediment samples. Plant-related activation, corrosion, or fission products were not detected during 2013 and no unusual trends were noted.
(4) Terrestrial Vegetation Naturally occurring Be-7 and K-40 activity were detected in terrestrial vegetation indicator location samples. No other radionuclides were detected in terrestrial vegetation. Plant-related activation, corrosion or fission products were not detected during 2013 in terrestrial vegetation samples and no unusual trends were noted.
(5) Soil Naturally occurring K-40 activity was detected in soil samples obtained from the indicator locations. K-40 activity was also detected during pre-operational soil monitoring.
Cs-137 activity (range 148 to 250 pCi/kg) was detected in soil samples obtained from the indicator locations. Data was reviewed for soil samples collected pre-operationally. The detected Cs-137 activity range from February of 1985 was 255 to 2,160 pCi/kg. The decay corrected range of pre-operational Cs-137 activity detected in soil is approximately 134 to 1,137 pCi/kg. The detected Cs-137 activity in soil sampled in 2013 is within the decay corrected pre-operational range and is likely due to fallout.
Plant-related activation, corrosion, or fission products were not detected during 2013 in soil samples and no unusual trends were noted.
(6) Deer Naturally occurring K-40 activity was detected in the deer sample obtained from the indicator location.
Tritium activity (251 pCi/kg) was also detected in the deer sample. The detected tritium activity was attributable to plant operation.
No other radionuclides were detected in the deer sample. No unusual trends were identified.
No other radionuclides were detected in the deer sample. No unusual trends were identified.
Ill. PROGRAM REVISIONS/CHANGES Based upon the 2012 Land Use Census Report, Revision 1, broadleaf vegetation sample location A-3 was added to AP 07B-004 and broadleaf vegetation sample location N-1 was
Ill. PROGRAM REVISIONS/CHANGES Based upon the 2012 Land Use Census Report, Revision 1, broadleaf vegetation sample location A-3 was added to AP 07B-004 and broadleaf vegetation sample location N-1 was changed to an alternate sample location.
AP 07B-004 was revised to update the description of dosimeter location 44 to Wilson Cadman Wildlife Education Area to match the recent name change.
2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station                                                Page 9 of 32
 
IV. PROGRAM DEVIATIONS Air Samples The following air sample locations failed to meet the requirement for "continuous sampler operation." As described in footnote (1) of procedure AP 07B-004, Offsite Dose Calculation Manual (RadiologicalEnvironmental Monitoring Program), Table 5-1, deviations are permitted from the required sampling schedule due to malfunction of sampling equipment and other legitimate reasons. Discrepancies greater than five percent between Total Military Time and Total Digital Flow Meter Time, which resulted in a loss of air sample collected, are listed in the following table.
Location        Sample Period            Percent      Explanation of DeviationlComments Discrepancy/    Condition Report Number Hours Unavailable 32      06/24/13 - 07/01/13          Unknown      Power Outage!
Equipment Malfunction /
Condition Report 00071046 37      08/05/13 - 08/12/13        6.17%/


==SUMMARY==
==SUMMARY==
Name of Facility:
 
Wolf Creek Generating Station Docket No.: 50-482 Location of Facility:
Name of Facility: Wolf Creek Generating Station         Docket No.: 50-482 Location of Facility: Coffey County, Kansas       Reporting Period: Annual 2013 Medium of                             ODCM         All Indicator     Indicator Location with               Control Locations Pathway         Analysis and         Lower         Locations       Highest Annual Mean                                       Number of Sampled         Total Number of       Limit of                       Name                                                       Nonroutine (Unit of         Analysis Performed   Detection     ** Mean (f)     Distance and         ** Mean (f)     ** Mean (f)         Reported Measurement)                           (LLD)         ** Range         Direction             ** Range         ** Range           Measurements **
Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection  
Air Particulate                                                                                               Station 53 (pCi/m 3)       Gross Beta (318)         0.01       0.026 (265/265) 49                    0.027 (53/53)   0.026 (53/53)       0 (0.009 - 0.050) 0.8 miles NNE        (0.013 - 0.050) (0.011 - 0.052)
** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction  
Gamma (24)
** Range ** Range Measurements  
Be-7                            0.076 (20/20)   32                    0.081 (4/4)     0.076 (4/4)         0 (0.052 - 0.092) 3.1 miles WNW        (0.070 - 0.088) (0.063 - 0.087)
**Air Particulate (pCi/m 3)Gross Beta (318)0.01 0.026 (265/265)(0.009 -0.050)49 0.8 miles NNE 32 3.1 miles WNW 0.027 (53/53)(0.013 -0.050)0.081 (4/4)(0.070 -0.088)Station 53 0.026 (53/53)(0.011 -0.052)0.076 (4/4)(0.063 -0.087)0 Gamma (24)Be-7 0.076 (20/20)(0.052 -0.092)0 Air Radioiodine (pCi/mi 3)Direct Radiation Dosimeters (mR per std.90-day Qtr.)Surface Water (pCi/I)Station 53-(0/53)1-131 (318)0.07 -(0/265)N/A N/A 0 Stations 39 & 53 Gamma Dose (172)Gamma (24)Tritium (24)Fe-55 (8)1-131 (32)Gamma (32)Tritium (32)18.7 (164/164)(12.3 -27.6)47 0.16 miles S 24.2 (4/4)(20.4 -27.6)19.5 (8/8)(15.4 -21.5)0-(0/12)N/A N/A 3,000 11,100 (12/12)(9,295-13,170)
Air Radioiodine                                                                                              Station 53 (pCi/mi3 )       1-131 (318)               0.07       -(0/265)         N/A                   N/A             - (0/53)            0 Direct Radiation                                                                                              Stations 39 & 53 Dosimeters (mR per std. Gamma Dose                           18.7 (164/164)   47                    24.2 (4/4)       19.5 (8/8)         0 90-day Qtr.)     (172)                               (12.3 - 27.6)   0.16 miles S         (20.4 - 27.6)   (15.4 - 21.5)
SP 3.2 miles SSE 11,100 (12/12)(9,295-13,170)
Surface Water                                                                                                JRR (pCi/I)          Gamma (24)                          - (0/12)         N/A                   N/A             - (0/12)            0 Tritium (24)            3,000       11,100 (12/12)   SP                    11,100 (12/12)  - (0/12)            0 (9,295-13,170)   3.2 miles SSE         (9,295-13,170)
JRR-(0/12)-(0/12)-(0/4)-(0/4)Ground Water (pCi/I)1 -(0/28)N/A N/A N/A N/A N/A N/A N/A N/A B-12-(0/4)-(0/4)-(0/4)0 0 0 0 0 0-(0/28)2,000 -(0/28)Page B-2** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
Fe-55 (8)                           - (0/4)         N/A                  N/A              - (0/4)             0 Ground Water                                                                                                 B-12 (pCi/I)         1-131 (32)                  1      - (0/28)         N/A                   N/A             - (0/4)             0 Gamma (32)                          - (0/28)         N/A                  N/A              - (0/4)             0 Tritium (32)            2,000      - (0/28)         N/A                  N/A              - (0/4)             0 Page B-2
** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
 
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM  
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM  


==SUMMARY==
==SUMMARY==
Name of Facility:
 
Wolf Creek Generating Station Docket No.: 50-482 Location of Facility:
Name of Facility: Wolf Creek Generating Station         Docket No.: 50-482 Location of Facility: Coffey County, Kansas       Reporting Period: Annual 2013 Medium of                             ODCM         All Indicator     Indicator Location with               Control Locations Pathway         Analysis and         Lower         Locations         Highest Annual Mean                                       Number of Sampled         Total Number of       Limit of                       Name                                                       Nonroutine (Unit of         Analysis Performed   Detection     ** Mean (f)       Distance and         ** Mean (f)     ** Mean (f)       Reported Measurement)                           (LLD)         ** Range         Direction             ** Range         ** Range           Measurements **
Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection  
Drinking                                                                                                     BW-1 5 Water           1-131 (24)                 1       -(0/12)           N/A                  N/A              -  (0/12)           0 (pCi/I)
** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction  
Gross Beta (24)            4       2.9 (12/12)       1O-DW                 2.9 (12/12)     3.1 (12/12)         0 (2.0 - 4.0)       26.1 miles SSE        (2.0-4.0)       (2.2-4.0)
** Range ** Range Measurements  
Gamma (24)                          - (0/12)          N/A                   N/A             - (0/12)           0 Tritium (8)              2,000      -(0/4)           N/A                  N/A              -  (0/4)           0 Shoreline        Gamma (6)                                                                                   JRR Sediment (pCi/kg dry)         K-40                  -        9,209 (4/4)      EEA                  11,557 (2/2)    11,994 (2/2)       0 (6,368 - 11,893) 3.0 miles NNW         (11,221-11,893)  (10,926- 13,061)
**Drinking Water (pCi/I)1-131 (24)Gross Beta (24)Gamma (24)1 -(0/12)4 2.9 (12/12)(2.0 -4.0)-(0/12)2,000 -(0/4)-9,209 (4/4)(6,368 -11,893)N/A 1O-DW 26.1 miles SSE N/A BW-1 5-(0/12)3.1 (12/12)(2.2-4.0)2.9 (12/12)(2.0-4.0)N/A N/A N/A N/A-(0/12)-(0/4)Tritium (8)Gamma (6)0 0 0 0 0 0 Shoreline Sediment (pCi/kg dry)JRR 11,994 (2/2)(10,926- 13,061)K-40 EEA 3.0 miles NNW EEA 3.0 miles NNW 11,557 (2/2)(11,221-11,893)
Cs-1 37               180       89(1/4)           EEA                  89 (1/2)         - (0/2)             0 3.0 miles NNW Fish             Gamma (16)                                                                                   JRR (pCi/kg wet)
Cs-1 37 180 89(1/4)89 (1/2)-(0/2)Fish (pCi/kg wet)Gamma (16)JRR 3,416 (6/6)(2,990 -3,669)K-40-3,129 (10/10)(2,698 -3,690)-7,743 (10/10)(6,985 -8,852)CCL 0.6 miles E to NNW CCL 0.6 miles E to NNW 3,129 (10/10)(2,698 -3,690)7,743 (10/10)(6,985 -8,852)0 Tritium (16)-(0/6)0 Page B-3** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
K-40                   -       3,129 (10/10)     CCL                  3,129 (10/10)   3,416 (6/6)        0 (2,698 - 3,690)   0.6 miles E to       (2,698 - 3,690) (2,990 - 3,669)
NNW Tritium (16)              -        7,743 (10/10)     CCL                  7,743 (10/10)     - (0/6)            0 (6,985 - 8,852)   0.6 miles E to      (6,985 - 8,852)
NNW Page B-3
** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
 
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM  
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM  


==SUMMARY==
==SUMMARY==
Name of Facility:
 
Wolf Creek Generating Station Docket No.: 50-482 Location of Facility:
Name of Facility: Wolf Creek Generating Station         Docket No.: 50-482 Location of Facility: Coffey County, Kansas       Reporting Period: Annual 2013 Medium of                             ODCM         All Indicator     Indicator Location with               Control Locations Pathway         Analysis and         Lower         Locations         Highest Annual Mean                                       Number of Sampled         Total Number of       Limit of                       Name                                                       Nonroutine (Unit of         Analysis Performed   Detection     ** Mean (f)       Distance and         ** Mean (f)     ** Mean (f)         Reported Measurement)                           (LLD)         ** Range         Direction             ** Range         ** Range           Measurements **
Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection  
Food and         Gamma (18)                                                                                  D-2 Garden (pCi/kg wet)       Be-7                             657 (11/12)       Q-6                  1,031 (2/2)     756 (5/6)           0 (281 - 1,691)     2.4 miles NW         (372- 1,691)     (397 - 1,259)
** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction  
K-40                    -        5,346 (12/12)     H-2                  5,640 (4/4)     5,871 (6/6)         0 (4,689 - 6,915)   3.0 miles SSE        (5,157 - 6,915) (4,719 - 6,804)
** Range ** Range Measurements  
NR-U1 Crops           Gamma (4)
**Food and Garden (pCi/kg wet)Gamma (18)Be-7 K-40 657 (11/12)(281 -1,691)-5,346 (12/12)(4,689 -6,915)Q-6 2.4 miles NW H-2 3.0 miles SSE 1,031 (2/2)(372- 1,691)5,640 (4/4)(5,157 -6,915)D-2 756 (5/6)(397 -1,259)5,871 (6/6)(4,719 -6,804)0 0 NR-U1 Crops (pCi/kg wet)Bottom Sediment (pCi/kg dry)Gamma (4)K-40-14,612 (2/2)(12,882-16,342)
(pCi/kg wet)
NR-D1 8.9 miles S 16,342 (1/1)Gamma (19)7,606 (2/2)(2,544 -12,669)JRR 12,206 (2/2)(11,660 -12,752)0 K-40 10,118 (17/17)(5,110- 12,602)EEA 3.0 miles NNW 11,461 (2/2)(11,346-11,576) 0 Cs-137 72(12/17)
K-40                   -       14,612 (2/2)     NR-D1                 16,342 (1/1)     7,606 (2/2)         0 (12,882-16,342)  8.9 miles S                            (2,544 - 12,669)
DC 93(2/2) 85(1/2) 0 (38- 108) 0.9 miles WNW (90-97)Fe-55 (14) -(0/14) N/A N/A 0 Page B-4** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
Bottom          Gamma (19)                                                                                  JRR Sediment (pCi/kg dry)
K-40                             10,118 (17/17)   EEA                  11,461 (2/2)    12,206 (2/2)        0 (5,110- 12,602)   3.0 miles NNW         (11,346-11,576) (11,660 - 12,752)
Cs-137                           72(12/17)         DC                   93(2/2)         85(1/2)             0 (38- 108)         0.9 miles WNW         (90-97)
Fe-55 (14)                         -(0/14)           N/A                   N/A                                 0 Page B-4
** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
 
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM  
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM  


==SUMMARY==
==SUMMARY==
Name of Facility:
 
Wolf Creek Generatinq Station Docket No.: 50-482 Location of Facility:
Name of Facility: Wolf Creek Generatinq Station        Docket No.: 50-482 Location of Facility: Coffey County, Kansas      Reporting Period: Annual 2013 Medium of                              ODCM          All Indicator    Indicator Location with                Control Locations Pathway          Analysis and          Lower          Locations        Highest Annual Mean                                        Number of Sampled          Total Number of      Limit of                        Name                                                      Nonroutine (Unit of        Analysis Performed    Detection      ** Mean (f)      Distance and          ** Mean (f)      ** Mean (f)        Reported Measurement)                          (LLD)          ** Range        Direction            ** Range        ** Range            Measurements **
Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection
Aquatic          Gamma (3)                                                                                    No Control Vegetation (pCi/kg wet)          Be-7                            1,086 (2/3)      DC-ALT                1,873(1/1)                          0 (299 - 1,873)    1.5 miles NW K-40                            3,047 (3/3)      EEA                  4,998 (1/1)                          0 (1,861 - 4,998)  3.0 miles NNW Terrestrial      Gamma (2)                                                                                    No Control Vegetation (pCi/kg wet)          Be-7                            1,424 (2/2)      MUDS                  1,830(1/1)                          0 (1,018 - 1,830)  1.5 miles WNW K-40                          6,667 (2/2)      EEA                  7,467 (1/1)                          0 (5,868 - 7,467
** Mean (f) Distance and ** Mean (f


==SUMMARY==
==SUMMARY==
The 2013 Land Use Census Report has been revised to incorporate the re-calculated D/Qs for the broadleaf vegetation locations using the data from Engineering Evaluation SA-1 3-002.The annual Land Use Census of rural residents within five miles of the Wolf Creek Generating Station (WCGS) has been completed in 2013 in accordance with AP 07B-004, [Offsite Dose Calculation Manual (Radiological Environmental Monitoring Program)].
 
No program changes are necessary regarding milk locations.
The 2013 Land Use Census Report has been revised to incorporate the re-calculated D/Qs for the broadleaf vegetation locations using the data from Engineering Evaluation SA-1 3-002.
Again, no milk sampling locations were identified.
The annual Land Use Census of rural residents within five miles of the Wolf Creek Generating Station (WCGS) has been completed in 2013 in accordance with AP 07B-004, [Offsite Dose Calculation Manual (Radiological Environmental Monitoring Program)].
The two broadleaf vegetation locations with the highest calculated annual average D/Q rankings are A2.60-17TE1527 and Q2.35-MILA1619.
No program changes are necessary regarding milk locations. Again, no milk sampling locations were identified.
AP 07B-004 specifies, "Alternate sampling locations may be used to provide continued monitoring".
The two broadleaf vegetation locations with the highest calculated annual average D/Q rankings are A2.60-17TE1527 and Q2.35-MILA1619.               AP 07B-004 specifies, "Alternate sampling locations may be used to provide continued monitoring". The third-ranked garden is N2.38-RODR9. Since these gardens are currently listed as sample locations for the Radiological Environmental Monitoring Program in procedure AP 07B-004 (locations A-3, Q-6 and N-I), no program changes are necessary regarding broadleaf vegetation locations.
The third-ranked garden is N2.38-RODR9. Since these gardens are currently listed as sample locations for the Radiological Environmental Monitoring Program in procedure AP 07B-004 (locations A-3, Q-6 and N-I), no program changes are necessary regarding broadleaf vegetation locations.
BACKGROUND Section 5.2, Attachment A, of procedure AP 07B-004, directs that "a Land Use Census shall be conducted annually during the growing season to identify the nearest (1) milk animal, (2) residence, and (3) garden of greater than 500 square feet producing broadleaf vegetation in each of the 16 meteorological sections within five miles of the WCGS site."
BACKGROUND Section 5.2, Attachment A, of procedure AP 07B-004, directs that "a Land Use Census shall be conducted annually during the growing season to identify the nearest (1) milk animal, (2)residence, and (3) garden of greater than 500 square feet producing broadleaf vegetation in each of the 16 meteorological sections within five miles of the WCGS site." Table 5-1, Attachment A, of procedure AP 07B-004, requires that broadleaf vegetation samples be collected from "two indicator locations (using the criteria from the "Land Use Census" section) with highest calculated annual average D/Q." Table 5-1, Attachment A, of procedure AP 07B-004, also requires that milk samples be collected from "three indicator locations within 5 miles of the site having the highest dose potential." METHODOLOGY Over two hundred surveys were mailed to the rural residents living within five miles of WCGS.A follow-up survey was sent to residents who did not respond. The survey excluded the residents of New Strawn and Burlington.
Table 5-1, Attachment A, of procedure AP 07B-004, requires that broadleaf vegetation samples be collected from "two indicator locations (using the criteria from the "Land Use Census" section) with highest calculated annual average D/Q."
These locations were excluded due to the large number of households and the low likelihood that information gained from these residences would affect the locations chosen for REMP sampling.
Table 5-1, Attachment A, of procedure AP 07B-004, also requires that milk samples be collected from "three indicator locations within 5 miles of the site having the highest dose potential."
Drive-by information was collected for the nearest residences in each sector that did not return surveys.The information collected was compiled and the results are identified in Tables 1-3.Calculations were performed so that garden locations could be ranked by their respective D/Q.These results are contained in Table 4.2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -2 RESULTS NOTE: A Global Positioning System was used to verify residence distances and sectors.Two changes were noted for the nearest occupied residences in each sector. These changes occurred in sectors A and E.Seven changes were noted for the nearest garden producing broadleaf vegetation.
METHODOLOGY Over two hundred surveys were mailed to the rural residents living within five miles of WCGS.
These changes are identified in Table 3.There were no changes regarding milk sample locations.
A follow-up survey was sent to residents who did not respond. The survey excluded the residents of New Strawn and Burlington. These locations were excluded due to the large number of households and the low likelihood that information gained from these residences would affect the locations chosen for REMP sampling. Drive-by information was collected for the nearest residences in each sector that did not return surveys.
Again, no locations were identified that routinely milked animals for human consumption.
The information collected was compiled and the results are identified in Tables 1-3.
It should be noted that since the last Land Use Census some of the address numbers were changed by the County. Addresses that were affected are identified by an asterisk on Table 2 and Table 3.2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -3 TABLE I 2013 Land Use Census Data Location of Nearest: Sector A B C D E F G H J K L M N P Q R Residence A2.47-17RD1474 B3.53-QURD1755 Cl .92-16RD1703 D2.03-QULA1571 E1.77-QULA1485 F1.84-QULA1419 G3.03-13RD1820 H3.09-12RD1711 J3.70-11 RD1540 K2.70-12LA1439 L2.10-NARD 1339 M2.34-14RD1 346 N2.08-15RD1350 P2.76-HW751534 Q2.35-MILA1619 R2.08-NALN 1650 Milkingq Animals None None None None None None None None None None None None None None None None Broadleaf Garden A2.60-17TEl 527 None C3.58-RERD1675 D3.00-16RD1829 None F2.44-RERD1391 G3.77-12RD1831 H3.89-1 1 RD1 655 J3.70-1 1RD1540 K4.10-NARD1120 L2.39-NARD1309 M3.78-LYRD1 390 N2.38-RODR9 P2.93-BRST250 Q2.35-MILA1619 None Identifiers are based upon the following protocol: EXAMPLE: A2.47-17RD1474"A" = Sector A"2.47" = 2.47 miles from the reactor"17RD1474" = address 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -4 TABLE 2 SECTOR 2012 NEAREST 2013 NEAREST RESIDENCE RESIDENCE A A2.60-17TE1520 A2.47-17RD1474 B B3.53-QURD1755 B3.53-QURD1755 C Cl.92-16RD1655 Cl.92-16RD1703*
Calculations were performed so that garden locations could be ranked by their respective D/Q.
D D2.03-QULA1571 D2.03-QULA1571 E EI.78-QULA1451 E1.77-QULA1485 F F1.84-QULA1419 F1.84-QULA1419 G G3.03-13RD1820 G3.03-13RD1820 H H3.09-12RD1711 H3.09-12RD1711 J J3.70-11RD1540 J3.70-11RD1540 K K2.70-12LA1439 K2.70-12LA1439 L L2.1 0-NARD1 339 L2.1 0-NARD1 339 M M2.34-14RD1330 M2.34-14RD1346*
These results are contained in Table 4.
N N2.08-15RD1350 N2.08-15RD1350 P P2.76-HW751534 P2.76-HW751534 Q Q2.35-MILA1619 Q2.35-MILA1619 R R2.08-NALN1650 R2.08-NALN1650 NOTE: Entries underlined indicate changes from the 2012 Land Use Census.2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -5 TABLE 3 2013 Land Use Census Milk and Garden Data SECTOR 2012 2013 2012 NEAREST 2013 NEAREST MILKING MILKING GARDEN GARDEN ANIMALS ANIMALS PRODUCING PRODUCING BROADLEAF BROADLEAF VEGETATION VEGETATION A None None A2.60-17TE1520 A2.60-17TE1527*
2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 2
B None None None None C None None C3.38-17RD1755 C3.58-RERD1675 D None None D2.33-RERD1520 D3.00-16RD1829 E None None None None F None None F2.44-RERD1391 F2.44-RERD1391 G None None None G3.77-12RD1831 H None None H4.87-10RD1670 H3.89-11RD1655 J None None J3.84-11RD1499 J3.70-11RD1540 K None None K4.10-NARD1120 K4.10-NARD1120 L None None L2.39-NARD1309 L2.39-NARD1309 M None None M4.42-LYRD1231 M3.78-LYRD1390 N None None N2.38-RODR9 N2.38-RODR9 P None None P3.17-WDST425 P2.93-BRST250 Q None None Q2.35-MILA1619 Q2.35-MILA1619 R None None None None NOTE: Underlined entries indicate changes from the 2012 Land Use Census.2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -6 TABLE 4 Information Used for DIQ Calculations FROM LAND USE FROM SA-13-002 DIST CALC NEAR NEAR FAR FAR SECTOR SECTOR (MI) (METERS) DIST D/Q DIST D/Q CALC RANKING A 2.60 4184 4000 1.86E-09 5000 1.26E-09 1.75E-09 1 B C 3.58 5761 5000 2.51E-10 6000 1.85E-10 2.01E-10 13 D 3.00 4828 4000 2.93E-10 5000 1.99E-10 2.15E-10 12 E F 2.44 3927 3000 6.15E-10 4000 3.69E-10 3.87E-10 8 G 3.77 6067 6000 3.57E-10 7000 2.65E-10 3.51E-10 10 H 3.89 6260 6000 5.16E-10 7000 3.83E-10 4.81E-10 6 J 3.70 5955 5000 6.06E-10 6000 4.46E-10 4.53E-10 7 K 4.10 6598 6000 4.46E-10 7000. 3.31E-10 3.77E-10 9 L 2.39 3846 3000 1.1OE-09 4000 6.62E-10 7.29E-10 4 M 3.78 6083 6000 2.67E-10 7000 1.99E-10 2.61E-10 11 N 2.38 3830 3000 1.17E-09 4000 7.OOE-10 7.80E-10 3 P 2.93 4715 4000 7.64E-10 5000 5.19E-10 5.89E-10 5 Q 2.35 3782 3000 1.46E-09 4000 8.79E-10 1.01E-09 2 R Originated by: Verified by: Je?~~b Date: 12-31-13 Date: 1/7/14 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -7}}
 
RESULTS NOTE: A Global Positioning System was used to verify residence distances and sectors.
Two changes were noted for the nearest occupied residences in each sector. These changes occurred in sectors A and E.
Seven changes were noted for the nearest garden producing broadleaf vegetation.       These changes are identified in Table 3.
There were no changes regarding milk sample locations. Again, no locations were identified that routinely milked animals for human consumption.
It should be noted that since the last Land Use Census some of the address numbers were changed by the County. Addresses that were affected are identified by an asterisk on Table 2 and Table 3.
2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 3
 
TABLE I 2013 Land Use Census Data Location of Nearest:
Sector         Residence                  Milkingq Animals Broadleaf Garden A        A2.47-17RD1474                       None      A2.60-17TEl 527 B        B3.53-QURD1755                         None            None C        Cl .92-16RD1703                       None      C3.58-RERD1675 D        D2.03-QULA1571                       None      D3.00-16RD1829 E        E1.77-QULA1485                       None            None F        F1.84-QULA1419                       None      F2.44-RERD1391 G        G3.03-13RD1820                       None      G3.77-12RD1831 H        H3.09-12RD1711                       None      H3.89-1 1RD1 655 J        J3.70-11 RD1540                       None      J3.70-1 1RD1540 K        K2.70-12LA1439                       None      K4.10-NARD1120 L        L2.10-NARD 1339                       None      L2.39-NARD1309 M        M2.34-14RD1 346                       None      M3.78-LYRD1 390 N        N2.08-15RD1350                       None        N2.38-RODR9 P        P2.76-HW751534                       None      P2.93-BRST250 Q        Q2.35-MILA1619                       None      Q2.35-MILA1619 R        R2.08-NALN 1650                       None           None Identifiers are based upon the following protocol:
EXAMPLE: A2.47-17RD1474 "A" = Sector A "2.47" = 2.47 miles from the reactor "17RD1474" = address 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -4
 
TABLE 2 SECTOR                2012 NEAREST            2013 NEAREST RESIDENCE              RESIDENCE A                A2.60-17TE1520        A2.47-17RD1474 B              B3.53-QURD1755          B3.53-QURD1755 C              Cl.92-16RD1655        Cl.92-16RD1703*
D              D2.03-QULA1571          D2.03-QULA1571 E              EI.78-QULA1451          E1.77-QULA1485 F              F1.84-QULA1419          F1.84-QULA1419 G              G3.03-13RD1820          G3.03-13RD1820 H                H3.09-12RD1711        H3.09-12RD1711 J                J3.70-11RD1540        J3.70-11RD1540 K                K2.70-12LA1439        K2.70-12LA1439 L              L2.1 0-NARD1 339        L2.1 0-NARD1 339 M              M2.34-14RD1330        M2.34-14RD1346*
N                N2.08-15RD1350        N2.08-15RD1350 P              P2.76-HW751534          P2.76-HW751534 Q                Q2.35-MILA1619        Q2.35-MILA1619 R              R2.08-NALN1650          R2.08-NALN1650 NOTE: Entries underlined indicate changes from the 2012 Land Use Census.
2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 5
 
TABLE 3 2013 Land Use Census Milk and Garden Data SECTOR        2012          2013      2012 NEAREST        2013 NEAREST MILKING      MILKING          GARDEN              GARDEN ANIMALS      ANIMALS        PRODUCING          PRODUCING BROADLEAF          BROADLEAF VEGETATION          VEGETATION A          None          None      A2.60-17TE1520    A2.60-17TE1527*
B          None          None            None                None C          None          None      C3.38-17RD1755    C3.58-RERD1675 D          None          None      D2.33-RERD1520      D3.00-16RD1829 E          None          None            None                None F          None          None      F2.44-RERD1391      F2.44-RERD1391 G          None          None            None        G3.77-12RD1831 H          None          None      H4.87-10RD1670    H3.89-11RD1655 J          None         None       J3.84-11RD1499      J3.70-11RD1540 K          None         None     K4.10-NARD1120      K4.10-NARD1120 L          None         None       L2.39-NARD1309    L2.39-NARD1309 M          None         None     M4.42-LYRD1231      M3.78-LYRD1390 N          None         None       N2.38-RODR9        N2.38-RODR9 P          None         None       P3.17-WDST425      P2.93-BRST250 Q          None         None       Q2.35-MILA1619    Q2.35-MILA1619 R          None         None             None               None NOTE: Underlined entries indicate changes from the 2012 Land Use Census.
2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 6
 
TABLE 4 Information Used for DIQ Calculations FROM LAND USE                  FROM SA-13-002 DIST    CALC      NEAR    NEAR      FAR      FAR              SECTOR SECTOR      (MI) (METERS)      DIST    D/Q      DIST    D/Q      CALC    RANKING A        2.60    4184      4000  1.86E-09    5000  1.26E-09 1.75E-09        1 B
C        3.58    5761      5000  2.51E-10    6000  1.85E-10 2.01E-10        13 D        3.00    4828      4000  2.93E-10    5000  1.99E-10 2.15E-10        12 E
F        2.44    3927      3000  6.15E-10  4000    3.69E-10 3.87E-10         8 G        3.77    6067      6000   3.57E-10   7000  2.65E-10 3.51E-10       10 H        3.89    6260      6000  5.16E-10   7000  3.83E-10 4.81E-10         6 J        3.70    5955      5000  6.06E-10   6000   4.46E-10 4.53E-10         7 K        4.10   6598      6000   4.46E-10   7000. 3.31E-10 3.77E-10         9 L        2.39    3846       3000   1.1OE-09   4000   6.62E-10 7.29E-10         4 M       3.78   6083       6000   2.67E-10   7000   1.99E-10 2.61E-10       11 N       2.38   3830       3000   1.17E-09   4000   7.OOE-10 7.80E-10         3 P       2.93   4715       4000   7.64E-10   5000   5.19E-10 5.89E-10         5 Q       2.35   3782       3000   1.46E-09   4000   8.79E-10 1.01E-09         2 R
Originated by:               Je?~~b                     Date:     12-31-13 Verified by:                                          Date:
1/7/14 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 7}}

Revision as of 05:18, 4 November 2019

Submittal of 2013 Annual Radiological Environmental Operating Report
ML14119A105
Person / Time
Site: Wolf Creek Wolf Creek Nuclear Operating Corporation icon.png
Issue date: 04/23/2014
From: Westman M
Wolf Creek
To:
Document Control Desk, Office of Nuclear Reactor Regulation
References
RA 14-0048
Download: ML14119A105 (171)
v • d • e


Text

W9LF CREEK NUCLEAR OPERATING CORPORATION Michael J. Westman Manager Regulatory Affairs April 23, 2014 RA 14-0048 U. S. Nuclear Regulatory Commission ATTN: Document Control Desk Washington, DC 20555

Subject:

Docket No. 50-482: 2013 Annual Radiological Environmental Operating Report Gentlemen:

The purpose of this letter is to submit the enclosed Annual Radiological Environmental Operating Report, which is being submitted pursuant to Wolf Creek Generating Station (WCGS) Technical Specification 5.6.2. This report covers radiological environmental monitoring around WCGS for the period of January 1, 2013, through December 31, 2013.

This letter contains no commitments. If you have any questions concerning this matter, please contact me at (620) 364-4009, or Mr. William Muilenburg, at (620) 364-4186.

Sincerely, Michael J. Westman MJW/rlt

Enclosure:

2013 Annual Radiological Environmental Operating Report cc: M. L. Dapas (NRC), w/e C. F. Lyon (NRC), w/e N. F. O'Keefe (NRC), w/e Senior Resident Inspector (NRC), w/e P.O. Box 411 / Burlington, KS 66839 / Phone: (620) 364-8831 An Equal Opportunity Employer MIFIHCNET 44-

/

Enclosure to RA 14-0048 Wolf Creek Nuclear Operating Corporation Wolf Creek Generating Station 2013 Annual Radiological Environmental Operating Report (169 pages)

WOLF CREEK NUCLEAR OPERATING CORPORATION WOLF CREEK GENERATING STATION 2013 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT

'F April 15, 2014

TABLE OF CONTENTS List of Tables ii List of Figures ii List of Charts ii Executive Summary 1 Introduction 1 I. Program Description 1 I1. Discussion of Results 4 Ill. Program Revisions/Changes 9 IV. Program Deviations 10 V. Interlaboratory Comparison Program 10 VI. Comparison to the Radioactive Effluent Release Program 11 Tables 12 Figures 21 Charts 26 Appendix A - Interlaboratory Comparison Program Results A-1 Appendix B - Summary Tables B-1 Appendix C - Individual Sample Results C-1 Air Particulate and Charcoal Filters C-1 Quarterly Air Particulate - Gamma C-13 Surface Water C-25 Ground Water C-33 Drinking Water C-49 Quarterly Drinking Water - Tritium C-57 Shoreline Sediment C-59 Fish C-62 Food/Garden C-67 Feed and Forage C-74 Bottom Sediment C-77 Aquatic Vegetation C-93 Terrestrial Vegetation C-96 Soil C-98 Deer C-100 Appendix D - Land Use Census Report D-1

LIST OF TABLES 1 Radiological Environmental Monitoring Program Description 12 2 Sample Location Identifiers, Distances (Miles) and Directions (Sectors) 17 3 OSL Dosimeter Results 20 LIST OF FIGURES 1 Airborne Pathway Sampling Locations 21 2 Direct Radiation Pathway Sampling Locations 22 3 Waterborne Pathway Sampling Locations 23 4 Ingestion Pathway Sampling Locations 24 5 Distant Sampling Locations 25 LIST OF CHARTS 1 Airborne Gross Beta Weekly Results 26 2 Historical Airborne Smoothed Indicator and Control Gross Beta 27 3 OSL Dosimeters - Indicator and Control Locations 28 4 Historical TLD Nearsite Locations and Control Locations 29 5 Coffey County Lake Surface Water Tritium Data 30 6 Drinking Water Gross Beta (5 years) 31 7 Detected Cs-1 37 Activity in Bottom Sediment 32 ii

EXECUTIVE

SUMMARY

Plant-related activation, corrosion, or fission products were not detected during 2013 in airborne particulate and radioiodine, filters, drinking water, ground water, broadleaf vegetation, shoreline sediment, crops, aquatic vegetation, terrestrial vegetation, bottom sediment, or soil samples.

Activation, corrosion or fission products attributable to plant operation were detected during 2013 in surface water, fish, and deer samples.

Nuclides detected in Radiological Environmental Monitoring Program (REMP) samples were below applicable Nuclear Regulatory Commission (NRC) reporting levels.

Based upon the radiological environmental monitoring program results, it was concluded station operations had no significant radiological impact on the health and safety of the public or the environment.

INTRODUCTION The 2013 Annual Radiological Environmental Operating Report for Wolf Creek Generating Station (WCGS) covers the period from January 1 through December 31, 2013. WCGS is located in Coffey County, Kansas, approximately five miles northeast of Burlington, Kansas.

Fuel loading commenced at WCGS on March 12, 1985. The operational phase of the REMP began with initial criticality on May 22, 1985, and the first detectable quantities of radioactivity were reported in plant effluents in June 1985.

This report contains a description of the REMP conducted by Wolf Creek Nuclear Operating Corporation (WCNOC), a discussion of monitoring program results, the revisions or changes to the program, program deviations, the Interlaboratory Comparison Program and a comparison to the Radioactive Effluent Release Program. The Interlaboratory Comparison Program results, a summary of results in the NRC Branch Technical Position specified format, the individual sample results, and the Land Use Census Report are included as appendices.

I. PROGRAM DESCRIPTION Radiological environmental monitoring samples were collected according to the schedule in WCGS procedure AP 07B-004, Offsite Dose Calculation Manual (Radiological Environmental Monitoring Program). Radiological environmental monitoring program samples were collected by the WCGS Environmental Management group and were analyzed by Environmental, Inc.

Landauer, Inc. processed the environmental optically stimulated luminescence (OSL) dosimeters. Table 1 identifies the exposure pathway/sample type, number of samples and sample locations, sample collection frequency, and type and frequency of analysis. Table 2 lists the sample location identifiers, distances and directions from the plant. Samples in addition to those required by AP 07B-004 were also obtained and analyzed.

The following is a description of the sampling and analysis program by individual pathways.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 1 of 32

A. Airborne Pathway Low volume air sampling pumps with digital flow meters continuously collected air particulate and radioiodine samples on 47 mm glass fiber filters and charcoal canisters, respectively. The air particulate filters and charcoal canisters were changed out weekly. Gross beta analysis was performed on the air particulate filters. Air particulate filters were also analyzed quarterly for gamma emitting isotopes. Charcoal canisters were analyzed for 1-131.

Air samples were collected from six locations. The five indicator locations sampled included 2, 18, 32, 37 and 49. A control location near the intersection of 20th Road and Yearling Road (location 53) was also sampled. Indicator sample locations are shown in Figure 1 and the control sample location is shown in Figure 5.

B: Direct Radiation Pathway Optically stimulated luminescence (OSL) dosimeters were used continuously at 43 locations during the sample year to measure direct radiation. The OSLs were typically positioned roughly 3 to 4 feet above the ground in plastic thermostat boxes. Three OSLs were placed at each designated location. The OSLs were changed out quarterly and analyzed for gamma dose.

Transit dose was measured and subtracted from the ambient dose. Indicator OSL sample locations are illustrated in Figure 2 and control sample locations are shown in Figure 5. Control sample locations were 39 (Beto Junction) and 53 (near the intersection of 2 0 th Road and Yearling Road).

C. Waterborne Pathway Water samples were analyzed to determine if gamma emitters were present. In addition to gamma isotopic analysis, radiochemical analysis for 1-131 was performed on drinking water and ground water samples. Gross beta analysis was also performed on drinking water samples.

Tritium analysis was performed monthly by liquid scintillation for surface water and quarterly for drinking water. Tritium analysis was also performed on ground water samples. Four surface water samples from the Coffey County Lake Spillway (SP) location and four surface water samples from the John Redmond Reservoir (JRR) location were also analyzed for Fe-55. The waterborne pathway sample locations are shown in Figures 3 and 5.

Monthly grab samples of surface water were collected from the JRR control location and from the SP indicator location. The SP indicator sample location is located near the spillway of Coffey County Lake, formerly known as Wolf Creek Lake.

Quarterly grab samples of ground water were collected from seven wells. Six locations (C-10, C-49, F-1, G-2, J-1 and J-2) located hydrologically down gradient from the site were used as indicator sample locations. Location B-12 located hydrologically up gradient from the site was used as a control sample location.

Drinking water was sampled at the water treatment facilities in the towns of Iola (indicator sample location IO-DW) and Burlington (control sample location BW-15). The Iola facility is located downstream of the site and the Burlington facility is located upstream of the confluence of the Coffey County Lake discharge and the Neosho River. Composite samples were obtained monthly from automatic samplers at each location. The drinking water automatic samplers collected approximately 27 milliliters of water every two hours.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 2 of 32

Shoreline sediments were sampled semiannually. Gamma isotopic analyses were performed on the shoreline sediment samples. Shoreline sediment sample locations were the Coffey County Lake discharge cove (DC) indicator location and the JRR control location.

D. Ingestion Pathway Milk was not collected during the sample year. The Land Use Census did not identify any locations producing milk for human consumption within five miles of the plant.

Fish were sampled semiannually from the Coffey County Lake (indicator sample location) and from the tail waters of JRR (control sample location). These sample locations are identified in Figure 4. Gamma isotopic analyses were performed on the boneless edible portions of the fish.

Several species of game fish and rough fish were sampled. Fish were also analyzed for tritium.

Broadleaf vegetation samples were collected monthly when available during the growing season. Three indicator (B-1, H-2 and Q-6) gardens (Figure 4) and one control (D-2) garden (Figure 5) were sampled. Gamma isotopic analyses were performed on these samples.

Crop samples were obtained from two indicator sample locations (NR-D1 and NR-D2) downstream of the confluence of Wolf Creek and the Neosho River. Crops were also sampled from control location NR-U1. Gamma isotopic analysis was performed on each sample. Crop sample locations are identified on Figure 5.

E. Additional Samples Collected (not required by AP 07B-004)

Quarterly, duplicate ground water grab samples were obtained from indicator location C-49 and were labeled L-49. These duplicate samples served as laboratory quality checks. The ground water samples were analyzed for gamma emitters, 1-131, and tritium.

Bottom sediment samples were collected from indicator sample locations at the Coffey County Lake discharge cove (DC), Environmental Education Area (EEA), Make-Up Discharge Structure (MUDS), Ultimate Heat Sink (UHS), Essential Service Water (ESW) channel, and the control sample location (JRR). Gamma isotopic analyses were performed on the bottom sediment samples. Samples obtained from DC, ESW and UHS were also analyzed for Fe-55. Some of the bottom sediment samples were collected as part of a cooperative sampling effort with the Kansas Department of Health and Environment (KDHE). The sample locations are identified on Figure 3.

Shoreline sediment samples were collected from indicator sample location EEA. Gamma isotopic analyses were performed on the samples. These samples were collected as part of a cooperative sampling effort with the KDHE. This sample location is identified on Figure 3.

Aquatic vegetation was collected from indicator sample locations DC ALT, EEA and MUDS.

Gamma isotopic analyses were performed on the aquatic vegetation samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 3.

Terrestrial vegetation (grass) was sampled from the EEA and MUDS indicator sample locations.

Gamma isotopic analyses were performed on the grass samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 4.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 3 of 32

Soil was sampled from the EEA and MUDS indicator sample locations. Gamma isotopic analyses were performed on the soil samples. These samples were collected as part of a cooperative sampling effort with the KDHE. The sample locations are identified on Figure 4.

A deer was sampled from indicator sample location R2.7. Gamma isotopic analysis and tritium analysis was performed on the deer sample. This sample was collected as part of a cooperative sampling effort with the KDHE. The sample location is identified on Figure 4.

II. DISCUSSION OF RESULTS Analysis results for pathways are summarized in Appendix B using the format described in Radiological Assessment Branch Technical Position, Revision 1, November 1979 (NRC Generic Letter 79-065). Results for individual samples are listed in Appendix C.

A. Airborne Pathway Chart 1 graphically illustrates weekly gross beta results for the sample year for all of the airborne sample locations. Chart 2 represents the gross beta historical airborne smoothed averages of indicator sample locations and control sample locations. Charts 1 and 2 demonstrate how closely the indicator and control sample locations tracked together. Chart 2 reveals a seasonal cyclic trend; the gross beta values peak in the winter months (December or January) and decrease to a low point in the spring months (May or June). This trend is expected and is attributed to seasonal meteorological changes, i.e., changes in prevailing winds and precipitation.

The gross beta results of 2013 were compared to pre-operational monitoring results of 1983 and 1984. The weekly gross beta analyses range for 1983 and 1984 was 0.0064 to 0.084 pCi/m 3 .

The 2013 weekly gross beta analyses range for indicator locations was 0.009 to 0.050 pCi/mi3 .

The 2013 weekly gross beta analyses range was lower than the 1983 and 1984 pre-operational range. Additionally, the annual mean for indicator locations for 2013 (0.026 pCi/m 3) was lower than the annual mean for 1983 (0.032 pCi/m 3).

The gross beta results for the indicator locations were also compared to the control location.

The annual mean for indicator locations for 2013 (0.026 pCi/m 3 ) was the same as the annual mean of the control location (0.026 pCi/m 3). The indicator location with the highest gross beta annual mean was location 49 (0.027 pCi/m 3) and was slightly higher than the annual mean of the control location (0.026 pCi/m 3).

Naturally occurring Be-7 activity was detected, as was the case during pre-operational monitoring. In 1984, the range for Be-7 detected activity was 0.024 to 0.211 pCi/m 3 for indicator locations and the annual mean for indicator locations was 0.069 pCi/m 3 . In 2013, the range for Be-7 detected activity was 0.052 to 0.092 pCi/m 3 for indicator locations and the annual mean for indicator locations was 0.076 pCi/m 3 . The annual mean of the indicator locations (0.076 pCi/m 3) was the same as the annual mean of the control location (0.076 pCi/m 3).

1-131 activity was not detected in the weekly analysis of charcoal filters at any location.

The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in airborne particulate and radioiodine filters and no unusual trends were noted.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 4 of 32

B. Direct Radiation Pathway Quarterly OSL dosimeter results for each location are shown in Table 3. Measured values have been converted to a standardized 90-day quarter.

The annual mean of indicator sample locations in 2013 was 18.7 mR per standardized 90-day quarter. The annual mean of the control sample locations in 2013 was 19.5 mR per standardized 90-day quarter.

For pre-operational comparison, in 1981, the annual mean of indicator sample locations was 18.9 mR per standardized 90-day quarter and the annual mean for the control sample locations was 17.1 mR per standardized 90-day quarter. It should be noted WCGS changed from thermoluminescence dosimeters (TLD) to optically stimulated luminescence (OSL) dosimeters in 2008.

The indicator sample location with the highest annual mean was 47 (24.2 mR per standardized 90-day quarter). The close proximity of location 47 to the Radwaste Building is likely the reason direct radiation levels are higher at this location.

Based upon Condition Report 00027489, improvements were made in measuring and subtracting transit dose in 2010. As expected, the OSL results have increased since 2010.

Chart 3 visibly displays the increase of the OSL results. Chart 3 also displays how closely the indicator and control location OSL dosimeter results are for 2013.

Chart 4 displays the TLD nearsite sample locations (1, 2, 7-9, 11-14, 18, 26, 27, 29, 30, 37 and

38) and the control sample locations (locations 39 and 48) for the preoperational years through 2007.

C. Waterborne Pathway (1) Surface Water Tritium, attributable to WCGS operation, was detected in surface water samples collected from the Coffey County Lake Spillway (SP) indicator sample location. The annual mean for detected tritium activity at the SP location was 11,100 pCi/L and the range was 9,295 to 13,170 pCi/L.

The detected tritium activity was below the'30,000 pCi/L AP 07B-004 reporting level. Chart 5 illustrates the yearly averages of surface water tritium data for the spillway (SP) location. Chart 5 indicates the average tritium concentration of the Coffey County Lake spillway (SP) location has reached equilibrium. Tritium activity was not detected in samples obtained from the control sample location (JRR).

During pre-operational radiological environmental monitoring, measured radiological activity was not detected in surface water samples.

The AP 07B-004 required lower limits of detection were met. Radionuclides were not detected by the gamma isotopic analyses or by Fe-55 analyses.

Tritium was the only activity detected during 2013 in surface water samples and no unusual trends were noted.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 5 of 32

(2) Ground Water The AP 07B-004 required lower limits of detection were met for 1-131, tritium and gamma isotopic analyses. Radioactivity was not detected in any ground water samples. No unusual trends were noted. Plant-related activation, corrosion or fission products were not detected during 2013 in ground water samples.

(3) Drinking Water Gross beta activity was detected in drinking water samples collected from the indicator sample location and in samples collected from the control sample location. The annual mean of the indicator sample location gross beta activity (2.9 pCi/L) was lower when compared to the annual mean of the control sample location gross beta activity (3.1 pCi/L). The 2013 annual means of gross beta activity for both the indicator and control sample locations were lower than those of the pre-operational monitoring year of 1984. In 1984, the annual mean of the indicator sample location gross beta activity was 7.5 pCi/L and the annual mean of the control sample location gross beta activity was 6.4 pCi/L.

Chart 6 illustrates the drinking water gross beta results for the last five years and how closely the gross beta results compared for the indicator and control sample locations.

Radionuclides were not detected by the 1-131 or gamma isotopic analyses.

The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in drinking water samples and no unusual trends were noted.

(4) Shoreline Sediment Naturally occurring K-40 was detected in shoreline sediment samples collected from the DC (indicator sample location) and JRR (control sample location). K-40 was also detected during pre-operational shoreline sediment monitoring.

No other radionuclides were detected in the DC or JRR shoreline sediment samples during 2013.

The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in shoreline sediment samples and no unusual trends were noted.

D. Ingestion Pathway (1) Milk Milk was not collected during the sample year since no indicator locations within five miles of the plant were identified during the Land Use Census.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 6 of 32

(2) Fish Naturally occurring K-40 activity was detected in fish samples obtained from the CCL indicator sample location and in fish samples obtained from the JRR control sample location. K-40 activity was also detected during pre-operational fish monitoring.

Fish samples were also analyzed for tritium. Fish samples collected from Coffey County Lake had tritium activity detected (7,743 pCi/kg annual mean). The detected tritium activity was attributable to plant operation. An adult consuming 21 kilograms of fish, at the maximum measured tritium concentration (8,852 pCi/kg), would receive a committed effective dose equivalent of 0.012 mRem.

Tritium activity was not detected in the control location samples collected from JRR.

No other radionuclides were detected in fish samples during 2013. The AP 07B-004 required lower limits of detection were met and no unusual trends were noted.

(3) Broadleaf Vegetation Gamma analyses of broadleaf vegetation samples obtained from indicator and control sample locations detected naturally occurring gamma emitters Be-7 and K-40. Be-7 and K-40 activity were also detected pre-operationally.

No other radionuclides were detected in broadleaf vegetation samples during the year.

The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in broadleaf vegetation samples no unusual trends were noted.

(4) Crop Samples Gamma analysis detected naturally occurring K-40 activity to be present in the samples collected from the indicator sample locations and in the samples collected from the control sample location. K-40 activity was also detected during pre-operational crop monitoring. K-40 was the only activity detected in the crop samples.

The AP 07B-004 required lower limits of detection were met. Plant-related activation, corrosion, or fission products were not detected during 2013 in crop samples and no unusual trends were noted.

E. Additional Samples Collected (not required by AP 07B-004)

(1) Bottom Sediment Gamma analysis detected naturally occurring K-40 activity to be present in the samples collected from the indicator sample locations and in the samples collected from the control sample location. K-40 activity was also detected during pre-operational bottom sediment monitoring.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 7 of 32

Cs-137 activity was detected in twelve samples obtained from indicator locations (range 38 to 108 pCi/kg, dry). Cs-137 activity was also detected in one sample obtained from the control sample location (85 pCi/kg, dry).

Cs-137 activity was detected in pre-operational samples. The Cs-137 activity detected in 2013 indicator sample location bottom sediment samples was within the pre-operational range.

(Cs-137 activity detected in 1981 and 1982 was in the range of 79 to 953 pCi/kg. The decay corrected range of pre-operational Cs-1 37 activity detected is approximately 38 to 457 pCi/kg.)

The detected Cs-137 activity in the samples collected from the indicator sample locations was likely due to fallout since the measured activity is within the decay corrected range of pre-operational Cs-137 detected activity and Cs-137 activity has also been detected in samples collected at the control sample location.

Chart 7 plots the Cs-1 37 detected activity from the discharge cove indicator sample location and JRR control sample location bottom sediment samples. The detected Cs-137 activity measured from the discharge cove location reflects a decreasing trend. The Chart 7 trendline indicates Cs-137 activity detected at the JRR control location has also been decreasing. Chart 7 also displays that in recent years, the detected Cs-1 37 activity for the JRR and DC sample locations overlap.

Fe-55 activity was not detected in the fourteen samples obtained from indicator sample locations. No other radionuclides were detected in bottom sediment samples.

Plant-related activation, corrosion, or fission products were not detected during 2013 in bottom sediment samples and no unusual trends were noted.

(2) Aquatic Vegetation Gamma analyses of aquatic vegetation samples obtained from indicator sample locations detected naturally occurring gamma emitters Be-7 and K-40. Be-7 and K-40 activity were also detected during pre-operational monitoring.

No other radionuclides were detected in aquatic vegetation samples. Plant-related activation, corrosion, or fission products were not detected during 2013 in aquatic vegetation samples and no unusual trends were noted.

(3) Shoreline Sediment Naturally occurring K-40 activity was detected in the shoreline sediment samples obtained from the EEA indicator sample location. K-40 activity was also detected during pre-operational monitoring.

Cs-137 activity (89.2 pCi/kg, dry) was detected in a shoreline sediment sample obtained from the EEA indicator sample location. Cs-137 activity was also detected in pre-operational shoreline sediment samples. Cs-137 activity detected in shoreline sediment samples collected from the DC location from 1982 to 1984 was in the range of 224 to 437 pCi/kg, dry. The decay corrected range of pre-operational Cs-1 37 activity detected is approximately 115 to 218 pCi/kg, dry. The detected Cs-137 activity in the shoreline sediment sample was likely due to fallout since the results are lower than the pre-operational decay corrected range. Additionally, Cs-1 37 activity is routinely detected in soil and sediment samples collected from the control locations.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 8 of 32

No other radionuclides were detected in the EEA shoreline sediment samples. Plant-related activation, corrosion, or fission products were not detected during 2013 and no unusual trends were noted.

(4) Terrestrial Vegetation Naturally occurring Be-7 and K-40 activity were detected in terrestrial vegetation indicator location samples. No other radionuclides were detected in terrestrial vegetation. Plant-related activation, corrosion or fission products were not detected during 2013 in terrestrial vegetation samples and no unusual trends were noted.

(5) Soil Naturally occurring K-40 activity was detected in soil samples obtained from the indicator locations. K-40 activity was also detected during pre-operational soil monitoring.

Cs-137 activity (range 148 to 250 pCi/kg) was detected in soil samples obtained from the indicator locations. Data was reviewed for soil samples collected pre-operationally. The detected Cs-137 activity range from February of 1985 was 255 to 2,160 pCi/kg. The decay corrected range of pre-operational Cs-137 activity detected in soil is approximately 134 to 1,137 pCi/kg. The detected Cs-137 activity in soil sampled in 2013 is within the decay corrected pre-operational range and is likely due to fallout.

Plant-related activation, corrosion, or fission products were not detected during 2013 in soil samples and no unusual trends were noted.

(6) Deer Naturally occurring K-40 activity was detected in the deer sample obtained from the indicator location.

Tritium activity (251 pCi/kg) was also detected in the deer sample. The detected tritium activity was attributable to plant operation.

No other radionuclides were detected in the deer sample. No unusual trends were identified.

Ill. PROGRAM REVISIONS/CHANGES Based upon the 2012 Land Use Census Report, Revision 1, broadleaf vegetation sample location A-3 was added to AP 07B-004 and broadleaf vegetation sample location N-1 was changed to an alternate sample location.

AP 07B-004 was revised to update the description of dosimeter location 44 to Wilson Cadman Wildlife Education Area to match the recent name change.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 9 of 32

IV. PROGRAM DEVIATIONS Air Samples The following air sample locations failed to meet the requirement for "continuous sampler operation." As described in footnote (1) of procedure AP 07B-004, Offsite Dose Calculation Manual (RadiologicalEnvironmental Monitoring Program), Table 5-1, deviations are permitted from the required sampling schedule due to malfunction of sampling equipment and other legitimate reasons. Discrepancies greater than five percent between Total Military Time and Total Digital Flow Meter Time, which resulted in a loss of air sample collected, are listed in the following table.

Location Sample Period Percent Explanation of DeviationlComments Discrepancy/ Condition Report Number Hours Unavailable 32 06/24/13 - 07/01/13 Unknown Power Outage!

Equipment Malfunction /

Condition Report 00071046 37 08/05/13 - 08/12/13 6.17%/10.42 Power Outage /

Equipment Operated as Expected /

Condition Report 00072632 Dosimeters During the third quarter, one dosimeter result was not received from the vendor processor for location 16. The vendor processor performed an investigation and the dosimeter was not located at the vendor facility. All of the other dosimeter results for the third quarter were received. The results for the other two dosimeters at location 16 have been received; this meets the requirements of AP 07B-004. (Condition Report 00077756)

Ground Water Protection The following information is being provided in association with the Nuclear Energy Institute (NEI) Groundwater Protection Industry Initiative:

Describe offsite ground water or surface water sample results that exceeded the REMP reporting criteria that were voluntarily communicated to State/Local officials during the calendar year- None.

V. INTERLABORATORY COMPARISON PROGRAM Environmental, Inc., Midwest Laboratory was contracted to perform radiological analysis of environmental samples for WCNOC. The lab participated in the intercomparison studies administered by Environmental Resources Associates. Appendix A is the Interlaboratory Comparison Program Results for Environmental, Inc., Midwest Laboratory. Intercomparison results, in-house spikes, blanks, duplicates and mixed analyte performance evaluation program results are also contained in Appendix A.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 10 of 32

VI. COMPARISON TO THE RADIOACTIVE EFFLUENT RELEASE PROGRAM As described in the section discussing radioisotopes found in fish from Coffey County Lake, dose that may be received as a result of tritium released from WCGS is comparable with the theoretical doses calculated by the Radioactive Effluent Release Program.

The theoretical doses calculated by the Radioactive Effluent Release Program assume a person drinks the water from Coffey County Lake and eats the fish from Coffey County Lake. Based upon these assumptions the dose to man from both pathways was calculated to be 0.165 mRem for 2013.

Using sample data obtained from the REMP, an adult drinking 2 liters per day of surface water from Coffey County Lake, using the average tritium activity (11,100 pCi/L), would receive a committed effective dose equivalent of 0.507 mRem per year. For an adult eating 21 kg of fish per year from Coffey County Lake, using the average tritium activity (7,743 pCi/kg), would receive a committed effective dose equivalent of 0.010 mRem per year. Based upon the REMP results, the dose from both pathways was calculated to be 0.517 mRem per year.

It should be noted Coffey County Lake is not used as a drinking water source. Calculating the dose to man for tritium detected in the Coffey County Lake surface water is for comparison purposes only.

The tritium dose values are being compared on a qualitative basis. It is not expected that the annual doses, as calculated in the Radioactive Effluent Release Report, would compare directly to those calculated from the REMP. The Radioactive Effluent Release Report provides a "snap shot" of potential dose resulting from the year's releases. The REMP data indicates the accumulated result of releasing tritium into the lake since the start of plant operation.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 11 of 32

TABLE 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM DESCRIPTION (SAMPLE COLLECTION SPECIFIED BY AP 07B-004)

EXPOSURE NUMBER OF SAMPLE COLLECTION TYPE AND PATHWAY/ SAMPLES AND FREQUENCY FREQUENCY OF SAMPLE TYPE SAMPLE LOCATIONS ANALYSIS AIRBORNE (See Figures 1 & 5)

Radioiodine and Samples from six Continuous sampler Analyze radioiodine Particulates locations operation with sample canister weekly for collection weekly, or more 1-131 frequently if required, by dust loading.

Samples from locations Analyze particulate near the site boundary filter weekly for in three sectors having gross beta activity; the highest calculated perform quarterly annual average D/Q gamma isotopic and one supplemental analysis composite location (Locations 2, (by location) 18, 37, or 49 on Figure 1)

Sample from the vicinity of a community having the highest calculated annual average D/Q (Location 32 on Figure 1, New Strawn)

Sample from a control location 9.5 to 18.5 miles distant in a low ranked D/Q sector (Location 53 on Figure 5) 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 12 of 32

TABLE I (Cont.)

EXPOSURE NUMBER OF SAMPLE COLLECTION TYPE AND PATHWAY/ SAMPLES AND FREQUENCY FREQUENCY OF SAMPLE TYPE SAMPLE LOCATIONS ANALYSIS DIRECT (See Figures 2 & 5)

RADIATION 40 routine monitoring Quarterly Gamma dose stations with two or quarterly more dosimeters measuring dose continuously, placed as follows:

An inner ring of stations, one in each meteorological sector 0-3 mile range from the site (Locations 1, 7, 9, 11-13, 18, 26, 27, 29, 30, 37, 38, 46, 47, & 49 on Figure 2).

An outer ring of stations, one in each meteorological sector in the 3 to 5 mile range from the site (Locations 4, 5,15-17,19, 22-25, 32, 34-36, 50 & 51 on Figure 2). Four sectors

[A, B, G & J] contain an additional station (Locations 2, 8, 14 &

20).

The balance of the stations to be placed in special interest areas such as population centers (Locations 23, 32 & 52), nearby residences 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 13 of 32

TABLE I (Cont.)

EXPOSURE NUMBER OF SAMPLE COLLECTION TYPE AND PATHWAY/ SAMPLES AND FREQUENCY FREQUENCY OF SAMPLE TYPE SAMPLE LOCATIONS ANALYSIS DIRECT RADIATION (cont.)

(many locations are near a residence),

schools (Locations 23

& 52), Wilson Cadman Wildlife Education Area (44), CCL Public Fishing Area (46) and in two areas to serve as control stations 10-20 miles distant from the site (Locations 39 and 53 on Figure 5).

WATERBORNE (See Figure 3)

Surface One sample upstream Monthly grab sample Monthly gamma (Location JRR on isotopic analysis and Figure 3) and one composite for tritium sample downstream analysis quarterly (Location SP on Figure 3).

Ground Samples from one or Quarterly grab sample Quarterly gamma two sources only if isotopic analysis and likely to be affected. tritium analysis Indicator samples at locations hydrologically down-gradient of the site (Locations C-10, C-49, F-1, G-2, J-1 and J-2 on Figure 3);

control sample at a location hydrologically upgradient of the site (Location B-12 on Figure 3).

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 14 of 32

TABLE 1 (Cont.)

EXPOSURE NUMBER OF SAMPLE COLLECTION TYPE AND PATHWAY/ SAMPLES AND FREQUENCY FREQUENCY OF SAMPLE TYPE SAMPLE LOCATIONS ANALYSIS WATERBORNE (cont.)

Drinking Sample of municipal Monthly Composite Monthly gamma water supply at an isotopic analysis and indicator location gross beta analysis downstream of the site of composite (Location IO-DW on sample. Quarterly Figure 5); control tritium analysis of sample from location composites.

upstream of the site (Location BW-1 5 on Figure 3).

Shoreline One sample from the Semiannually Semiannual gamma Sediment vicinity of Coffey isotopic analysis County Lake discharge cove (Location DC on Figure 3); control sample from John Redmond Reservoir (Location JRR on Figure 3).

INGESTION (See Figures 4 & 5)

Milk Samples from milking Semimonthly April to Gamma isotopic animals at three November; monthly analysis and 1-131 indicator locations December-March analysis of each within 5 miles of the sample site having the highest dose potential (currently there are no locations producing milk for human consumption within 5 miles of the site); one sample from a control location greater than 10 miles from the site if indicator locations are sampled.

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 15 of 32

TABLE I (Cont.)

EXPOSURE NUMBER OF SAMPLE COLLECTION TYPE AND PATHWAY/ SAMPLES AND FREQUENCY FREQUENCY OF SAMPLE TYPE SAMPLE LOCATIONS ANALYSIS INGESTION (cont.)

Fish Indicator samples of 1 Semiannually Gamma isotopic to 3 recreationally analysis on edible important species from portions Coffey County Lake; control samples of similar species from John Redmond Reservoir spillway (Figure 4).

Broadleaf Samples of available Monthly when available Gamma isotopic Vegetation broadleaf vegetation analysis on edible from two indicator portions locations (using the criteria from the "Land Use Census" section) with highest calculated annual average D/Q (Locations A-3 and Q-6 and alternate locations B-i, H-2, N-1 and R-2 on Figure 4); sample of similar broadleaf vegetation from a control location 9.5 to 18.5 miles distant in a low ranked D/Q sector (Location D-2 on Figure 5).

Irrigated Crops Sample of crops At time of harvest Gamma isotopic irrigated with water analysis on edible from the Neosho River portions downstream of the Neosho River - Wolf Creek confluence (locations will vary from year to year, e.g.,

Location NR-D1 and NR-D2 on Figure 5).

2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 16 of 32

TABLE 2 SAMPLE LOCATION IDENTIFIERS, DISTANCES (Miles) AND DIRECTIONS (Sectors)

Sample Type Location Distance from Direction Sector Identifier Reactor Air Particulates and Radioiodine 2 2.7 N A 18 3.0 SSE H 32 3.1 WNW P 37 2.0 NNW R 49 0.8 NNE B 53 10.8 ENE D Dosimeters 1 1.4 N A 2 2.7 N A 4 4.0 NNE B 5 4.1 NE C 7 2.1 NE C 8 1.7 NNE B 9 2.0 ENE D 11 1.7 E E 12 1.9 ESE F 13 1.6 SE G 14 2.5 SE G 15 4.6 ESE F 16 4.3 E E 17 3.7 SE G 18 3.0 SSE H 19 3.9 SSE H 20 3.3 S J 22 3.9 SSW K 23 4.3 SW L 24 4.1 WSW M 25 3.4 W N 26 2.4 WSW M 27 2.2 SW L 29 2.7 SSW K 30 2.5 W N 32 3.1 WNW P 34 4.4 NW Q 35 4.6 NNW R 36 4.2 N A 37 2.0 NNW R 38 1.2 NW Q 39 13.1 N A 41 0.8 NNW R 42 0.8 SSE H 43 0.7 WNW P 44 3.0 NNW R 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 17 of 32

TABLE 2 (Cont.)

SAMPLE LOCATION IDENTIFIERS, DISTANCES (Miles) AND DIRECTIONS (Sectors)

Sample Type Location Distance from Direction Sector Identifier Reactor Dosimeters 46 1.6 WNW P 47 0.16 S J 49 0.8 NNE B 50 3.6 ENE D 51 4.3 S J 52 3.6 SW L 53 10.8 ENE D Surface Water JRR 3.7 W N SP 3.2 SSE H Ground Water B-12 1.9 NNE B C-10 2.7 W N C-49/L-49 2.8 SW L F-1 2.5 ESE F G-2 3.6 SE G J-1 3.8 S J J-2 4.3 S J Drinking Water BW-15 3.9 SW L IO-DW 26.1 SSE H Shoreline Sediment DC 0.8 WNW P EEA 3.0 NNW R JRR 3.6 W N Fish CCL 0.6 E to NNW E to R JRR 3.7 W N Food/Garden B-1 0.8 NNE B D-2 14.8 ENE D H-2 3.0 SSE H Q-6 2.4 NW Q Crops NR-D1 8.9 S J NR-D2 11.5 S J NR-U1 4.0 SSW K Bottom Sediment DC 0.9 WNW P EEA 3.0 NNW R ESW 0.5 E E JRR 3.7 W N MUDS 1.5 WNW P UHS 0.6 E E Aquatic Vegetation DC ALT 1.5 NW Q EEA 3.0 NNW R MUDS 1.5 WNW P 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 18 of 32

TABLE 2 (Cont.)

SAMPLE LOCATION IDENTIFIERS, DISTANCES (Miles) AND DIRECTIONS (Sectors)

Sample Type Location Distance from Direction Sector Identifier Reactor Terrestrial Vegetation EEA 3.0 NNW R MUDS 1.5 WNW P Soil EEA 3.0 NNW R MUDS 1.5 WNW P Meat (Deer) R2.7 2.7 NNW R 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 19 of 32

TABLE 3 OSL Dosimeter Results mR/Standardized 90-day Quarter)

Location Qtr. I Qtr. 2 Qtr. 3 Qtr. 4 Total Annual mR) (mR) (mR) (mR) Exposure (mR) 1 19.1 19.6 21.5 21.8 81.9 2 17.8 18.3 18.5 19.4 74.1 4 19.1 20.5 21.4 20.6 81.7 5 17.8 17.2 14.6 17.2 66.9 7 17.5 17.0 18.9 19.2 72.6 8 20.3 18.8 21.7 22.5 83.3 9 18.5 19.2 15.9 17.3 71.0 11 20.1 23.1 19.6 20.6 83.4 12 20.7 20.5 20.1 21.2 82.5 13 20.7 20.4 18.5 17.3 76.9 14 17.5 20.1 18.0 17.8 73.4 15 19.1 18.8 17.8 17.8 73.4 16 17.0 16.2 17.3 16.9 67.3 17 18.2 20.4 17.5 20.9 76.9 18 17.8 20.1 15.4 19.7 72.9 19 20.6 21.8 18.5 20.9 81.9 20 18.0 17.5 18.5 19.5 73.5 22 18.0 18.8 19.6 22.0 78.3 23 15.9 17.0 21.7 20.0 74.6 24 18.4 20.9 19.6 19.5 78.4 25 17.3 16.3 17.3 17.3 68.3 26 18.3 16.6 16.8 19.5 71.2 27 19.2 19.2 20.7 17.7 76.7 29 14.8 14.0 14.3 16.1 59.2 30 19.4 14.9 19.2 21.5 75.1 32 18.4 16.1 17.1 18.3 69.8 34 20.6 17.9 19.2 20.8 78.5 35 19.6 19.2 18.5 20.5 77.8 36 19.6 18.3 19.9 20.0 77.8 37 17.3 16.6 15.3 18.8 68.0 38 19.4 20.1 18.5 21.1 79.1 39 19.6 18.7 17.9 15.4 71.5 41 18.4 20.6 19.4 18.3 76.7 42 13.0 12.7 12.4 12.8 51.0 43 12.4 12.8 12.3 12.5 50.0 44 15.9 20.5 18.5 20.6 75.5 46 18.3 19.2 18.9 20.6 77.0 47 20.4 24.8 24.1 27.6 96.9 49 19.4 16.1 17.5 18.7 71.8 50 20.0 22.2 20.9 19.2 82.3 51 20.1 19.7 21.7 20.4 81.9 52 20.6 20.1 18.2 17.7 76.5 53 20.9 20.7 21.5 21.3 84.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 20 of 32

FIGURE 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 21 of 32

FIGURE 2 DIRECT RADIATION PATHWAY SAMPLING LOCATIONS

FIGURE 3 WATERBORNE PATHWAY SAMPLING LOCATIONS

  • = DRINKING WATER A = SURFACE WATER 0 = GROUND WATER 0 = SHORELINE SEDIMENT

FIGURE 4 INGESTION PATHWAY SAMPLING LOCATIONS A = FISH (JRR) *- BROADLEAF VEGETATION *= SOIL

- FISH (CCL) TERRESTRIAL VEGETATION =DEER 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 24 of 32

FIGURE 5 A

CHART I 2013 Airborne Gross Beta Weekly Results 0.070 0.060 0.050 I a) A a)

E 0.040 0 k A4 V I -I

+

0 0

a) 0.030 U 4 2 M a M co 0.020 2O 0D 0.010 0.000 I I I I 0 4 8 12 16 20 24 28 32 36 40 44 48 52 Week Number 2013 Annual Radiological Environmental Operating Report - Wolf Creek Generating Station Page 26 of 32

CHART 2 0.060 a)

E 0 0.050 CU a) 0.040 CD 04 c'J 0 0.030 a)

-C 0

0 0.020 E

(n)

N\R 0.010 Q0

§ Z

\

Smoothed Avg. Indicator Locations Smoothed Avg. Control Locations 2013 Annual Radiological Environmental Operating Report - Wolf Creek Generating Station Page 27 of 32

CHART 3 OSL Dosimeters - Indicator and Control Locations mR per Standardized 90-Day Quarter 24.0 22.0 based upon Condition 20.0 18.0 16.0 S14.0 E

12.0 10.0 8.0 6.0 11\ P I N\ I \

4.0 J\ P  %\ C8 4V P e P I \ 1 J\

Year/Quarter

-- Indicator Locations Standardized 90-Day Quarter (mR) Control Locations Standardized 90-Day Quarter (mR) 2013 Annual Radiological Environmental Operating Report - Wolf Creek Generating Station Page 28 of 32

CHART 4 Historical TLD Nearsite Locations and Control Locations 32.0 30.0 Elevated resul 28.0 longer expi 26.0 24.0 22.0 0 E4 20.0 A A 18.0 o .., _ f,.*

16.0 A* . .,

14.0 A A 12.0 1980 1982 1984 1986 1988 1990 1992 1994 1996 1998 2000 2002 2004 2006

  • Avg. of Nearsite Locations A Avg. of Control Locations

- Moving Avg. of Nearsite Locations (2 period) ---- Moving Avg. of Control Locations (2 period) 2013 Annual Radiological Environmental Operating Report - Wolf Creek Generating Station Page 29 of 32

CHART 5 Coffey County Lake Surface Water Tritium Data 16,000 14,000 12,000 10,000

.I-

-J 8,000 6,000 4,000 2,000 0 4-1987 1992 1997 2002 2007 2012 s-Yearly Average of Spillway Location - Polynomial Trendline 2013 Annual Radiological Environmental Operating Report - Wolf Creek Generating Station Page 30 of 32

CHART 6 Drinking Water Gross Beta (5 years) 6 5

. 0 0.

U)

C--

om u3 00 2

1 o CD N) N 0~ 0~ 0~ 0~ 0~ 0

'- C~) (0 N-' C0 - N U ( - C

" N Q N N 'N Q NNN N NZ~ N N N Ný N

_ M-0 T N ,q, U)O U LO O - M-M-LO (0 M~ U) r- 0)M ' M~ U) - 0)M - ~ U) - 0)M ' M U) I- 0)M I- BW1 5 (Control) - - I00W (Indicator)I 2013 Annual Radiological Environmental Operating Report - Wolf Creek Generating Station Page 31 of 32

CHART 7 Detected Cs-1 37 Activity in Bottom Sediment 1,000 900 800 700 600 6; 500 400 300 200 100 0

0 N- I tr r- M 0 N M 10 NI_ 0) C N MO 1" 10 (0 NI_ M O N'-

Co !2 cO CO CO O* 0M 0* 0 0)

M 0M 0 0 0 0 0 0 0 0 0 "- '-

1O 1O N

0 0

co C)

N 00 N 0

-

0 oco N

1O N N

Co 10 N

1-0 N ~ 0 10 N

(0 o 0M Co 0)

N- Q- ,- -'- '- '- N N NC-0 C0 0- Co co 00- 0) 10- V) V- It O (0 10 0 0 C 10 Co -0 o) o T- 0) 0) 0 0 0 0 0 0 0 03 0D 0D - r"0 0) 0

7,*7II I Environmental, Midwest Laboratory Inc.

700 LandwehrRoad

  • Nodhorook. IL 60062-2310 phone (847) 564-0700- fax (847) 564-4517 APPENDIX A INTERLABORATORY COMPARISON PROGRAM RESULTS NOTE: Environmental Inc., Midwest Laboratory participates in intercomparison studies administered by Environmental Resources Associates, and serves as a replacement for studies conducted previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada. Results are reported inAppendix A. TLD Intercomparison results, in-house spikes, blanks, duplicates and mixed analyte performance evaluation program results are also reported. Appendix A is updated four times a year; the complete Appendix is included in March, June, September and December monthly progress reports only.

January through December, 2013

Appendix A Interlaboratory Comparison Program Results Environmental, Inc., Midwest Laboratory has participated in interlaboratory comparison (crosscheck) programs since the formulation of its quality control program in December 1971. These programs are operated by agencies which supply environmental type samples containing concentrations of radionuclides known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent check on a laboratory's analytical procedures and to alert it of any possible problems.

Participant laboratories measure the concentration of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used.

Results in Table A-1 were obtained through participation in the environmental sample crosscheck program administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada.

Table A-2 lists results for thermoluminescent dosimeters (TLDs), via International Intercomparison of Environmental Dosimeters, when available, and internal laboratory testing.

Table A-3 lists results of the analyses on in-house "spiked" samples for the past twelve months. All samples are prepared using NIST traceable sources. Data for previous years available upon request.

Table A-4 lists results of the analyses on in-house "blank" samples for the past twelve months. Data for previous years available upon request.

Table A-5 lists REMP specific analytical results from the in-house "duplicate" program for the past twelve months. Acceptance is based on the difference of the results being less than the sum of the errors. Complete analytical data for duplicate analyses is available upon request.

The results in Table A-6 were obtained through participation in the Mixed Analyte Performance Evaluation Program.

Results in Table A-7 were obtained through participation in the environmental sample crosscheck program administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the Environmental Measurement Laboratory Quality Assessment Program (EML).

Attachment A lists the laboratory precision at the 1 sigma level for various analyses. The acceptance criteria in Table A-3 is set at +/- 2 sigma.

Out-of-limit results are explained directly below the result.

Al

Attachment A ACCEPTANCE CRITERIA FOR "SPIKED" SAMPLES LABORATORY PRECISION: ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa One standard deviation Analysis Level for single determination Gamma Emitters 5 to 100 pCi/liter or kg 5.0 pCi/liter

> 100 pCi/liter or kg 5% of known value Strontium-89b 5 to 50 pCi/liter or kg 5.0 pCi/liter

> 50 pCi/liter or kg 10% of known value Strontium-90b 2 to 30 pCi/liter or kg 5.0 pCi/liter

> 30 pCi/liter or kg 10% of known value Potassium-40 > 0.1 g/liter or kg 5% of known value Gross alpha < 20 pCi/liter 5.0 pCi/liter

> 20 pCi/liter 25% of known value Gross beta < 100 pCi/liter 5.0 pCi/liter

> 100 pCi/liter 5% of known value Tritium 5 4,000 pCi/liter +/-lG =

0 0 933 169.85 x (known)

> 4,000 pCi/liter 10% of known value Radium-226,-228 > 0.1 pCi/liter 15% of known value Plutonium >0.1 pCi/liter, gram, or sample 10% of known value Iodine-131, < 55 pCi/liter 6 pCi/liter Iodine-1 2 9 b > 55 pCi/liter 10% of known value Uranium-238, < 35 pCi/liter 6 pCi/liter Nickel-63b > 35 pCi/liter 15% of known value Technetium-99b Iron-55b 50 to 100 pCi/liter 10 pCi/liter

> 100 pCi/liter 10% of known value Other Analyses b 20% of known value a From EPA publication, "Environmental Radioactivity Laboratory Intercomparison Studies Program, Fiscal Year, 1981-1982, EPA-600/4-81-004.

b Laboratory limit.

A2

TABLE A-1. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.

Concentration (pCi/L)

Lab Code Date Analysis Laboratory ERA Control Result b Result Limits Acceptance ERW-76 01/07/13 Ra-226 10.04 + 0.55 9.91 7.42-11.60 Pass ERW-76 01/07/13 Ra-228 6.11 + 1.29 5.22 3.14 -6.96 Pass ERW-76 01/07/13 Uranium 5.90 +/- 0.58 5.96 4.47 -7.13 Pass ERW-1 593 04/08/13 Sr-89 43.60 +/- 4.32 41.30 31.60 - 48.40 Pass ERW-1593 04/08/13 Sr-90 23.20 +/- 1.70 23.90 17.20 - 28.00 Pass ERW-1 596 04/08/13 Ba-1 33 74.80 +/- 4.00 82.10 69.00 - 90.30 Pass ERW-1596 04108/13 Co-60 65.50 +/- 3.42 65.90 59.30 - 75.00 Pass ERW-1 596 04/08/13 Cs-1 34 41.10 +/- 3.47 42.80 34.20 - 47.10 Pass ERW-1 596 04/08/13 Cs-137 42.30 +/- 4.03 41.70 37.00 - 48.80 Pass ERW-1596 04/08/13 Zn-65 200.3 +/- 10.1 189.0 170.0 - 222.0 Pass ERW-1598 04/08/13 Gr. Alpha 34.30 +/- 1.98 40.80 21.10 - 51.90 Pass ERW-1598 04/08/13 Gr. Beta 18.70 +/- 0.98 21.60 13.00 - 29.70 Pass ERW-1600 04/08/13 1-131 23.00 +/- 1.10 23.80 19.70 - 28.30 Pass ERW-1600 04/08/13 1-131(G) 23.48 +/- 9.44 23.80 19.70 -28.30 Pass ERW-1605 04/08/13 Ra-226 16.30 +/- 0.70 15.40 11.50 - 17.70 Pass ERW-1605 04/08/13 Ra-228 5.32 +/- 1.30 4.36 2.54 -5.98 Pass ERW-1605 04/08/13 Uranium 57.30 +/- 4.20 61.20 49.80 - 67.90 Pass ERW-1606 04/08/13 H-3 4041 +/- 194 4050 3450 - 4460 Pass ERW-6009 10/07/13 Sr-89 22.00 +/- 2.80 21.90 14.40 +/- 28.20 Pass ERW-6009 10/07/13 Sr-90 17.10 +/- 2.55 18.10 12.80 +/- 21.50 Pass ERW-6012 10/07/13 Ba-1 33 48.20 +/- 4.29 54.20 44.70 +/- 59.90 Pass ERW-6012 10/07/13 Co-60 100.8 +/-4.7 102.0 91.80 +/- 114.00 Pass ERW-6012 10/07/13 Cs-1 34 87.30 +/- 4.35 86.70 71.10 +/- 95.40 Pass ERW-6012 10/07/13 Cs-137 199.6 +/- 7.4 206.0 185.0 - 228.0 Pass ERW-6012 10/07/13 Zn-65 356.2 +/- 13.2 333.0 300.0 - 389.0 Pass ERW-6015 10/07/13 Gr. Alpha 30.70 +/- 11.90 42.80 22.20 +/- 54.30 Pass ERW-6015 10/07/13 Gr. Beta 25.70 +/- 6.48 32.20 20.80 +/- 39.90 Pass ERW-6019 10/07/13 1-131 22.50 +/- 1.01 23.60 19.60 +/- 28.00 Pass ERW-6022 10/07/13 Ra-226 12.70 +/- 1.62 12.10 9.04 +/- 14.00 Pass ERW-6022 d 10/07/13 Ra-228 5.70 +/- 0.56 4.02 2.30 +/- 5.59 Fail ERW-6022 10/07/13 Uranium 6.59 +/- 0.38 6.24 4.70 +/- 7.44 Pass ERW-6024 10/07/13 H-3 18397 +/-695 17700 15500 - 19500 Pass 8 Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the crosscheck program for proficiency testing in drinking water conducted by Environmental Resources Associates (ERA).

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

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

d The reported result was obtained in the first cycle of counting. It can be positively biased due to extra beta counts contributed by Pb-214 and Bi-214 daughters of Rn-222. Result of second cycle of counting 4.47 pCi/L.

Al-1

TABLE A-2. Thermoluminescent Dosimetry, (TLD, CaSO4: Dy Cards).

mR Lab Code Date Known Lab Result Control Description Value +/-12 sigma Limits Acceptance Environmental, Inc.

2013-1 5/6/2013 40 cm. 34.26 39.92 +/- 2.67 23.98 - 44.54 Pass 2013-1 5/6/2013 50 cm. 21.93 25.44 +/- 3.31 15.35 - 28.51 Pass 2013-1 5/6/2013 60 cm. 15.23 15.88 +/- 1.12 10.66 - 19.80 Pass 2013-1 5/6/2013 70 cm. 11.19 10.89 +/- 0.66 7.83 -14.55 Pass 2013-1 5/6/2013 80 cm. 8.57 9.21 +/- 0.41 6.00 -11.14 Pass 2013-1 5/6/2013 90 cm. 6.77 6.52 +/- 0.34 4.74 -8.80 Pass 2013-1 5/6/2013 100 cm. 5.48 5.02 +/- 0.53 3.84 -7.12 Pass 2013-1 5/6/2013 110 cm. 4.53 4.51 +/- 0.34 3.17 -5.89 Pass 2013-1 5/6/2013 120 cm. 3.81 4.28 +/- 0.35 2.67 -4.95 Pass 2013-1 5/6/2013 135 cm. 3.01 2.64 +/- 0.18 2.11 -3.91 Pass 2013-1 5/6/2013 150 cm. 2.44 2.10 +/- 0.25 1.71 -3.17 Pass 2013-1 5/6/2013 180 cm. 1.69 1.78 +/- 0.33 1.18 -2.20 Pass Environmental, Inc.

2013-2 11/18/2013 50 cm. 19.93 22.75 +/- 3.67 13.95 - 25.91 Pass 2013-2 11/18/2013 60 cm. 13.84 15.75 +/- 1.94 9.69 -17.99 Pass 2013-2 11/18/2013 70 cm. 10.17 11.24 +/- 0.88 7.12 -13.22 Pass 2013-2 11/18/2013 75 cm. 8.86 9.18 +/- 1.23 6.20 -11.52 Pass 2013-2 11/18/2013 80 cm. 7.79 7.81 +/- 1.10 5.45 -10.13 Pass 2013-2 11/18/2013 90 cm. 6.15 5.98 +/- 0.90 4.31 -8.00 Pass 2013-2 11/18/2013 100 cm. 4.98 5.13 +/- 0.73 3.49 -6.47 Pass 2013-2 11/18/2013 110 cm. 4.12 3.87 +/- 0.32 2.88 -5.36 Pass 2013-2 11/18/2013 120 cm. 3.46 3.11 +/- 0.39 2.42 -4.50 Pass 2013-2 11/18/2013 135 cm. 2.73 2.71 +/- 0.83 1.91 -3.55 Pass 2013-2 11/18/2013 150 cm. 2.21 2.11 +/- 0.63 1.55 -2.87 Pass 2013-2 11/18/2013 180 cm. 1.54 1.81 +/- 0.10 1.08 -2.00 Pass A2-1

TABLE A-3. In-House "Spiked" Samples Concentration (pCi/L)a Lab Code b Date Analysis Laboratory results Known Control 2s, n=1 c Activity Limits d Acceptance SPW-66 1/9/2013 Tc-99 1009 +/-5 1078 754.9 - 1402.0 Pass SPW-1891 1/18/2013 Ra-228 35.60 +/- 2.75 30.85 21.60 - 40.11 Pass SPSO-12313S 1/23/2013 Tc-99 103.5 +/- 2.2 107.8 75.46 - 140.14 Pass SPMI-264 1/25/2013 Cs-1 34 110.9 +/-6.7 107.5 96.73 - 118.23 Pass SPMI-264 1/25/2013 Cs-1 37 82.84 +/- 7.47 77.48 67.48 - 87.48 Pass SPMI-264 1/25/2013 Sr-90 38.19 +/- 1.49 40.11 32.09 - 48.13 Pass SPW-266 1/25/2013 Co-60 46.89 +/- 4.68 44.48 34.48 - 54.48 Pass SPW-266 1/25/2013 Cs-134 105.9 +/- 8.0 107.5 96.73 - 118.23 Pass SPW-266 1/25/2013 Cs-137 42.17 +/- 5.65 39.49 29.49 - 49.49 Pass SPW-266 1/25/2013 Sr-90 39.84 +/- 1.65 40.11 32.09 - 48.13 Pass SPAP-376 2/1/2013 Gr. Beta 44.20 +/- 0.11 45.68 27.41 - 63.95 Pass SPAP-378 2/1/2013 Cs-1 34 3.71 +/- 0.65 3.87 2.32 - 5.42 Pass SPAP-378 2/1/2013 Cs-137 97.47 +/- 2.50 102.9 92.61 -113.19 Pass SPW-391 2/1/2013 H-3 63719 +/- 703 65626 52501 -78751 Pass SPW-380 2/10/2013 Ni-63 217.0 +/- 3.7 205.3 143.7 - 266.9 Pass W-30413 3/4/2013 Gr. Alpha 19.77 +/- 0.40 20.00 10.00 - 30.00 Pass W-30413 3/4/2013 Gr. Beta 30.48 +/- 0.34 30.90 20.90 - 40.90 Pass W-30713 3/7/2013 Ra-226 18.06 +/- 0.51 16.70 11.69 - 21.71 Pass W-42713 4/27/2013 Gr. Alpha 20.67 +/- 0.40 20.00 10.00 - 30.00 Pass W-42713 4/27/2013 Gr. Beta 28.44 +/- 0.32 30.90 20.90 - 40.90 Pass WW-2870 5/7/2013 Co-60 166.1 +/-7.4 161.6 145.4 - 177.8 Pass WW-2870 5/7/2013 Cs-137 161.2 +/-9.3 149.0 134.1 - 163.9 Pass WW-2870 5/7/2013 H-3 6853 +/- 250 6735 5388 - 8082 Pass W-53113 5/31/2013 Ra-226 16.83 +/- 0.41 16.70 11.69 - 21.71 Pass SPAP-3332 6/19/2013 Am-241 4.60 +/- 0.14 4.00 2.40 - 5.60 Pass SPW-3334 6/19/2013 Th-230 4.36 +/- 0.34 4.00 2.40 - 5.60 Pass SPW-3458 6/24/2013 C-14 3825 +/- 13 4736 2842 - 6630 Pass SPAP-3529 6/27/2013 Cs-134 3.49 +/- 1.26 3.30 1.98 -4.62 Pass SPAP-3529 6127/2013 Cs-137 102.0 +/- 2.9 101.1 90.99 -111.21 Pass SPAP-3531 6/27/2013 Gr. Beta 45.64 +/- 0.11 45.42 27.25 - 63.59 Pass SPF-3533 6/27/2013 Cs- 134 1.31 +/- 0.14 1.50 0.90 -2.10 Pass SPF-3533 6/27/2013 Cs-137 2.77 +/- 0.27 2.43 1.46 - 3.40 Pass SPW-3535 6/27/2013 Ni-63 204.3 +/- 3.5 204.8 143.4 - 266.2 Pass SPW-3537 6/27/2013 Tc-99 104.5 +/- 1.7 107.8 75.46 - 140.14 Pass SPW-3539 6/27/2013 Fe-55 97015 +/- 860 90677 72542 - 108812 Pass SPW-1 893 6/28/2013 Ra-228 30.16 -2.73 30.85 21.60 - 40.11 Pass A3-1

TABLE A-3. In-House "Spiked" Samples Concentration (pCi/L)a Lab Code b Date Analysis Laboratory results Known Control 2s, n=1 c Activity Limits d Acceptance SPW-72913S 7/29/2013 Tc-99 126.6 +/- 2.2 107.8 75.46 +/- 140.14 Pass SPW-4373 7/31/2013 Cs-134 91.71 +/- 6.02 90.94 80.94 +/- 100.94 Pass SPW-4373 7/31/2013 Cs-137 83.05 +/- 7.20 76.57 66.57 +/- 86.57 Pass SPW-4373 7/31/2013 Sr-90 39.28 +/- 1.77 39.64 31.71 +/- 47.57 Pass SPW-4374 7/31/2013 Sr-90 42.17 +/- 1.71 39.64 31.71 +/- 47.57 Pass SPMI-4376 7/31/2013 Cs-1 34 82.22 -7.23 90.94 80.94 +/- 100.94 Pass SPMI-4376 7/31/2013 Cs-137 83.31 - 8.29 76.57 66.57 +/- 86.57 Pass SPMI-4376A 7/31/2013 Sr-90 35.00 +/- 1.63 39.64 31.71 +/- 47.57 Pass W-73113 7/31/2013 Ra-226 17.61 +/- 0.41 16.70 11.69 +/- 21.71 Pass SPS-4514 8/5/2013 Sr-90 78.63 +/- 2.95 79.28 63.42 +/- 95.14 Pass W-82013 8/20/2013 Gr. Alpha 21.53 +/- 0.45 20.00 10.00 +/- 30.00 Pass W-82013 8/20/2013 Gr. Beta 28.03 +/- 0.32 30.90 20.90 +/- 40.90 Pass SPW-1 894 8/28/2013 Ra-228 32.49 +/- 3.00 30.85 21.60 +/- 40.11 Pass W-90913 9/9/2013 Gr. Alpha 19.08 +/- 0.51 20.10 10.05 +/- 30.15 Pass W-90913 9/9/2013 Gr. Beta 32.12 +/- 0.35 32.10 22.10 +/- 42.10 Pass WW-5623 10/3/2013 Co-60 157.0 +/-7.0 155.3 139.8 - 170.8 Pass WW-5623 10/3/2013 Cs-1 37 156.0 +/- 8.8 148.1 133.3 - 162.9 Pass WW-5623 10/3/2013 H-3 6590 +/- 245 6322 5058 - 7586 Pass WW-5750 10/3/2013 Co-60 87.00 +/- 7.80 77.40 77.00 +/- 97.00 Pass WW-5750 10/3/2013 Cs-137 82.30 +/- 7.80 78.80 68.80 +/- 88.80 Pass WW-5750 10/3/2013 H-3 6181 +/- 238 6322 5058 - 7586 Pass W-102813 10/28/2013 Ra-226 15.69 +/- 0.37 16.70 11.69 +/- 21.71 Pass SPW-1898 12/17/2013 Ra-228 28.15 +/- 2.37 30.85 21.60 +/- 40.11 Pass W-122313 12/23/2013 Gr. Alpha 20.96 +/- 0.47 20.10 10.05 +/- 30.15 Pass W-122313 12/23/2013 Gr. Beta 31.00 +/- 0.34 32.10 22.10 +/- 42.10 Pass a Liquid sample results are reported in pCi/Liter, air filters( pCi/m 3), charcoal (pCi/charcoal canister), and solid samples (pCi/kg).

b Laboratory codes: W (Water), Ml (milk), AP (air filter), SO (soil), VE (vegetation), CH (charcoal canister), F (fish), U (urine).

c Results are based on single determinations.

d Control limits are established from the precision values listed in Attachment A of this report, adjusted to +/- 2s.

NOTE: For fish, Jello is used for the Spike matrix. For Vegetation, cabbage is used for the Spike matrix.

A3-2

TABLE A-4. In-House "Blank" Samples Concentration (pCi/L)8 Lab Code Sample Date Analysisb Laboratory results (4.66a) Acceptance Type LLD Activityc Criteria (4.66 a)

SPW-67 Water 1/9/2013 Tc-99 1.10 0.69 +/- 0.68 10 SPW-190 Water 1/18/2013 Ra-228 0.74 0.66 +/- 0.43 2 SPW-1901 Water 1/18/2013 Ra-228 0.74 0.66 +/-0.43 2 SPMI-263 Milk 1/25/2013 Sr-90 0.64 0.31 +/- 0.34 1 SPMI-263 Milk 1/25/2013 Sr-90 0.64 0.31 +/- 0.34 1 SPW-265 Water 1/25/2013 Co-60 2.86 2.10 +/- 1.72 10 SPW-265 Water 1/25/2013 Cs-134 2.98 2.25 +/- 1.57 10 SPW-265 Water 1/25/2013 Cs-1 37 2.71 0.44 +/- 1.61 10 SPW-266 Water 1/25/2013 Sr-90 0.72 -0.12 +/- 0.32 1 SPAP-375 Air Filter 2/1/2013 Gr. Beta 0.003 0.016 +/- 0.003 0.010 SPAP-377 Air Filter 2/1/2013 Co-60 2.31 -0.34 +/- 1.75 100 SPAP-377 Air Filter 2/1/2013 Cs-134 2.72 1.22 +/- 1.62 100 SPAP-377 Air Filter 2/1/2013 Cs-137 1.50 -0.52 +/- 1.80 100 SPW-391 Water 2/1/2013 H-3 92.04 -29.44 +/- 69.24 200 SPW-379 Water 2/10/2013 Ni-63 2.11 0.91 +/- 1.30 20 W-30413 Water 3/4/2013 Gr. Alpha 0.35 0.08 +/- 0.26 1 W-30413 Water 3/4/2013 Gr. Beta 0.73 0.10 +/- 0.51 3.2 W-30713 Water 3/7/2013 Ra-226 0.031 0.032 +/- 0.024 1 W-42713 Water 4/27/2013 Gr. Alpha 0.45 -0.14 +/- 0.30 1 W-42713 Water 4/27/2013 Gr. Beta 0.72 -0.23 +/- 0.50 3.2 W-53113 Water 5/31/2013 Ra-226 0.03 0.01 +/- 0.02 1 SPW-3335 Water 6/19/2013 Th-230 0.01 0.01 +/- 0.01 1 SPW-3459 Water 6/24/2013 C-14 10.89 10.44 +/- 6.82 200 SPAP-3528 Air Filter 6/27/2013 Cs-1 34 2.10 -0.98 +/- 1.11 100 SPAP-3528 Air Filter 6/27/2013 Cs-137 2.71 -0.24 +/- 1.36 100 SPAP-3530 Air Filter 6/27/2013 Gr. Beta 0.004 0.018 +/- 0.003 0.010 SPF-3532 Fish 6/27/2013 Cs-134 8.38 -1.39 +/- 5.69 100 SPF-3532 Fish 6/27/2013 Cs-137 8.37 -1.88 +/- 6.41 100 SPW-3534 Water 6/27/2013 Ni-63 2.47 -1.04 +/- 1.48 20 SPW-3536 Water 6/27/2013 Tc-99 1.15 -1.11 +/- 0.68 10 SPW-3538 water 6/27/2013 Fe-55 170.27 -17.50 +/- 102.70 1000 SPW-1903 Water 6/28/2013 Ra-228 0.85 -0.02 +/- 0.39 2 A4-1

TABLE A-4. In-House "Blank" Samples Concentration (pCi/L)a Lab Code Sample Date Analysiso Laboratory results (4.66a) Acceptance Type LLD Activityc Criteria (4.66 (Y)

SPW-72913B Water 7/29/2013 Tc-99 1.44 -0.33 +/- 0.87 10 SPW-4372 Water 7/31/2013 Co-60 1.41 -1.42 +/- 3.00 10 SPW-4372 Water 7/31/2013 Cs-134 3.68 -2.66 +/- 3.46 10 SPW-4372 Water 7/31/2013 Cs-137 3.53 0.29 +/- 3.31 10 SPMI-4375 Milk 7/31/2013 Co-60 3.92 2.65 +/- 2.26 10 SPMI-4375 Milk 7/31/2013 Cs-134 4.67 0.68 +/- 2.54 10 SPMI-4375 Milk 7/31/2013 Cs-137 4.79 1.30 +/-2.68 10 SPMI-4375 Milk 7/31/2013 Sr-90 0.57 0.32 +/- 0.30 1 W-73113 Water 7/31/2013 Ra-226 0.02 0.04 +/- 0.02 1 SPS-4515 Powder 8/5/2013 Sr-90 0.09 -0.01 +/- 0.04 1 W-82013 Water 8/20/2013 Gr. Alpha 0.42 -0.15 +/- 0.28 1 W-82013 Water 8/20/2013 Gr. Beta 0.74 -0.24 +/- 0.51 3.2 SPW-1904 Water 8/28/2013 Ra-228 0.96 0.85 +/- 0.56 2 CHW-90913 Water 9/9/2013 Gr. Alpha 0.25 0.20 +/- 0.29 1 CHW-90913 Water 9/9/2013 Gr. Beta 0.49 -0.18 +/- 0.53 3.2 CHW-102013 Water 10/20/2013 Gr. Alpha 0.29 0.24 +/-0.33 1 CHW-102013 Water 10/20/2013 Gr. Beta 0.54 -0.32 +/-0.54 3.2 W-102813 Water 10/28/2013 Ra-226 0.02 0.02 +/- 0.01 1 SPW-1908 Water 12/17/2013 Ra-228 0.69 0.55 +/- 0.39 2 CHW-122313 Water 12/23/2013 Gr. Alpha 0.25 -0.09 +/- 0.26 1 CHW-122313 Water 12/23/2013 Gr. Beta 0.48 0.05 +/- 0.53 3.2 CHW-122713 Water 12/27/2013 Gr. Alpha 0.28 0.04 +/- 0.31 1 CHW-122713 Water 12/27/2013 Gr. Beta 0.49 -0.33 +/- 0.53 3.2 a Liquid sample results are reported in pCi/Liter, air filters( pCi/m 3), charcoal (pCi/charcoal canister), and solid samples (pCi/kg).

b 1-131(G); iodine-131 as analyzed by gamma spectroscopy.

c Activity reported is a net activity result.

A4-2

TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)2 Averaged Lab Code Date Analysis First Result Second Result Result Acceptance CF-41, 42 1/212013 Gr. Beta 8.45 +/- 0.37 7.90 +/- 0.35 8.17 +/- 0.26 Pass CF-41, 42 1/2/2013 Sr-90 0.030 +/- 0.015 0.029 +/- 0.014 0.030 +/- 0.010 Pass SWT-8243, 8244 1/2/2013 Gr. Beta 1.07 +/- 0.54 0.98 +/- 0.51 1.03 +/- 0.37 Pass AP-8454, 8455 1/2/2013 Be-7 0.053 +/- 0.010 0.042 +/- 0.010 0.048 +/- 0.007 Pass AP-8517, 8518 1/3/2013 Be-7 0.051 +/- 0.015 0.049 +/- 0.017 0.050 +/- 0.011 Pass MI-62, 63 1/8/2013 K-40 1317.70 +/- 91.70 1351.90 +/- 72.50 1334.80 +/- 58.45 Pass WW-151, 152 1/8/2013 H-3 222.70 +/- 81.00 289.70 +/- 84.10 256.20 +/- 58.38 Pass SG-107, 108 1/11/2013 Ra-226 55.20 +/- 5.53 58.60 +/- 5.94 56.90 +/- 4.06 Pass SG-107, 108 1/11/2013 Ra-228 71.60 +/- 1.10 74.30 +/- 1.70 72.95 +/- 1.01 Pass SG-130, 131 1/14/2013 Ra-226 3.91 +/- 0.20 3.45 +/- 0.27 3.68 +/- 0.17 Pass SG-130, 131 1/14/2013 Ra-228 2.40 +/- 0.33 2.70 +/- 0.39 2.55 +/- 0.26 Pass WW-277, 278 1/17/2013 H-3 159.71 +/- 77.91 196.57 +/- 79.72 178.14 +/- 55.73 Pass WW-256, 257 1/22/2013 H-3 502.70 +/- 93.40 483.30 +/- 92.60 493.00 +/- 65.76 Pass DW-40010, 40011 1/24/2013 Ra-226 2.55 +/- 0.18 2.86 +/- 0.20 2.71 +/- 0.13 Pass DW-40010, 40011 1/24/2013 Ra-228 1.78 +/- 0.62 2.22 +/- 0.62 2.00 +/- 0.44 Pass SWT-361, 362 1/29/2013 Gr. Beta 0.90 +/- 0.40 1.01 +/- 0.38 0.96 +/- 0.28 Pass DW-484, 485 1/29/2013 Gr. Beta 14.85 +/- 1.93 14.81 +/- 2.06 14.83 +/- 1.41 Pass S-945, 946 1/29/2013 Cs-1 37 14.50 +/- 0.18 14.45 +/- 0.19 14.48 +/- 0.13 Pass S-945, 946 1/29/2013 K-40 7.90 +/- 0.74 8.00 +/- 0.73 7.95 +/- 0.52 Pass S-340, 341 1/31/2013 Cs-137 0.16 +/- 0.05 0.15 +/- 0.06 0.15 +/- 0.04 Pass S-340, 341 1/31/2013 K-40 17.35 +/- 1.34 19.75 +/- 1.25 18.55 +/- 0.92 Pass AP-463, 464 1/31/2013 Be-7 0.27 +/- 0.10 0.26 +/- 0.10 0.26 +/- 0.07 Pass MI-631, 632 2/13/2013 K-40 1350.50 +/- 105.20 1413.70 +/- 85.94 1382.10 +/- 67.92 Pass WW-769, 770 2/25/2013 Gr. Beta 1.20 +/- 0.33 1.35 +/- 0.34 1.28 +/- 0.24 Pass DW-736, 737 2/26/2013 Gr. Beta 1.09 +/- 0.54 1.57 +/- 0.58 1.33 +/- 0.40 Pass SWU-790, 791 2/26/2013 Gr. Beta 2.68 +/- 0.96 2.08 +/- 0.95 2.38 +/- 0.67 Pass W-925, 926 2/27/2013 H-3 2265.00 +/- 153.00 2329.00 +/- 154.00 2297.00 +/- 108.54 Pass AP-1034, 1035 3/7/2013 Be-7 0.17 +/- 0.08 0.16 +/- 0.09 0.17 +/- 0.06 Pass MI-1076, 1077 3/13/2013 K-40 1347.70 +/- 99.32 1396.10 +/- 108.00 1371.90 +/- 73.36 Pass CH-1118, 1119 3/14/2013 1-131 (G) 109.41 +/- 5.69 103.88 +/- 7.76 106.65 +/- 4.81 Pass WW-1221, 1222 3/14/2013 H-3 452.11 +/- 97.43 403.29 +/- 95.46 427.70 +/- 68.20 Pass P-1368, 1369 3/15/2013 H-3 735.24 +/- 113.99 666.04 +/- 111.41 700.64 +/- 79.70 Pass DW-40017, 40018 3/19/2013 Gr. Alpha 1.43 +/- 0.94 1.61 +/- 1.00 1.52 +/- 0.69 Pass MI-1473, 1474 4/1/2013 K-40 1618.00 +/- 107.00 1767.00 +/- 129.00 1692.50 +/- 83.80 Pass AP-2014, 2015 4/1/2013 Be-7 0.055 +/- 0.008 0.057 +/- 0.006 0.056 +/- 0.005 Pass DW-40023, 40024 4/1/2013 Ra-226 2.29 +/- 0.18 2.54 +/- 0.20 2.42 +/- 0.13 Pass DW-40023, 40024 4/1/2013 Ra-228 2.99 +/- 0.69 2.96 +/- 0.67 2.98 +/- 0.48 Pass SWU-736, 737 4/2/2013 Gr. Beta 4.80 +/- 0.95 4.43 +/- 0.86 4.62 +/- 0.64 Pass AP-2035, 2036 4/2/2013 Be-7 0.070 +/- 0.013 0.065 +/- 0.013 0.068 +/- 0.009 Pass BS-1680, 1681 4/8/2013 K-40 1995.30 +/- 265.70 1992.00 +/- 289.40 1993.65 +/- 196.44 Pass SW-1638, 1639 4/9/2013 H-3 1350.77 +/- 130.08 1320.45 +/- 129.25 1335.61 +/- 91.69 Pass A5-1

TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance WW-2394, 2395 4/9/2013 H-3 348.08 +/- 88.40 302.43 +/- 86.41 325.25 +/- 61.81 Pass DW-40035,40036 4/12/2013 Ra-226 1.36 +/- 0.15 1.29 +/- 0.13 1.33 +/- 0.10 Pass DW-40035, 40036 4/12/2013 Ra-228 1.22 +/- 0.49 1.38 +/- 0.53 1.30 +/- 0.36 Pass MI-1825, 1826 4/15/2013 K-40 1290.20 +/- 113.80 1378.60 +/- 91.99 1334.40 +/- 73.17 Pass MI-1825, 1826 411512013 Sr-90 0.68 +/- 0.32 0.46 +/- 0.31 0,57 +/- 0.22 Pass DW-40049, 40050 4/15/2013 Gr. Alpha 1.88 +/- 0.69 2.51 +/- 0.71 2.20 +/- 0.50 Pass WW-1 909,1910 4/16/2013 H-3 2145.68 +/- 156.65 2108.32 +/- 155.80 2127.00 +/- 110.47 Pass DW-40064, 40065 4/23/2013 Gr. Alpha 1.95 +/- 0.79 1.80 +/- 0.81 1.88 +/- 0.57 Pass DW-40066, 40067 4/23/2013 Ra-226 1.98 +/- 0.17 1.66 +/- 0.16 1.82 +/- 0.12 Pass DW-40066, 40067 4/23/2013 Ra-228 2.30 +/- 0.59 2.32 +/- 0.59 2.31 +/- 0.42 Pass F-2225, 2226 5/1/2013 K-40 2.81 +/- 0.37 2.67 +/- 0.39 2.74 +/- 0.27 Pass BS-2267, 2268 5/1/2013 K-40 13.46 +/- 0.64 13.59 +/- 0.62 13.52 +/- 0.45 Pass SG-2235, 2236 5/2/2013 Ac-228 18.30 +/- 0.60 18.50 +/- 0.60 18.40 +/- 0.42 Pass SG-2235,2236 5/2/2013 Gr. Alpha 54.00 +/- 3.70 51.90 +/- 3.40 52.95 +/- 2.51 Pass SG-2235, 2236 5/2/2013 Pb-214 11.30 +/- 0.30 11.20 +/- 0.20 11.25 +/- 0.18 Pass AP-2288, 2289 5/2/2013 Be-7 0.19 + 0.10 0.19 +/- 0.08 0.19 +/- 0.07 Pass WW-3091, 3092 5/2/2013 H-3 1107.91 + 153.49 1263.37 +/- 157.43 1185.64 +/- 109.94 Pass SW-2373,2374 5/8/2013 H-3 324.80 +/- 86.81 364.61 +/- 88.53 344.71 +/- 62.00 Pass W-2352,2353 5/9/2013 Ra-226 0.91 + 0.20 1.29 +/- 0.22 1.10 +/- 0.15 Pass W-2352,2353 5/9/2013 Ra-228 1.28 + 0.87 1.03 +/- 0.94 1.16 +/- 0.64 Pass CF-2499, 2500 5/13/2013 K-40 11.52 00.45 12.55 +/- 0.61 12.04 +/- 0.38 Pass F-3987, 3988 5/20/2013 K-40 3.07 +/- 0.48 3.05 +/- 0.43 3.06 +/- 0.32 Pass BS-4113, 4114 5/20/2013 K-40 8.06 +/- 0.44 7.99 +/- 0.44 8.02 +/- 0.31 Pass SO-2902, 2903 5/22/2013 Th-228 0.57 +/- 0.07 0.51 +/- 0.06 0.54 +/- 0.05 Pass SO-2902, 2903 5/22/2013 Th-230 0.39 +/- 0.06 0.40 +/- 0.05 0.40 +/- 0.04 Pass SO-2902,2903 5/22/2013 Th-232 0.55 +/- 0.07 0.62 +/- 0.06 0.59 +/- 0.05 Pass WW-2776, 2777 5/23/2013 H-3 261.76 +/- 100.85 283.17 +/- 101.68 272.46 +/- 71.61 Pass WW-2818, 2819 5/23/2013 H-3 999.35 +/- 126.15 880.63 +/- 122.43 939.99 +/- 87.90 Pass S-7271, 7272 5/27/2013 Cs-1 37 2.82 +/- 0.10 2.91 +/- 0.09 2.86 +/- 0.07 Pass S-7271, 7272 5/27/2013 K-40 21.52 +/- 0.97 21.13 +/- 1.02 21.32 +/- 0.70 Pass P-2923, 2924 5/29/2013 H-3 441.31 +/- 92.75 374.30 +/- 89.94 407.80 +/- 64.60 Pass WW-3133, 3134 6/1/2013 H-3 278.42 +/- 86.54 209.45 +/- 83.44 243.93 +/- 60.11 Pass WW-3049, 3050 6/5/2013 H-3 156.08 +/- 79.16 244.66 +/- 83.86 200.37 +/- 57.66 Pass DW-40079, 40080 615/2013 Ra-226 6.67 +/- 0.30 7.03 +/- 0.35 6.85 +/- 0.23 Pass DW-40079, 40080 6/5/2013 Ra-228 5.55 +/- 0.75 6.11 +/- 0.77 5.83 +/- 0.54 Pass DW-40089, 40090 6/5/2013 Gr. Alpha 6.82 +/- 0.90 5.64 +/- 1.02 6.23 +/- 0.68 Pass DW-40091, 40092 6/5/2013 Ra-226 3.44 +/- 0.19 3.66 +/- 0.19 3.55 +/- 0.13 Pass DW-40091, 40092 6/5/2013 Ra-228 3.70 +/- 0.68 4.69 +/- 0.73 4.20 +/- 0.50 Pass DW-40103, 40104 6/5/2013 Ra-226 0.98 +/- 0.22 0.62 +/- 0.15 0.80 +/- 0.13 Pass MI-3154, 3155 6/12/2013 K-40 1513.00 +/- 128.10 1456.70 +/- 110.30 1484.85 +/- 84.52 Pass P-3385, 3386 6/14/2013 H-3 236.88 +/- 87.87 242.87 +/- 88.14 239.88 +/- 62.23 Pass F-3776, 3777 6/16/2013 Cs-1 37 0.039 +/- 0.015 0.048 +/- 0.019 0.044 +/- 0.012 Pass F-3776, 3777 6/16/2013 Gr. Beta 4.52 +/- 0.09 4.63 +/- 0.09 4.57 +/- 0.06 Pass F-3776, 3777 6/16/2013 K-40 3.40 +/- 0.41 3.52 +/- 0.39 3.46 +/- 0.29 Pass A5-2

TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance S-3238, 3239 6/17/2013 Be-7 1139.80 +/- 215.00 1102.00 +/- 194.70 1120.90 +/- 145.03 Pass S-3238, 3239 6/17/2013 Cs-1 34 26.23 +/- 13.23 39.91 +/- 11.73 33.07 +/- 8.84 Pass S-3238, 3239 6/17/2013 Cs-137 72.75 +/- 25.99 85.91 +/- 22.58 79.33 +/- 17.21 Pass S-3238, 3239 6/17/2013 K-40 21847.00 +/- 656.50 22158.00 +/- 622.80 22002.50 +/- 452.46 Pass SO-3343, 3344 6/17/2013 Cs-1 37 0.087 +/- 0.022 0.084 +/- 0.017 0.086 +/- 0.014 Pass SO-3343, 3344 6/17/2013 K-40 8.90 +/- 0.53 9.47 +/- 0.49 9.19 +/- 0.36 Pass DW-40118, 40119 6/26/2013 Gr. Alpha 3.56 +/- 1.07 4.51 +/- 0.96 4.04 +/- 0.72 Pass DW-40118, 40119 6/26/2013 Ra-226 2.52 +/- 0.22 2.48 +/- 0.19 2.50 +/- 0.15 Pass DW-40118, 40119 6/26/2013 Ra-228 2.75 +/- 0.71 2.86 +/- 0.75 2.81 +/- 0.52 Pass WW-3583, 3584 6/27/2013 H-3 6732.57 +/- 246.74 6807.94 +/- 247.98 6770.26 +/- 174.91 Pass AP-4092, 4093 6/28/2013 Be-7 0.078 +/- 0.015 0.083 +/- 0.017 0.080 +/- 0.011 Pass E-3608, 3609 7/1/2013 K-40 1.28 +/- 0.13 1.29 +/- 0.11 1.28 +/- 0.09 Pass MI-3629, 3630 7/1/2013 K-40 1840.70 +/- 130.10 1804.90 +/- 143.00 1822.80 +/- 96.66 Pass AP-4050, 4051 7/1/2013 Be-7 0.094 +/- 0.009 0.093 +/- 0.009 0.093 +/- 0.006 Pass DW-40134, 40135 7/1/2013 Ra-226 1.75 +/- 0.15 1.56 +/- 0.15 1.66 +/- 0.11 Pass DW-40134, 40135 7/1/2013 Ra-228 2.07 +/- 0.60 1.61 +/- 0.57 1.84 +/- 0.41 Pass AP-4071, 4072 7/3/2013 Be-7 0.066 +/- 0.009 0.069 +/- 0.011 0.067 +/- 0.007 Pass DW-40144, 40145 7/9/2013 Gr. Alpha 3.66 +/- 0.85 2.85 +/- 0.79 3.26 +/- 0.58 Pass DW-40146, 40147 7/9/2013 Ra-226 0.70 +/- 0.11 0.72 +/- 0.11 0.71 +/- 0.08 Pass DW-40146, 40147 7/9/2013 Ra-228 1.00 +/- 0.58 0.70 +/- 0.52 0.85 +/- 0.39 Pass VE-3818, 3819 7/9/2013 Be-7 0.41 +/- 0.11 0.46 +/- 0.18 0.43 +/- 0.11 Pass VE-3818, 3819 7/9/2013 K-40 4.67 +/- 0.30 4.52 +/- 0.43 4.60 +/- 0.26 Pass XW-4646, 4647 7/15/2013 H-3 465.00 +/- 111.00 525.00 +/- 114.00 495.00 +/- 79.56 Pass WW-4134, 4135 7/16/2013 H-3 315.86 +/- 123.54 264.98 +/- 121.78 290.42 +/- 86.73 Pass AP-4155, 4156 7/18/2013 Be-7 0.20 +/- 0.11 0.16 +/- 0.09 0.18 +/- 0.07 Pass MI-4218, 4219 7/22/2013 K-40 1426.80 +/- 117.50 1335.70 +/- 110.60 1381.25 +/- 80.68 Pass MI-4218, 4219 7/22/2013 Sr-90 0.62 +/- 0.32 0.67 +/- 0.32 0.65 +/- 0.23 Pass WW-4239, 4240 7/23/2013 H-3 223.71 +/- 92.64 221.74 +/- 92.56 222.73 +/- 65.48 Pass WW-4394, 4395 7/30/2013 Gr. Alpha 2.63 +/- 1.49 2.57 +/- 1.11 2.60 +/- 0.93 Pass WW-4394, 4395 7/30/2013 Gr. Beta 3.72 +/- 1.17 2.63 +/- 1.29 3.18 +/- 0.87 Pass WW-4394, 4395 7/30/2013 H-3 271.50 +/- 91.30 297.60 +/- 91.50 284.55 +/- 64.63 Pass SWU-4478, 4479 7/30/2013 Gr. Beta 2.07 +/- 0.54 2.24 +/- 0.55 2.16 +/- 0.39 Pass DW-40159, 40160 7/31/2013 Ra-226 3.39 +/- 0.63 2.39 +/- 0.45 2.89 +/- 0.39 Pass DW-40159, 40160 7/31/2013 Ra-228 3.29 +/- 0.73 2.94 +/- 0.68 3.12 +/- 0.50 Pass VE-4436, 4437 8/1/2013 Be-7 0.98 +/- 0.21 0.89 +/- 0.17 0.94 +/- 0.14 Pass VE-4436, 4437 811/2013 K-40 3.95 +/- 0.39 3.75 +/- 0.31 3.85 +/- 0.25 Pass G-4457, 4458 8/1/2013 Be-7 0.78 +/- 0.19 0.67 +/- 0.16 0.72 +/- 0.12 Pass G-4457, 4458 8/1/2013 Gr. Beta 6.15 +/- 0.14 6.10 +/- 0.14 6.13 +/- 0.10 Pass G-4457, 4458 8/1/2013 K-40 4.25 +/- 0.36 4.60 +/- 0.41 4.42 +/- 0.27 Pass VE-4520, 4521 8/1/2013 K-40 2.20 +/- 0.16 2.09 +/- 0.17 2.15 +/- 0.12 Pass WW-4772, 4773 8/6/2013 H-3 143.80 +/- 86.70 157.80 +/- 87.30 150.80 +/- 61.52 Pass A5-3

TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L) 8 Averaged Lab Code Date Analysis First Result Second Result Result Acceptance VE-4709, 4710 8/8/2013 Gr. Beta 31.40 +/- 1.00 30.70 +/- 1.00 31.05 +/- 0.71 Pass VE-4709, 4710 8/8/2013 H-3 1504.00 +/- 132.00 1468.00 +/- 131.00 1486.00 +/- 92.99 Pass VE-4709, 4710 8/8/2013 U-233/4 0.009 +/- 0.002 0.005 +/- 0.002 0.007 +/- 0.001 Pass VE-4709, 4710 8/8/2013 U-238 0.005 +/- 0.002 0.004 +/- 0.001 0.005 +/- 0.001 Pass WW-4562, 4563 8/8/2013 H-3 208.82 +/- 105.55 213.13 +/- 105.73 210.97 +/- 74.70 Pass SG-4651, 4652 8/13/2013 Gr. Alpha 29.00 +/- 3.10 28.80 +/- 3.20 28.90 +/- 2.23 Pass SG-4651, 4652 8/13/2013 Gr. Beta 34.10 +/- 1.80 34.00 +/- 1.80 34.05 +/- 1.27 Pass SG-4651, 4652 8/13/2013 Ra-226 9.00 +/- 0.20 8.70 +/- 0.20 8.85 +/- 0.14 Pass VE-4835, 4836 8/13/2013 K-40 3.01 +/- 0.24 3.08 +/- 0.28 3.04 +/- 0.19 Pass WW-4877, 4878 8/14/2013 H-3 217.35 +/- 87.57 276.63 +/- 90.20 246.99 +/- 62.86 Pass LW-4856, 4857 8/15/2013 Gr. Beta 0.96 +/- 0.40 0.94 +/- 0.38 0.95 +/- 0.28 Pass W-4982, 4983 8/16/2013 H-3 757.43 +/- 112.40 767.56 +/- 112.76 762.50 +/- 79.60 Pass VE-4919, 4920 8/19/2013 K-40 4891.90 +/- 407.90 4907.40 +/- 350.40 4899.65 +/- 268.87 Pass VE-4919, 4920 8/19/2013 Be-7 470.50 +/- 159.60 325.10 +/- 104.10 397.80 +/- 95.27 Pass DW-40184, 40185 8/19/2013 Ra-228 2.35 +/- 0.72 2.53 +/- 0.70 2.44 +/- 0.50 Pass DW-40184, 40185 8/19/2013 Ra-228 1.44 +/- 0.35 2.30 +/- 0.56 1.87 +/- 0.33 Pass AP-5003, 5004 8/22/2013 Be-7 0.23 +/- 0.10 0.21 +/- 0.10 0.22 +/- 0.07 Pass LW-5229, 5230 8/29/2013 Gr. Beta 1.09 +/- 0.86 2.28 +/- 0.96 1.69 +/- 0.64 Pass SS-5333, 5334 9/3/2013 Cs-1 37 89.20 +/- 41.60 97.80 +/- 34.60 93.50 +/- 27.05 Pass SS-5333, 5334 9/3/2013 K-40 11893.00 +/- 681.30 12353.00 +/- 778.90 12123.00 +/- 517.41 Pass VE-5313, 5314 9/3/2013 K-40 1.84 +/- 0.20 1.85 +/- 0.20 1.85 +/- 0.14 Pass VE-5313, 5314 9/3/2013 Gr. Beta 2.38 +/- 0.04 2.43 +/- 0.04 2.41 +/- 0.03 Pass WW-5617, 5618 9/5/2013 H-3 1987.00 +/- 147.00 2094.00 +/- 150.00 2040.50 +/- 105.01 Pass AP-5355, 5356 9/5/2013 Be-7 0.22 +/- 0.12 0.27 +/- 0.14 0.25 +/- 0.09 Pass XW-5694, 5695 9/8/2013 C-14 0.94 +/- 0.09 0.78 +/- 0.10 0.86 +/- 0.07 Pass VE-5409, 5410 9/9/2013 K-40 3.60 +/- 0.26 3.33 +/- 0.29 3.46 +/- 0.19 Pass AP-5430, 5431 9/12/2013 Be-7 0.26 +/- 0.10 0.26 +/- 0.10 0.26 +/- 0.07 Pass MI-5401, 5402 9/12/2013 K-40 1404.60 +/- 114.10 1356.10 +/- 128.60 1380.35 +/- 85.96 Pass WW-5451, 5452 9/12/2013 H-3 196.66 +/- 84.44 200.78 +/- 84.64 198.72 +/- 59.78 Pass MI-5484, 5485 9/16/2013 K-40 1398.50 +/- 88.93 1364.60 +/- 113.30 1381.55 +/- 72.02 Pass WW-5568, 5569 9/17/2013 H-3 274.69 +/- 87.95 203.72 +/- 84.71 239.20 +/- 61.05 Pass BS-5764, 5765 9/20/2013 Cs-137 0.40 +/- 0.03 0.37 +/- 0.02 0.39 +/- 0.02 Pass BS-5764, 5765 9/20/2013 K-40 17.97 +/- 0.59 17.54 +/- 0.55 17.76 +/- 0.40 Pass VE-5638, 5639 9/23/2013 K-40 4.15 +/- 0.33 4.46 +/- 0.38 4.31 +/- 0.25 Pass WW-5596, 5597 9/23/2013 Gr. Beta 5.97 +/- 1.39 5.95 +/- 1.45 5.96 +/- 1.01 Pass G-5680, 5681 9/25/2013 Be-7 0.36 +/- 0.13 0.35 +/- 0.09 0.35 +/- 0.08 Pass G-5680, 5681 9/25/2013 Gr. Beta 3.81 +/- 0.11 3.77 +/- 0.11 3.79 +/- 0.08 Pass G-5680, 5681 9/25/2013 K-40 3.23 +/- 0.32 2.99 +/- 0.24 3.11 +/- 0.20 Pass S-5659, 5660 9/26/2013 Ac-228 1.19 +/- 0.21 1.06 +/- 0.21 1.13 +/- 0.15 Pass S-5659, 5660 9/26/2013 Cs-137 0.13 +/- 0.04 0.14 +/- 0.05 0.14 +/- 0.03 Pass S-5659, 5660 9/26/2013 K-40 16.08 +/- 1.39 16.65 +/- 1.46 16.37 +/- 1.01 Pass S-5659, 5660 9/26/2013 Pb-214 0.97 +/- 0.15 1.10 +/- 0.16 1.04 +/- 0.11 Pass AP-6345, 6346 9/30/2013 Be-7 0.077 +/- 0.010 0.081 +/- 0.008 0.079 +/- 0.006 Pass AP-6366, 6367 9/30/2013 Be-7 0.078 +/- 0.012 0.083 +/- 0.014 0.081 +/- 0.009 Pass A5-4

TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance DW-5701, 5702 9/30/2013 Gr. Beta 14.48 +/- 2.04 13.32 +/- 1.84 13.90 +/- 1.37 Pass SG-5722, 5723 9/30/2013 Ra-226 12.41 +/-+0.47 11.98 +/- 0.59 12.20 +/- 0.38 Pass SG-5722, 5723 9/30/2013 Ra-228 7.84 +/- 0.71 8.13 +/- 0.97 7.99 +/- 0.60 Pass G-5806, 5807 10/1/2013 Be-7 3.26 +/- 0.30 3.11 +/- 0.13 3.19 +/- 0.16 Pass G-5806, 5807 10/1/2013 K-40 6.65 +/- 0.21 6.68 +/- 0.50 6.67 +/- 0.27 Pass SG-5827, 5828 10/1/2013 Ac-228 4.08 +/- 0.33 3.92 +/- 0.40 4.00 +/- 0.26 Pass SG-5827, 5828 10/1/2013 K-40 2.55 +/- 0.65 2.37 +/- 0.63 2.46 +/- 0.45 Pass SG-5827, 5828 1011/2013 Pb-214 3.82 +/- 0.17 3.93 +/- 0.20 3.88 +/-0.13 Pass VE-5848, 5849 10/1/2013 K-40 1.62 +/- 0.16 1.57 +/- 0.14 1.60 +/- 0.11 Pass AP-6408, 6409 10/3/2013 Be-7 0.072 +/- 0.015 0.063 +/- 0.012 0.068 +/- 0.010 Pass f-5954, 5955 10/3/2013 K-40 2.74 +/- 0.36 3.02 +/- 0.34 2.88 +/- 0.25 Pass P-6035, 6036 10/7/2013 H-3 198.41 +/- 85.00 288.60 +/- 89.15 243.51 +/- 61.59 Pass SG-6115, 6116 10/8/2013 Ac-228 5.22 +/- 0.50 4.87 +/- 0.48 5.05 +/- 0.35 Pass SG-6115, 6116 10/8/2013 K-40 5.61 +/- 1.08 6.61 +/- 1.04 6.11 +/- 0.75 Pass SG-6115, 6116 10/8/2013 Pb-214 4.29 +/- 0.24 4.24 +/- 0.20 4.27 +/- 0.16 Pass VE-6136, 6137 10/8/2013 Be-7 0.55 +/- 0.18 0.60 +/- 0.15 0.58 +/- 0.12 Pass VE-6136, 6137 10/812013 K-40 2.78 +/- 0.35 2.61 +/- 0.33 2.69 +/- 0.24 Pass WW-6198, 6199 10/8/2013 H-3 12973.70 +/- 332.60 12757.80 +/- 330.00 12865.75 +/- 234.27 Pass VE-6240, 6241 10/9/2013 K-40 14.29 +/- 0.29 14.95 +/- 0.54 14.62 +/- 0.31 Pass W-5996, 5997 10/9/2013 Gr. Alpha 3.87 +/- 1.18 4.07 +/- 1.08 3.97 +/- 0.80 Pass W-5996, 5997 10/9/2013 Gr. Beta 9.82 +/- 0.85 8.53 +/- 0.82 9.18 +/- 0.59 Pass W-5996, 5997 10/9/2013 Ra-228 3.42 +/- 1.02 3.39 +/- 1.01 3.41 +/- 0.72 Pass DW-40224, 40225 10/11/2013 Ra-226 0.62 +/- 0.10 0.76 +/- 0.10 0.69 +/- 0.07 Pass DW-40224, 40225 10/11/2013 Ra-228 0.87 +/- 0.55 1.00 +/- 0.54 0.94 +/- 0.39 Pass WW-6219, 6220 10/11/2013 H-3 455.41 +/- 111.54 354.66 +/- 107.84 405.03 +/- 77.57 Pass CF-6261, 6262 10/14/2013 Be-7 1.97 +/- 0.24 2.06 +/- 0.22 2.01 +/- 0.16 Pass CF-6261, 6262 10/14/2013 K-40 11.55 +/- 0.56 12.06 +/- 0.61 11.80 +/- 0.41 Pass MI-6303, 6304 10/14/2013 K-40 1507.30 +/- 110.80 1482.40 +/- 110.00 1494.85 +/- 78.07 Pass VE-6534, 6535 10/17/2013 K-40 15.96 +/- 0.17 16.16 +/- 0.36 16.06 +/- 0.20 Pass S-6471, 6472 10/18/2013 Ac-228 0.94 +/- 0.19 0.78 +/- 0.18 0.86 +/- 0.13 Pass S-6471, 6472 10/18/2013 K-40 12.82 +/- 1.05 12.90 +/- 1.17 12.86 +/- 0.79 Pass S-6471, 6472 10/18/2013 Pb-214 0.88 +/- 0.11 0.72 +/- 0.12 0.80 +/- 0.08 Pass VE-6597, 6598 10/22/2013 K-40 2.46 +/- 0.22 2.58 +/- 0.20 2.52 +/- 0.15 Pass WW-6576, 6577 10/22/2013 H-3 745.60 +/- 110.70 663.30 +/- 107.60 704.45 +/- 77.19 Pass LW-6681, 6682 10/29/2013 Gr. Beta 2.00 +/- 0.92 2.17 +/- 0.98 2.09 +/- 0.67 Pass SWU-6765, 6766 10/29/2013 Gr. Beta 3.07 +/- 0.61 2.90 +/- 0.65 2.99 +/- 0.45 Pass WW-6849, 6850 10/29/2013 H-3 863.00 +/- 113.80 826.60 +/- 112.50 844.80 +/- 80.01 Pass MI-6786, 6787 10/30/2013 K-40 1370.60 +/- 109.60 1449.20 +/- 105.50 1409.90 +/- 76.06 Pass SO-6744, 6745 10/30/2013 Ac-228 0.46 +/- 0.11 0.51 +/- 0.11 0.48 +/- 0.08 Pass SO-6744, 6745 10130/2013 Bi-214 0.48 +/- 0.10 0.30 +/- 0.10 0.39 +/- 0.07 Pass SO-6744, 6745 10/30/2013 Cs-1 37 0.21 +/- 0.04 0.24 +/- 0.04 0.23 +/- 0.03 Pass SO-6744, 6745 10/3012013 Gr. Beta 27.40 +/- 1.14 27.44 +/- 1.11 27.42 +/- 0.80 Pass SO-6744, 6745 10/3012013 K-40 14.93 +/- 0.88 15.20 + 0.90 15.07 +/- 0.63 Pass SO-6744, 6745 10/30/2013 Pb-212 0.43 +/- 0.04 0.40 +/- 0.05 0.42 +/- 0.03 Pass SO-6744, 6745 10/30/2013 Ra-226 1.47 +/- 0.35 1.31 + 0.36 1.39 +/- 0.25 Pass SO-6744, 6745 10/30/2013 TI-208 0.16 +/- 0.04 0.16 +/- 0.04 0.16 +/- 0.03 Pass A5-5

TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance DW-40238, 40239 10/31/2013 Ra-228 0.94 +/- 0.41 1.60 +/- 0.55 1.27 +/- 0.34 Pass WW-7018, 7019 11/1/2013 H-3 593.09 +/- 104.72 648.69 +/- 106.89 620.89 +/- 74.82 Pass CF-6870, 6871 1114/2013 K-40 12.67 +/- 0.49 13.30 +/- 0.47 12.98 +/- 0.34 Pass XW-6828, 6829 11/4/2013 K-40 97.99 +/- 55.33 160.21 +/- 74.99 129.10 +/- 46.60 Pass BS-6891, 6892 11/5/2013 Cs-137 0.018 +/- 0.010 0.018 +/- 0.009 0.018 +/- 0.007 Pass BS-6891, 6892 11/5/2013 Gr. Beta 12.41 +/- 1.74 9.97 +/- 1.57 11.19 +/- 1.17 Pass BS-6891, 6892 11/5/2013 K-40 6.49 +/- 0.33 6.28 +/- 0.40 6.39 +/- 0.26 Pass WW-6912, 6913 11/5(2013 Gr. Alpha 2.87 +/- 1.30 4.46 +/- 1.47 3.67 +/- 0.98 Pass WW-6912, 6913 11/5/2013 Gr. Beta 3.18 +/- 0.87 3.18 +/- 0.87 3.18 +/- 0.62 Pass WW-6912, 6913 11/5/2013 H-3 349.01 +/- 101.42 430.14 +/- 98.06 389.58 +/- 70.54 Pass SO-6954, 6955 11/6/2013 Cs-137 0.14 +/- 0.03 0.12 +/- 0.02 0.13 +/- 0.02 Pass SO-6954, 6955 11/6/2013 K-40 15.16 +/- 0.72 14.11 +/- 0.64 14.64 +/- 0.48 Pass S-6976, 6977 11/13/2013 K-40 22.36 +/- 0.69 22.62 +/- 0.72 22.49 +/- 0.50 Pass DW-40246, 40247 11/15/2013 Gr. Alpha 15.00 +/- 3.41 20.31 +/- 4.00 17.65 +/- 2.63 Pass CF-7102, 7103 11/18/2013 Be-7 17.79 +/- 0.51 18.09 +/- 0.80 17.94 +/- 0.48 Pass DW-40250, 40251 11/18/2013 Ra-226 27.77 +/- 2.84 26.15 +/- 2.67 26.96 +/- 1.95 Pass DW-40250, 40251 11/18/2013 Ra-228 7.91 +/- 0.94 6.32 +/- 0.84 7.12 +/- 0.63 Pass WW-7164, 7165 11/19/2013 H-3 266.90 +/- 91.10 268.90 +/- 91.20 267.90 +/- 64.45 Pass SS-7334, 7335 11/20/2013 K-40 15.51 +/- 0.72 14.14 +/- 0.80 14.83 +/- 0.54 Pass WW-7558, 7559 11/22/2013 H-3 229.86 +/- 83.89 191.77 +/- 82.05 210.82 +/- 58.67 Pass LW-7292, 7293 11/26/2013 Gr. Beta 1.92 +/- 0.75 2.38 +/- 0.77 2.15 +/- 0.54 Pass W-7229, 7230 12/1/2013 Ra-226 0.87 +/- 0.23 0.88 +/- 0.25 0.88 +/- 0.17 Pass W-7229, 7230 12/1/2013 Ra-228 3.00 +/- 0.98 3.27 +/- 1.16 3.14 +/- 0.76 Pass SG-7313, 7314 12/2/2013 Ac-228 6.33 +/- 0.23 6.69 +/- 0.30 6.51 +/- 0.19 Pass SG-7313, 7314 12/2/2013 K-40 5.47 +/- 0.61 6.24 +/- 0.74 5.86 +/- 0.48 Pass SG-7313, 7314 12/2/2013 Pb-214 5.60 +/- 0.14 5.37 +/- 0.16 5.49 +/- 0.11 Pass W-7432, 7433 12/4/2013 Gr. Beta 5.35 +/- 1.20 3.89 +/- 1.23 4.62 +/- 0.86 Pass WW-7516, 7517 12/10/2013 H-3 369.30 +/- 95.64 269.22 +/- 91.35 319.26 +/- 66.13 Pass SG-7579, 7580 12/20/2013 Ra-226 3.72 +/-0.11 3.85 +/- 0.30 3.79 +/- 0.16 Pass SG-7579, 7580 12/20/2013 Ra-228 2.38 +/- 0.18 2.77 +/- 0.44 2.58 +/- 0.24 Pass LW-7684, 7685 12/23/2013 Gr. Beta 0.84 +/- 0.51 1.96 +/- 0.61 1.40 +/- 0.40 Pass DW-40261, 40262 12/27/2013 Ra-226 0.54 +/- 0.10 0.67 +/- 0.10 0.61 +/- 0.07 Pass DW-40261, 40262 12/27/2013 Ra-228 1.09 +/- 0.51 1.12 +/- 0.43 1.11 +/- 0.33 Pass SWU-7663, 7664 12/30/2013 Gr. Beta 2.85 +/- 0.71 3.88 +/- 0.77 3.37 +/- 0.52 Pass Note: Duplicate analyses are performed on every twentieth sample received in-house. Results are not listed for those analyses with activities that measure below the LLD.

a Results are reported in units of pCi/L, except for air filters (pCi/Filter), food products, vegetation, soil, sediment (pCi/g).

A5-6

TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).

Concentration 8 Known Control Lab Code b Date Analysis Laboratory result Activity Limits c Acceptance MAAP-738 02/01/13 Am-241 0.10 +/- 0.02 0.10 0.07 -0.14 Pass MAAP-738 02/01/13 Co-57 2.58 +/- 0.06 2.36 1.65 - 3.07 Pass MAAP-738 02/01/13 Co-60 0.01 +/- 0.03 0.00 NAC Pass MAAP-738 02/01/13 Cs-1 34 1.82 +/-0.13 1.78 1.25 -2.31 Pass MAAP-738 02/01/13 Cs-1 37 2.93 +/-0.10 2.60 1.82 - 3.38 Pass MAAP-738 02/01/13 Mn-54 4.87 +/-0.13 4.26 2.98 - 5.54 Pass MAAP-738 02/01/13 Pu-238 0.12 +/- 0.02 0.13 0.09 -0.17 Pass MAAP-738 02/01/13 Pu-239/40 0.11 +/-0.02 0.12 0.09 -0.16 Pass MAAP-738 02/01/13 Sr-90 1.39 +/- 0.14 1.49 1.04-1.94 Pass MAAP-738 02/01/13 U-233/4 0.03 +/- 0.01 0.03 0.02 - 0.04 Pass MAAP-738 02/01/13 U-238 0.23 +/- 0.03 0.23 0.16 -0.30 Pass MAAP-738 02/01/13 Zn-65 3.84 +/- 0.20 3.13 2.19 -4.07 Pass MAAP-738 8 02/01/13 Gr. Alpha 0.14 +/- 0.03 1.20 0.36 - 2.04 Fail MAAP-738 02/01/13 Gr. Beta 0.93 +/- 0.06 0.85 0.43 - 1.28 Pass MAW-806 02/01/13 Am-241 0.71 +/- 0.08 0.69 0.48 - 0.90 Pass MAW-806 02/01/13 Co-57 31.20 +/- 0.40 30.90 21.60 -40.20 Pass MAW-806 02/01/13 Co-60 19.70 +/- 0.30 16.56 13.69 - 25.43 Pass MAW-806 02/01/13 Cs-1 34 23.20 +/- 0.50 24.40 17.10 - 31.70 Pass MAW-806 02/01/13 Cs-137 0.03 +/- 0.12 0.00 NAC Pass MAW-806 02/01/13 Fe-55 34.00 +/- 3.30 44.00 30.80 - 57.20 Pass MAW-806 02/01/13 H-3 511.60 +/- 12.50 507.00 355.00 - 659.00 Pass MAW-806 02/01/13 K-40 2.20 +/- 0.90 0.00 NAc Pass MAW-806 02/01/13 Mn-54 27.60 +/- 0.50 27.40 19.20 -35.60 Pass MAW-806 02/01/13 Ni-63 34.30 +/- 2.80 33.40 23.40 - 43.40 Pass MAW-806 02/01/13 Pu-238 0.83 +/- 0.10 0.88 0.62 -1.15 Pass NA d MAW-806 02/01/13 Pu-239/40 0.02 +/- 0.02 0.01 Pass MAW-806 02/01/13 Sr-90 9.30 +/- 0.80 10.50 7.40 - 13.70 Pass MAW-806 02/01/13 Tc-99 10.25 +/- 0.40 13.10 9.20 - 17.00 Pass MAW-806 02/01/13 U-233/4 0.31 +/- 0.05 0.32 0.22 - 0.41 Pass MAW-806 02/01/13 U-238 1.91 +/- 0.13 1.95 1.37 -2.54 Pass MAW-806 02/01/13 Zn-65 31.60 +/- 0.80 30.40 21.30 -39.50 Pass MAW-811 02/01/13 Gr. Alpha 1.87 +/- 0.09 2.31 0.69 - 3.93 Pass MAW-811 02/01/13 Gr. Beta 13.04 +/- 0.13 13.00 6.50 - 19.50 Pass MAW-811 02/01/13 1-129 4.60 +/- 0.19 6.06 4.24 - 7.88 Pass A6-1

TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).

Concentration a Known Control Lab Code b Date Analysis Laboratory result Activity Limits c Acceptance MASO-739 02/01/13 Am-241 106.90 +/- 11.40 113.00 79.00 - 147.00 Pass MASO-739 02/01/13 Co-57 0.60 +/- 0.50 0.00 NA c Pass MASO-739 02/01/13 Co-60 739.20 +/- 28.50 691.00 484.00 - 898.00 Pass MASO-739 02/01/13 Cs-1 34 863.30 +/- 34.10 887.00 621.00 -1153.00 Pass MASO-739 02/01/13 Cs-1 37 661.80 +/- 25.70 587.00 411.00 -763.00 Pass MASO-739 02/01/13 K-40 745.80 +/- 33.30 625.30 437.70 -812.90 Pass MASO-739 02/01/13 Mn-54 1.10 +/- 1.00 0.00 NA c Pass MASO-739 02/01/13 Zn-65 1109.60 +/- 44.10 995.00 697.00 - 1294.00 Pass MASO-744 02/01/13 Ni-63 682.60 +/- 16.80 670.00 469.00 - 871.00 Pass MASO-744 02/01/13 Pu-238 0.20 +/- 0.90 0.52 NA d Pass MASO-744 02/01/13 Pu-239/40 88.30 +/- 9.00 79.50 55.70 - 103.40 Pass MASO-744 02/01/13 Sr-90 408.40 +/- 14.00 628.00 440.00 - 816.00 Fail MASO-744 02/01/13 Tc-99 380.50 +/- 16.80 444.00 311.00 - 577.00 Pass MASO-744 02/01/13 U-233/4 53.20 +/- 4.80 62.50 43.80 -81.30 Pass MASO-744 02/01/13 U-238 242.10 +/- 10.20 281.00 197.00 - 365.00 Pass MAVE-747 02/01/13 Co-57 10.37 +/- 0.17 8.68 6.08 -11.28 Pass MAVE-747 02/01/13 Co-60 6.48 +/- 0.17 5.85 4.10 -7.61 Pass MAVE-747 02/01/13 Cs-134 0.02 +/- 0.04 0.00 NA c Pass MAVE-747 02/01/13 Cs-1 37 7.79 +/- 0.21 6.87 4.81 - 8.93 Pass MAVE-747 02/01/13 Mn-54 0.00 +/- 0.05 0.00 NA c Pass MAVE-747 02/01/13 Zn-65 7.29 +/- 0.33 6.25 4.38 -8.13 Pass MASO-5043 08/01/13 Am-241 1.40 +/- 1.70 0.00 NA c Pass MASO-5043 g 08/01/13 Co-57 699.60 +/- 3.90 0.00 NA c Fail MASO-5043 08/01/13 Cs-1 34 1191.70 +/- 23.00 1172.00 820.00 - 1524.00 Pass MASO-5043 08/01/13 Cs-1 37 1072.00 +/- 5.10 977.00 684.00 - 1270.00 Pass MASO-5043 08/01/13 K-40 760.00 +/- 16.20 633.00 443.00 - 823.00 Pass MASO-5043 08/01/13 Mn-54 753.80 +/- 4.90 674.00 472.00 - 876.00 Pass MASO-5043 08/01/13 Ni-63 560.00 +/- 23.70 571.00 400.00 - 742.00 Pass MASO-5043 08/01/13 Pu-238 68.40 +/- 7.50 61.50 43.10 - 80.00 Pass 0.40 +/- 0.80 NA d Pass MASO-5043 08/01/13 Pu-239/40 0.36 MASO-5043 08/01/13 Sr-90 383.90 +/- 14.50 460.00 322.00 - 598.00 Pass MASO-5043 08/01/13 Tc-99 -1.00 +/- 10.50 0.00 NAc Pass MASO-5043 08/01/13 U-233/4 23.80 +/- 3.30 30.00 21.00 - 39.00 Pass MASO-5043 08/01/13 U-238 26.80 +/- 3.50 34.00 23.80 -44.20 Pass MASO-5043 08/01/13 Zn-65 -351.50 +/- 5.50 0.00 NAC Pass A6-2

TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).

Concentration a Known Control Lab Code b Date Analysis Laboratory result Activity Limits c Acceptance MAW-5052 08/01/13 1-129 2.75 +/- 0.20 3.79 2.65 -4.93 Pass MAW-5094 08/01/13 Am-241 0.00 +/- 0.01 0.00 NA Pass MAW-5094 08/01/13 Co-57 0.01 +/- 0.09 0.00 NA Pass MAW-5094 08/01/13 Co-60 23.20 +/- 0.32 23.58 16.51 - 30.65 Pass MAW-5094 08/01/13 Cs-134 27.60 +/- 0.58 30.40 21.00 - 39.00 Pass MAW-5094 08/01/13 Cs-137 32.31 +/-0.52 31.60 22.10 -41.10 Pass MAW-5094 08/01/13 Fe-55 39.20 +/- 3.50 53.30 37.30 - 69.30 Pass MAW-5094 08/01/13 Gr. Alpha 0.54 +/- 0.05 0.70 0.21 - 1.19 Pass MAW-5094 08/01/13 Gr. Beta 5.85 +/- 0.09 5.94 2.97 -8.91 Pass MAW-5094 08/01/13 H-3 1.20 +/- 3.00 0.00 NA c Pass MAW-5094 08/01/13 K-40 2.22 +/- 0.90 0.00 NA c Pass MAW-5094 08/01/13 Mn-54 0.01 +/- 0.11 0.00 NA c Pass MAW-5094 08/01/13 Ni-63 21.80 +/- 3.30 26.40 18.50 - 34.30 Pass MAW-5094 08/01/13 Pu-238 1.30 +/- 0.11 1.22 0.85 -1.58 Pass MAW-5094 08/01/13 Pu-239/40 0.98 +/- 0.09 1.00 0.70 -1.30 Pass MAW-5094 08/01/13 Sr-90 6.40 +/- 0.60 7.22 5.05 -9.39 Pass MAW-5094 08101113 Tc-99 13.10 +/- 0.70 16.20 11.30 - 21.10 Pass MAW-5094 08/01/13 U-233/4 0.08 +/- 0.02 0.07 NA d Pass MAW-5094 08/01/13 U-238 0.03 +/- 0.01 0.03 NA d Pass MAW-5094 08/01/13 Zn-65 35.30 +/- 0.90 34.60 24.20 - 45.00 Pass MAVE-5046 08/01/13 Co-57 0.01 +/- 0.03 0.00 NA c Pass MAVE-5046 08/01/13 Co-60 0.00 +/- 0.04 0.00 NA' Pass MAVE-5046 08/01/13 Cs-134 5.71 +/- 0.23 5.20 3.64 -6.76 Pass MAVE-5046 08/01/13 Cs-137 7.64 +/- 0.20 6.60 4.62 -8.58 Pass MAVE-5046 08/01/13 Mn-54 9.08 +/- 0.24 7.88 5.52 - 10.24 Pass MAVE-5046 08/01/13 Zn-65 2.92 +/- 0.25 2.63 1.84 -3.42 Pass A6-3

TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).

Concentration a Known Control Lab Code b Date Analysis Laboratory result Activity Limits ' Acceptance MAAP-5046 08/01/13 Am-241 0.01 +/- 0.02 0.00 NA C Pass MAAP-5046 08/01/13 Co-57 3.48 +/- 0.14 3.40 1.90 -3.50 Pass MAAP-5046 08/01/13 Co-60 2.44 +/- 0.08 3.40 1.60 -3.00 Pass MAAP-5046 08/01/13 Cs-134 0.01 +/- 0.03 0.00 NA c Pass MAAP-5046 08/01/13 Cs-137 3.09 +/- 0.13 2.70 1.90 -3.50 Pass MAAP-5046 08/01/13 Gr. Alpha 0.28 +/- 0.04 0.90 0.27-1.53 Pass MAAP-5046 08/01/13 Gr. Beta 1.90 +/- 0.08 1.63 0.82 -2.45 Pass MAAP-5046 08/01/13 Mn-54 3.95 +/- 0.12 3.50 2.50 -4.60 Pass MAAP-5046 08/01/13 Pu-238 0.14 +/- 0.028 0.12 0.087 -0.16 Pass MAAP-5046 08/01/13 Pu-239/40 0.10 +/- 0.022 0.092 0.064 -0.12 Pass MAAP-5046 08/01/13 Sr-90 1.69 +/- 4.10 1.81 1.27 -2.35 Pass MAAP-5046 h 08/01/13 U-233/4 0.04 +/- 0.01 0.03 0.02 -0.04 Fail MAAP-5046 08/01/13 U-238 0.19 +/- 0.027 0.21 0.14 -0.27 Pass MAAP-5046 08/01/13 Zn-65 3.27 +/- 0.18 2.70 2.50 -4.60 Pass a Results are reported in units of Bq/kg (soil), Bq/L (water) or Bq/total sample (filters, vegetation).

b Laboratory codes as follows: MAW (water), MAAP (air filter), MASO (soil), MAVE (vegetation).

cMAPEP results are presented as the known values and expected laboratory precision (1 sigma, 1 determination) and control limits as defined by the MAPEP. A known value of "zero" indicates an analysis was included inthe testing series as a "false positive". MAPEP does not provide control limits.

d Provided inthe series for "sensitivity evaluation". MAPEP does not provide control limits.

0 The filter was recounted overnight, no significant alpha activity could be detected.

t The sample was reanalyzed using additional fuming nitric separations. Result of reanalysis: 574.4 +/- 35.2 Bq/kg.

g Interference from Eu-1 52 resulted in misidentification of Co-57.

h Result of repeat analysis: 0.031 +/- 0.013 pCi/filter.

A6-4

TABLE A-7. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.

Concentration (pCi/L) b Lab Code b Date Analysis Laboratory ERA Control Result c Result d Limits Acceptance ERAP-1 174 03/18/13 Am-241 65.2 +/- 4.4 66.8 41.2 -90.4 Pass ERAP-1 174 03/18/13 Co-60 226.5 +/- 4.1 214.0 166.0 - 267.0 Pass ERAP-1174 03/18/13 Cs-1 34 1101.2 +/- 23.6 1110.0 706.0 - 1380.0 Pass ERAP-1 174 03/18/13 Cs-1 37 1065.6 +/- 21.4 940.0 706.0 - 1230.0 Pass ERAP-1 174 03/18/13 Fe-55 178.8 +/- 88.0 225.0 69.8 - 440.0 Pass ERAP-1 174 03/18/13 Mn-54 <3.1 0.0 0.0 - 50.0 Pass ERAP-1 174 03/18/13 Pu-238 50.0 +/- 3.0 51.1 34.3 - 65.9 Pass ERAP-1 174 03/18/13 Pu-239/40 65.7 +/- 2.6 65.2 47.2 - 85.2 Pass ERAP-1 174 03/18/13 U-233/4

  • 54.0 +/- 2.5 59.4 36.8 - 89.6 Pass ERAP-1 174 03/18/13 U-238 55.6 +/- 2.6 58.9 38.1 -81.4 Pass ERAP-1 174 03/18/13 Uranium 112.0 +/-5.6 121.0 67.0 - 184.0 Pass ERAP-1 174 03/18/13 Zn-65 236.6 +/- 13.8 199.0 142.0 - 275.0 Pass ERAP-1175 03/18/13 Gr. Alpha 52.3 +/- 2.8 42.3 14.2 - 65.7 Pass ERAP-1 175 03/18/13 Gr. Beta 36.2 +/- 2.0 25.1 15.9 -36.6 Pass ERSO-1176 03/18/13 Am-241 293.1 +/- 97.4 229.0 134.0 - 297.0 Pass ERSO-1176 03/18/13 Pu-238 909.0 +/- 180.0 788.0 474.0 - 1090.0 Pass ERSO-1 176 03/18/13 Pu-239/40 432.0 +/- 120.0 366.0 239.0 - 506.0 Pass ERSO-1176 03/18/13 Sr-90 8050.8 +/- 376.0 8530.0 3250.0 - 13500.0 Pass ERSO-1176 03/18/13 U-233/4 1662.6 +/- 150.0 1920.0 1170.0 - 2460.0 Pass ERSO-1176 03/18/13 U-238 1682.8 +/- 160.0 1900.0 1180.0 - 2410.0 Pass ERSO-1176 03/18/13 Uranium 3404.0 +/- 330.5 3920.0 2130.0 - 5170.0 Pass ERSO-1 176 03/18/13 Ac-228 1335.0 +/- 132.0 1240.0 795.0 - 1720.0 Pass ERSO-1 176 03/18/13 Bi-212 1420.0 +/- 311.0 1240.0 330.0 - 1820.0 Pass ERSO-1176 03/18/13 Bi-214 2626.0 +/- 60.0 3660.0 2200.0 - 5270.0 Pass ERSO-1 176 03/18/13 Co-60 7951.0 +/- 45.4 7920.0 5360.0 - 10900.0 Pass ERSO-1176 03/18/13 Cs-134 5785.0 +/- 51.0 6370.0 4160.0 - 7650.0 Pass ERSO-1 176 03/18/13 Cs-1 37 6106.0 +/- 47.9 6120.0 4690.0 - 7870.0 Pass ERSO-1 176 03/18/13 K-40 11756.0 +/- 284.3 10300.0 7520.0 - 13800.0 Pass ERSO-1176 03/18/13 Mn-54 < 28.0 0.0 0.0 - 1000.0 Pass ERSO-1 176 03/18/13 Pb-212 1096.0 +/- 29.1 1240.0 812.0 - 1730.0 Pass ERSO-1 176 03/18/13 Pb-214 2875.0 +/- 60.0 3660.0 2140.0 - 5460.0 Pass ERSO-1 176 03/18/13 Th-234 2404.0 +/- 218.3 1900.0 601.0 - 3570.0 Pass ERSO-1 176 03/18/13 Zn-65 1542.0 +/- 56.4 1400.0 1110.0 - 1860.0 Pass A7-1

TABLE A-7. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)".

Concentration (pCi/L) b Lab Code b Date Analysis Laboratory ERA Control Result c Result d Limits Acceptance ERVE-1 180 03/18/13 Am-241 569.8 +/- 81.7 553.0 338.0 - 735.0 Pass ERVE-1 180 03/18/13 Cm-244 1260.9 +/- 107.3 1340.0 657.0 -2090.0 Pass ERVE-1 180 03/18/13 Co-60 2130.5 +/- 48.0 1920.0 1320.0 - 2680.0 Pass ERVE-1 180 03/18/13 Cs-1 34 1296.5 +/- 68.0 1240.0 797.0 - 1610.0 Pass ERVE-1 180 03/18/13 Cs-137 600.1 +/- 34.3 544.0 394.0 - 757.0 Pass ERVE-1 180 03/18/13 K-40 34078.0 +/- 787.0 31900.0 23000.0 - 44800.0 Pass ERVE-1 180 03/18/13 Mn-54 < 28.7 0.0 0.0 - 300.0 Pass ERVE-1 180 03/18/13 Pu-238 2476.5 +/- 259.4 1980.0 1180.0 -2710.0 Pass ERVE-1 180 03/18/13 Pu-239/40 2659.3 +/- 273.2 2260.0 1390.0 -3110.0 Pass ERVE-1 180 03/18/13 Sr-90 3809.7 +/- 420.5 3840.0 2190.0 - 5090.0 Pass ERVE-1 180 03/18/13 U-233/4 2460.6 +/- 205.0 2460.0 1620.0 - 3160.0 Pass ERVE-1 180 03/18/13 U-238 2319.1 +/- 189.6 2440.0 1630.0 -3100.0 Pass ERVE-1180 03/18/13 Uranium 4866.3 +/- 375.6 5010.0 3390.0 - 6230.0 Pass ERVE-1 180 03/18/13 Zn-65 1052.5 +/- 82.1 878.0 633.0 - 1230.0 Pass ERW-1 184 03/18/13 Am-241 114.5 +/-8.1 118.0 79.5 -158.0 Pass ERW-1184 03/18/13 Co-60 2221.8 +/- 17.0 2270.0 1970.0 - 2660.0 Pass ERW-1184 03/18/13 Cs-1 34 1309.4 +/- 58.4 1400.0 1030.0 -1610.0 Pass ERW-1184 03/18/13 Cs-137 1865.9 +/- 22.0 1880.0 1600.0 -2250.0 Pass ERW-1184 03/18/13 Fe-55 503.1 +/- 105.0 712.0 424.0 - 966.0 Pass ERW-1184 03/18/13 Mn-54 < 9.4 0.0 0.0 - 100.0 Pass ERW-1184 03/18/13 Pu-238 98.4 +/- 5.6 98.8 73.1 -123.0 Pass ERW-1184 03/18/13 Pu-239/40 184.5 +/- 7.7 185.0 144.0 -233.0 Pass ERW-1184 03/18/13 Sr-90 125.7 +/-6.0 137.0 89.2 -181.0 Pass ERW-1184 03/18/13 U-233/4 44.9 +/- 3.4 48.8 36.7 -62.9 Pass ERW-1184 03/18/13 U-238 46.5 +/- 3.5 48.4 36.9 - 59.4 Pass ERW-1184 03/18/13 Uranium 93.3 +/- 7.1 99.5 73.1 -129.0 Pass ERW-1184 03/18/13 Zn-65 412.8 +/- 32.0 384.0 320.0 - 484.0 Pass ERW-1 186 03/18/13 Gr. Alpha 109.1 +/-5.7 130.0 46.2 -201.0 Pass ERW-1186 03/18/13 Gr. Beta 74.5 +/- 6.4 78.9 45.2 -117.0 Pass ERW-1188 03/18/13 H-3 12279.0 +/- 319.0 12300.0 8240.0 - 17500.0 Pass a Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the crosscheck program for proficiency testing administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the Environmental Measurements Laboratory Quality Assessment Program (EML).

Laboratory codes as follows: ERW (water), ERAP (air filter), ERSO (soil), ERVE (vegetation). Results are reported in units of pCi/L, except for air filters (pCi/Filter), vegetation and soil (pCi/kg).

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

d Results are presented as the known values, expected laboratory precision (1 sigma, 1 determination) and control limits as provided by ERA. A known value of "zero" indicates an analysis was included in the testing series as a "false positive". Control limits are not provided.

A7-2

Appendix B Summary Tables in the format of NRC Radiological Assessment Branch Technical Position Revision 1, November 1979 Page B-1

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Name of Facility: Wolf Creek Generating Station Docket No.: 50-482 Location of Facility: Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection ** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction ** Range ** Range Measurements **

Air Particulate Station 53 (pCi/m 3) Gross Beta (318) 0.01 0.026 (265/265) 49 0.027 (53/53) 0.026 (53/53) 0 (0.009 - 0.050) 0.8 miles NNE (0.013 - 0.050) (0.011 - 0.052)

Gamma (24)

Be-7 0.076 (20/20) 32 0.081 (4/4) 0.076 (4/4) 0 (0.052 - 0.092) 3.1 miles WNW (0.070 - 0.088) (0.063 - 0.087)

Air Radioiodine Station 53 (pCi/mi3 ) 1-131 (318) 0.07 -(0/265) N/A N/A - (0/53) 0 Direct Radiation Stations 39 & 53 Dosimeters (mR per std. Gamma Dose 18.7 (164/164) 47 24.2 (4/4) 19.5 (8/8) 0 90-day Qtr.) (172) (12.3 - 27.6) 0.16 miles S (20.4 - 27.6) (15.4 - 21.5)

Surface Water JRR (pCi/I) Gamma (24) - (0/12) N/A N/A - (0/12) 0 Tritium (24) 3,000 11,100 (12/12) SP 11,100 (12/12) - (0/12) 0 (9,295-13,170) 3.2 miles SSE (9,295-13,170)

Fe-55 (8) - (0/4) N/A N/A - (0/4) 0 Ground Water B-12 (pCi/I) 1-131 (32) 1 - (0/28) N/A N/A - (0/4) 0 Gamma (32) - (0/28) N/A N/A - (0/4) 0 Tritium (32) 2,000 - (0/28) N/A N/A - (0/4) 0 Page B-2

    • Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Name of Facility: Wolf Creek Generating Station Docket No.: 50-482 Location of Facility: Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection ** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction ** Range ** Range Measurements **

Drinking BW-1 5 Water 1-131 (24) 1 -(0/12) N/A N/A - (0/12) 0 (pCi/I)

Gross Beta (24) 4 2.9 (12/12) 1O-DW 2.9 (12/12) 3.1 (12/12) 0 (2.0 - 4.0) 26.1 miles SSE (2.0-4.0) (2.2-4.0)

Gamma (24) - (0/12) N/A N/A - (0/12) 0 Tritium (8) 2,000 -(0/4) N/A N/A - (0/4) 0 Shoreline Gamma (6) JRR Sediment (pCi/kg dry) K-40 - 9,209 (4/4) EEA 11,557 (2/2) 11,994 (2/2) 0 (6,368 - 11,893) 3.0 miles NNW (11,221-11,893) (10,926- 13,061)

Cs-1 37 180 89(1/4) EEA 89 (1/2) - (0/2) 0 3.0 miles NNW Fish Gamma (16) JRR (pCi/kg wet)

K-40 - 3,129 (10/10) CCL 3,129 (10/10) 3,416 (6/6) 0 (2,698 - 3,690) 0.6 miles E to (2,698 - 3,690) (2,990 - 3,669)

NNW Tritium (16) - 7,743 (10/10) CCL 7,743 (10/10) - (0/6) 0 (6,985 - 8,852) 0.6 miles E to (6,985 - 8,852)

NNW Page B-3

    • Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Name of Facility: Wolf Creek Generating Station Docket No.: 50-482 Location of Facility: Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection ** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction ** Range ** Range Measurements **

Food and Gamma (18) D-2 Garden (pCi/kg wet) Be-7 657 (11/12) Q-6 1,031 (2/2) 756 (5/6) 0 (281 - 1,691) 2.4 miles NW (372- 1,691) (397 - 1,259)

K-40 - 5,346 (12/12) H-2 5,640 (4/4) 5,871 (6/6) 0 (4,689 - 6,915) 3.0 miles SSE (5,157 - 6,915) (4,719 - 6,804)

NR-U1 Crops Gamma (4)

(pCi/kg wet)

K-40 - 14,612 (2/2) NR-D1 16,342 (1/1) 7,606 (2/2) 0 (12,882-16,342) 8.9 miles S (2,544 - 12,669)

Bottom Gamma (19) JRR Sediment (pCi/kg dry)

K-40 10,118 (17/17) EEA 11,461 (2/2) 12,206 (2/2) 0 (5,110- 12,602) 3.0 miles NNW (11,346-11,576) (11,660 - 12,752)

Cs-137 72(12/17) DC 93(2/2) 85(1/2) 0 (38- 108) 0.9 miles WNW (90-97)

Fe-55 (14) -(0/14) N/A N/A 0 Page B-4

    • Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Name of Facility: Wolf Creek Generatinq Station Docket No.: 50-482 Location of Facility: Coffey County, Kansas Reporting Period: Annual 2013 Medium of ODCM All Indicator Indicator Location with Control Locations Pathway Analysis and Lower Locations Highest Annual Mean Number of Sampled Total Number of Limit of Name Nonroutine (Unit of Analysis Performed Detection ** Mean (f) Distance and ** Mean (f) ** Mean (f) Reported Measurement) (LLD) ** Range Direction ** Range ** Range Measurements **

Aquatic Gamma (3) No Control Vegetation (pCi/kg wet) Be-7 1,086 (2/3) DC-ALT 1,873(1/1) 0 (299 - 1,873) 1.5 miles NW K-40 3,047 (3/3) EEA 4,998 (1/1) 0 (1,861 - 4,998) 3.0 miles NNW Terrestrial Gamma (2) No Control Vegetation (pCi/kg wet) Be-7 1,424 (2/2) MUDS 1,830(1/1) 0 (1,018 - 1,830) 1.5 miles WNW K-40 6,667 (2/2) EEA 7,467 (1/1) 0 (5,868 - 7,467) 3.0 miles NNW Soil Gamma (3) No Control (pCi/kg dry)

K-40 - 10,441 (3/3) MUDS 11,641 (1/1) 0 (8,935 - 11,641) 1.5 miles WNW Cs-1 37 - 191 (3/3) EEA 212 (2/2) 0 (148-250) 3.0 miles NNW (174-250)

Deer Gamma (1) No Control (pCi/kg wet)

K-40 - 3,071 (1/1) R2.7 3,071 (1/1) 0 2.7 miles NNW Tritium (1) - 251 (1/1) R2.7 251 (1/1) 0 2.7 miles NNW Page B-5

    • Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)

Appendix C Individual Sample Results

Air Particulate and Charcoal Filters Location: 002 Collection Collection Volume Gross Beta 1-131 Duplicate 3

Start Date End Date m Concentration Concentration Analysis (pCi/m 3 ) (pCi/m 3) 31-DEC-12 07-JAN- 13 313 0.037 +1- 0.004 0.013 07-JAN-1 3 14-JAN-1 3 293 0.032 +1- 0.005 0.019 14-JAN-13 21-JAN-13 297 0.029 +1- 0.004 0.012 21-JAN-13 28-JAN-1 3 295 0.037 +1- 0.005 0.008 28-JAN-13 05-FEB-13 355 0.036 +1- 0.004 0.013 05-FEB-13 12-FEB-13 280 0.031 +1- 0.005 0.010 12-FEB-13 19-FEB-1 3 301 0.024 +1- 0.004 0.011 19-FEB-13 25-FEB-13 258 0.025 +1- 0.005 0.011 25-FEB-1 3 05-MAR-1 3 338 0.038 +1- 0.004 0.009 05-MAR-13 12-MAR-13 302 0.024 +1- 0.004 0.012 12-MAR-1 3 19-MAR-1 3 295 0.020 +1- 0.004 0.017 19-MAR-1 3 26-MAR-13 308 0.023 +1- 0.004 0.013 26-MAR- 13 01-APR-13 247 0.022 +1- 0.005 0.017 01-APR-13 08-APR-13 294 0.026 +1- 0.004 01-APR-13 08-APR- 13 294 0.017 08-APR-13 15-APR-13 300 0.016 +1- 0.004 0.006 15-APR-1 3 22-APR-1 3 309 0.016 +1- 0.004 0.007 15-APR-13 22-APR-13 309 0.017 +1- 0.004 Duplicate 22-APR-1 3 29-APR-1 3 301 0.022 +1- 0.004 0.009 29-APR-13 06-MAY-1 3 310 0.025 +1- 0.004 0.007 06-MAY-1 3 13-MAY- 13 294 0.018 +1- 0.004 0.014 06-MAY-13 13-MAY-1 3 294 0.018 +1- 0.004 Duplicate 13-MAY-1 3 20-MAY- 13 290 0.028 +1- 0.004 0.014 20-MAY- 13 28-MAY-1 3 349 0.009 +1- 0.003 0.013 28-MAY-1 3 03-JUN-13 262 0.015 +1- 0.004 0.013 03-JUN-13 10-JUN-13 288 0.020 +1- 0.004 0.011 10-JUN-13 17-JUN-13 304 0.023 +1- 0.004 0.013 17-JUN-13 24-JUN-13 301 0.026 +1- 0.004 0.010 24-JUN-13 01-JUL-13 293 0.023 +1- 0.005 0.015 01-JUL-13 08-JUL-13 296 0.021 +1- 0.004 0.011 08-JUL-13 15-JUL-13 301 0.025 +1- 0.004 0.012 15-JUL-13 22-JUL-13 298 0.015 +1- 0.004 0.010 22-JUL-13 29-JUL-13 306 0.018 +1- 0.004 0.011 29-JUL-13 05-AUG-13 297 0.026 +1- 0.004 0.010 05-AUG-13 12-AUG-13 303 0.025 +1- 0.004 0.008 12-AUG-13 19-AUG-13 297 0.025 +1- 0.004 0.012 19-AUG-13 26-AUG-13 300 0.036 +1- 0.005 0.011 26-AUG-13 03-SEP-13 339 0.023 +1- 0.004 0.014 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 1

Air Particulate and Charcoal Filters Location: 002 Collection Collection Volume Gross Beta 1-131 Duplicate Start Date End Date m3 Concentration Concentration Analysis (pCi/m 3 ) (pCi/m 3 )

03-SEP-1 3 09-SEP-13 261 0.039 +1- 0.005 < 0.017 09-SEP-13 17-SEP-1 3 349 0.029 +1- 0.004 < 0.012 17-SEP-13 23-SEP-13 255 0.027 +1- 0.005 < 0.010 23-SEP-13 30-SEP-13 294 0.032 +1- 0.005 < 0.014 30-SEP-1 3 07-OCT-13 301 0.017 +1- 0.004 < 0.007 07-OCT-13 14-OCT-13 299 0.022 +1- 0.004 < 0.020 14-OCT-1 3 21-OCT-1 3 300 0.016 +1- 0.004 < 0.015 21-OCT-13 29-OCT-1 3 337 0.020 +1- 0.004 < 0.007 29-OCT-1 3 04-NOV-1 3 260 0.019 +1- 0.005 < 0.011 04-NOV-13 11-NOV-13 299 0.019 +1- 0.004 < 0.011 11-NOV-13 18-NOV-13 306 0.025 +1- 0.004 < 0.009 18-NOV- 13 25-NOV-13 311 0.024 +1- 0.004 < 0.010 25-NOV-13 02-DEC-13 302 0.033 +1- 0.004 < 0.013 02-DEC-1 3 09-DEC-1 3 306 0.038 +1- 0.005 < 0.018 09-DEC-13 16-DEC-13 289 0.045 +1- 0.005 < 0.011 16-DEC-13 23-DEC-1 3 308 0.036 +1- 0.005 < 0.015 23-DEC-1 3 30-DEC-1 3 299 0.036 +1- 0.005 < 0.012 30-DEC-13 07-JAN-14 353 0.031 +/- 0.004 < 0.008 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 2

Air Particulate and Charcoal Filters Location: 018 Collection Collection Volume Gross Beta 1-131 Duplicate 3

Start Date End Date m Concentration Concentration Analysis (pCi/m 3 ) (pCi/m 3 )

31-DEC-1 2 07-JAN-13 315 0.046 +1- 0.005 0.013 07-JAN-13 14-JAN-1 3 299 0.037 +1- 0.005 0.019 14-JAN-1 3 21-JAN-13 297 0.029 +1- 0.004 0.012 21-JAN-13 28-JAN-13 302 0.041 +1- 0.005 0.008 28-JAN-13 05-FEB-1 3 349 0.036 +1- 0.004 0.014 05-FEB-13 12-FEB-13 302 0.032 +1- 0.004 0.009 12-FEB-1 3 19-FEB-1 3 304 0.024 +1- 0.004 0.011 19-FEB-1 3 25-FEB-13 257 0.027 +1- 0.005 0.011 25-FEB-13 05-MAR-1 3 340 0.036 +1- 0.004 0.009 05-MAR-1 3 12-MAR-13 299 0.026 +1- 0.004 Duplicate 05-MAR-13 12-MAR- 13 299 0.023 4/- 0.004 0.012 12-MAR- 13 19-MAR-1 3 300 0.028 +1- 0.004 0.017 19-MAR-1 3 26-MAR- 13 311 0.021 +1- 0.004 0.013 26-MAR-13 01-APR-13 248 0.025 +1- 0.005 0.017 01-APR-13 08-APR-13 293 0.023 +1- 0.004 01-APR-13 08-APR-1 3 293 0.021 4/- 0.004 Duplicate 01-APR-13 08-APR-13 293 0.017 08-APR-13 15-APR-13 300 0.018 +1- 0.004 0.006 15-APR- 13 22-APR-1 3 314 0.018 +1- 0.004 0.007 22-APR-13 29-APR-13 299 0.020 +1- 0.004 0.009 29-APR-13 06-MAY- 13 311 0.018 +1- 0.004 0.007 06-MAY-1 3 13-MAY-1 3 294 0.023 +1- 0.004 0.014 13-MAY- 13 20-MAY-13 298 0.025 +1- 0.004 Duplicate 13-MAY- 13 20-MAY-13 298 0.030 +1- 0.004 0.014 20-MAY-1 3 28-MAY- 13 360 0.013 +1- 0.003 0.013 28-MAY-13 03-JUN-13 254 0.014 4/- 0.004 0.013 03-JUN-13 10-JUN-13 295 0.020 +1- 0.004 0.011 10-JUN-13 17-JUN-13 310 0.021 +1- 0.004 0.013 17-JUN-13 24-JUN-13 303 0.025 4/- 0.004 0.010 24-JUN-13 01-JUL-13 299 0.022 +1- 0.004 0.015 01-JUL-13 08-JUL-13 302 0.026 +1- 0.005 0.011 08-JUL-13 15-JUL-13 300 0.021 +1- 0.004 0.012 15-JUL-13 22-JUL-13 293 0.017 +1- 0.004 0.010 22-JUL-13 29-JUL-13 303 0.023 +1- 0.004 0.011 29-JUL-13 05-AUG-13 298 0.026 +1- 0.004 0.010 05-AUG-13 12-AUG- 13 298 0.023 +1- 0.004 0.008 12-AUG-13 19-AUG- 13 298 0.026 +1- 0.004 0.012 19-AUG-13 26-AUG-13 306 0.034 +1- 0.005 0.010 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 3

Air Particulate and Charcoal Filters Location: 018 Collection Collection Volume 3

Gross Beta 1-131 Duplicate m

Start Date End Date Concentration Concentration Analysis (pCi/m 3 ) (pCilm 3) 26-AUG-13 03-SEP-13 337 0.024 +1- 0.004 0.014 03-SEP-13 09-SEP-1 3 263 0.041 +1- 0.005 0.017 09-SEP-13 17-SEP-13 349 0.028 +1- 0.004 0.012 17-SEP-13 23-SEP-13 254 0.029 +1- 0.005 0.010 23-SEP-1 3 30-SEP-13 303 0.033 +1- 0.005 0.014 30-SEP-13 07-OCT-1 3 297 0.016 +1- 0.004 0.007 07-OCT-1 3 14-OCT-13 302 0.024 +1- 0.004 0.020 14-OCT-1 3 21-OCT-13 302 0.016 +1- 0.004 0.015 21-OCT- 13 29-OCT-1 3 342 0.024 +1- 0.004 0.007 29-OCT-1 3 04-NOV-13 260 0.023 +1- 0.005 0.011 04-NOV-13 11-NOV-13 307 0.018 +1- 0.004 0.011 11-NOV-13 18-NOV- 13 312 0.024 +1- 0.004 0.009 18-NOV-13 25-NOV-1 3 318 0.025 +1- 0.004 0.009 25-NOV-13 02-DEC-1 3 305 0.035 +1- 0.004 0.013 02-DEC-13 09-DEC-13 315 0.037 +1- 0.004 0.017 09-DEC-1 3 16-DEC-1 3 296 0.047 +1- 0.005 0.011 16-DEC-1 3 23-DEC-1 3 308 0.037 +1- 0.005 0.015 23-DEC-13 30-DEC-13 294 0.037 +1- 0.005 0.013 30-DEC-1 3 07-JAN-1 4 351 0.036 +1- 0.004 0.008 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 4

Air Particulate and Charcoal Filters Location: 032 Collection Collection Volume Gross Beta 1-131 Duplicate m 3 Start Date End Date Concentration Concentration Analysis (pCi/m 3 ) (pCi/m 3 )

31-DEC-1 2 07-JAN-13 318 0.046 +1- 0.005 0.013 07-JAN-1 3 14-JAN-1 3 296 0.034 +1- 0.005 0.019 14-JAN-1 3 21-JAN-13 297 0.024 +1- 0.004 0.012 21-JAN-13 28-JAN-1 3 307 0.036 +1- 0.005 0.008 28-JAN-1 3 05-FEB-13 347 0.035 +1- 0.004 0.014 05-FEB-1 3 12-FEB-1 3 304 0.030 +1- 0.004 0.009 12-FEB-13 19-FEB-13 302 0.023 +1- 0.004 0.011 19-FEB-1 3 25-FEB-13 254 0.029 +1- 0.005 0.011 25-FEB-13 05-MAR-1 3 343 0.036 .1-I- 0.004 0.009 05-MAR-13 12-MAR-13 302 0.023 +1- 0.004 0.012 12-MAR-1 3 19-MAR-1 3 300 0.028 +1- 0.004 0.017 19-MAR-13 26-MAR-1 3 309 0.022 +1- 0.004 0.013 26-MAR-1 3 01 -APR- 13 248 0.025 +1- 0.005 0.017 26-MAR-13 01-APR-13 248 0.022 +1- 0.005 Duplicate 01-APR-13 08-APR-1 3 299 < 0.017 01 -APR- 13 08-APR-13 299 0.023 +1- 0.004 08-APR-13 15-APR-1 3 304 0.017 +1- 0.004 0.006 15-APR-1 3 22-APR-13 311 0.016 +1- 0.004 0.007 22-APR-13 29-APR-13 301 0.024 +1- 0.004 0.009 29-APR-13 06-MAY- 13 306 0.014 +1- 0.004 0.007 06-MAY-1 3 13-MAY-1 3 295 0.022 +1- 0.004 0.014 13-MAY-13 20-MAY- 13 304 0.026 +1- 0.004 0.013 20-MAY-1 3 28-MAY-1 3 344 0.012 +1- 0.003 0.013 28-MAY-13 03-JUN-13 260 0.013 +1- 0.004 0.013 03-JUN-13 10-JUN-13 294 0.020 +1- 0.004 0.011 10-JUN-13 17-JUN-13 305 0.019 +1- 0.004 0.013 17-JUN-13 24-JUN-13 304 0.026 +1- 0.004 0.010 24-JUN-13 27-JUN-13 140 0.025 +1- 0.009 0.037 01-JUL-13 08-JUL-13 289 0.024 +1- 0.005 0.011 08-JUL-13 15-JUL-13 298 0.023 +1- 0.004 0.012 15-JUL-13 22-JUL-13 296 0.018 +1- 0.004 0.010 22-JUL-13 29-JUL-13 303 0.022 +1- 0.004 0.011 29-JUL-13 05-AUG-13 298 0.029 +1- 0.004 0.010 05-AUG-13 12-AUG-13 302 0.020 +1- 0.004 0.008 12-AUG-13 19-AUG-13 297 0.026 +1- 0.004 0.012 19-AUG- 13 26-AUG-13 300 0.041 +1- 0.005 0.011 26-AUG-13 03-SEP-13 335 0.025 +1- 0.004 0.015 03-SEP-1 3 09-SEP-13 264 0.038 +1- 0.005 0.017 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 5

Air Particulate and Charcoal Filters Location: 032 Collection Collection Volume Gross Beta 1-131 Duplicate m3 Start Date End Date Concentration Concentration Analysis (pCi/r 3 ) (pCi/m 3 )

09-SEP-1 3 17-SEP-13 337 0.026 +1- 0.004 0.012 17-SEP-1 3 23-SEP-13 256 0.025 +1- 0.005 0.010 23-SEP-13 30-SEP-13 296 0.036 +1- 0.005 0.014 30-SEP-1 3 07-OCT-1 3 299 0.018 +1- 0.004 0.007 07-OCT-1 3 14-OCT-1 3 300 0.023 +1- 0.004 0.020 14-OCT-1 3 21-OCT-1 3 301 0.019 +1- 0.004 0.015 21-OCT-13 29-OCT-13 341 0.021 +1- 0.004 0.007 29-OCT-1 3 04-NOV-1 3 258 0.026 +1- 0.005 0.011 04-NOV-13 11-NOV-13 311 0.018 +1- 0.004 0.011 11-NOV-13 18-NOV-13 304 0.025 +1- 0.004 0.009 18-NOV-13 25-NOV-1 3 314 0.022 +1- 0.004 0.010 25-NOV-1 3 02-DEC-1 3 308 0.036 +1- 0.004 0.012 25-NOV-13 02-DEC-13 308 0.037 +1- 0.005 Duplicate 02-DEC-13 09-DEC-1 3 305 0.039 +1- 0.005 0.018 09-DEC-1 3 16-DEC-13 289 0.045 +1- 0.005 0.011 16-DEC-1 3 23-DEC-1 3 307 0.040 +1- 0.005 0.015 23-DEC-1 3 30-DEC-13 289 0.035 +1- 0.005 0.013 30-DEC-1 3 07-JAN-14 341 0.032 +1- 0.004 0.008 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 6

Air Particulate and Charcoal Filters Location: 037 Collection Collection Volume3 Gross Beta 1-131 Duplicate m

Start Date End Date Concentration Concentration Analysis (pCi/m 3 ) (pCi/m 3) 31-DEC-12 07-JAN-1 3 321 0.045 +1- 0.005 0.013 07-JAN-1 3 14-JAN-13 297 0.034 +1- 0.005 0.019 14-JAN-13 21-JAN-1 3 296 0.025 +1- 0.004 0.012 21-JAN-13 28-JAN-1 3 301 0.037 +1- 0.005 Duplicate 21-JAN-1 3 28-JAN-1 3 301 0.039 +1- 0.005 0.008 28-JAN-13 05-FEB-1 3 360 0.034 +1- 0.004 0.013 05-FEB-13 12-FEB-13 303 0.033 +1- 0.004 0.009 05-FEB-13 12-FEB-1 3 303 0.031 +1- 0.004 Duplicate 12-FEB-13 19-FEB-13 301 0.023 +1- 0.004 0.011 19-FEB-13 25-FEB-13 260 0.026 +1- 0.005 0.010 25-FEB-1 3 05-MAR-13 345 0.034 +1- 0.004 0.009 05-MAR-13 12-MAR-1 3 300 0.024 +1- 0.004 0.012 12-MAR-1 3 19-MAR- 13 299 0.026 +1- 0.004 0.017 12-MAR- 13 19-MAR-1 3 299 0.027 +1- 0.004 Duplicate 19-MAR-1 3 26-MAR- 13 313 0.022 +1- 0.004 Duplicate 19-MAR-13 26-MAR-1 3 313 0.021 +1- 0.004 0.013 26-MAR-1 3 01-APR-13 249 0.023 +1- 0.005 0.017 01-APR-13 08-APR-1 3 295 0.017 01-APR-13 08-APR-13 295 0.021 +1- 0.004 08-APR-13 15-APR- 13 305 0.017 +1- 0.004 0.006 15-APR-13 22-APR-13 311 0.015 +1- 0.004 0.007 22-APR-13 29-APR-1 3 304 0.020 +1- 0.004 0.009 29-APR-1 3 06-MAY-1 3 309 0.017 +1- 0.004 0.007 29-APR-13 06-MAY-13 309 0.015 +1- 0.004 Duplicate 06-MAY-13 13-MAY-1 3 296 0.022 +1- 0.004 0.014 13-MAY-1 3 20-MAY-13 300 0.029 +1- 0.004 0.013 20-MAY- 13 28-MAY-1 3 347 0.011 +1- 0.003 0.013 28-MAY-1 3 03-JUN-13 257 0.014 +1- 0.004 0.013 03-JUN-13 10-JUN-13 293 0.018 +1- 0.004 0.011 10-JUN-13 17-JUN-13 303 0.019 +1- 0.004 0.013 17-JUN-13 24-JUN-13 302 0.026 +1- 0.004 0.010 24-JUN-13 01-JUL-13 288 0.027 +1- 0.005 0.015 01-JUL-13 08-JUL-13 301 0.025 +1- 0.004 0.011 08-JUL-13 15-JUL-13 299 0.023 +1- 0.004 0.012 15-JUL-13 22-JUL-13 300 0.018 +1- 0.004 0.010 22-JUL-13 29-JUL-13 307 0.018 +1- 0.004 0.011 29-JUL-13 05-AUG-13 299 0.023 +1- 0.004 0.010 05-AUG-13 12-AUG-13 285 0.028 +1- 0.005 0.009 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 7

Air Particulate and Charcoal Filters Location: 037 Collection Collection Volume Gross Beta 1-131 Duplicate Start Date End Date m3 Concentration Concentration Analysis (pCilm 3 ) (pCi/m 3) 12-AUG- 13 19-AUG-13 300 0.024 +1- 0.004 < 0.012 19-AUG-13 26-AUG-1 3 300 0.041 +1- 0.005 < 0.011 26-AUG-13 03-SEP-1 3 341 0.021 +1- 0.004 < 0.014 26-AUG-13 03-SEP-13 341 0.026 +1- 0.004 Duplicate 03-SEP-13 09-SEP-1 3 264 0.043 +1- 0.005 0.017 09-SEP-13 17-SEP-13 338 0.027 +1- 0.004 0.012 17-SEP-13 23-SEP-1 3 255 0.025 +1- 0.005 0.010 23-SEP-1 3 30-SEP-13 297 0.033 +1- 0.005 0.014 30-SEP-13 07-OCT-1 3 301 0.017 +1- 0.004 0.007 07-OCT-1 3 14-OCT-13 297 0.023 +1- 0.004 0.020 14-OCT-1 3 21-OCT-13 303 0.018 +1- 0.004 0.015 21-OCT-13 29-OCT-13 340 0.022 +1- 0.004 0.007 29-OCT-1 3 04-NOV-1 3 261 0.023 +1- 0.005 0.011 04-NOV-13 11-NOV-13 301 0.020 +1- 0.004 0.011 11 -NOV-13 18-NOV-13 308 0.022 +1- 0.004 0.009 18-NOV- 13 25-NOV-1 3 320 0.024 +1- 0.004 0.009 25-NOV-1 3 02-DEC-1 3 306 0.034 +1- 0.004 0.012 02-DEC-13 09-DEC-13 315 0.045 +1- 0.005 0.017 09-DEC-1 3 16-DEC-1 3 289 0.049 +1- 0.005 0.011 16-DEC-13 23-DEC-13 309 0.037 +1- 0.005 0.015 23-DEC-1 3 30-DEC-1 3 289 0.035 +1- 0.005 0.013 30-DEC-13 07-JAN-14 353 0.031 +1- 0.004 0.008 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 8

Air Particulate and Charcoal Filters Location: 049 Collection Collection Volume 3

Gross Beta 1-131 Duplicate m

Start Date End Date Concentration Concentration Analysis (pCi/m 3 ) (pCi/m 3 )

31-DEC-12 07-JAN-13 307 0.049 +1- 0.005 0.013 07-JAN-1 3 14-JAN-13 297 0.040 +1- 0.005 0.019 14-JAN-13 21-JAN-13 296 0.025 +1- 0.004 0.012 21-JAN-13 28-JAN-1 3 302 0.037 +1- 0.005 0.008 28-JAN-1 3 05-FEB-13 355 0.038 +1- 0.004 0.013 05-FEB-1 3 12-FEB-13 303 0.031 +1- 0.004 0.009 12-FEB-13 19-FEB-13 300 0.026 +1- 0.004 0.011 19-FEB-1 3 25-FEB-1 3 263 0.027 +1- 0.005 0.010 25-FEB-13 05-MAR-13 347 0.037 +1- 0.004 0.009 05-MAR-1 3 12-MAR-1 3 297 0.023 +1- 0.004 0.012 12-MAR-1 3 19-MAR- 13 297 0.031 +1- 0.004 0.017 19-MAR- 13 26-MAR-1 3 312 0.023 +1- 0.004 0.013 26-MAR-1 3 01-APR-13 248 0.026 +1- 0.005 0.017 01-APR-13 08-APR-13 294 0.017 01-APR-13 08-APR-1 3 294 0.021 +1- 0.004 08-APR-13 15-APR- 13 306 0.014 +1- 0.004 0.006 15-APR-1 3 22-APR-1 3 310 0.018 +1- 0.004 0.007 22-APR-13 29-APR-1 3 301 0.021 +1- 0.004 0.009 29-APR-1 3 06-MAY-1 3 311 0.015 +1- 0.004 0.007 06-MAY-13 13-MAY- 13 296 0.022 +1- 0.004 0.014 13-MAY-1 3 20-MAY-1 3 296 0.026 +1- 0.004 0.014 20-MAY-13 28-MAY-13 348 0.013 +1- 0.003 0.013 28-MAY-1 3 03-JUN-13 258 0.014 +1- 0.004 0.013 03-JUN-13 10-JUN-13 291 0.017 +1- 0.004 0.011 10-JUN-13 17-JUN-13 302 0.023 +1- 0.004 0.013 17-JUN-13 24-JUN-13 302 0.029 +1- 0.005 0.010 24-JUN-13 01-JUL-13 295 0.023 +1- 0.004 0.015 01-JUL-13 08-JUL-13 299 0.021 +1- 0.004 0.011 08-JUL-13 15-JUL-13 299 0.023 +1- 0.004 0.012 15-JUL-13 22-JUL-13 297 0.016 +1- 0.004 0.010 22-JUL-13 29-JUL-13 304 0.021 +1- 0.004 0.011 29-JUL-13 05-AUG-13 295 0.026 +1- 0.004 0.010 05-AUG-13 12-AUG-13 304 0.024 +1- 0.004 0.008 12-AUG-13 19-AUG-13 300 0.024 +1- 0.004 0.012 19-AUG- 13 26-AUG-13 300 0.040 +1- 0.005 0.011 26-AUG-13 03-SEP-1 3 341 0.025 +1- 0.004 0.014 03-SEP-13 09-SEP-13 261 0.040 +1- 0.005 0.017 09-SEP-13 17-SEP-13 350 0.029 +1- 0.004 0.012 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 9

Air Particulate and Charcoal Filters Location: 049 Collection Collection Volume Gross Beta 1-131 Duplicate Start Date End Date m3 Concentration Concentration Analysis (pCiIm3 ) (pCi/m 3 )

09-SEP-13 17-SEP-13 350 0.026 -'-I- 0.004 Duplicate 17-SEP-13 23-SEP-13 256 0.026 +1- 0.005 0.010 23-SEP-13 30-SEP-13 300 0.031 +1- 0.005 0.014 30-SEP-1 3 07-OCT-13 300 0.015 +1- 0.004 0.007 07-OCT-13 14-OCT-1 3 299 0.022 +1- 0.004 0.020 14-OCT-1 3 21-OCT-13 303 0.019 +1- 0.004 0.015 21-OCT-13 29-OCT-1 3 343 0.022 +1- 0.004 0.007 29-OCT-1 3 04-NOV-13 261 0.024 +1- 0.005 0.011 29-OCT-1 3 04-NOV-1 3 261 0.025 +1- 0.005 Duplicate 04-NOV-1 3 11-NOV-13 329 0.018 +1- 0.004 0.010 11-NOV-13 18-NOV-13 309 0.027 +1- 0.004 0.009 18-NOV- 13 25-NOV-1 3 314 0.022 +1- 0.004 0.010 25-NOV-1 3 02-DEC-13 309 0.036 +1- 0.004 0.012 02-DEC-1 3 09-DEC-13 311 0.042 +1- 0.005 0.018 09-DEC-13 16-DEC- 13 290 0.050 +1- 0.005 0.011 16-DEC-1 3 23-DEC-13 309 0.041 +1- 0.005 0.015 23-DEC-13 30-DEC-1 3 291 0.037 +1- 0.005 0.013 30-DEC-13 07-JAN-14 353 0.031 +1- 0.004 0.008 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 10

Air Particulate and Charcoal Filters Location: 053 Collection Collection Volume Gross Beta 1-131 Duplicate Start Date End Date m3 Concentration Concentration Analysis (pCilm3 ) (pCi/m 3 )

31 -DEC-1 2 07-JAN-1 3 304 0.052 +1- 0.005 < 0.013 07-JAN-13 14-JAN-13 298 0.036 +1- 0.005 < 0.019 14-JAN-1 3 21-JAN-13 297 0.025 +1- 0.004 Duplicate 14-JAN-13 21-JAN-13 297 0.032 +1- 0.005 0.012 21-JAN-1 3 28-JAN-1 3 298 0.038 +1- 0.005 0.008 28-JAN-13 05-FEB-13 351 0.034 +1- 0.004 0.014 05-FEB-13 12-FEB-13 299 0.029 +1- 0.004 0.009 12-FEB-1 3 19-FEB-13 300 0.026 +1- 0.004 0.011 19-FEB-13 25-FEB-13 258 0.027 +1- 0.005 0.011 25-FEB-1 3 05-MAR-13 334 0.032 +1- 0.004 0.009 05-MAR- 13 12-MAR-1 3 296 0.019 +1- 0.004 0.012 12-MAR-13 19-MAR-13 294 0.028 +1- 0.004 0.017 19-MAR-13 26-MAR-1 3 313 0.024 +1- 0.004 0.013 26-MAR-1 3 01-APR-13 247 0.020 +1- 0.005 0.017 01-APR-13 08-APR-1 3 293 0.024 +1- 0.004 01-APR-13 08-APR-13 293 0.017 08-APR- 13 15-APR-13 305 0.017 +1- 0.004 0.006 15-APR-1 3 22-APR-1 3 313 0.014 +1- 0.004 0.007 22-APR-13 29-APR-1 3 299 0.021 +1- 0.004 0.009 29-APR-1 3 06-MAY-13 308 0.015 +1- 0.004 0.007 06-MAY-13 13-MAY-1 3 261 0.020 +1- 0.005 0.016 13-MAY-1 3 20-MAY- 13 292 0.024 +1- 0.004 0.014 20-MAY-13 28-MAY-1 3 351 0.011 +1- 0.003 0.013 20-MAY-1 3 28-MAY-1 3 351 0.012 0.003 Duplicate 28-MAY- 13 03-JUN-13 255 0.014 +1- 0.004 0.013 03-JUN-13 10-JUN-13 293 0.017 +1- 0.004 0.011 10-JUN-13 17-JUN-13 304 0.020 +1- 0.004 0.013 17-JUN-13 24-JUN-13 304 0.024 +1- 0.004 0.010 24-JUN-13 01-JUL-13 295 0.021 +1- 0.004 0.015 01-JUL-13 08-JUL-13 296 0.020 +1- 0.004 0.011 08-JUL-13 15-JUL-13 297 0.021 +1- 0.004 0.012 15-JUL-13 22-JUL-13 294 0.016 +1- 0.004 0.010 22-JUL-13 29-JUL-13 303 0.023 +1- 0.004 0.011 29-JUL-13 05-AUG-13 299 0.029 +1- 0.004 0.010 05-AUG-13 12-AUG-13 299 0.021 +1- 0.004 0.008 12-AUG-13 19-AUG-13 298 0.025 +1- 0.004 0.012 19-AUG- 13 26-AUG-13 305 0.041 +1- 0.005 0.010 26-AUG-13 03-SEP-1 3 335 0.023 +1- 0.004 0.015 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 11

Air Particulate and Charcoal Filters Location: 053 Collection Collection Volume Gross Beta 1-131 Duplicate 3

Start Date End Date m Concentration Concentration Analysis (pCi/m 3 ) (pCilm 3) 03-SEP-13 09-SEP-13 261 0.036 +1- 0.005 0.017 09-SEP-13 17-SEP-13 338 0.026 +1- 0.004 0.012 17-SEP-1 3 23-SEP-13 261 0.029 +1- 0.005 0.010 23-SEP-1 3 30-SEP-13 302 0.029 +1- 0.004 0.014 30-SEP-13 07-OCT-1 3 295 0.016 +1- 0.004 0.007 07-OCT-13 14-OCT-1 3 300 0.022 +1- 0.004 0.020 14-OCT-13 21-OCT- 13 301 0.017 +1- 0.004 0.015 21-OCT-13 29-OCT-1 3 339 0.021 +1- 0.004 0.007 29-OCT-1 3 04-NOV-1 3 263 0.019 +1- 0.005 0.010 04-NOV-1 3 11-NOV-13 312 0.017 +1- 0.004 0.011 11-NOV-13 18-NOV-13 304 0.025 +1- 0.004 0.009 18-NOV-13 25-NOV-13 314 0.025 +1- 0.004 0.010 25-NOV-13 02-DEC- 13 306 0.033 +1- 0.004 0.012 02-DEC-13 09-DEC-13 306 0.040 +1- 0.005 0.018 09-DEC-13 16-DEC-13 290 0.044 +1- 0.005 0.011 16-DEC-1 3 23-DEC-13 308 0.038 +1- 0.005 0.015 23-DEC-1 3 30-DEC-1 3 293 0.030 +1- 0.004 0.013 30-DEC-13 07-JAN-14 347 0.033 +1- 0.004 0.008 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 12

Quarterly Air Particulate - Gamma Location: 002 01-APR-13 Nuclide Concentration (pCi/m 3 )

BE-7 0.064+/- 0.011 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-1 37 < 0.001 01-JUL-13 3 Nuclide Concentration (pCilm )

BE-7 0.092+/- 0.015 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-1 37 < 0.001 30-SEP-1 3 3 Nuclide Concentration (pCi/m )

BE-7 0.080+/- 0.017 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-1 37 < 0.001

Quarterly Air Particulate - Gamma Location: 002 30-DEC-1 3 Nuclide Concentration (pCi/lm 3 )

BE-7 0.052+/- 0.012 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 018 01 -APR-13 Nuclide Concentration (pCilm 3 )

BE-7 0.079+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-1 37 < 0.001 01-JUL-13 3 Nuclide Concentration (pCilm )

BE-7 0.079+/- 0.014 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001 30-SEP-13 3 Nuclide Concentration (pCi/m )

BE-7 0.070+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 018 30-DEC-1 3 Nuclide Concentration (DCilm 3 )

BE-7 0.065+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 032 01-APR-13 Nuclide Concentration (pCi/m 3 )

BE-7 0.080+/- 0.015 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-1 37 < 0.001 01-JUL-13 3 Nuclide Concentration (pCilm )

BE-7 0.084+/- 0.015 MN-54 < 0.001 C0-58 < 0.001 FE-59 < 0.002 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-1 37 < 0.001 30-SEP-1 3 3 Nuclide Concentration (pCi/m )

BE-7 0.088+/- 0.016 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.002 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 032 30-DEC-1 3 Nuclide Concentration (pCilm 3 )

BE-7 0.070+/- 0.014 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 037 01-APR-13 Nuclide Concentration (pCiIm 3 )

BE-7 0.075+/- 0.014 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001 01-JUL-13 3 Nuclide Concentration (pCi/m )

BE-7 0.083+/- 0.010 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-137 < 0.001 30-SEP-13 3 Nuclide Concentration (pCilm )

BE-7 0.074+/- 0.015 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-1 37 < 0.001

Quarterly Air Particulate - Gamma Location: 037 30-DEC-1 3 Nuclide Concentration (pCi/m 3 )

BE-7 0.069+/- 0.016 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 049 01-APR-13 Nuclide Concentration (pCilm 3 )

BE-7 0.080+/- 0.015 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001 01-JUL-13 3 Nuclide Concentration (pCiIm )

BE-7 0.088+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001 30-SEP-13 3 Nuclide Concentration (pCi/m )

BE-7 0.083+/- 0.014 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-134 < 0.001 CS-1 37 < 0.001

Quarterly Air Particulate - Gamma Location: 049 30-DEC-1 3 Nuclide Concentration (pCilm 3 )

BE-7 0.063+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Quarterly Air Particulate - Gamma Location: 053 01-APR-13 Nuclide Concentration (pCilm 3 )

BE-7 0.073+/- 0.012 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-1 37 < 0.001 01-JUL-13 3 Nuclide Concentration (pCi/m )

BE-7 0.087+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.002 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001 30-SEP-1 3 3 Nuclide Concentration (pCiIm )

BE-7 0.081+/- 0.013 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-i 34 < 0.001 CS-1 37 < 0.001

Quarterly Air Particulate - Gamma Location: 053 30-DEC-1 3 Nuclide Concentration (pCilm 3 )

BE-7 0.063+/- 0.015 MN-54 < 0.001 CO-58 < 0.001 FE-59 < 0.001 CO-60 < 0.001 ZN-65 < 0.001 ZR-NB-95 < 0.001 CS-1 34 < 0.001 CS-137 < 0.001

Exposure Pathway - Waterborne Surface Water Location JRR Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 14-JAN-13 MN-54 3.5 14-JAN-13 CO-58 2.9 14-JAN-1 3 FE-59 4.1 14-JAN-13 CO-60 3.3 14-JAN-13 ZN-65 5.9 14-JAN-1 3 ZR-NB-95 5.3 14-JAN-13 1-131 7.5 14-JAN-13 CS-134 4.0 14-JAN-1 3 CS-137 4.8 14-JAN-13 BA-LA-140 4.6 14-JAN-1 3 H-3 138.0 19-FEB-13 MN-54 3.7 19-FEB-13 CO-58 3.9 19-FEB-13 FE-59 4.1 19-FEB-13 CO-60 4.9 19-FEB-1 3 ZN-65 6.8 19-FEB-13 ZR-NB-95 1.9 19-FEB-13 1-131 3.7 19-FEB-13 CS-134 3.0 19-FEB-13 CS-137 4.8 19-FEB-13 BA-LA-140 5.3 19-FEB-1 3 H-3 143.0 19-FEB-13 FE-55 157.8 14-MAR-13 MN-54 4.9 Duplicate 14-MAR-1 3 MN-54 2.6 14-MAR-1 3 CO-58 5.6 Duplicate 14-MAR-13 CO-58 1.6 14-MAR-13 FE-59 8.7 Duplicate 14-MAR-1 3 FE-59 7.0 14-MAR-13 CO-60 1.8 Duplicate 14-MAR-13 CO-60 2.8 14-MAR-1 3 ZN-65 4.9 Duplicate 14-MAR-13 ZN-65 3.4 14-MAR-13 ZR-NB-95 4.0 Duplicate 14-MAR-1 3 ZR-NB-95 3.5 14-MAR-13 1-131 6.0 Duplicate 14-MAR-1 3 1-131 3.6 14-MAR-1 3 CS-134 4.9 Duplicate 14-MAR-13 CS-134 2.8 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 25

Exposure Pathway - Waterborne Surface Water Location JRR Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 14-MAR-13 CS-137 2.7 Duplicate 14-MAR-13 CS-137 3.6 14-MAR- 13 BA-LA- 140 6.9 Duplicate 14-MAR-13 BA-LA-140 3.6 14-MAR-13 H-3 145.0 Duplicate 14-MAR-1 3 H-3 145.0 16-APR-13 MN-54 2.6 16-APR- 13 CO-58 2.6 16-APR-13 FE-59 4.7 16-APR- 13 CO-60 2.2 16-APR-13 ZN-65 5.6 16-APR- 13 ZR-NB-95 1.7 16-APR-13 1-131 5.4 16-APR-13 CS-134 3.0 16-APR- 13 CS-137 2.8 16-APR-13 BA-LA- 140 2.3 16-APR-13 H-3 145.0 20-MAY-1 3 MN-54 2.0 20-MAY-1 3 CO-58 1.9 20-MAY-13 FE-59 3.6 20-MAY-13 CO-60 2.4 20-MAY-1 3 ZN-65 3.0 20-MAY-13 ZR-NB-95 3.0 20-MAY-13 1-131 7.8 20-MAY-1 3 CS-134 2.9 20-MAY-1 3 CS-1 37 2.9 20-MAY-13 BA-LA-140 1.9 20-MAY-13 H-3 145.0 20-MAY-13 FE-55 150.3 11-JUN-13 MN-54 3.3 11-JUN-13 CO-58 2.4 11-JUN-13 FE-59 2.6 11-JUN-13 CO-60 2.5 11-JUN-13 ZN-65 2.4 11-JUN-13 ZR-NB-95 2.6 11-JUN-13 1-131 5.5 11-JUN-13 CS-1 34 2.7 11-JUN-13 CS-137 3.5 11-JUN-13 BA-LA-140 2.6 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 26

Exposure Pathway - Waterborne Surface Water Location JRR Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 11-JUN-13 H-3 142.0 15-JUL-13 MN-54 5.7 15-JUL-13 CO-58 3.4 15-JUL-13 FE-59 7.9 15-JUL-13 CO-60 5.0 15-JUL-13 ZN-65 6.1 15-JUL-13 ZR-NB-95 4.7 15-JUL-13 1-131 8.5 15-JUL-13 CS-134 5.2 15-JUL-13 CS-1 37 3.8 15-JUL-13 BA-LA-140 3.5 15-JUL-13 H-3 159.0 26-AUG-13 MN-54 2.4 26-AUG-13 CO-58 1.7 26-AUG-13 FE-59 6.2 26-AUG-13 CO-60 4.3 26-AUG- 13 ZN-65 2.0 26-AUG-13 ZR-NB-95 3.8 26-AUG-13 1-131 6.9 26-AUG-13 CS-134 3.7 26-AUG-13 CS-137 3.5 26-AUG-13 BA-LA- 140 3.1 26-AUG-1 3 H-3 149.0 26-AUG-13 FE-55 148.6 23-SEP-13 MN-54 1.5 23-SEP-1 3 CO-58 1.8 23-SEP-13 FE-59 5.4 23-SEP-13 CO-60 0.9 23-SEP-1 3 ZN-65 4.3 23-SEP-13 ZR-NB-95 2.8 23-SEP-13 1-131 4.0 23-SEP-13 CS-134 2.9 23-SEP-13 CS-137 3.3 23-SEP-1 3 BA-LA-140 1.4 23-SEP-13 H-3 146.0 21-OCT- 13 MN-54 6.2 21-OCT-1 3 CO-58 3.5 21-OCT-13 FE-59 2.7 21-OCT- 13 CO-60 4.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 27

Exposure Pathway - Waterborne Surface Water Location JRR Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 21-OCT-13 ZN-65 4.1 21-OCT-13 ZR-NB-95 5.2 21-OCT-13 1-131 6.8 21-OCT-13 CS-134 5.6 21-OCT-13 CS-1 37 5.6 21-OCT-13 BA-LA-140 3.6 21-OCT-13 H-3 148.0 18-NOV-13 MN-54 4.3 18-NOV-13 CO-58 1.9 18-NOV-13 FE-59 3.5 18-NOV- 13 CO-60 2.5 18-NOV- 13 ZN-65 6.5 18-NOV- 13 ZR-NB-95 5.0 18-NOV-13 1-131 6.6 18-NOV-13 CS-134 4.3 18-NOV-13 CS-137 4.8 18-NOV- 13 BA-LA- 140 2.0 18-NOV-13 H-3 149.0 18-NOV-13 FE-55 157.3 16-DEC-1 3 MN-54 1.8 16-DEC-13 CO-58 2.5 16-DEC-1 3 FE-59 5.2 16-DEC-1 3 CO-60 1.4 16-DEC-13 ZN-65 3.3 16-DEC-13 ZR-NB-95 3.1 16-DEC-13 1-131 2.8 16-DEC-13 CS-134 2.9 16-DEC-13 CS-137 3.2 16-DEC-13 BA-LA-140 2.5 16-DEC-1 3 H-3 145.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 28

Exposure Pathway - Waterborne Surface Water Location SP Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 14-JAN-13 MN-54 2.4 14-JAN-13 CO-58 2.8 14-JAN-1 3 FE-59 5.0 14-JAN-1 3 CO-60 2.3 14-JAN-13 ZN-65 5.1 14-JAN-1 3 ZR-NB-95 2.6 14-JAN- 13 1-131 3.8 14-JAN-1 3 CS-134 2.9 14-JAN-13 CS-137 2.6 14-JAN-1 3 BA-LA-140 3.0 14-JAN-1 3 H-3 11,358+1 305.0 19-FEB-13 MN-54 2.5 19-FEB-1 3 CO-58 3.3 19-FEB-1 3 FE-59 4.8 19-FEB-13 CO-60 3.4 19-FEB-13 ZN-65 8.2 19-FEB-1 3 ZR-NB-95 5.3 19-FEB-13 1-131 5.0 19-FEB-13 CS-134 3.2 19-FEB-1 3 CS-137 3.8 19-FEB-13 BA-LA-140 4.2 19-FEB-13 H-3 13,170+1 324.0 19-FEB-13 FE-55 151.1 14-MAR-1 3 MN-54 3.4 14-MAR-13 CO-58 3.5 14-MAR-13 FE-59 6.1 14-MAR-1 3 CO-60 3.0 14-MAR-13 ZN-65 5.3 14-MAR-1 3 ZR-NB-95 3.7 14-MAR-1 3 1-131 5.2 14-MAR-13 CS-134 3.0 14-MAR-1 3 CS-1 37 3.7 14-MAR-13 BA-LA-140 4.6 14-MAR-1 3 H-3 12,805+1 328.0 16-APR-13 MN-54 3.2 16-APR- 13 CO-58 3.2 16-APR-13 FE-59 5.3 16-APR-1 3 CO-60 3.6 16-APR-13 ZN-65 7.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 29

Exposure Pathway - Waterborne Surface Water Location SP Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 16-APR-13 ZR-NB-95 5.5 16-APR-1 3 1-131 7.9 16-APR- 13 CS-1 34 2.5 16-APR- 13 CS-1 37 4.2 16-APR-1 3 BA-LA-140 5.2 16-APR-1 3 H-3 12,354 +/- 320.0 20-MAY- 13 MN-54 2.4 20-MAY-13 CO-58 1.9 20-MAY-13 FE-59 4.3 20-MAY-1 3 CO-60 1.6 20-MAY- 13 ZN-65 2.6 20-MAY-13 ZR-NB-95 3.1 20-MAY-1 3 1-131 6.4 20-MAY- 13 CS-134 2.8 20-MAY-13 CS-137 2.0 20-MAY-13 BA-LA- 140 5.3 20-MAY- 13 H-3 11,536+1 306.0 20-MAY-1 3 FE-55 151.2 11-JUN-13 MN-54 4.8 11-JUN-13 CO-58 2.3 11-JUN-13 FE-59 6.3 11-JUN-13 CO-60 4.1 11-JUN-13 ZN-65 3.9 11-JUN-13 ZR-NB-95 3.9 11-JUN-13 1-131 9.3 11-JUN-13 CS-134 4.3 11-JUN-13 CS-137 5.0 11-JUN-13 BA-LA-140 4.9 11-JUN-13 H-3 11,175+1 305.0 15-JUL-13 MN-54 2.8 15-JUL-13 CO-58 3.6 15-JUL-13 FE-59 5.0 15-JUL-13 CO-60 2.9 15-JUL-13 ZN-65 6.9 15-JUL-13 ZR-NB-95 4.3 15-JUL-13 1-131 5.6 15-JUL-13 CS-1 34 3.8 15-JUL-13 CS-1 37 4.1 15-JUL-13 BA-LA- 140 4.8 2013 Annual Radiological Enviironmental Operating Report Wolf Creek Generating Station Page C - 30

Exposure Pathway - Waterborne Surface Water Location SP Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 15-JUL-13 H-3 10,867 +/- 309.0 26-AUG-13 MN-54 5.5 26-AUG- 13 CO-58 2.7 26-AUG-13 FE-59 9.2 26-AUG-13 CO-60 3.3 26-AUG-13 ZN-65 6.0 26-AUG-13 ZR-NB-95 5.3 26-AUG-13 1-131 4.9 26-AUG- 13 CS-134 3.7 26-AUG-1 3 CS-1 37 5.0 26-AUG-1 3 BA-LA-140 4.8 26-AUG-13 H-3 9,295+1 280.0 26-AUG-1 3 FE-55 153.9 23-SEP-13 MN-54 1.3 23-SEP-13 CO-58 1.6 23-SEP-13 FE-59 3.2 23-SEP-13 CO-60 1.8 23-SEP-13 ZN-65 2.2 23-SEP-13 ZR-NB-95 1.6 23-SEP-13 1-131 3.8 23-SEP-13 CS-134 1.7 23-SEP-1 3 CS-1 37 3.3 23-SEP-13 BA-LA-140 2.8 23-SEP-13 H-3 9,340+- 282.0 21-OCT-13 MN-54 6.0 21-OCT-13 CO-58 2.3 21-OCT-13 FE-59 5.0 21-OCT- 13 CO-60 2.1 21-OCT-13 ZN-65 8.8 21 -OCT-1 3 ZR-NB-95 7.3 21 -OCT-1 3 1-131 4.4 21-OCT-13 CS-134 5.7 21-OCT-13 CS-137 6.3 21-OCT-1 3 BA-LA-140 5.5 21-OCT- 13 H-3 9,970+1 293.0 18-NOV-13 MN-54 3.0 18-NOV-1 3 CO-58 1.5 18-NOV-13 FE-59 4.3 18-NOV- 13 CO-60 2.2 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 31

Exposure Pathway - Waterborne Surface Water Location SP Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 18-NOV-13 ZN-65 6.2 18-NOV-13 ZR-NB-95 2.6 18-NOV-13 1-131 5.2 18-NOV-13 CS-134 3.4 18-NOV- 13 CS-137 3.3 18-NOV- 13 BA-LA-140 3.2 18-NOV-13 H-3 11,024 +1 309.0 18-NOV-13 FE-55 155.4 16-DEC-13 MN-54 2.6 16-DEC-1 3 CO-58 2.1 16-DEC-13 FE-59 4.6 16-DEC-13 CO-60 1.5 16-DEC-13 ZN-65 2.2 16-DEC-13 ZR-NB-95 2.1 16-DEC-1 3 1-131 4.0 16-DEC-13 CS-1 34 2.4 16-DEC-1 3 CS-1 37 2.7 16-DEC-1 3 BA-LA-140 1.1 16-DEC-13 H-3 10,309+1 296.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 32

Exposure Pathway - Waterborne Ground Water Location B-12 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 08-MAR-1 3 MN-54 2.6 08-MAR- 13 CO-58 2.3 08-MAR-13 FE-59 4.2 08-MAR-1 3 CO-60 3.1 08-MAR- 13 ZN-65 3.9 08-MAR-1 3 ZR-NB-95 2.8 08-MAR-13 CS-134 2.4 08-MAR-13 CS-137 3.4 08-MAR-13 BA-LA-140 1.6 08-MAR-1 3 H-3 141.0 08-MAR-13 1-131 (CHEM) 0.291 20-MAY-1 3 MN-54 4.1 20-MAY- 13 CO-58 3.2 20-MAY-1 3 FE-59 7.5 20-MAY-1 3 CO-60 2.9 20-MAY-13 ZN-65 4.6 20-MAY-1 3 ZR-NB-95 2.9 20-MAY-1 3 CS-134 2.8 20-MAY- 13 CS-137 3.9 20-MAY-1 3 BA-LA- 140 3.3 20-MAY-1 3 H-3 145.0 20-MAY-13 1-131 (CHEM) 0.273 26-AUG-13 MN-54 3.4 26-AUG-13 CO-58 2.8 26-AUG-13 FE-59 8.4 26-AUG-13 CO-60 4.0 26-AUG-1 3 ZN-65 5.9 26-AUG-13 ZR-NB-95 4.0 26-AUG-13 CS-1 34 3.0 26-AUG-1 3 CS-137 3.9 26-AUG-13 BA-LA-140 3.4 26-AUG-13 H-3 149.0 26-AUG-1 3 1-131 (CHEM) 0.224 18-NOV-13 MN-54 4.9 18-NOV- 13 CO-58 5.2 18-NOV-13 FE-59 7.0 18-NOV-13 CO-60 6.2 18-NOV- 13 ZN-65 7.9 18-NOV- 13 ZR-NB-95 5.2 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 33

Exposure Pathway - Waterborne Ground Water Location B-12 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 18-NOV- 13 CS-1 34 < 5.8 18-NOV- 13 CS-137

  • 4.3 18-NOV-13 BA-LA-140

Exposure Pathway - Waterborne Ground Water Location C-10 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 08-MAR- 13 MN-54 3.6 08-MAR-13 CO-58 3.3 08-MAR-13 FE-59 4.4 08-MAR-1 3 CO-60 2.6 08-MAR-13 ZN-65 5.3 08-MAR-13 ZR-NB-95 3.3 08-MAR-1 3 CS-134 2.9 08-MAR-1 3 CS-137 3.2 08-MAR-13 BA-LA-140 3.3 08-MAR-1 3 H-3 141.0 08-MAR-1 3 1-131 (CHEM) 0.283 20-MAY-13 MN-54 2.5 20-MAY-1 3 CO-58 2.7 20-MAY-1 3 FE-59 3.2 20-MAY-13 CO-60 2.5 20-MAY-13 ZN-65 3.0 20-MAY-1 3 ZR-NB-95 3.2 20-MAY-1 3 CS-134 2.8 20-MAY-1 3 CS-137 3.6 20-MAY-13 BA-LA- 140 6.1 20-MAY-1 3 H-3 145.0 20-MAY-1 3 1-131 (CHEM) 0.249 26-AUG-1 3 MN-54 3.4 26-AUG-13 CO-58 2.3 26-AUG-1 3 FE-59 5.6 26-AUG-1 3 CO-60 2.9 26-AUG-1 3 ZN-65 5.7 26-AUG-13 ZR-NB-95 5.0 26-AUG-13 CS-134 3.1 26-AUG-13 CS-1 37 2.4 26-AUG-13 BA-LA-140 2.7 26-AUG-1 3 H-3 149.0 26-AUG-13 1-131 (CHEM) 0.236 25-NOV-13 MN-54 4.0 25-NOV-13 CO-58 2.5 25-NOV-13 FE-59 3.8 25-NOV-13 CO-60 3.2 25-NOV-1 3 ZN-65 3.5 25-NOV-1 3 ZR-NB-95 4.2 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 35

Exposure Pathway - Waterborne Ground Water Location C-10 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 25-NOV-1 3 CS-134 < 4.1 25-NOV-13 CS-137 < 2.2 25-NOV-13 BA-LA- 140 < 3.2 25-NOV-13 H-3 < 155.0 25-NOV-1 3 1-131 (CHEM) < 0.376 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 36

Exposure Pathway - Waterborne Ground Water Location C-49 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 08-MAR-1 3 MN-54 2.6 08-MAR-1 3 CO-58 2.4 08-MAR- 13 FE-59 4.4 08-MAR-1 3 CO-60 2.7 08-MAR-1 3 ZN-65 4.1 08-MAR- 13 ZR-NB-95 2.9 08-MAR-1 3 CS-134 3.2 08-MAR-1 3 CS-1 37 3.3 08-MAR-1 3 BA-LA-140 2.3 08-MAR-1 3 H-3 140.0 08-MAR-1 3 1-131 (CHEM) 0.399 20-MAY-1 3 MN-54 2.2 20-MAY-1 3 CO-58 2.8 20-MAY- 13 FE-59 6.3 20-MAY-13 CO-60 2.3 20-MAY-1 3 ZN-65 6.4 20-MAY-1 3 ZR-NB-95 4.2 20-MAY-13 CS-134 3.2 20-MAY-1 3 CS-137 3.7 20-MAY-1 3 BA-LA-140 4.0 20-MAY-13 H-3 145.0 20-MAY-13 1-131 (CHEM) 0.496 26-AUG-13 MN-54 3.1 26-AUG-13 CO-58 1.9 26-AUG-13 FE-59 4.6 26-AUG-13 CO-60 2.0 26-AUG-13 ZN-65 2.2 26-AUG-1 3 ZR-NB-95 2.5 26-AUG-13 CS-134 2.3 26-AUG-1 3 CS-137 3.5 26-AUG-13 BA-LA-140 2.5 26-AUG-13 H-3 149.0 26-AUG-13 1-131 (CHEM) 0.259 18-NOV- 13 MN-54 5.0 18-NOV-13 CO-58 3.3 18-NOV-13 FE-59 4.7 18-NOV-13 CO-60 5.5 18-NOV-13 ZN-65 11.2 18-NOV-13 ZR-NB-95 4.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 37

Exposure Pathway - Waterborne Ground Water Location C-49 Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 18-NOV-13 CS-134 < 6.3 18-NOV-13 CS-1 37

  • 4.9 18-NOV-13 BA-LA-140

Exposure Pathway - Waterborne Ground Water Location F-1 Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 08-MAR-1 3 MN-54 2.9 08-MAR-1 3 CO-58 1.7 08-MAR- 13 FE-59 4.6 08-MAR-1 3 CO-60 2.6 08-MAR-1 3 ZN-65 4.1 08-MAR-13 ZR-NB-95 2.9 08-MAR-13 CS-134 2.9 08-MAR-1 3 CS-1 37 2.9 08-MAR-1 3 BA-LA-140 2.3 08-MAR-13 H-3 141.0 08-MAR- 13 1-131 (CHEM) 0.403 20-MAY-1 3 MN-54 1.8 20-MAY- 13 CO-58 1.4 20-MAY-13 FE-59 3.4 20-MAY-1 3 CO-60 2.0 20-MAY-1 3 ZN-65 2.9 20-MAY-13 ZR-NB-95 1.8 20-MAY-1 3 CS-134 2.5 20-MAY-1 3 CS-1 37 2.4 20-MAY- 13 BA-LA- 140 4.0 20-MAY-13 H-3 145.0 20-MAY-1 3 1-131 (CHEM) 0.281 26-AUG-13 MN-54 3.2 26-AUG-13 MN-54 3.7 Duplicate 26-AUG-13 CO-58 3.2 Duplicate 26-AUG-13 CO-58 1.7 26-AUG-13 FE-59 6.8 Duplicate 26-AUG-13 FE-59 3.8 26-AUG-13 CO-60 1.5 26-AUG-13 CO-60 2.5 Duplicate 26-AUG-1 3 ZN-65 5.6 Duplicate 26-AUG-13 ZN-65 3.2 26-AUG-13 ZR-NB-95 4.5 Duplicate 26-AUG-13 ZR-NB-95 1.9 26-AUG-1 3 CS-134 3.7 26-AUG-13 CS-134 4.7 Duplicate 26-AUG-13 CS-137 4.0 Duplicate 26-AUG-13 CS-1 37 3.6 26-AUG-13 BA-LA-140 1.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 39

Exposure Pathway - Waterborne Ground Water Location F-I Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 26-AUG-13 BA-LA- 140 3.1 Duplicate 26-AUG-13 H-3 149.0 Duplicate 26-AUG- 13 H-3 149.0 26-AUG-13 1-131 (CHEM) 0.319 26-AUG-13 1-131 (CHEM) 0.303 Duplicate 18-NOV-13 MN-54 2.3 18-NOV- 13 CO-58 2.9 18-NOV-13 FE-59 4.2 18-NOV-13 CO-60 2.8 18-NOV- 13 ZN-65 4.2 18-NOV- 13 ZR-NB-95 3.6 18-NOV-13 CS-1 34 3.2 18-NOV- 13 CS-137 2.7 18-NOV-13 BA-LA-140 4.2 18-NOV-13 H-3 149.0 18-NOV-13 1-131 (CHEM) 0.459 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 40

Exposure Pathway - Waterborne Ground Water Location G-2 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 08-MAR-1 3 MN-54 3.3 08-MAR-13 CO-58 3.2 08-MAR-1 3 FE-59 6.5 08-MAR-1 3 CO-60 3.5 08-MAR-13 ZN-65 7.8 08-MAR-1 3 ZR-NB-95 2.9 08-MAR-1 3 CS-1 34 3.1 08-MAR-13 CS-137 2.3 08-MAR-13 BA-LA-140 4.2 08-MAR-1 3 H-3 141.0 08-MAR-13 1-131 (CHEM) 0.608 20-MAY-1 3 MN-54 2.9 20-MAY- 13 CO-58 2.8 20-MAY-13 FE-59 4.3 20-MAY-1 3 CO-60 2.3 20-MAY-1 3 ZN-65 5.6 20-MAY-13 ZR-NB-95 4.7 20-MAY-13 CS-134 3.9 20-MAY-1 3 CS-137 3.0 20-MAY-13 BA-LA-140 3.9 20-MAY-13 H-3 145.0 20-MAY-13 1-131 (CHEM) 0.298 26-AUG-13 MN-54 2.7 26-AUG-1 3 CO-58 3.5 26-AUG-13 FE-59 7.4 26-AUG-13 CO-60 2.7 26-AUG-13 ZN-65 6.3 26-AUG-13 ZR-NB-95 3.9 26-AUG-13 CS-134 3.1 26-AUG-13 CS-137 2.9 26-AUG-1 3 BA-LA-140 2.3 26-AUG-13 H-3 149.0 26-AUG-13 1-131 (CHEM) 0.218 18-NOV-13 MN-54 4.6 Duplicate 18-NOV-13 MN-54 2.4 18-NOV-13 CO-58 1.9 18-NOV-13 CO-58 5.2 Duplicate 18-NOV-13 FE-59 4.7 Duplicate 18-NOV-13 FE-59 4.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 41

Exposure Pathway - Waterborne Ground Water Location G-2 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 18-NOV-13 CO-60 5.9 Duplicate 18-NOV- 13 CO-60 1.7 18-NOV- 13 ZN-65 5.8 Duplicate 18-NOV- 13 ZN-65 4.2 18-NOV-13 ZR-NB-95 3.0 18-NOV- 13 ZR-NB-95 3.0 Duplicate 18-NOV- 13 CS-1 34 2.6 18-NOV-13 CS-134 5.6 Duplicate 18-NOV-13 CS-137 2.4 18-NOV- 13 CS-1 37 4.2 Duplicate 18-NOV-13 BA-LA-140 3.2 Duplicate 18-NOV-13 BA-LA-140 2.2 18-NOV-13 H-3 149.0 18-NOV- 13 H-3 149.0 Duplicate 18-NOV-13 1-131 (CHEM) 0.456 Duplicate 18-NOV-13 1-131 (CHEM) 0.233 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 42

Exposure Pathway - Waterborne Ground Water Location J-1 Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 08-MAR-1 3 MN-54 3.1 08-MAR- 13 CO-58 2.8 08-MAR-1 3 FE-59 4.9 08-MAR-1 3 CO-60 3.3 08-MAR- 13 ZN-65 6.8 08-MAR-1 3 ZR-NB-95 4.5 08-MAR-1 3 CS-134 2.4 08-MAR-13 CS-137 2.9 08-MAR-1 3 BA-LA- 140 3.1 08-MAR-1 3 H-3 141.0 08-MAR- 13 1-131 (CHEM) 0.364 20-MAY- 13 MN-54 3.2 20-MAY-13 CO-58 1.7 20-MAY-1 3 FE-59 2.1 20-MAY- 13 CO-60 1.8 20-MAY-13 ZN-65 3.7 20-MAY-1 3 ZR-NB-95 2.5 20-MAY-13 CS-134 3.2 20-MAY-13 CS-1 37 3.4 20-MAY-1 3 BA-LA-140 2.8 20-MAY-13 H-3 145.0 20-MAY-13 1-131 (CHEM) 0.286 26-AUG-1 3 MN-54 2.1 26-AUG-1 3 CO-58 2.2 26-AUG-13 FE-59 2.9 26-AUG-1 3 CO-60 2.3 26-AUG-13 ZN-65 5.7 26-AUG-13 ZR-NB-95 2.3 26-AUG-13 CS-134 2.5 26-AUG-1 3 CS-1 37 2.7 26-AUG-13 BA-LA-140 1.9 26-AUG-13 H-3 149.0 26-AUG-1 3 1-131 (CHEM) 0.236 18-NOV- 13 MN-54 3.2 18-NOV-13 CO-58 3.2 18-NOV-13 FE-59 4.9 18-NOV-1 3 CO-60 3.1 18-NOV- 13 ZN-65 6.1 18-NOV-13 ZR-NB-95 3.9 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 43

Exposure Pathway - Waterborne Ground Water Location J-1 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 18-NOV- 13 CS-134 < 3.5 18-NOV- 13 CS-137 < 3.1 18-NOV-13 BA-LA-140 < 2.0 18-NOV- 13 H-3 < 149.0 18-NOV-13 1-131 (CHEM) < 0.262 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 44

Exposure Pathway - Waterborne Ground Water Location J-2 Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 08-MAR-1 3 MN-54 3.4 08-MAR-13 CO-58 1.9 08-MAR-1 3 FE-59 3.9 08-MAR-1 3 CO-60 2.6 08-MAR-13 ZN-65 5.8 08-MAR-1 3 ZR-NB-95 3.2 08-MAR-1 3 CS-1 34 2.9 08-MAR-13 CS-1 37 4.1 08-MAR-13 BA-LA- 140 5.9 08-MAR-1 3 H-3 141.0 08-MAR-1 3 1-131 (CHEM) 0.399 20-MAY-1 3 MN-54 2.7 20-MAY-13 CO-58 3.2 20-MAY-13 FE-59 3.6 20-MAY-1 3 CO-60 1.8 20-MAY-1 3 ZN-65 3.9 20-MAY-13 ZR-NB-95 3.4 20-MAY-1 3 CS-134 3.1 20-MAY-13 CS-137 2.8 20-MAY-13 BA-LA-140 4.9 20-MAY-13 H-3 145.0 20-MAY-1 3 1-131 (CHEM) 0.347 26-AUG-13 MN-54 3.2 26-AUG-13 CO-58 2.7 26-AUG-13 FE-59 4.0 26-AUG-1 3 CO-60 2.2 26-AUG-13 ZN-65 4.6 26-AUG-13 ZR-NB-95 3.4 26-AUG-13 CS-134 2.4 26-AUG-13 CS-137 2.9 26-AUG-13 BA-LA-140 2.8 26-AUG-13 H-3 149.0 26-AUG-13 1-131 (CHEM) 0.21 25-NOV-13 MN-54 3.2 25-NOV-13 CO-58 1.6 25-NOV-13 FE-59 5.2 25-NOV-13 CO-60 2.7 25-NOV-13 ZN-65 4.1 25-NOV-13 ZR-NB-95 3.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 45

Exposure Pathway - Waterborne Ground Water Location J-2 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 25-NOV-13 CS-134

Exposure Pathway - Waterborne Ground Water Location L-49 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 08-MAR- 13 MN-54 2.0 08-MAR-13 CO-58 2.6 08-MAR-1 3 FE-59 3.5 08-MAR-1 3 CO-60 2.0 08-MAR-13 ZN-65 3.1 08-MAR- 13 ZR-NB-95 2.4 08-MAR-13 CS-134 3.1 08-MAR-1 3 CS-137 2.5 08-MAR-1 3 BA-LA- 140 1.8 08-MAR-13 H-3 141.0 08-MAR-13 1-131 (CHEM) 0.423 20-MAY-1 3 MN-54 4.3 20-MAY- 13 CO-58 2.3 20-MAY-13 FE-59 4.7 20-MAY-13 CO-60 2.3 20-MAY-1 3 ZN-65 6.8 20-MAY-1 3 ZR-NB-95 3.8 20-MAY- 13 CS-1 34 3.1 20-MAY-13 CS-137 3.0 20-MAY-13 BA-LA-140 3.8 20-MAY-1 3 H-3 145.0 20-MAY-1 3 1-131 (CHEM) 0.284 26-AUG-13 MN-54 2.5 26-AUG-13 CO-58 2.2 26-AUG-13 FE-59 2.5 26-AUG-13 CO-60 2.5 26-AUG-1 3 ZN-65 2.9 26-AUG-13 ZR-NB-95 2.4 26-AUG-13 CS-134 2.6 26-AUG-13 CS-137 2.7 26-AUG-13 BA-LA-140 1.3 26-AUG-1 3 H-3 149.0 26-AUG-1 3 1-131 (CHEM) 0.21 18-NOV-13 MN-54 2.6 18-NOV-1 3 CO-58 2.6 18-NOV-1 3 FE-59 6.2 18-NOV- 13 CO-60 3.3 18-NOV-13 ZN-65 4.5 18-NOV-13 ZR-NB-95 2.7 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 47

Exposure Pathway - Waterborne Ground Water Location L-49 Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 18-NOV-13 CS-134 < 3.8 18-NOV-13 CS-1 37 < 2.7 18-NOV-13 BA-LA- 140 < 2.1 18-NOV- 13 H-3 < 149.0 18-NOV- 13 1-131 (CHEM) < 0.267 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 48

Exposure Pathway - Waterborne Drinking Water Location BW-15 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 05-FEB-13 MN-54 2.8 05-FEB-1 3 CO-58 3.0 05-FEB-1 3 FE-59 6.9 05-FEB-13 CO-60 3.5 05-FEB-13 ZN-65 3.7 05-FEB-1 3 ZR-NB-95 4.4 05-FEB-1 3 CS-1 34 2.9 05-FEB-13 CS-1 37 4.7 05-FEB-1 3 BA-LA- 140 3.9 05-FEB-13 GROSS BETA 3.302+/- 0.53 05-FEB-1 3 1-131 (CHEM) 0.376 05-MAR-13 MN-54 4.5 05-MAR-13 CO-58 5.5 05-MAR-1 3 FE-59 11.5 05-MAR-1 3 CO-60 < 4.2 05-MAR-13 ZN-65 < 5.8 05-MAR-13 ZR-NB-95 < 4.5 05-MAR-1 3 CS-134 4.4 05-MAR-1 3 CS-1 37 6.0 05-MAR-13 BA-LA- 140 6.8 05-MAR-13 GROSS BETA 2.173+/- 0.639 05-MAR-13 1-131 (CHEM) 0.282 01-APR-13 MN-54 2.0 01-APR-13 CO-58 2.5 01-APR-13 FE-59 4.5 01-APR-13 CO-60 2.5 01-APR-13 ZN-65 3.7 01-APR-13 ZR-NB-95 2.6 01-APR-13 CS-134 2.4 01-APR-13 CS-137 2.3 01-APR-13 BA-LA-140 1.7 01-APR-13 GROSS BETA 3.181 +/- 0.532 01-APR-13 1-131 (CHEM) 0.293 06-MAY-1 3 MN-54 2.1 06-MAY- 13 CO-58 2.7 06-MAY-13 FE-59 1.6 06-MAY-13 CO-60 1.9 06-MAY-1 3 ZN-65 1.7 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 49

Exposure Pathway - Waterborne Drinking Water Location BW-15 Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 06-MAY-1 3 ZR-NB-95 2.8 06-MAY-13 CS-134 2.0 06-MAY-13 CS-137 3.9 06-MAY-1 3 BA-LA-140 1.4 06-MAY-1 3 GROSS BETA 3.167+/- 0.71 06-MAY- 13 1-131 (CHEM) 0.308 03-JUN-13 MN-54 4.3 03-JUN-13 CO-58 2.5 03-JUN-13 FE-59 4.8 03-JUN-13 CO-60 2.9 03-JUN-13 ZN-65 7.6 03-JUN-1 3 ZR-NB-95 3.7 03-JUN-13 CS-134 < 4.4 03-JUN-13 CS-137 3.6 03-JUN-13 BA-LA-140 2.9 03-JUN-1 3 GROSS BETA 3.006 +/- 0.689 03-JUN-13 1-131 (CHEM) 0.43 01-JUL-13 MN-54 3.7 01-JUL-13 CO-58 2.3 01-JUL-13 FE-59 5.8 01-JUL-13 CO-60 2.9 01-JUL-13 ZN-65 4.1 01-JUL-13 ZR-NB-95 2.6 01-JUL-13 CS-134 3.0 01-JUL-13 CS-1 37 2.9 01-JUL-13 BA-LA-140 3.6 01-JUL-13 GROSS BETA 3.758 +/- 0.743 01-JUL-13 1-131 (CHEM) 0.278 05-AUG-13 MN-54 2.8 05-AUG-13 CO-58 1.6 05-AUG-13 FE-59 4.8 05-AUG-13 CO-60 1.7 05-AUG-1 3 ZN-65 3.5 05-AUG-13 ZR-NB-95 3.1 05-AUG-13 CS-134 2.9 05-AUG-13 CS-1 37 3.4 05-AUG-13 BA-LA-140 2.2 05-AUG-13 GROSS BETA 2.579 +/- 0.647 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 50

Exposure Pathway - Waterborne Drinking Water Location BW-1 5 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 05-AUG-13 1-131 (CHEM) 0.189 03-SEP-1 3 MN-54 1.9 03-SEP-13 CO-58 3.0 03-SEP-13 FE-59 3.4 03-SEP-1 3 CO-60 1.4 03-SEP-1 3 ZN-65 2.1 03-SEP-13 ZR-NB-95 1.9 03-SEP-13 CS-134 2.4 03-SEP-1 3 CS-137 2.9 03-SEP-1 3 BA-LA-1 40 1.2 03-SEP-13 GROSS BETA 3.997 +/- 0.746 03-SEP-13 1-131 (CHEM) 0.288 07-OCT-1 3 MN-54 3.9 07-OCT-1 3 CO-58 3.3 07-OCT-13 FE-59 5.6 07-OCT-13 CO-60 1.0 07-OCT-13 ZN-65 6.5 07-OCT-1 3 ZR-NB-95 3.0 07-OCT-13 CS-134 2.9 07-OCT-1 3 CS-137 2.3 07-OCT-1 3 BA-LA-140 1.3 07-OCT-13 GROSS BETA 3.152 +/- 0.691 07-OCT-1 3 1-131 (CHEM) 0.353 04-NOV-13 MN-54 3.8 04-NOV-13 CO-58 3.1 04-NOV-1 3 FE-59 7.2 04-NOV-1 3 CO-60 3.6 04-NOV-1 3 ZN-65 8.3 04-NOV-13 ZR-NB-95 4.0 04-NOV-13 CS-1 34 5.0 04-NOV-1 3 CS-137 4.5 04-NOV- 13 BA-LA-140 5.6 04-NOV-13 GROSS BETA 2.724 +/- 0.492 04-NOV-13 1-131 (CHEM) 0.262 05-DEC-13 MN-54 4.0 05-DEC-1 3 CO-58 3.5 05-DEC-13 FE-59 5.4 05-DEC-13 CO-60 2.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 51

Exposure Pathway - Waterborne Drinking Water Location BW-15 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 05-DEC-13 ZN-65 3.7 05-DEC-1 3 ZR-NB-95 2.5 05-DEC-1 3 CS-134 4.1 05-DEC-13 CS-137 3.3 05-DEC-1 3 BA-LA-140 2.6 05-DEC-1 3 GROSS BETA 3.273 +/- 0.691 05-DEC-1 3 1-131 (CHEM) 0.339 07-JAN-14 MN-54 2.0 07-JAN-14 CO-58 1.4 07-JAN-14 FE-59 2.8 07-JAN-14 CO-60 2.2 07-JAN-14 ZN-65 1.7 07-JAN-14 ZR-NB-95 2.5 07-JAN-14 CS-134 3.4 07-JAN-14 CS-137 3.3 07-JAN-14 BA-LA-140 2.7 07-JAN-14 GROSS BETA 2.568+/- 0.667 07-JAN-14 1-131 (CHEM) 0.456 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 52

Exposure Pathway - Waterborne Drinking Water Location 1O-DW Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 05-FEB-13 MN-54 3.6 05-FEB-1 3 CO-58 2.8 05-FEB-1 3 FE-59 3.7 05-FEB-13 CO-60 3.1 05-FEB-13 ZN-65 6.1 05-FEB-1 3 ZR-NB-95 2.5 05-FEB-1 3 CS-134 2.7 05-FEB-13 CS-137 2.8 05-FEB-13 BA-LA- 140 2.4 05-FEB-1 3 GROSS BETA 2.680 +/- 0.502 05-FEB-1 3 1-131 (CHEM) 0.458 05-MAR-13 MN-54 4.1 05-MAR-13 CO-58 < 4.6 05-MAR-1 3 FE-59 < 6.1 05-MAR-1 3 CO-60 < 4.8 05-MAR-13 ZN-65 4.9 05-MAR- 13 ZR-NB-95 3.6 05-MAR-13 CS-134 2.6 05-MAR-1 3 CS-1 37 4.7 05-MAR-13 BA-LA-140 4.1 05-MAR-13 GROSS BETA 2.602 +/- 0.707 05-MAR-1 3 1-131 (CHEM) 0.3 01-APR-13 MN-54 3.0 01-APR-13 CO-58 1.9 01-APR-13 FE-59 4.9 01-APR-13 CO-60 2.7 01-APR-13 ZN-65 4.3 01-APR-13 ZR-NB-95 2.0 01-APR-13 CS-134 2.7 01-APR-13 CS-1 37 2.6 01-APR-13 BA-LA- 140 2.0 01-APR-13 GROSS BETA 2.378+/- 0.501 01-APR-13 1-131 (CHEM) 0.316 06-MAY-1 3 MN-54 2.0 06-MAY- 13 CO-58 2.7 06-MAY-13 FE-59 4.2 06-MAY-13 CO-60 1.6 06-MAY- 13 ZN-65 3.9 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 53

Exposure Pathway - Waterborne Drinking Water Location 1O-DW Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 06-MAY- 13 ZR-NB-95 3.0 06-MAY-1 3 CS-134 2.6 06-MAY-1 3 CS-137 2.8 06-MAY-13 BA-LA-140 2.1 06-MAY-13 GROSS BETA 2.026+/- 0.66 06-MAY-1 3 1-131 (CHEM) 0.31 03-JUN-13 MN-54 < 3.6 03-JUN-13 CO-58 < 2.0 03-JUN-13 FE-59 < 5.3 03-JUN-13 CO-60 < 2.2 03-JUN-13 ZN-65 < 3.6 03-JUN-13 ZR-NB-95 < 3.6 03-JUN-13 CS-134 < 3.2 03-JUN-13 CS-137 < 2.3 03-JUN-13 BA-LA-140 4.3 03-JUN-13 GROSS BETA 3.007 +/- 0.696 03-JUN-13 1-131 (CHEM) 0.312 01-JUL-13 MN-54 2.2 01-JUL-13 CO-58 2.4 01-JUL-13 FE-59 1.8 01-JUL-13 CO-60 2.2 01-JUL-13 ZN-65 2.8 01-JUL-13 ZR-NB-95 2.7 01-JUL-13 CS-134 2.5 01-JUL-13 CS-137 2.8 01-JUL-13 BA-LA-140 3.1 01-JUL-13 GROSS BETA 2.101 +/- 0.667 01-JUL-13 1-131 (CHEM) 0.29 05-AUG-13 MN-54 2.0 05-AUG-13 CO-58 3.2 05-AUG-13 FE-59 6.3 05-AUG-13 CO-60 3.5 05-AUG-13 ZN-65 3.8 05-AUG-13 ZR-NB-95 2.4 05-AUG-1 3 CS-134 2.7 05-AUG-13 CS-137 3.9 05-AUG-13 BA-LA- 140 3.9 05-AUG-13 GROSS BETA 2.903 +/- 0.674 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 54

Exposure Pathway - Waterborne Drinking Water Location IO-DW Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 05-AUG-1 3 1-131 (CHEM) < 0.334 03-SEP-13 MN-54 < 3.4 03-SEP-13 CO-58 < 3.1 03-SEP-13 FE-59 < 8.5 03-SEP-13 CO-60 < 3.1 03-SEP-13 ZN-65 < 3.9 03-SEP-13 ZR-NB-95 < 2.9 03-SEP-13 CS-134 < 4.4 03-SEP-1 3 CS-137 4.5 03-SEP-13 BA-LA-140 2.4 03-SEP-13 GROSS BETA 3.471 +/- 0.76 03-SEP-1 3 1-131 (CHEM) 0.272 07-OCT-1 3 MN-54 3.3 07-OCT-13 CO-58 2.6 07-OCT-1 3 FE-59 5.6 07-OCT-1 3 CO-60 3.5 07-OCT-1 3 ZN-65 4.9 07-OCT-13 ZR-NB-95 3.2 07-OCT-13 CS-134 2.7 07-OCT-1 3 CS-137 2.5 07-OCT-13 BA-LA-140 3.2 07-OCT-13 GROSS BETA 3.316 +/- 0.703 07-OCT-1 3 1-131 (CHEM) 0.259 04-NOV-1 3 MN-54 2.5 04-NOV-1 3 CO-58 1.0 04-NOV-13 FE-59 3.7 04-NOV-13 CO-60 2.4 04-NOV-1 3 ZN-65 3.0 04-NOV-1 3 ZR-NB-95 1.8 04-NOV-13 CS-134 2.5 04-NOV-1 3 CS-137 3.1 04-NOV-1 3 BA-LA-140 2.5 04-NOV-13 GROSS BETA 3.703 +/- 0.567 04-NOV-13 1-131 (CHEM) 0.279 05-DEC-1 3 MN-54 3.6 05-DEC-13 CO-58 2.8 05-DEC-13 FE-59 3.5 05-DEC-13 CO-60 3.7 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 55

Exposure Pathway - Waterborne Drinking Water Location 1O-DW Collection Nuclide Concentration Duplicate Date (pCilLiter) Analysis 05-DEC-13 ZN-65 3.6 05-DEC-1 3 ZR-NB-95 2.7 05-DEC-1 3 CS-134 3.5 05-DEC-13 CS-137 3.6 05-DEC-13 BA-LA- 140 3.0 05-DEC-1 3 GROSS BETA 3.996 +/- 0.78 05-DEC-1 3 1-131 (CHEM) 0.334 07-JAN-14 MN-54 3.4 07-JAN-14 CO-58 2.0 07-JAN-1 4 FE-59 < 4.1 07-JAN-1 4 CO-60 < 3.1 07-JAN-14 ZN-65 < 6.0 07-JAN-14 ZR-NB-95 < 3.0 07-JAN-14 CS-134 < 4.0 07-JAN-14 CS-137 3.5 07-JAN-14 BA-LA-140 2.9 07-JAN-14 GROSS BETA 2.979 +/- 0.704 07-JAN-14 1-131 (CHEM) < 0.283 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 56

Exposure Pathway - Waterborne Drinking Water Quarterly Tritium Analysis Location BW-15 Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 01-APR-13 H-3 < 150 01-JUL-13 H-3 < 151 07-OCT-13 H-3 < 151 07-JAN-1 4 H-3 < 149 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 57

Exposure Pathway - Waterborne Drinking Water Quarterly Tritium Analysis Location IO-DW Collection Nuclide Concentration Duplicate Date (pCi/Liter) Analysis 01-APR-13 H-3 < 150 01-JUL-13 H-3 < 151 07-OCT-1 3 H-3 < 151 07-JAN-14 H-3 < 149 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 58

Exposure Pathway - Waterborne Shoreline Sediment Location DC Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 06-JUN-13 K-40 7,355.9 +/- 498.8 06-JUN-13 MN-54 24.4 06-JUN-13 CO-58 24.7 06-JUN-13 FE-59 40.4 06-JUN-13 CO-60 9.8 06-JUN-1 3 ZN-65 39.6 06-JUN-13 CS-134 16.5 06-JUN-13 CS-137 19.3 03-DEC-1 3 K-40 6,367.6+1 442.0 03-DEC-13 MN-54 13.2 03-DEC-1 3 CO-58 15.0 03-DEC-1 3 FE-59 40.4 03-DEC-1 3 CO-60 12.2 03-DEC-13 ZN-65 38.9 03-DEC-13 CS-134 15.8 03-DEC-13 CS-137 17.7 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 59

Exposure Pathway - Waterborne Shoreline Sediment Location EEA Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 30-APR-13 K-40 11,221.0 +/- 701.1 30-APR-13 MN-54

  • 23.4 30-APR-13 CO-58
  • 19.4 30-APR-1 3 ZN-65
  • 40.4 30-APR-1 3 CS-134
  • 24.4 03-SEP-1 3 K-40 12,353.0 +/- 778.9 Duplicate 03-SEP-13 K-40 11,893.0 +1- 681.3 03-SEP-13 MN-54 < 28.0 Duplicate 03-SEP-13 MN-54 < 24.4 03-SEP-1 3 CO-58 < 42.8 Duplicate 03-SEP-13 CO-58 < 22.1 03-SEP-13 FE-59 < 78.8 03-SEP-13 FE-59 < 103.8 Duplicate 03-SEP-1 3 CO-60 < 21.2 Duplicate 03-SEP-1 3 CO-60 < 9.6 03-SEP-13 ZN-65 < 46.4 03-SEP-13 ZN-65 < 65.6 Duplicate 03-SEP-13 CS-134 < 21.5 03-SEP-13 CS-134 < 19.6 Duplicate 03-SEP-1 3 CS-1 37 97.8 +/- 34.6 Duplicate 03-SEP-13 CS-137 89.2 +/- 41.6 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 60

Exposure Pathway - Waterborne Shoreline Sediment Location JRR Collection Nuclide Concentration Duplicate Date (pCilKg Dry) Analysis 11-JUN-13 K-40 12,349.0 +1- 663.0 Duplicate 11-JUN-13 K-40 13,061.0 +1- 712.2 11-JUN-13 MN-54 23.8 Duplicate 11-JUN-13 MN-54 27.6 11-JUN-13 CO-58 23.6 11-JUN-13 CO-58

  • 29.0 Duplicate 11-JUN-13 FE-59
  • 59.3 Duplicate 11-JUN-13 FE-59
  • 26.2 Duplicate 11-JUN-13 CO-60
  • 18.9 11-JUN-13 ZN-65
  • 58.0 11-JUN-13 ZN-65
  • 57.4 Duplicate 11-JUN-13 CS-1 34
  • 17.6 Duplicate 11-JUN-13 CS-134 19.2 11-JUN-13 CS-137 25.0 11-JUN-13 CS-1 37 23.9 Duplicate 03-DEC-1 3 K-40 10,926.0 +/- 595.2 03-DEC-1 3 MN-54 23.3 03-DEC-13 CO-58 28.2 03-DEC-13 FE-59 69.7 03-DEC-1 3 CO-60 10.9 03-DEC-1 3 ZN-65 45.0 03-DEC-13 CS-134 19.0 03-DEC-13 CS-1 37 23.5 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 61

Exposure Pathway - Ingestion Fish Location CCL Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 21-MAY-13 CHANNEL CATFISH K-40 3,689.8 +/- 421.3 21-MAY-13 CHANNEL CATFISH MN-54 13.7 21 -MAY-1 3 CHANNEL CATFISH CO-58 8.2 21 -MAY-1 3 CHANNEL CATFISH FE-59 16.8 21-MAY-13 CHANNEL CATFISH CO-60 6.1 21-MAY-13 CHANNEL CATFISH ZN-65 27.5 21 -MAY-1 3 CHANNEL CATFISH 1-131 13.3 21-MAY-1 3 CHANNEL CATFISH CS-1 34 11.0 21 -MAY-1 3 CHANNEL CATFISH CS-137 7.4 21-MAY-13 CHANNEL CATFISH H-3 8,852.0 +/- 242.0 21-MAY- 13 COMMON CARP K-40 3,604.5 +1- 402.7 21-MAY-1 3 COMMON CARP MN-54 12.7 21 -MAY-1 3 COMMON CARP CO-58 7.1 21-MAY-13 COMMON CARP FE-59 28.2 21-MAY-13 COMMON CARP CO-60 4.8 21-MAY-13 COMMON CARP ZN-65 16.4 21 -MAY-1 3 COMMON CARP 1-131 24.8 21 -MAY-1 3 COMMON CARP CS-134 10.6 21-MAY-13 COMMON CARP CS-137 10.0 21-MAY-13 COMMON CARP H-3 8,158.0 +1- 229.0 21-MAY-13 SMALLMOUTH BASS K-40 3,188.4 +/- 364.2 21 -MAY-1 3 SMALLMOUTH BASS MN-54 10.8 21-MAY-1 3 SMALLMOUTH BASS CO-58 4.7 21-MAY-13 SMALLMOUTH BASS FE-59 17.7 21-MAY-13 SMALLMOUTH BASS CO-60 4.4 21-MAY-13 SMALLMOUTH BASS ZN-65 20.2 21-MAY- 13 SMALLMOUTH BASS 1-131 12.6 21-MAY-1 3 SMALLMOUTH BASS CS-134 7.2 21-MAY-13 SMALLMOUTH BASS CS-1 37 12.4 21-MAY-13 SMALLMOUTH BASS H-3 8,140.0 +1- 233.0 21-MAY-13 SMALLMOUTH BUFFALO K-40 3,000.9 +/- 359.9 21 -MAY-1 3 SMALLMOUTH BUFFALO MN-54 12.2 21-MAY-13 SMALLMOUTH BUFFALO CO-58 6.6 21-MAY-1 3 SMALLMOUTH BUFFALO FE-59 27.9 21-MAY-13 SMALLMOUTH BUFFALO CO-60 6.9 21-MAY-13 SMALLMOUTH BUFFALO ZN-65 17.7 21-MAY-13 SMALLMOUTH BUFFALO 1-131 13.4 21-MAY- 13 SMALLMOUTH BUFFALO CS-134 12.6 21 -MAY- 13 SMALLMOUTH BUFFALO CS-137 11.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 62

Exposure Pathway - Ingestion Fish Location CCL Collection Sample Nuclide Concentration Duplicate Date Description (pCiIKg Wet) Analysis 21 -MAY-1 3 SMALLMOUTH BUFFALO H-3 8,022.0 +/- 223.0 17-OCT-1 3 BLUE CATFISH K-40 2,697.7 +/- 304.7 17-OCT-13 BLUE CATFISH MN-54 15.6 17-OCT-1 3 BLUE CATFISH CO-58 9.2 17-OCT-1 3 BLUE CATFISH FE-59 25.7 17-OCT-1 3 BLUE CATFISH CO-60 4.5 17-OCT-13 BLUE CATFISH ZN-65 12.6 17-OCT-13 BLUE CATFISH 1-131 47.5 17-OCT-1 3 BLUE CATFISH CS-134 11.9 17-OCT-1 3 BLUE CATFISH CS-1 37 12.4 17-OCT-13 BLUE CATFISH H-3 7,004.0 +1- 228.0 17-OCT-1 3 -CHANNEL CATFISH K-40 2,984.0 +/- 360.9 17-OCT-1 3 CHANNEL CATFISH MN-54 12.6 17-OCT-13 CHANNEL CATFISH CO-58 14.5 17-OCT-1 3 CHANNEL CATFISH FE-59 22.6 17-OCT- 13 CHANNEL CATFISH CO-60 3.4 17-OCT-1 3 CHANNEL CATFISH ZN-65 26.3 17-OCT-13 CHANNEL CATFISH 1-131 46.6 17-OCT-13 CHANNEL CATFISH CS-1 34 12.2 17-OCT-1 3 CHANNEL CATFISH CS-137 10.6 17-OCT-1 3 CHANNEL CATFISH H-3 8,007.0 +/- 242.0 17-OCT-13 COMMON CARP K-40 2,799.4 +1- 346.7 17-OCT-1 3 COMMON CARP MN-54 13.3 17-OCT-1 3 COMMON CARP CO-58 8.1 17-OCT-1 3 COMMON CARP FE-59 42.1 17-OCT-13 COMMON CARP CO-60 8.7 17-OCT- 13 COMMON CARP ZN-65 27.7 17-OCT-1 3 COMMON CARP 1-131 58.0 17-OCT- 13 COMMON CARP CS-134 12.8 17-OCT-13 COMMON CARP CS-1 37 17.1 17-OCT-13 COMMON CARP H-3 7,348.0 +1- 223.0 17-OCT-1 3 SMALLMOUTH BUFFALO K-40 2,840.3 +/- 353.8 17-OCT- 13 SMALLMOUTH BUFFALO MN-54 12.8 17-OCT-13 SMALLMOUTH BUFFALO CO-58 9.9 17-OCT- 13 SMALLMOUTH BUFFALO FE-59 32.0 17-OCT-1 3 SMALLMOUTH BUFFALO CO-60 10.8 17-OCT- 13 SMALLMOUTH BUFFALO ZN-65 32.2 17-OCT-13 SMALLMOUTH BUFFALO 1-131 71.2 17-OCT-1 3 SMALLMOUTH BUFFALO CS-134 13.9 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 63

Exposure Pathway - Ingestion Fish Location CCL Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 17-OCT- 13 SMALLMOUTH BUFFALO CS-137 12.4 17-OCT-1 3 SMALLMOUTH BUFFALO H-3 6,985.0 +/- 220.0 17-OCT-1 3 WALLEYE K-40 3,391.0 +/- 315.5 17-OCT-13 WALLEYE MN-54 8.9 17-OCT-13 WALLEYE CO-58 12.0 17-OCT-1 3 WALLEYE FE-59 27.0 17-OCT-13 WALLEYE CO-60 11.2 17-OCT-13 WALLEYE ZN-65 14.5 17-OCT-1 3 WALLEYE 1-131 41.0 17-OCT-1 3 WALLEYE CS-1 34 12.7 17-OCT-13 WALLEYE CS-137 12.1 17-OCT-13 WALLEYE H-3 7,414.0 +1- 228.0 17-OCT- 13 WHITE BASS K-40 3,095.1 +1- 312.8 17-OCT-1 3 WHITE BASS MN-54 9.9 17-OCT-13 WHITE BASS CO-58 11.5 17-OCT-13 WHITE BASS FE-59 28.7 17-OCT- 13 WHITE BASS CO-60 9.0 17-OCT-1 3 WHITE BASS ZN-65 25.8 17-OCT-1 3 WHITE BASS 1-131 78.3 17-OCT-13 WHITE BASS CS-134 13.1 17-OCT-1 3 WHITE BASS CS-1 37 13.2 17-OCT-1 3 WHITE BASS H-3 7,496.0 +/- 227.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 64

Exposure Pathway - Ingestion Fish Location JRR Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 11-JUN-13 CHANNEL CATFISH K-40 3,669.4 +/- 376.5 11-JUN-13 CHANNEL CATFISH MN-54 11.1 11-JUN-13 CHANNEL CATFISH CO-58 10.4 11-JUN-13 CHANNEL CATFISH FE-59 20.8 11-JUN-13 CHANNEL CATFISH CO-60 8.0 11-JUN-13 CHANNEL CATFISH ZN-65 29.1 11-JUN-13 CHANNEL CATFISH 1-131 27.4 11-JUN-13 CHANNEL CATFISH CS-1 34 13.6 11-JUN-13 CHANNEL CATFISH CS-137 13.1 11-JUN-13 CHANNEL CATFISH H-3 156.0 11-JUN-13 COMMON CARP K-40 3,660.4 +/- 415.6 11-JUN-13 COMMON CARP MN-54 16.1 11-JUN-13 COMMON CARP CO-58 9.2 11-JUN-13 COMMON CARP FE-59 27.7 11-JUN-13 COMMON CARP CO-60 10.2 11-JUN-13 COMMON CARP ZN-65 25.0 11-JUN-13 COMMON CARP 1-131 27.1 11-JUN-13 COMMON CARP CS-1 34 14.8 11-JUN-13 COMMON CARP CS-1 37 14.0 11-JUN-13 COMMON CARP H-3 156.0 11-JUN-13 SMALLMOUTH BUFFALO K-40 3,661 .9 +/- 378.2 11-JUN-13 SMALLMOUTH BUFFALO MN-54 10.1 11-JUN-13 SMALLMOUTH BUFFALO CO-58 11.8 11-JUN-13 SMALLMOUTH BUFFALO FE-59 25.9 11-JUN-13 SMALLMOUTH BUFFALO CO-60 10.6 11-JUN-13 SMALLMOUTH BUFFALO ZN-65 22.1 11-JUN-13 SMALLMOUTH BUFFALO 1-131 19.2 11-JUN-13 SMALLMOUTH BUFFALO CS-134 14.0 11-JUN-13 SMALLMOUTH BUFFALO CS-137 12.7 11-JUN-13 SMALLMOUTH BUFFALO H-3 156.0 03-DEC-1 3 CHANNEL CATFISH K-40 3,334.1 +/- 375.3 03-DEC-13 CHANNEL CATFISH MN-54 8.9 03-DEC-13 CHANNEL CATFISH CO-58 10.2 03-DEC-1 3 CHANNEL CATFISH FE-59 15.4 03-DEC-1 3 CHANNEL CATFISH CO-60 4.3 03-DEC-13 CHANNEL CATFISH ZN-65 10.4 03-DEC-13 CHANNEL CATFISH 1-131 27.5 03-DEC-13 CHANNEL CATFISH CS-134 16.0 03-DEC-13 CHANNEL CATFISH CS-137 7.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 65

Exposure Pathway - Ingestion Fish Location JRR Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 03-DEC-13 CHANNEL CATFISH H-3 113.0 03-DEC-13 COMMON CARP K-40 2,990.1 +/- 364.1 03-DEC-13 COMMON CARP MN-54 12.3 03-DEC-1 3 COMMON CARP CO-58 8.3 03-DEC-1 3 COMMON CARP FE-59 32.2 03-DEC-1 3 COMMON CARP CO-60 11.1 03-DEC-1 3 COMMON CARP ZN-65 27.3 03-DEC-13 COMMON CARP 1-131 26.1 03-DEC-13 COMMON CARP CS-134 14.9 03-DEC-13 COMMON CARP CS-1 37 12.3 03-DEC-1 3 COMMON CARP H-3 118.0 03-DEC-1 3 FRESHWATER DRUM K-40 3,i79.5 +/- 299.7 03-DEC-1 3 FRESHWATER DRUM MN-54 11.4 03-DEC-13 FRESHWATER DRUM CO-58 6.3 03-DEC-13 FRESHWATER DRUM FE-59 24.2 03-DEC-13 FRESHWATER DRUM CO-60 6.4 03-DEC-13 FRESHWATER DRUM ZN-65 26.0 03-DEC-1 3 FRESHWATER DRUM 1-131 19.1 03-DEC-1 3 FRESHWATER DRUM CS-134 11.2 03-DEC-1 3 FRESHWATER DRUM CS-137 14.5 03-DEC-1 3 FRESHWATER DRUM H-3 122.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 66

Exposure Pathway - Ingestion Food/Garden Location B-1 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 28-MAY-1 3 HORSERADISH LEAVES BE-7 362.5 +/- 101.6 28-MAY-1 3 HORSERADISH LEAVES K-40 5,075.4 +/- 337.9 28-MAY-13 HORSERADISH LEAVES MN-54

  • 11.0 28-MAY-13 HORSERADISH LEAVES CO-58
  • 10.5 28-MAY-1 3 HORSERADISH LEAVES FE-59
  • 22.0 28-MAY-1 3 HORSERADISH LEAVES CO-60
  • 12.6 28-MAY-1 3 HORSERADISH LEAVES ZN-65
  • 25.0 28-MAY- 13 HORSERADISH LEAVES ZR-NB-95 < 8.1 28-MAY-13 HORSERADISH LEAVES 1-131
  • 21.1 28-MAY-13 HORSERADISH LEAVES CS-134
  • 11.0 28-MAY-1 3 HORSERADISH LEAVES CS-1 37
  • 10.3 24-JUN-13 HORSERADISH LEAVES BE-7 831.1 +/- 157.6 24-JUN-13 HORSERADISH LEAVES K-40 5,710.0 +/- 418.8 24-JUN-13 HORSERADISH LEAVES MN-54 < 11.4 24-JUN-13 HORSERADISH LEAVES CO-58 < 9.0 24-JUN-13 HORSERADISH LEAVES FE-59 < 13.4 24-JUN-13 HORSERADISH LEAVES CO-60 < 10.4 24-JUN-13 HORSERADISH LEAVES ZN-65 < 28.2 24-JUN-13 HORSERADISH LEAVES ZR-NB-95 < 11.2 24-JUN-13 HORSERADISH LEAVES 1-131 < 22.7 24-JUN-13 HORSERADISH LEAVES CS-134 < 9.9 24-JUN-13 HORSERADISH LEAVES CS-1 37 < 10.8 22-JUL-13 HORSERADISH LEAVES BE-7 1,107.5 +/- 254.4 22-JUL-13 HORSERADISH LEAVES K-40 5,193.3 +/- 391.2 22-JUL-13 HORSERADISH LEAVES MN-54 < 9.9 22-JUL-13 HORSERADISH LEAVES CO-58 < 10.9 22-JUL-13 HORSERADISH LEAVES FE-59 < 25.5 22-JUL-13 HORSERADISH LEAVES CO-60 < 7.2 22-JUL-13 HORSERADISH LEAVES ZN-65 < 33.9 22-JUL-13 HORSERADISH LEAVES ZR-NB-95 < 11.5 22-JUL-13 HORSERADISH LEAVES 1-131 < 19.3 22-JUL-13 HORSERADISH LEAVES CS-1 34 < 9.9 22-JUL-13 HORSERADISH LEAVES CS-1 37 < 9.8 19-AUG- 13 HORSERADISH LEAVES BE-7 325.1 +/- 104.1 Duplicate 19-AUG- 13 HORSERADISH LEAVES BE-7 470.5 +/- 159.6 19-AUG- 13 HORSERADISH LEAVES K-40 4,907.4 +/- 350.4 Duplicate 19-AUG- 13 HORSERADISH LEAVES K-40 4,891.9 +/- 407.9 19-AUG-13 HORSERADISH LEAVES MN-54 < 11.5 19-AUG-13 HORSERADISH LEAVES MN-54 < 6.8 Duplicate 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 67

Exposure Pathway - Ingestion Food/Garden Location B-1 Collection Sample Nuclide Concentration Duplicate Date Description (pCiIKg Wet) Analysis 19-AUG- 13 HORSERADISH LEAVES CO-58 9.1 Duplicate 19-AUG-13 HORSERADISH LEAVES CO-58 14.6 19-AUG- 13 HORSERADISH LEAVES FE-59 14.3 Duplicate 19-AUG-13 HORSERADISH LEAVES FE-59 23.1 19-AUG- 13 HORSERADISH LEAVES CO-60 6.7 Duplicate 19-AUG-13 HORSERADISH LEAVES CO-60 12.1 19-AUG- 13 HORSERADISH LEAVES ZN-65 27.0 Duplicate 19-AUG- 13 HORSERADISH LEAVES ZN-65 21.5 19-AUG-13 HORSERADISH LEAVES ZR-NB-95 17.0 19-AUG- 13 HORSERADISH LEAVES ZR-NB-95 9.3 Duplicate 19-AUG-13 HORSERADISH LEAVES 1-131 21.5 19-AUG-13 HORSERADISH LEAVES 1-131 17.8 Duplicate 19-AUG-13 HORSERADISH LEAVES CS-134 9.5 Duplicate 19-AUG- 13 HORSERADISH LEAVES CS-134 11.4 19-AUG- 13 HORSERADISH LEAVES CS-137 7.9 19-AUG-13 HORSERADISH LEAVES CS-137 11.0 Duplicate 17-SEP-13 HORSERADISH LEAVES BE-7 281.4 +1- 147.4 17-SEP-13 HORSERADISH LEAVES K-40 5,745.2 +1- 408.3 17-SEP-13 HORSERADISH LEAVES MN-54 11.4 17-SEP-13 HORSERADISH LEAVES CO-58 12.9 17-SEP-13 HORSERADISH LEAVES FE-59 19.3 17-SEP-13 HORSERADISH LEAVES CO-60 14.3 17-SEP-13 HORSERADISH LEAVES ZN-65 26.3 17-SEP-13 HORSERADISH LEAVES ZR-NB-95 13.6 17-SEP-1 3 HORSERADISH LEAVES 1-131 28.1 17-SEP-13 HORSERADISH LEAVES CS-134 9.6 17-SEP-13 HORSERADISH LEAVES CS-1 37 12.5 14-OCT-13 HORSERADISH LEAVES BE-7 623.5 +1- 177.2 14-OCT-13 HORSERADISH LEAVES K-40 4,688.5 +1- 395.8 14-OCT-13 HORSERADISH LEAVES MN-54 8.2 14-OCT-1 3 HORSERADISH LEAVES CO-58 8.7 14-OCT-1 3 HORSERADISH LEAVES FE-59 19.3 14-OCT-1 3 HORSERADISH LEAVES CO-60 9.3 14-OCT-13 HORSERADISH LEAVES ZN-65 20.6 14-OCT-13 HORSERADISH LEAVES ZR-NB-95 10.1 14-OCT-13 HORSERADISH LEAVES 1-131 35.1 14-OCT-1 3 HORSERADISH LEAVES CS-1 34 13.7 14-OCT-1 3 HORSERADISH LEAVES CS-1 37 13.8 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 68

Exposure Pathway - Ingestion Food/Garden Location D-2 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 28-MAY-13 HORSERADISH LEAVES BE-7 411.8 +/- 132.9 28-MAY-1 3 HORSERADISH LEAVES K-40 5,011.0 +/- 344.2 28-MAY-1 3 HORSERADISH LEAVES MN-54 < 10.2 28-MAY-13 HORSERADISH LEAVES CO-58 < 10.9 28-MAY-13 HORSERADISH LEAVES FE-59 < 13.4 28-MAY-1 3 HORSERADISH LEAVES CO-60 < 9.3 28-MAY-1 3 HORSERADISH LEAVES ZN-65 < 22.8 28-MAY-13 HORSERADISH LEAVES ZR-NB-95 < 8.7 28-MAY-13 HORSERADISH LEAVES 1-131 < 24.5 28-MAY-1 3 HORSERADISH LEAVES CS-134 < 12.2 28-MAY-1 3 HORSERADISH LEAVES CS-137 < 10.6 24-JUN-13 HORSERADISH LEAVES BE-7 802.9 +1- 206.8 24-JUN-13 HORSERADISH LEAVES K-40 6,803.9 +/- 530.0 24-JUN-13 HORSERADISH LEAVES MN-54

  • 13.7 24-JUN-13 HORSERADISH LEAVES CO-58
  • 12.3 24-JUN-13 HORSERADISH LEAVES FE-59
  • 29.8 24-JUN-13 HORSERADISH LEAVES CO-60
  • 15.8 24-JUN-13 HORSERADISH LEAVES ZN-65
  • 44.3 24-JUN-13 HORSERADISH LEAVES ZR-NB-95
  • 17.8 24-JUN-13 HORSERADISH LEAVES 1-131
  • 31.0 24-JUN-13 HORSERADISH LEAVES CS-134
  • 13.3 24-JUN-13 HORSERADISH LEAVES CS-137
  • 18.0 22-JUL-13 HORSERADISH LEAVES BE-7 1,259.3 +/1- 189.9 22-JUL-13 HORSERADISH LEAVES K-40 5,725.8 +/- 410.5 22-JUL-13 HORSERADISH LEAVES MN-54 < 12.5 22-JUL-13 HORSERADISH LEAVES CO-58 < 6.0 22-JUL-13 HORSERADISH LEAVES FE-59 < 18.0 22-JUL-13 HORSERADISH LEAVES CO-60 < 12.3 22-JUL-13 HORSERADISH LEAVES ZN-65 < 12.3 22-JUL-13 HORSERADISH LEAVES ZR-NB-95 < 16.4 22-JUL-13 HORSERADISH LEAVES 1-131 < 29.9 22-JUL-13 HORSERADISH LEAVES CS-134 < 12.1 22-JUL-13 HORSERADISH LEAVES CS-137 < 14.9 19-AUG- 13 HORSERADISH LEAVES BE-7 908.3 +/- 164.6 19-AUG-13 HORSERADISH LEAVES K-40 4,718.7 +/- 409.4 19-AUG-1 3 HORSERADISH LEAVES MN-54 < 12.7 19-AUG- 13 HORSERADISH LEAVES CO-58 < 11.9 19-AUG- 13 HORSERADISH LEAVES FE-59 < 34.4 19-AUG-13 HORSERADISH LEAVES CO-60 < 10.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 69

Exposure Pathway - Ingestion FoodlGarden Location D-2 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 19-AUG-13 HORSERADISH LEAVES ZN-65 24.7 19-AUG- 13 HORSERADISH LEAVES ZR-NB-95 15.1 19-AUG- 13 HORSERADISH LEAVES 1-131 20.4 19-AUG-13 HORSERADISH LEAVES CS-134 10.6 19-AUG-13 HORSERADISH LEAVES CS-1 37 12.8 17-SEP-13 HORSERADISH LEAVES BE-7 396.7+/ 143.3 17-SEP-13 HORSERADISH LEAVES K-40 6,644.2 +/- 455.4 17-SEP-1 3 HORSERADISH LEAVES MN-54 10.0 17-SEP-13 HORSERADISH LEAVES CO-58 15.2 17-SEP-13 HORSERADISH LEAVES FE-59 34.6 17-SEP-13 HORSERADISH LEAVES CO-60 8.2 17-SEP-13 HORSERADISH LEAVES ZN-65 22.2 17-SEP-1 3 HORSERADISH LEAVES ZR-NB-95 8.8 17-SEP-1 3 HORSERADISH LEAVES 1-131 22.8 17-SEP-13 HORSERADISH LEAVES CS-134 11.3 17-SEP-13 HORSERADISH LEAVES CS-137 13.8 14-OCT-1 3 HORSERADISH LEAVES BE-7 214.6 14-OCT-1 3 HORSERADISH LEAVES K-40 6,321.7+- 531.2 14-OCT-1 3 HORSERADISH LEAVES MN-54 18.2 14-OCT-13 HORSERADISH LEAVES CO-58 14.8 14-OCT-13 HORSERADISH LEAVES FE-59 33.7 14-OCT-1 3 HORSERADISH LEAVES CO-60 15.9 14-OCT-1 3 HORSERADISH LEAVES ZN-65 23.3 14-OCT-1 3 HORSERADISH LEAVES ZR-NB-95 17.1 14-OCT-13 HORSERADISH LEAVES 1-131 39.2 14-OCT-13 HORSERADISH LEAVES CS-1 34 20.0 14-OCT-1 3 HORSERADISH LEAVES CS-1 37 18.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 70

Exposure Pathway - Ingestion Food/Garden Location H-2 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 28-MAY-1 3 HORSERADISH LEAVES BE-7 323.1 +/- 120.6 28-MAY-1 3 HORSERADISH LEAVES K-40 5,285.6 +1- 375.2 28-MAY-1 3 HORSERADISH LEAVES MN-54 10.5 28-MAY-1 3 HORSERADISH LEAVES CO-58 13.5 28-MAY-1 3 HORSERADISH LEAVES FE-59 17.5 28-MAY-1 3 HORSERADISH LEAVES CO-60 11.5 28-MAY-13 HORSERADISH LEAVES ZN-65 23.4 28-MAY-1 3 HORSERADISH LEAVES ZR-NB-95 13.1 28-MAY-1 3 HORSERADISH LEAVES 1-131 24.2 28-MAY- 13 HORSERADISH LEAVES CS-134 9.3 28-MAY-1 3 HORSERADISH LEAVES CS-1 37 11.8 19-AUG-13 HORSERADISH LEAVES BE-7 763.8+1 141.9 19-AUG-13 HORSERADISH LEAVES K-40 5,157.1+1 374.3 19-AUG-13 HORSERADISH LEAVES MN-54 8.7 19-AUG-1 3 HORSERADISH LEAVES CO-58 7.9 19-AUG- 13 HORSERADISH LEAVES FE-59 15.7 19-AUG-13 HORSERADISH LEAVES CO-60 8.9 19-AUG-1 3 HORSERADISH LEAVES ZN-65 26.3 19-AUG-13 HORSERADISH LEAVES ZR-NB-95 14.0 19-AUG-13 HORSERADISH LEAVES 1-131 17.1 19-AUG-13 HORSERADISH LEAVES CS-134 6.7 19-AUG- 13 HORSERADISH LEAVES CS-137 7.2 17-SEP-13 HORSERADISH LEAVES BE-7 131.1 17-SEP-13 HORSERADISH LEAVES K-40 5,201.6+1 400.6 17-SEP-13 HORSERADISH LEAVES MN-54 9.4 17-SEP-13 HORSERADISH LEAVES CO-58 10.5 17-SEP-13 HORSERADISH LEAVES FE-59 24.1 17-SEP-1 3 HORSERADISH LEAVES CO-60 8.5 17-SEP-13 HORSERADISH LEAVES ZN-65 24.4 17-SEP-13 HORSERADISH LEAVES ZR-NB-95 9.8 17-SEP-13 HORSERADISH LEAVES 1-131 29.7 17-SEP-13 HORSERADISH LEAVES CS-134 12.1 17-SEP-13 HORSERADISH LEAVES CS-137 7.7 14-OCT-1 3 HORSERADISH LEAVES BE-7 399.7+1 205.1 14-OCT-1 3 HORSERADISH LEAVES K-40 6,914.9+1 536.5 14-OCT-13 HORSERADISH LEAVES MN-54 17.0 14-OCT-13 HORSERADISH LEAVES CO-58 17.5 14-OCT-1 3 HORSERADISH LEAVES FE-59 24.0 14-OCT-1 3 HORSERADISH LEAVES CO-60 14.9 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 71

Exposure Pathway - Ingestion FoodlGarden Location H-2 Collection Sample Nuclide Concentration Duplicate Date Description (pCilKg Wet) Analysis 14-OCT-1 3 HORSERADISH LEAVES ZN-65

  • 28.9 14-OCT-1 3 HORSERADISH LEAVES ZR-NB-95
  • 18.6 14-OCT-1 3 HORSERADISH LEAVES 1-131
  • 35.1 14-OCT-1 3 HORSERADISH LEAVES CS-134
  • 16.0 14-OCT-13 HORSERADISH LEAVES CS-1 37

Exposure Pathway - Ingestion FoodlGarden Location Q-6 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 24-JUN-13 WATERMELON LEAVES BE-7 371.6 +1- 138.4 24-JUN-13 WATERMELON LEAVES K-40 5,584.6 +1- 454.8 24-JUN-13 WATERMELON LEAVES MN-54 13.2 24-JUN-13 WATERMELON LEAVES CO-58 13.3 24-JUN-13 WATERMELON LEAVES FE-59 15.9 24-JUN-13 WATERMELON LEAVES CO-60 12.3 24-JUN-13 WATERMELON LEAVES ZN-65 23.3 24-JUN-13 WATERMELON LEAVES ZR-NB-95 16.0 24-JUN-13 WATERMELON LEAVES 1-131 25.2 24-JUN-13 WATERMELON LEAVES CS-134 13.0 24-JUN-13 WATERMELON LEAVES CS-137 13.1 22-JUL-13 SQUASH LEAVES BE-7 1,690.7 +1- 208.8 22-JUL-13 SQUASH LEAVES K-40 4,698.5 +1- 357.2 22-JUL-13 SQUASH LEAVES MN-54 10.1 22-JUL-13 SQUASH LEAVES CO-58 12.6 22-JUL-13 SQUASH LEAVES FE-59 16.3 22-JUL-13 SQUASH LEAVES CO-60 10.0 22-JUL-13 SQUASH LEAVES ZN-65 14.4 22-JUL-13 SQUASH LEAVES ZR-NB-95 10.4 22-JUL-13 SQUASH LEAVES 1-131 28.0 22-JUL-13 SQUASH LEAVES CS-134 10.4 22-JUL-13 SQUASH LEAVES CS-137 11.8 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 73

Exposure Pathway - Ingestion Feed and Forage Location NR-D1 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 29-OCT-13 NON-IRRIGATED SOYBEANS BE-7 < 65.4 29-OCT-1 3 NON-IRRIGATED SOYBEANS K-40 16,342.0 +/- 514.3 29-OCT-1 3 NON-IRRIGATED SOYBEANS MN-54 < 8.8 29-OCT-13 NON-IRRIGATED SOYBEANS CO-58 < 11.8 29-OCT-13 NON-IRRIGATED SOYBEANS FE-59 < 27.9 29-OCT-13 NON-IRRIGATED SOYBEANS CO-60 < 9.0 29-OCT-1 3 NON-IRRIGATED SOYBEANS ZN-65 < 14.0 29-OCT-13 NON-IRRIGATED SOYBEANS ZR-NB-95 < 5.5 29-OCT-13 NON-IRRIGATED SOYBEANS 1-131 < 11.4 29-OCT-13 NON-IRRIGATED SOYBEANS CS-134 < 10.2 29-OCT-13 NON-IRRIGATED SOYBEANS CS-137 < 6.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 74

Exposure Pathway - Ingestion Feed and Forage Location NR-D2 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 14-OCT-1 3 IRRIGATED SOYBEANS BE-7 60.2 14-OCT-13 IRRIGATED SOYBEANS K-40 12,882.0 +/- 496.4 14-OCT-13 IRRIGATED SOYBEANS MN-54 5.1 14-OCT-1 3 IRRIGATED SOYBEANS CO-58 5.6 14-OCT-1 3 IRRIGATED SOYBEANS FE-59 < 18.6 14-OCT-13 IRRIGATED SOYBEANS CO-60 < 9.2 14-OCT-13 IRRIGATED SOYBEANS ZN-65 < 28.7 14-OCT-13 IRRIGATED SOYBEANS ZR-NB-95 < 11.8 14-OCT-1 3 IRRIGATED SOYBEANS 1-131 < 16.3 14-OCT-1 3 IRRIGATED SOYBEANS CS-134 < 11.2 14-OCT-13 IRRIGATED SOYBEANS CS-137 < 7.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 75

Exposure Pathway - Ingestion Feed and Forage Location NR-U1 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 10-OCT- 13 IRRIGATED CORN BE-7 < 57.4 10-OCT-1 3 IRRIGATED CORN K-40 2,543.7 +/- 201.9 10-OCT-1 3 IRRIGATED CORN MN-54 < 4.8 10-OCT-13 IRRIGATED CORN CO-58 < 3.9 10-OCT-13 IRRIGATED CORN FE-59 < 12.7 10-OCT-1 3 IRRIGATED CORN CO-60 < 5.4 10-OCT-1 3 IRRIGATED CORN ZN-65 < 18.9 10-OCT-1 3 IRRIGATED CORN ZR-NB-95 < 9.9 10-OCT- 13 IRRIGATED CORN 1-131 < 17.2 10-OCT-1 3 IRRIGATED CORN CS-134 < 6.3 10-OCT-1 3 IRRIGATED CORN CS-1 37 < 4.7 04-NOV-13 NON-IRRIGATED SOYBEANS BE-7 < 66.9 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS BE-7 < 57.1 04-NOV-13 NON-IRRIGATED SOYBEANS K-40 13,299.0 +/- 474.3 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS K-40 12,669.0 +/- 487.5 04-NOV-13 NON-IRRIGATED SOYBEANS MN-54 < 8.6 Duplicate 04-NOV-1 3 NON-IRRIGATED SOYBEANS MN-54 < 6.6 04-NOV-1 3 NON-IRRIGATED SOYBEANS CO-58 < 9.7 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS CO-58 < 7.8 04-NOV-13 NON-IRRIGATED SOYBEANS FE-59 < 25.6 Duplicate 04-NOV-1 3 NON-IRRIGATED SOYBEANS FE-59 < 15.4 04-NOV-13 NON-IRRIGATED SOYBEANS CO-60 < 11.3 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS CO-60 < 4.9 04-NOV-13 NON-IRRIGATED SOYBEANS ZN-65 < 33.3 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS ZN-65 < 11.8 04-NOV-1 3 NON-IRRIGATED SOYBEANS ZR-NB-95 < 11.1 Duplicate 04-NOV-1 3 NON-IRRIGATED SOYBEANS ZR-NB-95 < 6.1 04-NOV-1 3 NON-IRRIGATED SOYBEANS 1-131 < 14.0 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS 1-131 < 8.0 04-NOV-13 NON-IRRIGATED SOYBEANS CS-134 < 10.0 04-NOV-13 NON-IRRIGATED SOYBEANS CS-134 < 10.3 Duplicate 04-NOV-1 3 NON-IRRIGATED SOYBEANS CS-137 < 6.3 Duplicate 04-NOV-13 NON-IRRIGATED SOYBEANS CS-137 < 10.5 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 76

Exposure Pathway - Aquatic Bottom Sediment Location DC Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 06-JUN-13 K-40 11,336.0 +/- 1,043.0 06-JUN-13 MN-54 48.2 06-JUN-13 CO-58 61.0 06-JUN-13 FE-59 94.5 06-JUN-13 CO-60 33.7 06-JUN-13 ZN-65 86.8 06-JUN-13 CS-134 35.0 06-JUN-13 CS-137 97.4+- 40.6 06-JUN-13 FE-55 15,032.4 03-DEC-13 K-40 9,402.3+1 944.4 03-DEC-1 3 MN-54 39.0 03-DEC-13 CO-58 52.2 03-DEC-13 FE-59 51.0 03-DEC-1 3 CO-60 29.2 03-DEC-1 3 ZN-65 67.0 03-DEC-1 3 CS-134 39.9 03-DEC-13 CS-137 89.5+1 52.9 03-DEC-13 FE-55 15,670.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 77

Exposure Pathway - Aquatic Bottom Sediment Location EEA Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 30-APR-1 3 K-40 11,576.0 +/- 574.2 30-APR-1 3 MN-54 < 19.3 30-APR- 13 CO-58 < 17.9 30-APR-1 3 FE-59 < 47.1 30-APR-1 3 CO-60 < 12.3 30-APR-1 3 ZN-65 < 51.9 30-APR-13 CS-i 34 < 19.1 30-APR-13 CS-1 37 55.8 +/- 15.7 26-AUG-13 K-40 11,346.0 +/- 669.6 26-AUG-13 MN-54 < 26.0 26-AUG-1 3 CO-58 < 26.9 26-AUG-13 FE-59 < 68.3 26-AUG-13 CO-60 < 12.2 26-AUG-13 ZN-65 < 54.7 26-AUG-13 CS-134 < 23.6 26-AUG-13 CS-137 67.0 +/- 29.5 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 78

Exposure Pathway - Aquatic Bottom Sediment Location ESW 2013-5 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 06-JUN-13 K-40 9,303.1 +/- 901.4 06-JUN-13 MN-54 < 45.9 06-JUN-13 CO-58 < 73.0 06-JUN-13 FE-59 < 125.7 06-JUN-13 CO-60 < 36.4 06-JUN-13 ZN-65 < 108.5 06-JUN-13 CS-1 34 < 37.7 06-JUN-13 CS-1 37 < 47.7 06-JUN-13 FE-55 < 14,371.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 79

Exposure Pathway - Aquatic Bottom Sediment Location ESW 2013-6 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 03-DEC-1 3 K-40 5,110.1 +/- 683.3 03-DEC-1 3 MN-54 < 26.7 03-DEC-13 CO-58 < 30.4 03-DEC-1 3 FE-59 < 64.1 03-DEC-1 3 CO-60 < 10.5 03-DEC-13 ZN-65 < 66.1 03-DEC-13 CS-1 34 < 30.6 03-DEC-1 3 CS-137 < 32.7 03-DEC-1 3 FE-55 < 16,091.5 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 80

Exposure Pathway - Aquatic Bottom Sediment Location JRR Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 11-JUN-13 K-40 12,752.0 +/- 1,135.0 11-JUN-13 MN-54 < 57.2 11-JUN-13 CO-58 < 29.9 11-JUN-13 FE-59 < 121.9 11-JUN-13 CO-60 < 27.3 11-JUN-13 ZN-65 < 94.4 11-JUN-13 CS-134 < 39.6 11-JUN-13 CS-137 < 54.8 03-DEC-1 3 K-40 11,660.0 +/- 993.4 03-DEC-1 3 MN-54 < 38.1 03-DEC-13 CO-58 < 54.4 03-DEC-13 FE-59 < 134.2 03-DEC-1 3 CO-60 < 13.3 03-DEC-1 3 ZN-65 < 99.4 03-DEC-13 CS-1 34 < 33.0 03-DEC-13 CS-137 84.8 +/- 43.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 81

Exposure Pathway - Aquatic Bottom Sediment Location MUDS Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 16-SEP-13 K-40 10,357.0 +/- 645.8 16-SEP-13 MN-54 < 22.2 16-SEP-13 CO-58 < 23.1 16-SEP-13 FE-59 < 106.0 16-SEP-13 CO-60 < 9.8 16-SEP-13 ZN-65 < 58.7 16-SEP-13 CS-1 34 < 21.7 16-SEP-13 CS-1 37 38.4 +/- 22.6 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 82

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-17 Collection Nuclide Concentration Duplicate Date (pCilKg Dry) Analysis 06-JUN-13 K-40 12,602.0 +/- 690.7 06-JUN-13 MN-54 < 34.6 06-JUN-13 CO-58 < 43.8 06-JUN-13 FE-59 < 75.2 06-JUN-13 CO-60 < 22.1 06-JUN-13 ZN-65 < 78.0 06-JUN-13 CS-134 < 20.5 06-JUN-13 CS-1 37 65.8 +/- 27.9 06-JUN-13 FE-55 < 11,670.2 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 83

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-18 Collection Nuclide Concentration Duplicate Date (pCilKg Dry) Analysis 06-JUN-13 K-40 9,387.0 +/- 822.3 06-JUN-13 MN-54 < 39.2 06-JUN-13 CO-58 < 47.8 06-JUN-13 FE-59 < 116.9 06-JUN-13 CO-60 < 33.8 06-JUN-13 ZN-65 < 80.6 06-JUN-13 CS-134 < 24.4 06-JUN-13 CS-137 55.7 +/- 31.4 06-JUN-13 FE-55 < 14,371.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 84

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-19 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 06-JUN-13 K-40 9,395.4 +/- 937.7 06-JUN-13 MN-54 < 45.2 06-JUN-13 CO-58 < 46.7 06-JUN-13 FE-59 < 100.2 06-JUN-13 CO-60 < 26.1 06-JUN-13 ZN-65 < 69.6 06-JUN-13 CS-1 34 < 31.1 06-JUN-13 CS-137 103.3 +/- 39.2 06-JUN-13 FE-55 < 14,371.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 85

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-20 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 06-JUN-13 K-40 10,289.0 +/- 692.4 06-JUN-13 MN-54 32.9 06-JUN-13 CO-58 41.7 06-JUN-13 FE-59 112.5 06-JUN-13 CO-60 12.8 06-JUN-13 ZN-65 80.8 06-JUN-13 CS-134 20.6 06-JUN-13 CS-1 37 26.8 06-JUN-13 FE-55 14,371.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 86

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-21 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 03-DEC-13 K-40 9,508.7 +/- 749.2 03-DEC-13 MN-54 < 32.7 03-DEC-1 3 CO-58 < 40.0 03-DEC-1 3 FE-59 < 75.8 03-DEC-13 CO-60 < 24.2 03-DEC-13 ZN-65 < 48.0 03-DEC-1 3 CS-134 < 26.2 03-DEC-1 3 CS-1 37 58.1 +/- 22.0 03-DEC-13 FE-55 < 15,538.2 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 87

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-22 Collection Nuclide Concentration Duplicate Date (pCilKg Dry) Analysis 03-DEC-1 3 K-40 11,707.0 +/- 820.3 03-DEC-1 3 MN-54 < 29.6 03-DEC-13 CO-58 < 34.9 03-DEC-13 FE-59 < 56.8 03-DEC-13 CO-60 < 29.2 03-DEC-1 3 ZN-65 < 87.4 03-DEC-1 3 CS-134 < 27.3 03-DEC-1 3 CS-1 37 64.5 +/- 29.2 03-DEC-13 FE-55 < 15,918.5 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 88

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-23 Collection Nuclide Concentration Duplicate Date (pCilKg Dry) Analysis 03-DEC-13 K-40 8,718.5 +/- 782.4 03-DEC-13 MN-54 < 24.6 03-DEC-1 3 CO-58 < 32.8 03-DEC-1 3 FE-59 < 72.7 03-DEC-13 CO-60 < 21.1 03-DEC-13 ZN-65 < 67.2 03-DEC-1 3 CS-134 < 29.0 03-DEC-1 3 CS-1 37 < 34.4 03-DEC-13 FE-55 < 15,778.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 89

Exposure Pathway - Aquatic Bottom Sediment Location UHS 2013-24 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 03-DEC-1 3 K-40 11,811.0 +/- 1,010.0 03-DEC-13 MN-54 < 54.7 03-DEC-13 CO-58 < 52.7 03-DEC-1 3 FE-59 < 101.3 03-DEC-1 3 CO-60 < 46.8 03-DEC-1 3 ZN-65 < 94.3 03-DEC-1 3 CS-134 < 47.4 03-DEC-13 CS-137 < 62.9 03-DEC-13 FE-55 < 15,876.2 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 90

Exposure Pathway - Aquatic Bottom Sediment Location UHS HS-5 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 06-JUN-13 K-40 9,468.8 +/- 864.3 06-JUN-13 MN-54 < 47.6 06-JUN-13 CO-58 < 34.1 06-JUN-13 FE-59 < 133.5 06-JUN-13 CO-60 < 16.5 06-JUN-13 ZN-65 < 99.8 06-JUN-13 CS-134 < 28.9 06-JUN-13 CS-1 37 62.7 +/- 33.7 06-JUN-13 FE-55 < 14,942.8 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 91

Exposure Pathway - Aquatic Bottom Sediment Location UHS HS-6 Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 03-DEC-13 K-40 10,688.0 +/- 963.5 03-DEC-13 MN-54 < 51.6 03-DEC-1 3 CO-58 < 44.9 03-DEC-1 3 FE-59 < 108.8 03-DEC-13 CO-60 < 16.3 03-DEC-13 ZN-65 < 102.9 03-DEC-1 3 CS-134 < 40.0 03-DEC-1 3 CS-1 37 108.2 +/- 42.5 03-DEC-1 3 FE-55 < 15,915.3 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 92

Exposure Pathway - Aquatic Vegetation Location DC-ALT Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Sample 01-AUG-13 AMERICAN LOTUS BE-7 1,872.6 +/- 269.9 01-AUG-13 AMERICAN LOTUS K-40 2,282.7 +/- 388.3 01-AUG-13 AMERICAN LOTUS MN-54 < 19.3 01-AUG-13 AMERICAN LOTUS CO-58

  • 20.5 01-AUG-13 AMERICAN LOTUS FE-59
  • 21.6 01-AUG-13 AMERICAN LOTUS CO-60
  • 15.5 01-AUG-13 AMERICAN LOTUS ZN-65
  • 36.9 01-AUG-13 AMERICAN LOTUS ZR-NB-95
  • 27.3 01-AUG-13 AMERICAN LOTUS 1-131
  • 40.4 01-AUG-13 AMERICAN LOTUS CS-134
  • 15.5 01-AUG-13 AMERICAN LOTUS CS-1 37

Exposure Pathway - Aquatic Vegetation Location EEA Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Sample 03-SEP-1 3 ARROWHEAD BE-7 146.7 03-SEP-13 ARROWHEAD K-40 4,998.3 +/- 424.1 03-SEP-1 3 ARROWHEAD MN-54 13.3 03-SEP-13 ARROWHEAD CO-58 16.0 03-SEP-13 ARROWHEAD FE-59 15.8 03-SEP-13 ARROWHEAD CO-60 17.3 03-SEP-13 ARROWHEAD ZN-65 < 21.8 03-SEP-13 ARROWHEAD ZR-NB-95 < 13.6 03-SEP-13 ARROWHEAD 1-131 < 22.5 03-SEP-13 ARROWHEAD CS-134 < 14.5 03-SEP-13 ARROWHEAD CS-1 37 < 9.8 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 94

Exposure Pathway - Aquatic Vegetation Location MUDS Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Sample 16-SEP-13 AMERICAN PONDWEED BE-7 299.4 +1- 67.4 16-SEP-13 AMERICAN PONDWEED K-40 1,861.0 +1- 164.7 16-SEP-13 AMERICAN PONDWEED MN-54 6.1 16-SEP-13 AMERICAN PONDWEED CO-58 4.7 16-SEP-13 AMERICAN PONDWEED FE-59 4.6 16-SEP-13 AMERICAN PONDWEED CO-60 5.2 16-SEP-13 AMERICAN PONDWEED ZN-65 9.2 16-SEP-13 AMERICAN PONDWEED ZR-NB-95 4.9 16-SEP-13 AMERICAN PONDWEED 1-131 12.8 16-SEP-1 3 AMERICAN PONDWEED CS-134 5.3 16-SEP-13 AMERICAN PONDWEED CS-1 37 6.7 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 95

Exposure Pathway - Terrestrial Vegetation Location EEA Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 03-JUN-13 PASTURAGE BE-7 1,017.9+/- 200.4 03-JUN-13 PASTURAGE K-40 7,466.5 +/- 475.6 03-JUN-13 PASTURAGE MN-54 < 14.0 03-JUN-13 PASTURAGE CO-58 < 15.0 03-JUN-13 PASTURAGE FE-59 < 26.1 03-JUN-13 PASTURAGE CO-60 < 12.5 03-JUN-13 PASTURAGE ZN-65 < 32.4 03-JUN-13 PASTURAGE ZR-NB-95 < 16.6 03-JUN-13 PASTURAGE 1-131 < 33.2 03-JUN-13 PASTURAGE CS-134 < 11.9 03-JUN-13 PASTURAGE CS-137 < 14.4 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 96

Exposure Pathway - Terrestrial Vegetation Location MUDS Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 03-JUN-13 PASTURAGE BE-7 1,830.1 +/- 342.4 03-JUN-13 PASTURAGE K-40 5,868.0 +/- 644.2 03-JUN-13 PASTURAGE MN-54 24.4 03-JUN-13 PASTURAGE CO-58 19.5 03-JUN-13 PASTURAGE FE-59 41.4 03-JUN-13 PASTURAGE CO-60 16.2 03-JUN-13 PASTURAGE ZN-65 36.8 03-JUN-13 PASTURAGE ZR-NB-95 24.3 03-JUN-13 PASTURAGE 1-131 37.8 03-JUN-13 PASTURAGE CS-1 34 19.7 03-JUN-13 PASTURAGE CS-137 28.5 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C - 97

Exposure Pathway - Terrestrial Soil Location EEA Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 23-JAN-13 K-40 8,935.2 +/- 626.4 23-JAN-1 3 MN-54 28.5 23-JAN- 13 CO-58 37.6 23-JAN-1 3 FE-59 113.7 23-JAN-13 CO-60 17.5 23-JAN-1 3 ZN-65 58.3 23-JAN-1 3 CS-134 26.0 23-JAN- 13 CS-137 i73.8+- 29.5 28-OCT-13 K-40 10,747.0+- 678.9 28-OCT-1 3 MN-54 25.5 28-OCT-1 3 CO-58 20.5 28-OCT-13 FE-59 36.1 28-OCT-13 CO-60 25.8 28-OCT-1 3 ZN-65 45.0 28-OCT-13 CS-134 26.9 28-OCT-13 CS-137 249.6+- 40.4 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 98

Exposure Pathway - Terrestrial Soil Location MUDS Collection Nuclide Concentration Duplicate Date (pCi/Kg Dry) Analysis 23-JAN- 13 K-40 11,641.0 +/- 718.7 23-JAN-13 MN-54 < 34.0 23-JAN- 13 CO-58 < 31.5 23-JAN-1 3 FE-59 < 104.2 23-JAN-1 3 CO-60 < 9.8 23-JAN- 13 ZN-65 < 60.2 23-JAN- 13 CS-134 < 25.2 23-JAN-1 3 CS-137 148.3 +/- 39.1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 99

Exposure Pathway - Ingestion Meat Location R2.7 Collection Sample Nuclide Concentration Duplicate Date Description (pCi/Kg Wet) Analysis 18-NOV-13 DEER K-40 3,070.6 +/- 355.7 18-NOV- 13 DEER MN-54 14.0 18-NOV-13 DEER CO-58 9.5 18-NOV-13 DEER FE-59 12.3 18-NOV-13 DEER CO-60 9.7 18-NOV- 13 DEER ZN-65 11.9 18-NOV- 13 DEER CS-134 15.0 18-NOV-13 DEER CS-1 37 10.1 18-NOV-13 DEER H-3 251.0 +/- 74.0 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page C- 100

WOLF CREEK GENERATING STATION 2013 LAND USE CENSUS REPORT REVISION 1 Ad F

Prepared by:

12-31-13 Teresa L. Rice Date Peer Review:

1/7/14 Dan E. Haines Date Approved by:

1/13/14 Robert A. Hammond Date 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 1

EXECUTIVE

SUMMARY

The 2013 Land Use Census Report has been revised to incorporate the re-calculated D/Qs for the broadleaf vegetation locations using the data from Engineering Evaluation SA-1 3-002.

The annual Land Use Census of rural residents within five miles of the Wolf Creek Generating Station (WCGS) has been completed in 2013 in accordance with AP 07B-004, [Offsite Dose Calculation Manual (Radiological Environmental Monitoring Program)].

No program changes are necessary regarding milk locations. Again, no milk sampling locations were identified.

The two broadleaf vegetation locations with the highest calculated annual average D/Q rankings are A2.60-17TE1527 and Q2.35-MILA1619. AP 07B-004 specifies, "Alternate sampling locations may be used to provide continued monitoring". The third-ranked garden is N2.38-RODR9. Since these gardens are currently listed as sample locations for the Radiological Environmental Monitoring Program in procedure AP 07B-004 (locations A-3, Q-6 and N-I), no program changes are necessary regarding broadleaf vegetation locations.

BACKGROUND Section 5.2, Attachment A, of procedure AP 07B-004, directs that "a Land Use Census shall be conducted annually during the growing season to identify the nearest (1) milk animal, (2) residence, and (3) garden of greater than 500 square feet producing broadleaf vegetation in each of the 16 meteorological sections within five miles of the WCGS site."

Table 5-1, Attachment A, of procedure AP 07B-004, requires that broadleaf vegetation samples be collected from "two indicator locations (using the criteria from the "Land Use Census" section) with highest calculated annual average D/Q."

Table 5-1, Attachment A, of procedure AP 07B-004, also requires that milk samples be collected from "three indicator locations within 5 miles of the site having the highest dose potential."

METHODOLOGY Over two hundred surveys were mailed to the rural residents living within five miles of WCGS.

A follow-up survey was sent to residents who did not respond. The survey excluded the residents of New Strawn and Burlington. These locations were excluded due to the large number of households and the low likelihood that information gained from these residences would affect the locations chosen for REMP sampling. Drive-by information was collected for the nearest residences in each sector that did not return surveys.

The information collected was compiled and the results are identified in Tables 1-3.

Calculations were performed so that garden locations could be ranked by their respective D/Q.

These results are contained in Table 4.

2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 2

RESULTS NOTE: A Global Positioning System was used to verify residence distances and sectors.

Two changes were noted for the nearest occupied residences in each sector. These changes occurred in sectors A and E.

Seven changes were noted for the nearest garden producing broadleaf vegetation. These changes are identified in Table 3.

There were no changes regarding milk sample locations. Again, no locations were identified that routinely milked animals for human consumption.

It should be noted that since the last Land Use Census some of the address numbers were changed by the County. Addresses that were affected are identified by an asterisk on Table 2 and Table 3.

2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 3

TABLE I 2013 Land Use Census Data Location of Nearest:

Sector Residence Milkingq Animals Broadleaf Garden A A2.47-17RD1474 None A2.60-17TEl 527 B B3.53-QURD1755 None None C Cl .92-16RD1703 None C3.58-RERD1675 D D2.03-QULA1571 None D3.00-16RD1829 E E1.77-QULA1485 None None F F1.84-QULA1419 None F2.44-RERD1391 G G3.03-13RD1820 None G3.77-12RD1831 H H3.09-12RD1711 None H3.89-1 1RD1 655 J J3.70-11 RD1540 None J3.70-1 1RD1540 K K2.70-12LA1439 None K4.10-NARD1120 L L2.10-NARD 1339 None L2.39-NARD1309 M M2.34-14RD1 346 None M3.78-LYRD1 390 N N2.08-15RD1350 None N2.38-RODR9 P P2.76-HW751534 None P2.93-BRST250 Q Q2.35-MILA1619 None Q2.35-MILA1619 R R2.08-NALN 1650 None None Identifiers are based upon the following protocol:

EXAMPLE: A2.47-17RD1474 "A" = Sector A "2.47" = 2.47 miles from the reactor "17RD1474" = address 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D -4

TABLE 2 SECTOR 2012 NEAREST 2013 NEAREST RESIDENCE RESIDENCE A A2.60-17TE1520 A2.47-17RD1474 B B3.53-QURD1755 B3.53-QURD1755 C Cl.92-16RD1655 Cl.92-16RD1703*

D D2.03-QULA1571 D2.03-QULA1571 E EI.78-QULA1451 E1.77-QULA1485 F F1.84-QULA1419 F1.84-QULA1419 G G3.03-13RD1820 G3.03-13RD1820 H H3.09-12RD1711 H3.09-12RD1711 J J3.70-11RD1540 J3.70-11RD1540 K K2.70-12LA1439 K2.70-12LA1439 L L2.1 0-NARD1 339 L2.1 0-NARD1 339 M M2.34-14RD1330 M2.34-14RD1346*

N N2.08-15RD1350 N2.08-15RD1350 P P2.76-HW751534 P2.76-HW751534 Q Q2.35-MILA1619 Q2.35-MILA1619 R R2.08-NALN1650 R2.08-NALN1650 NOTE: Entries underlined indicate changes from the 2012 Land Use Census.

2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 5

TABLE 3 2013 Land Use Census Milk and Garden Data SECTOR 2012 2013 2012 NEAREST 2013 NEAREST MILKING MILKING GARDEN GARDEN ANIMALS ANIMALS PRODUCING PRODUCING BROADLEAF BROADLEAF VEGETATION VEGETATION A None None A2.60-17TE1520 A2.60-17TE1527*

B None None None None C None None C3.38-17RD1755 C3.58-RERD1675 D None None D2.33-RERD1520 D3.00-16RD1829 E None None None None F None None F2.44-RERD1391 F2.44-RERD1391 G None None None G3.77-12RD1831 H None None H4.87-10RD1670 H3.89-11RD1655 J None None J3.84-11RD1499 J3.70-11RD1540 K None None K4.10-NARD1120 K4.10-NARD1120 L None None L2.39-NARD1309 L2.39-NARD1309 M None None M4.42-LYRD1231 M3.78-LYRD1390 N None None N2.38-RODR9 N2.38-RODR9 P None None P3.17-WDST425 P2.93-BRST250 Q None None Q2.35-MILA1619 Q2.35-MILA1619 R None None None None NOTE: Underlined entries indicate changes from the 2012 Land Use Census.

2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 6

TABLE 4 Information Used for DIQ Calculations FROM LAND USE FROM SA-13-002 DIST CALC NEAR NEAR FAR FAR SECTOR SECTOR (MI) (METERS) DIST D/Q DIST D/Q CALC RANKING A 2.60 4184 4000 1.86E-09 5000 1.26E-09 1.75E-09 1 B

C 3.58 5761 5000 2.51E-10 6000 1.85E-10 2.01E-10 13 D 3.00 4828 4000 2.93E-10 5000 1.99E-10 2.15E-10 12 E

F 2.44 3927 3000 6.15E-10 4000 3.69E-10 3.87E-10 8 G 3.77 6067 6000 3.57E-10 7000 2.65E-10 3.51E-10 10 H 3.89 6260 6000 5.16E-10 7000 3.83E-10 4.81E-10 6 J 3.70 5955 5000 6.06E-10 6000 4.46E-10 4.53E-10 7 K 4.10 6598 6000 4.46E-10 7000. 3.31E-10 3.77E-10 9 L 2.39 3846 3000 1.1OE-09 4000 6.62E-10 7.29E-10 4 M 3.78 6083 6000 2.67E-10 7000 1.99E-10 2.61E-10 11 N 2.38 3830 3000 1.17E-09 4000 7.OOE-10 7.80E-10 3 P 2.93 4715 4000 7.64E-10 5000 5.19E-10 5.89E-10 5 Q 2.35 3782 3000 1.46E-09 4000 8.79E-10 1.01E-09 2 R

Originated by: Je?~~b Date: 12-31-13 Verified by: Date:

1/7/14 2013 Land Use Census Report, Revision 1 2013 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page D - 7

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