ML20140F410
| ML20140F410 | |
| Person / Time | |
|---|---|
| Site: | Wolf Creek  |
| Issue date: | 12/31/1996 |
| From: | Warren C WOLF CREEK NUCLEAR OPERATING CORP. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| WO-97-0046, WO-97-46, NUDOCS 9705020289 | |
| Download: ML20140F410 (137) | |
Text
{{#Wiki_filter:__ - _ - -- -_ - _ _ . . _ _ . i i WQLF CREEK NUCLEAR OPERATING CORPORATION i Clay C. Warren ' j Chief Operating Officer f I ! April 30, 1997 i ! WO 97-0046 1 U. S. Nuclear Regulatory Commission ATTN: Document Control Desk i Mail Station P1-137 i Washington, D. C. 20555 i j Subjact? Dockat No. 50-492: Annual Radiological Environmental
- Operating Reeort i
Gentlemen; { 4 Enclosed is tne Annual Radiological Environmental Opc r a t.1 r.g Peport whien is 1 being subnit t ed pursuant to Wolf Creek Generatina Stat:on (WCGS) Pacility Technical Specificatior. 6.9.1.6. This report covers tno opetation of WCGS for the period of Januc.ry 1, 1996 t o Cecerter 31, 1996. )
- If you should have any questions regarding this submittal, pl ecis e contact me 1 at (3t6) 364-8831, extension 4485. or Richard D. Eiarnivan at extension 4500.
l I Very truly yours, 1 i Clay C. Warren CCW/jad Attachment cc: E. W. Merschoff (NRC), w/a W. D. Johnson (NRC), w/a J. F. Ringwald (NRC), w/a J. C. Stone (NRC), w/a ., CLO(i 0200S0 9705020289 961231 p I PDR ADOCK 05000482 II I ((Uh ;c i
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l R PDR [L , )[ < PO. Box 411 i Burlington. KS 66839 / Phone: (316) 364-8831 An Equal Opportunity Employer M F HC VET
4 i i I t ! WOLF CREEK NUCLEAR OPERATING CORPORATION ! WOLF CREEK GENERATING STATION i i 1996 ANNUAL RADIOLOGICAL ! l
- ENVIRONMENTAL OPERATING REPORT i l 1
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1 i i TABLE OF CvaTENTS List of Tables 11 List of Figures 111 Introduction 1 I. Program Description 2 II. Discussion of Results 5 III. Annual Land Use Census Results and Program Revisions 9 IV. Program Deviations 11 V. EPA Interlaboratory Comparison Program Results 12 Tables 13 Figures 35 Appendix A A-1 Appendix B B-1 1 I i l l
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l I i l l LIST OF TABLES 1 1 1996 Radiological Environmental Monitoring Program Sample Collection 13 ' 2 Sample Location Numbers, Distances, and Directions 18 I l 3 1996 Airborne Particulate Gross Beta Analyses 19 ; ( 4 1996 Airborne Particulate Quarterly Composite Gamma Isotopic 21 1 Analyses , t 1 5 1996 First and Second Quarter TLD Results 22 ) l 1 6 1996 Third and Fourth Quarter TLD Results 23 ! 1 l I 7 1996 Drinking Water Radiological Analyses 24 l l 8 1996 Surface Water Radiological Analyses 25 9 1996 Ground Water Radiological Analyses 26 l 1 10 1996 Aquatic Plants Radiological Analyses 26 l l 11 1996 Shoreline Sediment Radiological Analyses 27 12 1996 Bottom Sediment Radiological Analyses 27 13 1996 Broadleaf Vegetation Radiological Analyses 28 14 1996 Irrigated Crops Radiological Analyses 28 15 1996 Milk Radiological Analyses 29 l l 16 1996 Fish Radiological Analyses 30 17 1996 Land Use Census Residence Data 31 l 18 1996 Land Use Census Miln and Garden Data 32 l 19 EPA Interlaboratory Comparison Program 1996 33 20 Analytics Cross Check Comparison Program 1996 34 l l l l l l l 1 11
i LIST OF FIGURES 1 Airborne Pathway Sampling Locations 35 l l 2 Direct Radiation Pathway Sampling Locations 36 I 3 Waterborne Pathway Sampling Locations 37 ! 4 Ingestion Pathway Sampling Locations 38 i l 5 Distant Sampling Locations 39 6 1996 Airborne Gross Beta Weekly Results 40 7 Historical Airborne Smoothed Indicator and Control Gross Beta 41 8 Airborne Particulate Gross Beta Indicator Weekly Average to Control 42 Ratio (Historical) 9 Historical Airborne Gross Beta Control and Indicator Location 43 Average 10 Variation of Nearsite TLD Averages Expressed as a Ratio to Control 44 Values 11 TLD Nearsite Locations and Control Locations 45 1 I 12 Wolf Creek Lake Surface Water Smoothed Tritium Data 46 13 Cumulative Liquid Effluent Tritium Data 47 1 14 Drinking Water Gross Beta, Historical 48 i I 15 Cs-137 in Shoreline Sediment (Location Discharge Cove) 49 16 Tritium in Wolf Creek Lake Fish 50 l l t i l ? 1 1 l 1 l l iii j l l l
INTRODUCTION The 1996 Annual Radiological Environmental Operating Report for Wolf Creek Generating Station (WCGS) covers the period from January 1, through December 31, 1996. WCGS is located in Coffey County, Kansas, approxinately i five miles northeast of Burlington, Kansas. Fuel loading commenced at WCGS on March 12, 1985. The operational phase of , the Radiological Environmental Monitoring Program (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), results of sample analyses, a discussion of monitoring program results, a description of revisions to and deviations from the program, and the results of the Interlaboratory Comparison Program. Individual sample results and a summary of results in the Nuclear Regulatory Commission (NRC) Branch Technical Position specified format are included as appendices. During 1996, activation products were not detected in airborne particulate and I radiciodine filters, broadleaf vegetation, crops, milk, ground water, I nondomestic meat, terrestrial vegetation or drinking water. During 1996, activation products attributable to piant operation were detected in algae, shoreline sediment, bottom sediment, surface water and fish samples. All nuclides detected in the REMP samples were below applicable NRC reporting levels. 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 1 of 50
, l I i 1 l I. PROGRAM DESCRIPTION Radiological environmental samples were collected according to the schedule in l Attachment A, Table 5-1 of the WCGS Offsite Dose Calculation Manual (ODCM). l Samples were collected by the WCGS Environmental Management group and were analyzed by Teledyne Brown Engineering Environmental Services of Westwood, New Jersey. Environmental TLDs were processed by WCGS Health Physics Technicians l
- the first three quarters of 1996, and Enrico Fermi 2 personnel processed the j TLDs during the fourth quarter of 1996. Table 1 lists sampling pathways and frequencies of sampling and analysis. Table 2 lists each sample location's I distance and direction from the plant. Samples in addition to those required by the WCGS ODCM were also obtained.
The following is a description of the sampling and analysis program by individual pathways. A. Airborne Low volume air sampling pumps continually collected particulate and radiciodine samples on (7 mm glara fiber filters and charcoal canisters, i respectively. Weekly, the filters and charcoal canisters were changed out, j labeled, and shipped to Teledyne Brown Engineering Environmental Services for analysis. The volume of air sampled was calculated from the average of initial and final flow rates and the total time of collection. Each pump was equipped with a time totalizer that was checked weekly against the elapsed time. Gross beta analysis of the air particulate samples was performed approximately j 72 hours post collection to allow the radon and thoron daughter products to I decay. ! Weekly air particulate filters were combined into quarterly composites for each location and analyzed for gamma emitting isotopes. Charcoal canisters were routinely counted in groups of five to determine the presence or absence of I-131. Positive indication of I-131 would have ret.ulted in analysis of each individual charcoal canister. l Air samples were collected from the three sectors with the highest ground level deposition constants (D/Q), the community of New Strawn, and a control l location. Distances and directions to sampling locations from the plant se listed in Table 2, locations are shown in Figure 1 (nearby locations) and Figure 5 (distant locations). I B. Direct Radiation Panasonic UD-814-AQ TLDs were used during the 1996 t, ample year. The TLDs I consist of one lithium-borate element and three calcium sulfate elements in a plastic case. TLDs were typically positioned roughly 3 to 4 feet above the ground. The TLDs were contained in either plastic thermostat boxes or fiberglass air sample pump housings. The boxes and housings protect the "JLDs from the elements and tampering. Two TLDs were placed at each designated location. TLD sample ' locations are illustrated in Figure 2 (nearby locations) and Figure 5 (distant j locations). Table 2 provides the distance and direction of each location from the plant. I 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 2 of 50 l l
l l C. Waterborne All water samples were analyzed to determine if gamma emitters were present. In addition to gamma analysis, radiochemical analysis for I-131 was performed on drinking water and ground water samples. Gross beta analysis was also l performed on drinking water samples. Tritium analysis was performed monthly by liquid scintillation for surface water and quarterly for drinking water. l Tritium analysis for ground water was performed quarterly by gas counting. Water sampling locations are listed in Table 2 and shown in Figures 3 and 5. Drinking water was sampled at the water treatment facilities for the towns of Burlington (control location) and LeRoy (indicator location). The Burlington facility is located upstream and the LeRoy facility is located downstream of the confluence of the discharge from Wolf Creek Lake (WCL) and the Neosho River. Monthly, composite samples were obtained from automatic composite samplers at each location that pulled approximately 10 ml samples hourly. Monthly, grab samples were drawn from each surface water location. Surface water was sampled from the outfall of John Redmond Reservoir (JRR) as a control location and from the discharge cove and spillway of WCL for indicator locations. Ground water samples were collected quarterly from four locations. One ground water well is hydrologically upgradient from the site (location B-12) and is used as a control location. Three additional samples (C-10, C-49, and D-65) were obtained from wells hydrologically downgradient from the site as indicator samples. Duplicate samples were obtained from location C-49 and were labeled L-49. These duplicate samples served as a lab quality check. Shoreline sediments were sampled semiannually for gamma analysis at the discharge cove (indicator, Figure 3), Make-up Water Discharge Structure (MUDS) [ indicator, Figure 3) and at JRR (control, Figure 3). Shoreline sediment i samples were also obtained from the Environmental Education Area (EEA) [ indicator, Figure 3]. Bottom sediments were collected semiannually for gamma analysis at the discharge cove (indicator, Figure 3), the location at WC&llth Road (indicator, Figure 3), and JRR (control, Figure 3). Algae from the discharge cove (indicator, Figure 3) was collected for gamma j analysis. D. Ingestion Milk samples were collected semimonthly from April through November and monthly during the months of January, February, March and December. No sampling locations that produce milk for human consumption were identified within 5 miles of the plant during 1996. Therefore, only control samples were obtained. Radiochemical I-131 and gamma isotopic analyses were performed on each sample. The control location (S-3) is illustrated on Figure 5. Broadleaf vegetation samples were collected monthly during the growing season from three gardens. Two indicator gardens (Figure 4) and a control garden (Figure 5) were sampled. Gamma isotopic analyses were performed on all samples. Two irrigated crop samples were obtained from cropland downstream of the confluence of Wolf Creek and the Neosho River (indicator, Figure 5) and two samples were obtained upstream (control, Figure 4) . Gamma isotopic analysis was performed on each sample. i l l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 3 of 50
l 1 l 1 Fish were sampled semiannually from the tail waters of JRR (control, Figure 4) j and from WCL (indicator, Figure 4) for gamma isotopic analysis. Several j species of gamefish and roughfish were sampled. Gamma isotopic analysis was ; performed on boneless meat portions of the fish. Fish were also analyzed for ! tritium. Meat from a road-killed deer was sampled (indicator, Figure 4). Gamma , isotopic analysis was performed on a boneless portion of the meat. Soil was sampled semiannually from two locations, the MUDS and EEA, for gamma isotopic analyses. These samples were a cooperative sampling effort with the Kansas Department of Health and Environment (KDHE). l Terrestrial vegetation was also sampled semiannually from locations MUDS and EEA for gamma isotopic analyses. These samples were a cooperative sampling j effort with the KDHE. I I Sampling locations listed in this section are outlined in Table 2. l l 1 l i I i i 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 4 of 50 l l
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t l II. DISCUSSION OF RESULTS ! Analysis results for all . pathways are summarized in Appendix A 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 B. In this section, results are discussed by pathway and analysis type. Operational results are related to controls, preoperational values, sources of f radioactivity, and effluent releases when applicable. Trends or seasonal ! effects are discussed. Associated errors for positive results on data 4 contained in Tables 3 through 16 may be obtained in Appendix B. ; l A. Airborne ! Results of the weekly gross beta analysis are summarized in Table 3. In addition, Figure 6 illustrates a graph of weekly gross beta results for 1996. i Figure 7 represents the historical smoothed averages of indicator and control ' gross beta. Figure 8 illustrates the historical indicator and control gross beta ratio. Figure 9 displays a historical plot of average weekly indicator ; and control gross beta values since initial criticality, t Figures 6 through 9 demonstrate how closely the indicator and control locations tracked together. Figure 7 reveals a seasonal cyclic trend in which gross beta values peak in the winter months (December or January) and decrease l to a low point in the spring months (May or June). ! l I-131 activity was not detected in the weekly analysis of charcoal filters. [ Results of the quarterly gamma analysis of air particulate filter composites j are summarized in Table 4. Naturally occurring Be-7 and K-40 were detected, j Eftects of plant operation were not seen via the airborne pathway for the year and no unusual trends were noted. I B. Direct Radiation Quarterly gamma exposures measured at each location for 1996 are shown in l Tables 5 and 6. Values are normalized to a standard 90-day quarter. Results from TLDs located near the plant (less than approximately three j miles), which would be most sensitive to changes due to plant operation, were j combined into quarterly averages. These nearsite averages, using locations 1, i 2, 7-14, 18, 26-30, 37 and 38, are compared to control location results (locations 39 and 40) in Figure 11. In addition, variation of the naarsite averages from the control location results is displayed graphically in Figure
- 10. These figures also include preoperational data for comparison. Note that q nearsite TLD locations have historically trended higher than the centrol I locations both prior to and after WCGS became operational.
Changes to area gamma exposure rates as a result of plant operation were not identified and no unusual trends were noted. C. Waterborne (1) Drinking Water Results of drinking water gamma isotopic analyses are summarized in Table 7. [ Figure 14 illustrates the historical drinking water gross beta data through ' 1996. ! t 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 5 of 50 :
Only gross beta activity was detected in drinking water and it was detected in ( all of the drinking water samples. No significant difference between the indicator and control locations was found. Activity due to plant operation was not evident in drinking water samples l during 1996 and no unusual trends were noted. l l (2) Surface Water Tritium, attributable to WCGS operation, was detected in all surface water samples collected from WCL in 1996. A total of 539.93 curies of liquid tritium was released during the year. Measured concentrations are shown in Table 8. (Note that the tritium levels are well below the 20,000 pCi/ liter reporting limit for drinking water sources and the 30,000 pCi/ liter limit for other water sources.) Figure 12 illustrates smoothed tritium data for i locations DC and SP from startup in May 1985 through 1996. The cumulative l curies of liquid tritium released to WCL is illustrated on Figure 13. During 1996, the annual mean for detected tritium at the discharge cove was 10,658 pCi/ liter. It can be seen in Figure 12 that monthly surface water i tritium concentrations appear to be slightly increasing since plant startup. This is expected until the tritium concentration of the lake reaches I equilibrium, which has been estimated at 13,074 pCi/ liter. l The only other activity detected in surface water at the discharge cove was Cobalt-60 (7.2 pCi/ liter). This activity is attributable to plant operation. No unusual trends were noted regarding surface water samples. i (3) Ground Water During 1996, the occurrenco of radioactivity was not detected in ground water samples. (4) Shoreline Sediment Naturally occurring nuclides (K-40, Ra-226 and Th-228) were detected in all shoreline sediment samples. Another naturally occurring nuclide (Be-7) was detected in an indicator location sample (WCL discharge cove). Cobalt-58 was detected in one indicator sample from the discharge cove (263 pCi/kg). This activity is attributable to plant operation. In two samples from the discharge cove, Co-60 was detected (258 pCi/kg and 82.2 pCi/kg). This activity is attributable to plant operation. ! Cs-137 was detected in two samples taken from indicator locations (DC and MUDS). Since Cs-134 was not detected in the samples from the indicator locations, this activity may indicate fallout as opposed to newly produced fission products. The presence of Cs-134 is expected if the occurrence of Cs-137 is related to plant operation. Since Cs-134 has a shorter half-life than Cs-137 (2 years versus 30 years), it is not expected to be found when the presence of Cs-137 is due to fallout. Figure 15 illustrates that Cs-137 activity was detected preoperationally and is routinely detected at the l discharge cove. A linear trendline indicates that the Cs-137 activity l detected in the discharge cive is showing a downward trend. Analysis results I are summarized in Table 11. l i 1996 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 6 of 50
_m _ _ _ _ _ _ _ _ _ _ - _ _ _ . _ , _ . _ _ _ _ . _ _ . . _ . . _ _ . _ _ _ . _ _ _ _ . , . -. _ l t D. Ingestion [ (1) Milk No indicator locations for milk existed during 1996 (see Program Deviation section for explanation). ' A control sample was routinely obtained for I analysis. All milk samples analyzed contained K-40. The yearly average K-40 concentration was 1322 pCi/ liter. Table 15 summarizes milk analysis results for 1996. l No other gamma emitters were detected. (2) Food and Garden Crops Gamma analyses of broadleaf vegetation samples during 1996 detected naturally occurring gamma emitters Be-7, K-40 and Th-228. Table 13 shows the results of l 1996 analysis. Additional gamma emitters were not detected in broadleaf 7 l vegetation samples. In addition to broadleaf vegetation, crop samples irrigated with water from r the Neosho River were collected. Two control samples were obtained from , cropland upstream of the confluence of Wolf Creek and the Neosho River, and i two indicator samples were obtained downstream. Gamma analysis detected . naturally occurring K-40 to be present in all of the samples, with no nuclides 4 detected due to plant operation. Results of crop analyses are summarized in ! Table 14. l (3) Fish ! Analysis results are illustrated in Table 16. Naturally occurring K-40 was detected in all fish samples. During 1996, fish were also analyzed for tritium. All fish samples taken from WCL and from the WCL outlet pool had tritium activity detected. The detected tritium activity is attributable to plant operation. An adult consuming 21 kilograms of fish, at the maximum measured tritium concentration for 1996 (9,400 pCi/kg) would receive a calculated committed dose of 0.012 mrem. ) Figure 16 illustrates the tritium concentrations detected in fish from Wolf Creek Lake. l E. Special Samples (not required by the WCGS ODCM) l l l (1) Nondonestic Meat (Deer) Naturally occurring K-40 was detected in a deer sample obtained from Sector 0 Other radionuclides were not detected and no effects of plant operation were detected in this sample. (2) Botton Sediment Table 12 shows gamma emitters detected during 1996 in bottom sediment samples. Naturelly occurring nuclides detected include K-40, Ra-226, and Th-228 Mn-54 and Co-58 were detected in both WCL discharge cove samples. This activity is attributable to plant operation and is regularly identified in plant effluents. i j Co-60 was detected in both samples obtained from the WCL discharge cove. Co-60 activity is attributable to plant operation and is commonly identified in plant effluents. i ! 1996 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 7 of 50
l Cs-137 activity was detected in samples taken from indicator locations and in samples taken from the control location. Since Cs-134 was not present and Cs-137 activity was also detected from the control' location samples, this activity is primarily due to fallout, and not to a newly produced fission product. l l No other radionuclides were detected. (3) Aquatic Vegetation Table 10 liets gamma emitters detected in an algae sample obtained from the WCL discharge cove. Naturally occurring Be-7, K-40, Ra-226 and Th-228 were detected. Other activity detected included Cr-51, Mn-54, Co-58, Fe-59, Co-60, Nb-95, Sb-125, Cs-134 and Cs-137. This activity is attributed to plant , operation and is regularly identified in plant effluents. (4) Terrestrial Vegetation Pasturage samples were obtained from two locations: EEA and MUDS. All samples had naturally occurring Be-7 and K-40 activity detected. No other nuclides were detected. (5) Soil Soil samples were obtained from two locations: EEA and MUDS. Naturally occurring Be-7, K-40, Ra-226 and Th-128 activity was detected. Cs-137 activity was detected in th: .1 of the fotr soil samples. The Cs-137 activity is attributable to fallout 2.nce Cs-134 activity was not detected and the activity levels for Cs-137 are well within the preoperational range (255 to 2160 pCi/kg). 1 l i i I l ! 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 8 of 50
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l l III. ANNUAL LAND USE CENSUS RESULTS AND PROGRAM REVISIONS i Introduction , The annual Land Use Census of rural residents within five miles of WCGS was
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l completed for 1996. The results and notable changes are summarized and ; Jllustrated in Tables 17 and 18. ! Background ; i Section 5.2, Attachment A, of the ODCM procedure (AP 07B-003), directs that "a 1 Land Use Census shall be conducted annually during the growing season to < l identify the nearest (1) milk animal, (2) residence, and (3) garden of greater I that 500 square feet producing broadleaf vegetation in each of the 16 meteorological sections within five miles of the WCGS site" and "the results , of the Land Use Census shall be included in the Annual Radiological l Environmental Operating Report." Table 5-1, Attachment A, of the ODCM requires that broadleaf vegetation samples be collected from "two indicator locations with the highest calculated annual average D/Q." Table 5-1, Attachment A, of the ODCM also requires that milk samples be collected from "three indicator locations within 5 miles of the site having the highest dose potential." Hethodology Surveys were mailed to the rural residents within five miles of WCGS during the first week of September 1996. A follow-up mailing was sent during the fourth week of September to residents that had not responded. The survey , excluded the residents of New Strawn, Burlington, and a trailer park just l l north of Burlington. These locations are excluded due to the large number of l l households and the low likelihood that information gained from these I residences would affect the locations chosen for REMP sampling. Of the 167 l surveys mailed to the rural residents, 121 were returned by mail and 31 ! responses were obtained through telephone conversations. Fifteen surveys were partially completed with information obtained by driving by the locations, since the residents could not be reached by telephone or the surveys were not returned by mail. This is a response rate of 91.02 percent for the 1996 census. The response rate for the 1995 census was 96.43 percent. : Results l l The estimated population for the 1996 Land Use Census is 490 persons. This is
- an increase from the 1995 Land Use Census in which the population was l estimated at 476 persons.
In all sectors, the only change in the nearest residence occurred in sector N. The nearest residence (N2.5-HW751439) in this sector is now 2.5 miles from the plant. Last year, the nearest residence in sector N was 2.1 miles from the plant. In all sectors, no milk locations were identified. Last year, two surveys indicated that dairy cattle were kept on the property, however, neither
- household was milking the dairy cattle.
l Numerous location changes were noted for the nearest garden producing broadleaf vegetation. In sectors H, N and P, the gardens are farther from the i plant than the gardens indicated in 1995. In sector A, no gardens producing broadleaf vegetation were identified. 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 9 of 50
i l Summary Based upon the data collected in the 1996 Land Use Census, changes are required in the REMP regarding broadleaf vegetation sample locations. The two locations with the highest calculated annual average D/O rankings are R2.1-NALA1650 and G1.6-QURD1384, respectively. The gardens located at R2.1-NALA1650 and G1.6-QURD1384 have previously been targeted for REMP sampling. The ODCM specifies that an " alternate location may be used to provide continued monitoring." The garden at F1.8-14RD1730 is third by the D/0 ranking, and the landowner has agreed to allow REMP sample collection. l
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1 1 l l 1996 Annual Radiological Environmental Operating Report ( Wolf Creek Generating Station Page 10 of 50
i i IV. PROGRAM DEVIATIONS Airborne Location 37 (August 6, 1996): While performing the weekly . air sample collection, the pump at location 37 was found inoperable. The pump was turned , on and off with no success. Eventually the pump started, and a final - flow I reading was taken. The air sample pump was replaced. It was estimated that , the pump at' location 37 was inoperable for approximately 63.4 hours. j (Performance Improvement Request (PIR) 96-1975) ' Location 2 (August 20, 1996): While performing the weekly air sample collection, the pump at location 2 was found inoperable. The air sample pump was replaced. ' The air particulate filter and the charcoal filter were submitted to the vendor lab with " unknown" as the volume. (PIR 96-2062) Location 32 (December 4, 1996): While performing the weekly air sample collection, the pump at location 32 was found inoperable. The air sample pump was replaced. Since a final flow value could not be obtained, the samples were sent to the vendor lab for analysis with the volume listed as " unknown". (PIR 96-3363) Drinking Water Location BW-15 (Burlington): Due to inaccurate drinking water sampler programming, drinking water was not sampled from March 19 to April 2, 1996. l The partial sample was submitted to the vendor lab for analysis, and a grab i sample was taken on April 2. (PIR 96-1092). Individuals qualified to obtain l l REMP samples were retrained on drinking water sampling. (PIR 96-1093) Location LW-40 (LeRoy): Samples were not taken from October 1 to October 18, 1996 since the drinking water sampler had not been started. A grab sample was taken and individuals qualified to obtain REMP drinking water samples were-retrained. (PIR 96-2734) !
- Milk l
Indicator sample locations are still unavailable within five miles of the
- plant. Refer to Section Ili, Annual Land Use Census Results and Program l Revisions.
1 l l l l ! l l i l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 11 of 50
V. EPA INTERLABORATORY COMPARISON PROGRAM RESULTS , Teledyne Brown Engineering Environmental Services is contracted to perform I radiological analysis of environmental samples for the WCGS. Teledyne l participated in the Environmental Protection Agency (EPA) Interlaboratory Comparison Program during 1996. l Table 19 shows intercomparison test results received during the year. The l table lists the collection date, the sample medium, the nuclide or analysis type, the known value reported by the EPA, the measured value reported by I Teledyne Brown Engineering Environmental Services (based upon triplicate l analysis), and the normalized deviation from the known. Results are listed l for sample media and analysis types corresponding to those performed for WCGS. All of the Teledyne Brown Engineering Environmental Services results were { within three standard deviations of the known EPA results. l Beginning with 1996, the EPA discontinued providing milk and air particulate ! filter samples. For replacements, Teledyne Brown Engineering Environmental l Services purchased comparable spiked samples from Analytics, Incorporated (see Table 20). l l l l I l I l i ( 1996 Annual Radic zjical Environmental Operating Report Wolf Creek Generating Station Page 12 of 50 l
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a d i 1 l TABLE 1 ! 1996 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SAMPLE COLLECTION EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS 1 , AIRBORNE Figures 1 & 5 l l Radioiodine Samples from five Continuous sampler Analyze 4 and locations operation with sample radioiodine Particulates collection weekly, or canister weekly l more frequently if for I-131 required by dust i loading. ! Samples from Analyze locations near the particulate ! site boundary in filter weekly
- three sectors for gross beta having the highest activity; e calculated annual perform
, average D/0 quarterly gamma l
- (Locations 2, 3, isotopic l and 37 on Figure 1) analysis composite (by location) ;
Sample from the j vicinity of a ' community having i the highest I l calculated annual average D/O i (Location 32 on ' Figure 1, New Strawn) Sample from a ) control location 10-20 miles distant in a low D/O sector (Location 40 on Figure 5) 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 13 of 50
4 l i TABLE 1 (Cont) EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND FREQUENCY PATHWAY / AND SAMPLE LOCATIONS COLLECTION FREQUENCY OF ANALYSIS j SAMPLE DIRECT RADIATION Figures 2 & 5 l l 40 routine Quarterly Gamma dose monitoring stations quarterly ; l l with two or more dosimeters measuring dose continuously,
- placed as follows:
l An inner ring of
- stations, one in l each meteorological sector 0-3 mile i range from the site (Locations 1, 7-9, ,
l 11-13, 18, 26, 27, 29-31, 37 and 38 on Figure 2) An outer ring of l . stations, one in each meteorological ; sector in the 3-5. mile range from the
- site (Locations 4- !
i 6, 15-17, 19-25, ! and 33-36 on Figure
- 2). Five sectors (A, B, D, G, and L]
l contain an i additional station , L (Locations 2, 3, 10,.14 and 28) ; 1 The balance of the stations to be l placed in special l interest areas such l as population i centers (Locations 23 and 32), nearby l residences ) 5 A 9 1996 Annual Radiological Environmental Operating Report ' Wolf Creek Generating Station Page 14 of 50 c
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1 TABLE 1 (Cont) EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND' i PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF i SAMPLE LOCATIONS ANALYSIS i l DIRECT RADIATION (cont) (many locations are near a residence),
)
schools (Location 23), and in one or two areas to serve as control stations 10-20 miles distant from the site (Locations 39 and ; 40 on Figure 5) i WATERBORNE Figure 3 Surface One sample upstream Monthly grab sample Monthly gamma i (Location MUSH on isotopic l
-Figure 3) and one analysis and l sample downstream composite for !
(Location DC on tritium analysis Figure 3), quarterly Ground Samples from one or Quarterly Quarterly gamma 1 two sources only if isotopic and J likely to be tritium analysis ! affected. Indicator sarples at locations i hydrologically downgradient of the site (Locations C-10, C-49, and D-65 on Figure 3); Control sample at a location hydrologically i- upgradient of the ! site (Location B-12 ; on Figure 3) J 1 i - ] , i 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 15 of 50
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TABLE 1 (Cont) EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND l PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS WATERBORNE (cont) Drinking Sample of municipal Monthly Composite Monthly gamma water. supply at an isotopic indicator location analysis and downstream of the gross beta site (Location analysis of LW-40 on Figure 5); composite control sample from sample. location upstream Quarterly of the site tritium analysis i (Location BW-15 on of composites. ( Figure 3) Shoreline One sample from the Semiannually Semiannual gamma I sediment vicinity of Wolf isotopic Creek Lake analysis discharge cove; control sample from John Redmond Reservoir (Locations DC and JRR respectively on Figure 3) INGESTION Figures 4 & 5 l Milk Samples from Semimonthly while Gamma isotopic milking animals at animals are on analysis and i three indicator pasture (April to I-131 analysis-locations within November) and monthly of each sample five miles of the during the remainder site having the of the year (January, highest dose February, March and l potential December) I (currently there are no locations producing milk for human consumption j within five miles l of the site); one . sample from a j control location ! greater than 10 miles from the site (Location S-3 on i Figure 5) l i ( 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 16 of 50
9 l
)
i l TABLE 1 (Cont) - EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS INGESTION (cont) l Fish Indicator samples Semiannually Gamma isotopic l of 1-3 analysis on # recreationally edible portions important species from Wolf Creek Lake; control samples of similar species from John Redmond Reservoir . spillway (Figure 4) Broadleaf Samples of Monthly when Gamma isotopic Vegetation available broadleaf available analysis on l vegetation from two edible portions indicator locations with highest l calculated annual average D/O (Locations A-3 and R-1 and alternate location G-1 on Figure 4); sample of similar broadleaf vegetation from a i control location :' greater than 10 miles from the site in a low D/O sector (Location S-4 on , Figure 5) l Irrigated Sample of crops At time of harvest Gamma isotopic ; Crops irrigated with analysis on water from the edible portions Neosho River downstream of the Neosho. River - Wolf Creek confluence (Location NR-D1 and l NR-D2 on Figure 5) I i t i ! h 1 l 1 l 4 1996 Annual Radiological Environmental Operating Report . Wolf Creek. Generating Station Page 17 of 50 l
l l l I TABLE 2 SAMPLE LOCATION NUMBI::RS, DISTANCES (Miles), AND DIRECTIONS Location Distance / Location Distance / Location Number Distance / Number Direction Number Direction Direction Air Particulates and Radioiodines 2 2.7/N 3 3.0/NNE 32 3.2/WNW 37 2.1/NNW 40 >15.0/WNW TLDs 1 1.4/N 17 3.6/SE 33 3.7/WNW 2 2.7/N 18 3.0/SSE 34 4.0/NW l 3 3.0/NNE 19 4.0/SSE 35 4.6/NNW l 4 4.0/NNE 20 3.3/S 36 4.2/N 5 4.0/NE 21 3.8/S 37 2.1/NNW 6 4.4/ENE 22 4.1/SSW 38 1.2/NW 7 1.9/NE 23 4.5/SW 39 13.0/N 8 1.6/NNE 24 4.1/WCW 40 >15.0/WNW 9 2.0/ENE 25 3.6/W 41 0.8/NNW 10 2.4/ENE 26 2.6/WSW 42 0.8/SSE 11 1.6/E 27 2.1/SW 43 0.8/WNW 12 1.8/ESE 28 2.8/SW 44 3.0/NNW 13 1.5/SE 29 2.6/SSW 45 1.6/WNW 14 2.6/SE 30 2.2/W 46 1.5/WNW 15 4.5/ESE 31 3.0/WNW 16 4.2/E 32 3.2/WNW Ground water Drinking water Surface water l B-12 2.2/NNE BW-15 3.9/SW MUSH 3.6/W C-10 2.8/W LW-40 >10.0/SSE DC 0.6/WNW C-49/L-49 2.9/SW SP 2.9/S D-65 3.9/S PSBR .2/WSW Milk Broadleaf vegetation Irrigated Crops S-3 >15.0/WNW G-1 1.6/SE NR-U1 4.2/SW R-1 2.1/NNW NR-D1 9.2/S S-4 >15.0/WNW NR-D2 >10.0/S Fish Shoreline Soil Aquatic Vegetation / Algae WCL 0.6/WNW DC 0.6/WNW DC 0.6/WNW JRR 4.0/W JRR 4.0/W EEA 3.0/NNW MUDS 1.5/WNW l Animals j Sector Q 3/NW Terrestrial Vegetation & Soil Bottom Sediment EEA 3.0/NNW DC 0.6/WNW MUDS 1.5/WNW JRR 4.0/W WC&1lth RD 3.8/S 1 1996 Annual Radiological Environmental Operating Report I Wolf Creek Generating Station Page 18 of 50 i l
TABLE 3 1996 Airborne Particulate Gross Beta Analyses (pCi/ cubic meter, analysis error reported in Appendix B) Date Location Beginning Ending 2 3 32 37 40 Control 12/26/95 01/03/96 0.040 0.047 0.040 0.043 0.045 01/03/96 01/09/96 0.035 0.040 0.037 0.041 0.044 01/09/96 01/16/96 0.026 0.033 0.028 0.033 0.028 01/16/96 01/24/96 0.030 0.037 0.033 0.038 0.033 01/24/96 01/30/96 0.031 0.029 0.033 0.032 - 0.031 01/30/96 02/06/96 0.037 0.039 0.039 0.038 0.038 02/06/96 02/13/96 0.022 0.022 0.025 0.025 0.026 02/13/96 02/20/96 0.025 0.026 0.022 0.028 0.027 02/20/96 02/27/96 0.027 0.029 0.029 0.031 0.029 02/27/96 03/05/96 0.028 0.028 0.029 0.027 0.028 03/05/96 03/12/96 0.029 0.024 0.032 0.036 0.033 03/12/96 03/16/96 0.024 0.022 0.023 0.025 0.025 03/16/96 03/26/96 0.024 0.024 0.020 0.025 0.025 03/26/96 04/02/96 0.027 0.025 0.023 0.029 0.024 04/02/96 04/09/96 0.029 0.027 0.028 0.031 0.026 04/09/96 04/16/96 0.021 0.018 0.020 0.022 0.019 I 04/16/96 04/23/96 0.018 0.017 0.023 0.018 0.020 I 04/23/96 04/30/96 0.015 0.014 0.014 0.014 0.015 l 04/30/96 05/08/96 0.018 0.019 0.019 0.019 0.018 05/08/96 05/14/96 0.017 0.017 0.017 0.020 0.017 05/14/96 05/21/96 0.020 0.023 0.025 0.022 0.019 05/21/96 05/28/96 0.017 0.020 0.021 0.019 0.019 05/28/96 06/04/96 0.017 0.016 0.016 0.017 0.020 06/04/96 06/11/96 0.022 0.018 0.021 0.022 0.017 06/11/96 06/18/96 0.023 0.023 0.031 0.027 0.024 06/18/96 06/25/96 0.020 0.022 0.024 0.020 0.022 06/25/96 07/02/96 0.021 0.022 0.024 0.024 0.027 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 19 of 50
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TABLE 3 (Cont) 1996 Airborne Particulate Gross Beta Analyses (pCi/ cubic meter, analysis error reported in Appendix B) Date Location Beginning Ending 2 3 32 37 40 Control 07/02/96 07/09/96 0.028 0.028 0.028 0.030 0.027 07/09/96 -07/16/96 0.018 0.020 0.019 0.017 0.022 07/16/96 07/23/96 0.015 0.018 0.020 0.017 0.016 ( 07/23/96 07/30/96 0.021 0.025 0.021 0.028 0.023 , 07/30/96 08/06/96 0.021 0.020 0.024 0.021 0.026 ! 08/06/96 08/13/96 0.023 0.026 0.030 0.027 0.027 08/13/96 08/20/96 *** 0.026 0.027 0.024 0.026 l 08/20/96 08/27/96 0.027 0.019 0.022 0.023 0.023 i 08/27/96 09/03/96 0.041 0.038 0.043 0.039 0.041 . 09/03/96 09/10/96 0.044 0.039 0.045 0.045 0.039 I 09/10/96 09/18/96 0.026 0.027 0.028 0.022 0.024 09/18/96 09/24/96 0.026 0.023 0.027 0.025 0.020 1 09/24/96 10/01/96 0.028 0.021 0.027 0.024 0.028 10/01/96 10/08/96 0.029 0.026 0.028 0.031 0.029 , 10/08/96 10/16/96 0.027 0.027 0.028 0.026 0.034 10/16/96 10/23/96 0.021 0.022 0.023 0.021 0.021 l 10/23/96 10/29/96 0.024 0.021 0.028 0.020 0.023 l l 10/29/96 11/05/96 0.028 0.025 0.030 0.029 0.028 11/05/96 11/12/96 0.024 0.022 0.023 0.022 0.024 11/12/96 11/19/96 0.024 0.025 0.025 0.026 0.026 l 11/19/96 11/26/96 0.028 0.029 0.032 0.031 0.030 11/26/96 12/05/96 0.027 0.029 *** 0.031 l 0.031 l 12/05/96 12/10/96 0.020 0.017 0.020 0.017 0.017 12/10/96 12/17/96 0.036 0.040 0.037 0.037 0.039 l 12/17/96 12/24/96 0.029 0.029 0.028 0.028 0.031 l 12/24/96 12/31/96 0.050 0.045 0.048 0.049 0.052 12/31/96 01-06-97 0.032 0.035 0.028 0.033 0.035 l
*** - Unavailable due to pump failure l
i I i I l I I i i i l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 20 of 50
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i l l TABLE 4 1996 Airborne Particulate Quarterly Composite Gamma Isotopic Analyses (pCi/ cubic meter, analysis error reported in Appendix B) I Location Quarter Be-7 K-40 l 2 1 0.0772 3 1 0.0958 0.00731 i f 32 1 0.0847 0.00562 i 37 1 0.0868 0.00845 40 1 0.0837 2 2 0.0894 3 2 0.0965 l 32 2 0.0953 ! l 37 2 0.0837 l l 40 2 0.0832 ! 2 3 0.0998 l l 3 3 0.0855 0.00713 l 32 3 0.1000 37 3 0.0987 40 3 0.1100 2 4 0.0682 3 4 0.0594 j 32 4 0.0691 i 37 4 0.0780 40 4 0.0614 i 1 1 1 1 l l l l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 21 of 50
l i i TABLE 5 1996 First and Second Quarter TLD Results (mr/90 day qtr) l First Quarter Second Quarter Location Days 90 Day Error (2 Location Days 90 Day Error (2 l Average std dev) Average std dev) 1 98.9 14.8 1.1 1 91.1 21.0 2.0 2 97.9 13.6 1.7 2 91.9 18.0 2.7 3 97.9 14.0 1.1 3 91.9 16.6 0.5 4 97.9 14.8 1.0 4 91.9 18.5 1.1 5 97.9 13.4 0.6 5 91.9 17.7 2.6 I 6 97.9 13.8 2.5 6 91.9 16.9 0.7 I 7 98.7 12.9 2.3 7 91.1 17.1 0.8 l 8 98.7 14.6 1.4 8 91.1 19.8 1.3 9 98.7 12.3 1.7 9 91.1 16.9 0.4 10 98.7 16.1 2.4 10 91.1 18.3 1.2 11 98.7 17.2 4.2 11 91.1 19.5 1.3 12 98.7 15.1 3.6 12 91.1 17.6 0.7 13 98.7 16.1 2.9 13 91.1 20.0 1.4 14 97.9 18.2 2.2 14 91.9 17.9 1.4 15 97.9 16.3 2.3 15 91.9 18.4 3.5 l 16 97.9 16.6 1.5 16 91.9 17.3 1.0 l 17 98.2 16.0 2.2 17 90.9 18.0 1.8 18 98.2 18.0 2.5 18 90.9 18.0 1.2 19 98.0 15.6 1.0 19 91.1 18.2 1.1 ; 20 98.0 15.3 1.4 20 91.1 19.7 0.6 l 21 98.0 12.7 1.0 21 91.1 17.8 1.8 l 22 98.0 14.8 1.8 22 91.1 17.6 0.8 l 23 98.0 14.2 1.7 23 91.1 17.4 0.9 2< 98.0 14.5 1.9 24 91 1 16.5 1.3 25 98.0 11.5 1.7 25 91.1 14.8 1.1 26 98.1 12.5 1.7 26 91.0 15.7 0.7 27 98.1 14.2 0.7 27 91.0 17.4 1.3 28 98.1 12.2 0.9 28 91.0 15.1 1.0 29 98.0 11.6 1.4 29 91.1 15.5 0.8 30 98.1 14.0 1.5 30 91.1 18.0 2.7 31 98.1 13.9 1.2 31 91.1 16.9 1.6 32 98.2 14.4 2.0 32 91.1 16.5 0.8 33 98.0 17.6 0.7 33 91.1 18.3 1.4 34 97.9 17.7 1.5 34 91.9 18.4 2.6 35 97.9 15.5 2.7 35 91.9 17.8 1.2 36 97.9 16.2 1.7 36 91.9 18.5 1.9 37 98.0 14.5 1.1 37 91.3 18.3 2.0 38 98.0 16.0 2.4 38 91.3 20.7 1.9 39 97.9 15.4 3.2 39 91.9 19.5 1.2 40 97.9 12.9 1.6 40 91.9 15.6 1.5 i 41 98.9 15.5 2.5 41 91.1 19.0 2.1 ! 42 98.1 8.7 0.8 42 91.1 11.9 0.9 l 43 98.1 9.1 2.9 43 91.1 11.5 0.7 44 98.7 14.9 2.3 44 91.1 20.0 1.5 45 98.1 15.5 1.6 45 91.0 19.9 2.8 t 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 22 of 50
TABLE 6 1996 Third and Fourth Quarter TLD Results (mr/90 day qtr) Third Quarter Fourth Quarter ! Location Days 90 Day Error (2 Location Days 90 Day Error (2 Average std dev) Average std dev) 1 83.9 20.9 3.4 1 102.0 17.5 1.8 l 2 84.1 18.5 1.4 2 101.9 15.7 1.7 3 84.1 19.0 0.8 3 101.9 15.8 0.5 l 4 84.1 20.2 0.9 4 101.9 16.3 1.3 5 84.1 18.0 0.9 5 101.9 14.9 1.1 6 84.1 19.4 3.3 6 101.9 15.4 1.0 7 84.1 18.3 1.1 7 102.0 15.1 1.1 l 8 84.1 20.1 1.0 8 102.0 16.9 1.3 9 84.1 17.6 0.6 9 102.0 14.5 1.8 10 84.1 22.1 0.9 10 101.9 16.5 1.0 11 84.1 22.8 4.6 11 102.0 18.3 1.0 12 84.1 20.8 3.2 12 102.0 16.3 0.8 l 13 84.1 21.8 4.4 13 102.0 17.7 0.9 14 84.2 23.1 1.5 14 102.0 17.1 0.8 15 84.1 20.7 1.8 15 101.9 16.4 0.7 ) 16 84.1 21.5 1.8 16 101.9 17.1 2.3 1 17 84.2 21.2 2.4 17 102.0 16.0 1.3 l 18 84.2 23.1 1.3 18 102.0 17.4 1.4 19 84.0 20.3 0.4 19 102.0 17.8 1.4 20 84.0 20.0 2.3 20 102.0 16.7 1.1 21 84.0 17.3 0.8 21 102.0 14.4 0.7 22 84.0 20.1 0.9 22 102.0 16.8 0.7 23 84.1 18.8 0.9 23 101.9 16.1 0.9 24 84.1 19.2 1.3 24 101.9 15.9 1.3 25 84.1 15.7 0.9 25 101.9 13.1 1.3 I 26 84.1 18.3 1.4 26 102.0 14.6 0.9 27 84.0 22.1 0.7 27 102.0 15.7 1.6 28 84.0 17.5 2.4 28 102.0 14.4 1.3 29 84.0 16.8 1.1 29 102.0 14.0 0.6 30 84.0 19.7 1.1 30 102.0 18.4 0.6 31 84.0 19.1 1.1 31 101.9 16.1 0.8 32 84.0 18.9 1.8 32 101.8 15.1 1.0 33 84.1 22.4 4.1 33 101.9 16.5 0.8 34 84.3 20.3 1.7 34 101.7 17.2 1.1 35 84.1 19.9 2.5 35 102.0 16.1 0.7 , 36 84.1 18.7 1.1 36 101.9 16.0 1.3 37 84.0 20.2 0.9 37 101.7 15.9 1.0 38 84.0 22.5 0.3 38 101.7 17.4 1.1 39 84.3 21.3 1.5 39 101.7 16.1 0.4 40 84.3 18.5 0.8 40 101.7 14.2 1.0 41 83.9 21.4 1.0 41 102.0 16.6 1.2 42 83.9 14.8 1.3 42 101.9 11.5 1.0 43 83.9 13.4 2.2 43 101.9 10.5 1.0 44 84.2 20.7 1.4 44 102.0 16.2 0.4 45 84.0 20.5 2.1 45 102.0 16.4 1.6 46 102.0 16.3 1.1 1996 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 23 of 50 i i
TABLE 7 1996 Drinking Water Radiological Analyses ! (pCi/ liter, analysis error reported in Appendix B) Location Start Date Gr-B i LW40 01/03/96 8.5 BW15 01/03/96 9.7 ! LW40 02/06/96 7.1 i BW15 02/06/96 8.7 LW40 03/05/96 7.2 BW15 03/05/96 8.1 l BW15 04/02/96 (Grab) 7.9 LW40 04/02/96 7.9 BW15 04/02/96 8.1 LW40 05/08/96 6.6 BW15 05/08/96 6.2 LW40 06/04/96 6.9 i BW15 06/04/96 6.1 l LW40 07/03/96 6.1 BW15 07/03/96 6.3 i LW40 08/06/96 6.6 BW15 08/06/96 6.8 , LW40 09/03/96 6.9 l BW15 09/03/96 6.2 LW40 10/18/96 (Grab) 7.5 LW40 10/18/96 5.1 BW15 10/01/96 8.2 LW40 11/05/96 6.6 BW15 11/05/96 7.5 LW40 12/04/96 9.9 BW15 12/04/96 7.1 l l l I
. 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 24 of 50
TABLE 8 1996 Surface Water Radiological Analyses (pCi/ liter, analysis error reported in Appendix B) Location Date H-3 Co-60 DC 1/16/96 9300 SP 1/16/96 9400 DC 2/20/96 14000 7.24 SP 2/27/96 12000 DC 3/26/96 13000 SP 3/26/96 13000 DC 4/23/96 12000 SP 4/23/96 13000 l DC 5/21/96 11000 SP 5/21/96 10000 DC 6/16/96 14000 SP 6/18/96 11000 DC 7/16/96 9700 l SP 7/16/96 9800 I DC 8/22/96 8900 SP 8/22/96 9200 DC 9/24/96 9300 SP 9/24/96 9500 l _, DC 10/23/96 8800 l SP 10/23/96 9300 DC 11/27/96 9100 SP 11/27/96 8400 l DC 12/19/96 8800 I SP 12/19/96 8000 l PSBR 12/16/96 8600 MUSH 12/24/96 210 l l l 1 I l 1996 Annual Radiological Environmental Oper,1 ting Report Wolf Creek Generating Station Page 25 of 50 l
l TABLE 9 1996 Ground Water Radiological Analyses (pci/ liter, analysis error reported in Appendix B) The occurrence of radioactivity was not detected in 1996 ground water samples, , 1 l l TABLE 10 1996 Aquatic Plants Radiological Analyses (pCi/kg, wet, analysis error reported in Appendix B) , 1 Algae collected from Location DC on 05/01/96 Be-7 K-40 Cr- Mn- Co- Fe- Co- Nb- Nb- Sb- Cs- Cs- Ra- Th-51 54 58 59 60 95 95/ 125 134 137 226 228 Zr-95 434 2660 240 80.1 857 140 527 145 64.1 131 24.5 58.2 670 282 l l l l [ I i i l l ) 1996 Annual Radiological Environmental Operating Report I Wolf Creek Generating Station Page 26 of 50
__ _ m. . . _ _ . _- . . _ . . . - _ _ _ . _ _ . - _ _ . _ _ . . . _ _ _ . . _ . _ . _ . . _ TABLE 11 1996 Shoreline Sediment Radiological Analyses (pCi/kg, dry, analysis error reported in Appendix B) Location Date Be-7 K-40 Co-58 Co-60 Cs-137 Ra-226 Th-228 DC 05/01/96 460 10300 263 258 161 1470 1010 JRR 05/01/96 6300 2990 1350 MUDS 05/08/96 13600 143 2260 1210 EEA 06/25/96 10300 1810 1140 DC 10/25/96 9030 82.2 1230 831 JRR 10/25/96 11900 2070 1400 MUDS 10/28/96 10300 2850 1340 TABLE 12 1996 Bottom Sediment Radiological Analyses (pCi/kg, dry, analysis error reported in Appendix B) Location Date K-40 Mn-54 Co-58 Co-60 Cs-137 Ra-226 Th-228 DC 05/01/96 11900 67.4 168 1240 485 2250 999 JRR 05/01/96 15800 186 1950 1530 WC&1lTH RD 05/24/96 10300 2140 978 WC&1lTH RD 10/23/96 11900 48.8 2220 12600 1010-DC 10/25/96 80.9 100 1600 491 2690 1130 JRR 10/25/96 17800 239 2150 1290 l I l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 27 of 50
TABLE 13 1996 Broadleaf Vegetation Radiological Analyses (pCi/kg, wet, analysis error reported in Appendix B) Type Location Date Be-7 K-40 Th-228 CABBAGE S-4 05/28/96 187 3900 CABBAGE G-1 05/28/96 4500 41.5 CABBAGE G-1 06/25/96 2890 CABBAGE S-4 06/25/96 304 4230 CABBAGE R-1 06/25/96 359 4730 CABBAGE G-1 07/30/96 432 2070 CABBAGE S-4 07/30/96 565 4390 CABBAGE S-4 08/27/96 817 3840 BROCCOLI LEAVES G-1 08/27/96 746 3550 TABLE 14 1996 Irrigated Crops Radiological Analyses (pCi/kg, wet, analysis error reported in Appendix B) Type Location Date K-40 SOYBEANS NR-U1 10/21/96 17900 CORN NR-U1 10/21/96 2840 CORN NR-D1 10/21/96 3060 CORN NR-D2 10/21/96 3450 l l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 28 of 50
1 1 TABLE 15 1996 Milk Radiological Analyses I (pCi/ liter, analysis error reported in Appendix B) ' LOC TYPE DATE K-40 j S-3 cow 01/09/96 1400 1 S-3 cow 02/13/96 1190 S-3 cow 03/12/96 1270 S-3 cow 04/09/96 1360 ; S-3 cow 04/23/96 1400 S-3 cow 05/14/96 1280 l S-3 cow 05/28/96 1340 l S-3 cow 06/11/96 1380 i S-3 cow 06/25/96 1320 S-3 cow 07/09/96 1340 S-3 cow 07/23/96 1470 S-3 cow 08/13/96 1330 1 S-3 cow 08/27/96 1160 l S-3 cow 09/10/96 1300 l S-3 cow 09/27/96 1290 4 S-3 cow 10/08/96 1340 ) S-3 cow 10/22/96 1340 l S-3 cow 11/12/96 1390 S-3 cow 11/26/96 1350 S-3 cow 12/10/96 1190 l I l l l l i l l I l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 29 of 50
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f l 1 ! TABLE 16 l 1996 Fish Radiological Analyses (pci/kg, wet, analysis error reported in Appendix B) l Species Lontion Date K-40 H-3 i was WHITE CRAPPIE WCL-DC 04/16/96 3440 9200 [ l CHANNEL CATFISH WCL-DC 04/36/96 3440 9400 l BM BUFFALO NCL-CAUSEWAY 04/16/96 3050 7600 WALLEYE WCL-UHS 04/16/96 3870 8900 COMMON CARP WCL-DC 04/16/96 3070 9330 FLATHEAD CATFISH /SM BUFFALO WCL-OUTLET POOL 06/12/96 3110 6400 l WALLEYE WCL-UHS 10/16/96 4710 6000 WIPER WCL-MAIN BODY 10/16/96 3450 6500 , CHANNEL CATFISH WCL-DC 10/16/96 3900 5900 l COMMON CARP WCL-DC 10/16/96 3300 6300 ! SM BUFFALO WCL-DC 10/16/96 3020 6200 [ i BM BUFFALO WCL-SP 10/16/96 3200 6000 i I l l l i i I I l l l l i l l l l i 1 i l -1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 30 of 50
TABLE 17 1996 Land Use Census Residence Data l SECTOR TOTAL NUMBER OF 1995 NEAREST 1996 NEAREST POPULATION RESPONSES / RESIDENCE RESIDENCE FOR SECTOR HOUSEHOLDS A 11 4/6 A2.6-17TE1520 A2.6-17TE1520 i B 17 7/7 B3.1-QURD1712 B3.1-QURD1712 l C 24 11/11 C1.9-16RD1655 C1.9-16RD1655 D Ig 6/6 D2.1-QULA1571 D2.1-QULA1571 E 10 4/5 E1.8-QULA1485 El.8-QULA1485 F 35 10/14 F1.6-14RD1711 F1.6-14RD1711 G 24 9/10 G1.6-QURD1384 G1.6-QURD1384 1 H 22 6/6 H3.1-12RD1711 H3.1-12RD1711 ] J 14 6/7 J3.3-OXLA1141 J3.3-OXLA1141 K 20 5/5 K2.6-12LA1439 K2.6-12LA1439 L 30 21/24 L2.4-NARD 1339 L2.4-NARD 1339 M 33 15/15 M1.6-NARD 1441 M1.6-NARD 1441 N 19 7/8 N2.1-15RD1350 N2.5-HW751439 P 96 27/28 P2.7-16RD1255 P2.7-16RD1255 0 29 11/12 Q1.4-NALA1574 Q1.4-NALA1574 , R 6 3/3 R2.1-NALA1650 R2.1-NALA1650 ! NOTE: Entries underlined indicate changes from the 1995 Land Use Census. Locations are identified based upon the following protocol: EXAMPLE: A1.4-16RD1525 First letter is based upon sector, thus "A" designates this residence is in ) sector A. The number immediately following the first letter designates the distance (in miles) from the powerblock. The characters following the dash represent a unique identifier bascd upon location address. The example is in sector A, 1.4 miles from the plant, at 1525 16th Road. l l l l l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 31 of 50
TABLE 18 1996 Land Use Census Milk and Garden Data SECTOR 1995 1996 1995 CLOSEST 1996 CLOSEST D/Q l MILK MILK GARDEN GARDEN PRODUCING RANKING l ANIMAL ANIMAL PRODUCING BROADLEAF BROADLEAF VEGETATION VEGETATION A none none A2.61-OXLA1731 none B B4.1-QURD1823 none B3.1-QURD1712 B3.1-QURD1712 5 C none none C2.2-16RD1670 C2.2-16RD1670 7 D none none D2.1-QULA1571 D2.1-QULA1571 12 E none none E1.8-QULA1485 E1.8-QULA1485 6 F none none F1.8-14RD1730 F1.8-14RD1730 3 G G3.6-RERD1150 none G1.6-QURD1384 G1.6-QURD1384 2 H none none H3.1-12RD1711 H4.9-10RD1698 14 J none none J3.8-11RD1535 J3.8-11RD1535 11 K none none K4.1-NARD 1120 K4.1-NARD 1120 13 L none none L2.6-NARD 1309 L2.6-NARD 1309 9 M none none M2.4-14RD1321 M2.4-14RD1321 8 N none none N2.6-HW751455 N2.8-HW751480 10 P none none P2.8-HW751534 P4.3-16RD1112 15 0 none none Q2.3-MILA1619 02.3-MILA1619 4 R none none R2.1-NALA1650 R2.1-NALA1650 1 NOTE: Underlined entries indicate changes from the 1995 Land Use Census. l l l l l t 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 32 of 50
TABLE 19 EPA Interlaboratory Comparison Program 1996 Environmental Collection Medium Nuclide EPA Result (a) Teledyne Brown Deviation l Date Engineering (c) [ Result (b) l 01-26-96 Water Gr-Beta 7.0 1 5.0 7.13 i .21 0.05 1 02-02-96 Water I-131 67.0 1 7.0 71.67 1 3.06 1.15 03-08-96 Water H-3 22002.0 1 2200.0 22000.00 1 0.00 0.00 04-16-96 Water Gr-Beta 166.9 1 25.0 160.00 1 0.00 -0.48 Co-60 31.0 1 5.0 31.67 1 1.15 0.23 Cs-134 46.0 1 5.0 42.33 1 1.53 -1.27 Cs-137 50.0 1 5.0 52.33 i 1.53 0.81 07-19-96 Water Gr-Beta 44.8 1 5.0 45.33 1 2.08 0.18 08-09-96 Water H-3 10879.0 1 1088.0 9800.00 346.41 -1.72 10-02-96 Water I-131 27.0 1 6.0 26.33 1 2.31 -0.19 Footnotes: a) EPA Results-Expected laboratory precision (1 sigma), Units are pCi/ liter for water. b) Teledyne Results - Average i one sigma. Units are pCi/ liter for water. c) Normalized deviation from the known. l l i i i .1996 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 33 of 50
l TABLE 20 Analytics Cross Check Comparison Program 1996 l Sample ID/ Medium Nuclide Teledyne Brown Analytics Result Ratio (b) l Date Engineering l Result (a) l TI #11912/ Water I-131 39 1 5 36 1 2 1.08 03-12-96 Ce-141 39i9 88 1 4 1.01 ! Cr-51 330 1 30 322 i 16 1.02 ' , Cs-134 53 i 5 58 1 3 0.91 l Cs-137 65 i 7 64 i 3 1.02 ; i Co-58 49 i 5 48 1 2 1.02 l l Mn-54 37 i 4 31 1 2 1.19 ) l Fe-59 93 1 9 83 i 4 1.12 ' Zn-65 100 1 10 97 5 1.03 Co-60 81 t 8 76 1 4 1.07 l TI #11914/ Milk I-131 16 1 6 13 i 1 1.23 I 03-12-96 Ce-141 240 20 234 1 12 1.03 Cr-51 880 1 90 858 1 43 1.03 Cs-134 150 1 20 154 i 8 0.97 Cs-137 180 20 170 i 9 1.06 { Co-58 140 1 10 128 6 1.09 Mn-54 93 i 9 84 1 4 1.11 Fe-59 250 1 30 223 1 11 1.12 Zn-65 260 1 30 260 1 13 1.00 Co-60 220 1 20 204 i 10 1.08 TI #11913/ Water H-3 2800 1 200 2982 1 149 0.94 03-12-96 TI #19220/ Air Gross 150 1 10 144 1 7 1.04 06-19-96 Filter Beta TI #19221/ Air Ce-141 500 50 400 20 1.25 06-19-96 Filter Cr-51 1200 100 1048 1 52 1.15 Cs-134 310 30 310 16 1.00 Cs-137 910 90 764 1 38 1.19 Co-58 210 20 173 9 1.21 Mn-54 690 1 70 559 1 28 1.23 Fe-59 190 1 20 144 7 1.32 Zn-65 140 i 10 108 1 5 1.30 Co-60 180 20 156 i 8 1.15 Footnotes: a) Teledyne Results - counting error is two standard deviations. Units are pCi/ liter for water and milk. For gamma results, if two deviations are less than 10%, then a 10% error is reported. Units are total pCi for air particulate filters. b) Ratio of Teledyne Brown Engineering to Analytics results. I l 1996 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 34 of 50 l
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# e e U $ g 8 8 g g g l l 10/11/94 10/11/94 f
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- f 5/15/95-b 5/15/95 3 10/11/95 -
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- - - - .- N - ~ w-- t'
j Appendix A i Summary Tables in the format of NRC Radiological Assessment Branch Technical Position Revision 1, November 1979 i l l l l l l 1 I i l l l l l l l l l l s i i Page A-1
t
+
i i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
i Name of Facility- Wolf Creek Generating Station Docket No.: 50-482 l Location of Facility: Coffey County, Kansas Reporting Period: Annual 1996 l Medium of Pathway Analysis and Lower AllIndicator Number of ! Sampled Total Number of Limit of Locations Location with liighest Annual Mean . Control Locations Nonroutine { (Unit of Analysis Detection " Mean (0 Name " Mean (0 " Mean (0 Reported 1 Measurement) Performed (LLD) ** Range Distance and Direction " Range ** Range Measurements " i f Station No. 40 l Air Particulate Gross Beta (270) 3 26 (216/216) 37 27 (54/54) 27 54/54) 0 (X10-$ (14-50) 2.1 miles NNW (14-49) (15-52) ; pCi/Cu.M.) 1-131 (270) 7 -(0/216) N/A N/A -(0/54) 0 ; o 3o Gamma (20)
}" Be-7 I 86 (16/16) 32 87 (4/4) 85 (4/4) 0 N 3.2 miles WNW ;
(59-100) (69-100) '(61-110) K-40 24 7.1(4/16) 37 8.5 (l/4) -(0/4) 0 (5.6-8.5) 2.1 miles NNW ; Animals Gamma (1) No Control (pCi/kg wet) ! K-40 500 3770 (1/l) Sector Q 3770 (1/1) 0 ! 3 miles NW Extemal Stations 39 & 40 Radiation (mR/ day) TLD (374) 0.079 0.188(356/356) 11 0.216 (8/8) 0.182 (18/18) 0 Quarterly (0.123-0.216) 1.6 miles E (0.191-0.253) (0.166-0.201) ,
- Nominal Lower Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction ofdetectable measurements at specified locations is indicated in parentheses (0
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 1996 Medium of Pathway Analysis and Lower AllIndicator Number of Sampled Total Number of Limit of Locations Location with Highest Annual Mean Control Locations Nonroutine (Unit of Analysis Detection " Mean (f) Name " Mean (f) ** Mean (f) Reported Measurement) Performed (LLD) " Range Distance and Direction " Range " Range Measurements " Fish Gamma (16) JRR ; (pCi/kg wet) K-40 500 3463 (12/12) WCL-UHS 4290(2/2) 3540 (4/4) 0 (3020-4710) 0.6 miles SE (3870-4710) (3330-3820) y Tritium (16) 300 7308 (12/12) WCL-DC 7717 (6/6) -(0/4) 0 (5900-9400) 0.6 miles WNW (5900-9400)
}" Food and Garden Gamma (9) S-4 W Crops (pCi/kg wet) Be-7 90 512 (3/5) G-1 589 (2/4) 468 (4/4) 0 (359-746) 1.6 miles SE (432-746) (I87-817)
K-40 500 3548(5/5) R-1 4730(1/1) 4090 (4/4) 0 (2070-4730) 2.1 miles NNW (3840-4390) Th-228 20 46(1/5) G-1 46(1/4) -(0/4) 0 ; 1.6 miles SE ! Irrigated Crop Gamma (4) NR-UI (pCi/kg wet) i K-40 500 3255 (2/2) NR-U1 10370 (2/2) 10370 (2/2) 0 (3060-3450) 4.2 miles SW (2840-17900) (2840-17900) f
- Nominal Lower Limit of Detection (LLD) ;
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
1 l l l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: Wolf Creek Generating Station Docket No.: 50-482 Location of Facility- CofTey County, Kansas Reporting Period: Annual 1996 Medium of Pathway Analysis and Lower AllIndicator Number of Sampled Total Number of Limit of Locations Location with liighest Annual Mean Control Locations Nonroutine (Unit of Analysis Detection " Mean (0 Name " Mean (0 " Mean (O Reported ' Measurement) Performed (LLD) " Range Distance and Direction " Range " Range Measurements " S-3 Milk I-131(20) 3 N/A N/A -(0/20) 0 (pCi/l) Gamma (20) K-40 100 N/A N/A 1322 (20/20) 0 (i160-1470) 2'
$ Sediment / Silt Gamma (6) JRR !
> (PCi/kg dry) ,
L K-40 500 11675 (4/4) JRR 16800 (2/2) 16800 (2C) 0 , (10300-12600) 4 miles W (15800-17800) (15800-17800) Mn-54 30 74 (2/4) DC 74 (2/2) -(0/2) 0 (67-81) 0.6 miles WNW (67-81) , Co-58 20 134 (2/4) DC 134 (2/2) -(0/2) 0 (100-168) 0.6 miles WNW (100-168) Co-60 20 1420 (2/4) DC 1420 (2/2) -(0/2) 0 , (1240-1600) 0.6 miles WNW (1240-1600) ; Cs-137 60 342 (3/4) DC 488 (2/2) 213 (2/2) 0 (49-491) 0.6 miles WNW (485-491) (186-239) Ra-226 500 2325 (4/4) DC 2470 (2/2) 2050 (2/2) 0 - (2140-2690) 0.6 miles WNW (2250-2690) (1950-2150) Th-228 40 1029(4/4) JRR 1410 (2/2) 1410 (2/2) 0 (978-1130) 4 miles W (1290-1530) (1290-1530) ; i
- Nominal Lower Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (0 ;
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility- WolfCreek Generating Station Docket No.: 50-482 Location of Facility: Coffey County, Kansas Reporting Period: Annual 1996 Medium of Pathway Analysis and Lower AllIndicator Number of Sampled Total Number of Limit of Locations Location with Highest Annual Mean Control Locations Nonroutine i (Unit of Analysis Detection " Mean (f) Name " Mean (f) " Mean (f) Reported ! Measurement) Performed (LLD) " Range Distance and Direction " Range " Range Measurements " JRR Shoreline Soil Gamma (7) (pCi/kg dry) Be-7 300 460 (1/5) DC 460 (1/2) -(0/2) 0 0.6 miles WNW , y K-40 500 10306 (5/5) MUDS 10950 (2/2) 9100 (2/2) 0 (9030-11600) 1.5 miles WNW (10300-11600) (6300-11900)
}" Co-58 20 263 (1/5) DC 263 (1/2) -(0/2) O m 0.6 miles WNW Co-60 30 170 (2/5) DC 170 (2/2) -{0/2) 0 (82-258) 0.6 miles WNW i
Cs-137 60 152 (2/5) DC 161 (1/2) -(0/2) 0 (143-161) 0.6 miles WNW Ra-226 500 1924 (5/5) MUDS 2555 (2/2) 2530 (2/2) 0 (1230-2850) 1.5 miles WNW (2260-2850) (2070-2990) Th-228 40 1106 (5/5) JRR 1375 (2/2) 1375 (2/2) 0 (831-1340) 4 miles W (1350-1400) (1350-1400)
- Nominal Lower Limit of Detection (LLD)
" 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 1996 Medium of Pathway Analysis and Lower AllIndicator Number of Sampled Total Number of Limit of Locations Location with flighest Annual Mean Control Locations Nonroutine (Unit of Analysis Detection " Mean (f) Name " Mean (f) " Mean (f) Reported Measurement) Performed (LLD) " Range Distance and Direction " Range ** Range Measurements " No Control Soil Gamma (4) (pCi/'Kg dry) Be-7 300 1160 (1/4) MUDS 1160 (1/2) 0 1.5 miles WNW y K-40 500 11900 (4/4) MUDS 12550 (2/2) 0 (10300-12800) 1.5 miles WNW (12300-12800) y Cs-137 60 272 (3/4) MUDS 442 (1/2) O m (164-442) 1.5 miles WNW Ra-226 500 1998 (4/4) EEA 2360(2/2) 0 (1270-2450) 3.0 miles NNW (2270-2450) Th-228 40 1185 (4/4) EEA 1235 (2/2) 0 (870-1400) 3.0 miles NNW (1070-1400)
- Nominal Lower Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f) t - - --. - - - - - - _ - - - - - - - - - _ _ _ _ _ _ _ _ - . . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _
~ . . ~ . . . ~ . ~ . - . . . . - . . - - . - . . . - - _ -
. . - ~ .
t i f RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: WolfCreek Generating Station Docket No.: 50-482 { Location of Facility: Coffey County, Kansas Reporting Period: Annual 1996 ; i Medium of . Pathway Analysis and Lower AllIndicator Number of ' Sampled Total Number of Limit of Locations Location with Highest Annual Mean Control Locations Nonroutine , (Unit of Analysis Detection " Mean (f) Name " Mean (f) " Mean (f) Repor;ed r Measurement) Performed (LLD) ** Range Distance and Direction " Range " Range Measurements " No Control l Vegetation Gamma (1) ; Aquatic (pCi/kg wet) Be-7 100 434 (1/I) DC 434 (1/l) 0 L 0.6 miles WNW i l K-40 500 2660 (1/1) DC 2660 (1/l) 0 ; o, O.6 miles WNW ; $ Mn-54 40 DC 0 3 80 (1/l) 80 (1/1) 4 0.6 miles WNW , Cr-51 500 240 (1/1) DC 240 (1/l) 0 . 0.6 miles WNW ! I Co-58 10 857 (1/l) DC 857 (1/1) O t 0.6 miles WNW [ Fe-59 40 140 (1/l) DC 140 (1/l) 0 0.6 miles WNW Co-60 10 527(1/1) DC 527 (1/l) 0 [ 0.6 miles WNW i Nb-95 40 145 (1/l) DC 145 (1/1) 0 O.6 miles WNW l t l t
- Nominal Lower Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f) j
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 1996 Medium of Pathway Analysis and Lower All Indicator Number of Sampled Total Number of Limit of Locations Location with Highest Annual Mean Control Locations Nonroutine (Unit of Analysis Detection " Mean (0 Name " Mean (0 " Mean (O Reported Measurement) Performed (Lt D) " Range Distance and Direction " Range " Range Measurements " Vegetation Nb-95/Zr-95 10 64 (1/l) DC 64 (1/l) 0 Aquatic 0.6 miles WNW (pCi/kg wet) Sb-125 50 131 (1/l) DC 131 (1/l) 0 0.6 miles WNW [ Cs-134 20 25 (1/1) DC 25 (1/l) 0
<D 0.6 miles WNW
?
- 0) Cs-137 10 58(1/l) DC 58(1/1) 0 0.6 miles WNW Ra-226 200 670 (1/1) DC 670 (1/1) 0 0.6 miles WNW Th-228 20 282 (1/l) DC 282 (1/l) 0 0.6 miles WNW Vegetation Gamma (4) No Control Terrestrial (pCi/kg wet) Be-7 100 3208 (4/4) MUDS 3245 (2/2) 0 (2360-4130) 1.5 miles WNW (2360-4130)
K-40 500 3913 (4/4) EEA 3990 (2/2) 0 (2550-5120) 3 miles NNW (3550-4430)
- Nominal Lower Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (0
i 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 1996 ; Medium of I Pathway Analysis and Lower All Indicator Number of Sampled Total Number of Limit of Locations Location with Highest Annual Mean Control Locations Nonroutine i (Unit of Analysis Detection " Mean (f) Name " Mean (f) " Mean (f) Reported i Measurement) Performed (LLD) " Range Distance and Direction " Range " Range Measurements " BW-15 l Water Drinking 1-131 (26) 0.5 -(0-13) N/A N/A -(0/13) 0 (pCill) Gross Beta (26) 2 7.1 (13/13) BW-15 7.5 (13/13) 7.5 (13/13) 0 ; (5. l-9.9) 3.9 miles SW (6.1-9.7) (6.1-9.7) Gamma (26) -
.{0/13) N/A N/A -(0/13) 0 i Tritium (8) 1000 -(0/4) N/A N/A -(0/4) 0
?> B-12
> Water Ground 1-131 (20) 0.5 -(0/16) N/A N/A -(0/4) 0 m (pCi/l) l Gamma (20) -
-(0/16) N/A N/A -(0/4) 0 Tritium (20) 1000 -(0/16) N/A N/A -(0/4) 0 i
Water Surface Gamma (37) MUSH (pCill) Co-60 5 7.2 (1/25) DC 7.2 (1/12) -(0/12) 0 0.6 miles WNW Tritium (37) 1000 10364 (25/25) DC 10658 (12/12) 210 (1/12) 0 (8000-14000) 0.6 miles WNW (8800-14000)
- Nominal Lower Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction ofdetectable measurements at specified locations is indicated in parentheses (f) i
Appendix B
- 1996 Individual Sample Results l- ,
l i l l l 1 i r
- i. t i
I l i i l l i I ! 2 i i 1 i 4 < l Page B-1 l i
. ~ . . . . . , _ . _ , - --
=
n m) L . 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 H 1 M. - - - - - - - - - - - - - - - - - - L 3C u E E E E E E E E E E E E E E E E E E A1/ . . . . . . . . . . . . . . . . . . _ OCp C R l 1 2 2 1 2 2 2 2 3 1 2 3 1 2 3 2 2 1 2 ( T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. A L L L L L L L L L L L L L L L L L L _ H _ C T N U 2 0 3 6 2 9 0 7 3 1 8 5 3 9 5 3 9 16 OEE CMT 1 2 2 2 0 0
/ / / / / / / / / / / / / / / / / /
1 1 2 0 0 1 2 2 0 1 2 I A 1 1 I 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ M M 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0 A 0- 0 -0 0- 0 0 0 - 0 0- 0 -0 0 - 0 0- 0 0 0- 0 _ 1 1 S R T ). - E E E E E E E E E E E E E E E E E E A R E T E B M. 4 4 4 3 4 4 4 3 4 3 4 3 3 3 3 3 3 3 R O L' E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 _ P I I FSC I Ol/ i 1 i i 1 i 1 1 i i 1 i i i i 1 1 _ R F PRC 5 6 6 0 I. 7 3 2 5 7 8 9 4 4 7 9 1 8 O L AG(p 3 2 2 3 3 3 4 2 2 2 2 2 2 2 2 2 2 1 C O O 0 A 2 N C 1 1 R R A E A R H B E C M P D U O N N T R A N N A E OI U 6 3 3 9 4 1 3 0 6 3 1 8 6 1 9 4 3 9 E OEE 2 2 0 2 0 0 1 2 2 AT T 1 2 2 2 0 1 1 1 1 L C L A CMT I A / / / / / / / / / / / / / / / / / / 1 1 1 1 2 2 2 2 2 3 3 3 3 4 4 4 4 4 U U T DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N C S I M E D E R E A R P C R IF A I O S W T I N C O O C O C OC OC OC OC CC OC OC OC OC OC OC OC OC E C ( O U E 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 U L E0 0E 0E 0E 0E0 E 0 E0 E01 E 0 80 E 0E 0E 0E 0E0 E0 E0 E E O 6 0 0 3 4 1 9 1 9 0 0 9 0 1 9 1 V 2 3 3 3 2 3 3 2 2 3 2 3 3 2 3 3 2 3 PE 9 6 16 4 0 6 6 3 01 7 25 220 9 6 21 9 1 6 32 0 0 1 2 0 1 2 3 0 0 OT TA
/ / / /1 / 1/ /1 / / / / / / / / / / /
1 1 2 2 2 2 2 3 3 3 3 4 4 4 4 i s SD 0 0 O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 sy l a n N A O e H t a . C *
- c
- ET LRE 3 9 9 6 0 0 0 1 4 2 3 3 0 0 0 6 3 0 7 252 20 9 6 12 91 6 2 1 0 0 1 l i p L A'A I
/ /1 / / / / / / / 1/ /2 /2 / / / / / / u OT 1 I 1 1 1 2 2 3 3 3 3 4 4 4 D CSD 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 0 0 *
[ N u
j ,f i ; b - t! I _ M, . - t ~ a ) . L . 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 I F M. 0- 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 L 1 u E E E E E E E E E E E E E E E E E A1/ 3C . . . . . . . . . . OC l 1 1 1 2 2 1 1 2 2 2 3 1 1 1 2 2 1 . C I p _ R ( T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. A L L L L L L L L L L L L L L L L L H C _ T _ N _ U 3 7 1 8 4 1 7 4 1 8 9 2 9 1 6 31 0 7 OEE CMT 0 0 1 1 2 3 0
/ / / / / / / / / / / / / / / / /
1 2 2 0 2 0 1 1 I A 5 5 5 5 5 5 6 6 6 6 7 7 7 7 8 8 8 _ DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 M N 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 O I A 0- 0 0 0 0 0- 0 0 0 - 0 0 0 0 0 0 0 T S RT). - - - E E E E E E E E E E E E E E E E E A R EEM 1 B 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 R E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O P T L FSC I I O1/ i i 1 i 1 i 1 1 1 i i i i i 1 i 1 R F PRC 5 4 8 7 0 7 7 2 3 0 1 8 8 5 1 1 3 O L A G (p 1 1 1 1 2 1 1 2 2 2 2 2 1 1 2 2 2 C G O 0 A 2 _ N C _ I T R R A R A H MEB E C P O D U N N T R A N N A ET O U 5 5 5 0 6 3 0 7 4 0 0 4 0 0 5 1 8 _ E I O EE 0 0 1 2 2 0 1 1 2 3 1 1 2 3 0 l 1 L C AL TA CMI'A I
/ / / / / / / / / / / / / / / / /
5 5 5 5 5 6 6 6 6 6 7 7 7 7 8 8 8 U U TS DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ N C I M K IT E R E A R P C R E A I I O S W T I N C C C C C C C C C C C C C C C C C O C O O O O O O O O O O O O O O O U E 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ U E E E E E E E E E E E E E E E E E _ L 0 0 10 0 0 0 0 0 0 10 0 1 0 0 0 0 0 0 O 1 3 6 9 0 9 0 0 8 0 9 0 9 0 V 3 3 3 2 2 3 3 3 2 3 3 2 3 2 3 2 3 _ PE 0 0 8 4 1 8 4 1 8 5 2 9 6 3 0 6 3 _ 3 3 0 1 2 2 0 1 1 2 0 0 1 2 3 0 1 DT I'A
/ / / / / / / / / / / / / / / / /
4 4 5 5 5 5 6 6 6 6 7 7 7 7 7 8 8 s SD i 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 s l y a _ N n - O A I T t e C - m ET IRE 2 3 0 8 2 3 0 4 1 1 2 2 0 8 4 1 1 1 8 3 2 9 6 3 0 61 2 0 0 2 3 0 i l p LAT / / / / / / / / / / / / / / / / / u OTA 4 4 4 5 5 5 5 6 6 6 6 7 7 7 7 7 8 D CSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
- 2S w N
WOtX CREEK NUCI2AR OPERATING CORPORATION AIR PARI 1CUIEIE AND CHARCOAL FILTERS STATION NUMBER 02 MID COUlTT A P .'lL1ER MID COUNT CHARCOAL F1LTER COLLECTION TIME l-131 START STOP TIME GROSS BETA UNITS DATE (pCl/Cu.M.) DATE (pCl/Cu.M.) DATE DATE VOLUME OC 08/25 5.8 i 0.8 E 00 08/22 LT.3.E00 08/13 " 08/20 3.00E 08 OC 09/03 2.7 i O.3 E-02 08/31 LT. 2. E-02 . 08/20 08/27 3.00E 08 CC 09/08 4.110.4 E-02 09/07 LT. 2. E-02 08/27 09/03 3.00E 08 OC 09/17 4.410.4 E-02 09/13 LT. 2. E-02 09/03 09/10 3.30E 08 CC 09/23 2.610.3 E-02 09/21 LT. 7. E-03 09/10 09/18 2.50E 08 OC 09/29 2.6 i 0.4 E-02 09/27 LT. 2. E-02
.o 09/18 09/24 2.50E 08 OC 09/30 2.6 i 0.4 E-02 09/28 LT. 2. E-02 09/18' 09/24 3.00E 08 OC 10/07 2.8 i 0.3 E-02 10/04 LT. 1. E-02 10/01
{ 09/24 2.9 i 0.3 E-02 10/11 LT. 1. E-02 10/01 10/08 2.90E 08 OC 10/14 3.40E 08 'JC 10/21 2.7 i 0.3 E-02 10/19 LT. 1. E-02 10/08 10/16 3.00E 08 OC 10/28 2.110.3 E-02 10/26 LT. 2. E-02 10/16 10/23 2.60E 08 OC 1I/04 2.4 i 0.3 E-02 11/02 LT. 2. E-02 l 10/23 10/29 2.90E 08 OC 11/10 2.8 i 0.3 E-02 11/09 LT. 3. E-02 10/29 11/05 3.10E 08 OC 11/18 2.4 i 0.3 E-02 I1/16 LT. 2. E-02 f 11/05 11/12 2.4 i 0.3 E-02 1I/23 LT. 2. E-02 f i 11/12 11/19 3.00E 08 OC 11/24 2.8 i 0.3 E-02 12/03 LT. 2. E-02 i 11/19 11/26 3.00E 08 G: 12/04' t 3.90E 08 OC 12/13 2.7 i 0.3 E-02 12/11 LT. 1. E-02 l 1I/26 12/05 2.010.4 E-02 12/14 LT. 2. E-02 12/05 12/10 2.10E 08 OC 12/15 I
- ?
- Duplicate Analysis
- " Pump found not running
- volume unknown - Total PCI t
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4 i
WOLF CREEE NUCl2AR OPERAT1NG CORPORATION 1 AIR PART1CULATE AND CilARCOAL FILTERS STATION NUMBER 02 COLIECTION MID COUNT A P FIL1ER MID COUNT CHARCOAL FlLTER START STOP TIME GROSS BETA TIME l-131 DATE DATE VOLUME UNITS DATE (pCl/Cu.M.) DATE (pCI/Cu.M.) 12/10 12/17 3.00E 08 CC 12/31 3.6 i 0.4 E-02 12/24 L.T. 3. E-02 12/17 12/24 2.90E 08 CC 01/02 2.9 i O.3 E-02 12/31 LT. 3. E-02 12/24 12/31 3.00E 08 CC 0I/08 5.010.4 E-02 01/04 LT. 2. E-02 E W T m i I
! I;l; l !iI !ll M
E _ _ T ) 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 L . 2 2 2 2 - I F M. 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 L 1u E E E E E E E E E E E E E E E E E E E _ A3C 1/ . 2 2 2 2 2 3 2 3 2 3 3 2 1 2 1 1 2 _ O l 1 I CIC R p T. T. T. T. T. T. T. T T. ( T. T. T. T. T. T. T. T. T. T. A L L L L L L L L L L L L L L L L L L L H C T _ _ N _ U 2 0 6 2 9 7 3 1 8 51 3 9 5 3 9 6 1 3 1 8 - OEE 2 0 1 1 2 0 0 2 2 0 1
/ /12 /2 0/ 0/2 / 2 / /
1 1 CMT I A 1 I
/ / / / / / / / / 4/ /4 2 2 3 3 3 3 3 4 4 5 5 5 DTD I
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 M _ N 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 020 0 0 0 A 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 S RT . E E E E E E E E E E E E E E E E E E E A R EE B )M. 4 4 4 4 4 3 4 3 4 3 3 3 3 3 3 3 3 3 3 T R E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0i O 0 O T I F SC i i i 1 i i 1 i i P L I Ot/ 1 i i i i i i i 1 9 7 R F 2 4 5 7 8 7 4 PRC 0 3 7 9 9 2 6 9 8 4 O L AG(p 4 3 3 2 3 2 2 2 2 2 2 2 2 2 1 1 1 C A 3 G O 0 _ N C _ I R R _ T A E _ A R H B E C M P D U O N N r f R A N l U 6 3 9 0 6 3 1 8 6 1 9 4 3 9 5 5 0 A E O OEE 2 2 0 4 1 1 2 2 0 1 1 2 0 0 1 2 2 0 1 2 R C A I T T A I CMT I 1 A / / / / / 1 1 1 2
/2 / / /
2 2 3
/ / 3/ / 3 3
/ / 4 / 4/ /4 / 4 4 5 5 5 U CU I
ST DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N I M K 1 T E R E A R P C R X A t I O S W T I N C O O CO OCO C C E ( CO OCO CO CCO CO C C CC CO OCO CO OC C U E 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 M U 0 E 0 E 0E 0 E 0 E 0 E0 0 E0 0 0 E 0 E0 0 0 0 0 0 0 0 0 0 0 L 0 0 0 0 0 0E 0E0 E 0 0E 0 E0 E 0 0E0 E E 3 6 E O 5 9 3 5 0 9 9 0 9 0 0 8 9 0 9 0 1 V 2 2 3 2 3 2 2 3 2 3 3 2 2 3 2 3 3 3 2 PE 0 9 6 1 4 2 3 0 0 6 3 02 7 1 2 0 5 2 9 6 2 1 1 2 0 9 60 3 0 2 8 1 3 04 1 DT TA
/
1
/ 1
/ 1
/ 1
/ 2
/ /
2 2 2
/ / / /
3 3 3 3
/ / / / 4 / 4 / 4 / /
4 4 5 5
.SD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
_. N 0 1 n n T 3 9 6 4 0 6 3 10 7 5 2 9 6 22 9 60 3 0 28 3 0 RE 0 1
/2 2/2 /2 2 /2 0/ 3/ 3/ /3 /3 /4 / 4 / 4/4 1 1 I
I OTA AT /0 0/ / / 2/3 / 1 1 1 I 1 1 0 4 5 CSD O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
t j WOEF CREEK NUCIEAR OPERATING CORPORATION AIR PAR 11CUIATE AND CHARCOAL ML'IERS STATION NUMBER 03 cot 1ECHON MID COUNT A P FIL'IER MID COUNT CHARCOAL HLarm START S'IOP TIME CROSS BETA TIME I-131 DATE DATE VOLUME UNITS DA1E (pCI/Cu.M.) DATE (pct /Cu.M.) 05/14 05/21 2.90E 08 OC 05/26 2.3 i 0.3 E-02 05/24 LT. 2. E-02 05/21 05/28 3.10E 08 OC 06/03 2.0 i 0.3 E-02 05/31 LT. 1. E-02 05/21' 05/28 3.10E 08 OC 06/03 1.7 i 0.3 E-02 06/01 LT. 1. E-02 05/28 06/04 3.20E 08 0C 06/10 1.6 i 0.3 E-02 06/07 LT. 1. E-02 . t 06/04 06/11 3.00E 08 OC 06/17 1.8 i 0.3 E-02 06/14 LT. 2. E-02
,o 06/11 06/18 3.00E 08 OC 06/24 2.3 i 0.3 E-02 06/21 LT. 2. E-02 o ,
- 06/18 06/25 3.lOE 08 OC 06/30 2.2 i 0.3 E-02 06/28 LT. 2. E-02 ;
m 0 06/25 07/02 3.10E 08 OC 07/10 2.210.3 E-02 07/09 LT. 3. E-02 2.8 i 0.3 E-02 07/02 07/09 3.00E 08 OC 07/14 07/12 LT. 9. E-03 07/09 07/16 3.00E 08 OC 07/20 2.010.3 E-02 07/19 LT. 1. E-02 07/16 07/23 3.00E 08 OC 07/30 1.8 i 0.3 E-02 07/26 LT. 1. E-02 07/23 07/30 3.10E 08 OC 08/05 2.5 i 0.3 E-02 08/03 LT. 2. E-02 I 07/30 08/06 2.90E 08 CC 08/11 2.0 i 0.3 E-02 08/10 LT. 2. E-02 08/06 08/13 3.00E 08 OC 08/18 2.6 i 0.3 E-02 08/17 LT. 1. E-02 I i 08/13 08/20 2.90E 08 OC 08/25 2.610.3 E-02 08/22 LT. 1. E-02 , 08/20 08/27 3.00E 08 OC 09/03 1.9 i 0.3 E-02 08/31 LT. 2. E-02 08/27 09/03 3.00E 08 OC 09/08 3.8 i 0.4 E-02 09/07 LT. 2. E-02 09/03 09/10 3.00E 08 OC 09/17 3.9 i 0.4 E-02 09/13 LT. 2. E-02 , t "Dupilmte Analysis
4 WOIX CREEK NUCLEAR OPERATING CORPORAT10N AIR PARI 1CULATE AND CilARCOAL FIL*IERS STATION NUMBER 03 A P FILTER MID COUNT CHARCOAL F1L'IER MID COUfff TIME I-131 COL 1EC110N - TIME GROSS BETA START STOP (pCl/Cu.M.) DATE (pCl/Cu.M.) DKIE VOLUME UNITS DA*IE DATE 2.710.3 E-02 09/21 LT. 7. E-03 ! 09/18 3.30E 08 OC 09/23 ! 09/10 LT. 2. E-02 - OC 09/29 2.310.3 E-02 09/27 09/18 09/24 2.50E 08 2.1 i 0.3 E-02 10/04 LT. 1. E-02 10/01 3.00E 08 OC 10/07 09/24 2.6 i 0.3 E-02 10/11 LT. 1. E-02 10/08 2.90E 08 OC 10/14 10/01 2.7 i 0.3 E-02 10/19 LT. 1. E-02 y 10/16 3.40E 08 OC 10/21 10/08 LT. 2. E-02 10/28 2.210.3 E-02 10/26 E 10/16 10/23 3.00E 08 OC 2.4 i 0.3 E-02 10/29 LT. 2. E-02 10/23 3.00E 08 OC 10/28 [ 10/16* LT. 2. E-02 OC 11/04 2.1 i 0.3 E-02 11/02 10/23 10/29 2.70E 08 2.5 i 0.3 E-02 11/09 LT. 2. E-02 1I/05 3.00E 08 OC 11/10 10/29 LT. 2. E-02 OC 11/18 2.2 i 0.3 E-02 11/16 1I/05 11/12 3.10E 08 2.510.3 E-02 11/23 LT. 2. E-02 11/19 3.00E 08 OC 1I/24 11/12 LT. 2. E-02 OC 12/04 2.9 i 0.3 E-02 12/03 1I/19 11/26 3.00E 08 2.9 i 0.3 E-02 12/11 LT. 1. E-02 12/05 4.10E 08 OC 12/13 11/26 LT. 2. E-02 OC 12/15 1.7 i O.3 E-02 12/14 i 12/05 12/10 2.30E 08 4.0 i D.4 E-02 12/24 LT. 3. E-02 12/17 3.00E 08 OC 12/31 l 12/10 LT. 3. E-02 OC 01/02 2.910.3 E-02 12/31 12/17 12/24 2.90E 08 f 4.5 i 0.4 E-02 01/04 LT 2. E-02 12/31 3.20E 08 OC 01/08 l 12/24 5 .
- Duplicate Analysis i
3
! I i l l l 1 , L l '.t f' M. -
t _ a ) L T 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 F M. 0- 0 -0 0 - 0 0 0 - 0 0- 0 0- 0 0 0- 0 0 0 - 0 L 1 u E E E E E E E E E E E E E E E E E E A13C O/ ClC l 2 2 2 2 1 2 3 1 2 3 1 2 3 2 2 1 2 1 p R ( T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. A L L L L L L L L L L L L L L L L L L H C r f _ P _ U 2 0 6 2 5 9 7 3 1 8 5 13 9 5 3 9 6 3 _ O EE 1 2 2 0 0 0 1 2 0 0 2 2 0 1 1 2 0 _ _ CMT I A / / / / / / / / / / / / / / / / / / 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 5 DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ M - N 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0 A 0- 0 0- 0 0 0 -0 0 - 0 0 - 0 0- 0 0- 0 0- 0 0-1 1 S RT) E . E E E E E E E E E E E E E E E E E E A R EBM. T 4 4 3 4 4 4 3 3 3 4 3 3 3 3 3 3 3 3 . R O T E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 FS C I _ P L I Ol/ i i 1 1 i i 1 i i i i i i 1 i 1 i i - R F PRC 7 8 3 3 1 9 5 2 9 9 2 3 0 3 8 0 3 4 _ O L A G (p 3 2 3 3 3 3 2 2 2 2 3 2 2 2 2 2 2 1 C A 2 G O 3 _ N C . I R R - T A A E R E C H MB _ P O D N N U T f - R A N f U A 2 TE 01 OEE 6 3 9 1 2 2 0 0 4 4 1 1 0 6 3 2 2 0 1 1 1 8 6 2 0 0 1 9 4 1 3 9 5 2 2 0 - C A A1T l CMT I A / / / / / / / / / / / / / / / / / / 1 I 1 2 2 2 2 2 3 3 3 3 4 4 4 4 4 5 I DTD - 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 U N CU S I K 11 M E R E A R P C R _ - F A l I O S W T I N C C C C C C C C C C C C C C C C C C _ O O C O O O O O O C O O O O O O O O U E 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 _ M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 U E E E E E E E E E E E E E E E E E E L 0 0 0 0 0 0 0 01 0 0 0 0 0 0 0 0 0 0 9 0 O 6 0 4 6 6 0 0 9 8 0 0 9 0 1 1 V 2 3 3 2 2 3 3 3 2 2 3 3 2 3 3 2 3 3 PE 9 6 4 0 0 6 3 0 1 7 5 2 9 6 2 19 61 3 20 0 0 2 3 0 1 2 3 3 0 2 2 0 1 OT / / / / / / / / / / / / / / / / / / s TA SD I I 1 1 1 2 2 2 2 3 3 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 4 4 4 4 i s l y a - N A n O e m t a c T 3 9 6 4 4" 0 6 3 10 72 52 2 9 6 12 91 6 23 0 0 l i N RE I AT 0 0
/
1 2 2 3 0
/ 1 / /1 / 1 / /1 / I/ / / / / / / / / / u 0 1 2 p OTA 1 2 2 2 2 3 3 3 3 4 4 4 4 D CSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
- h ?e
WOtX CREEK NUCIEAR OPERATING CORPORATION r AIR PARTICUIATE AND CHARCOAL FILTERS STATION NUMBER 32 MID COUNT A P FILTER M!D COUffr CHARCOAL FILmn COLLECHON . TIME GROSS BETA TIME I-131 START STOP (pct /Cu.M.) DATE (pct /Cu.M.) DATE DATE VOLUME UNITS DATE OC 05/15 1.9 i 0.3 E-02 05/11 LT. 1. E-02 04/30 05/08 3.10E 08 OC 05/20 1.7 i 0.3 E-02 05/18 LT. 2. E-02 05/08 05/14 2.70E 08 05/26 2.5 i 0.3 E-02 05/24 LT. 2. E-02 05/14 05/21 2.90E 08 OC CC 06/03 2.1 i 0.3 E-02 05/31 LT. 1. E-02 05/21 05/28 3.00E 08 OC 06/10 1.6 i 0.3 E-02 06/07 LT. 1. E-02 05/28 06/04 3.10E 08 OC 06/17 2.1 i 0.3 E-02 06/14 LT. 2. E-02 06/04 06/11 2.90E 08 OC 06/24 3 I 10.4 E-02 06/21 LT. 2. E-02
'o 06/11 06/18 3.00E 08 OC 06/30 2.4 i 0.3 E-02 06/28 LT. 2. E-02 06/18 06/25 3.00E 08 06/30 2.2 i 0.3 E-02 07/02 LT. 1. E-02 06/18* 06/25 3.00E 08 OC CE 07/10 2.4 i 0.4 E-02 07/09 LT. 3. E-02 06/25 07/02 3.00E 08 CC 07/14 2.8 i 0.3 E-02 07/12 LT. 1. E-02 07/02 07/09 2.80E 08 CC 07/20 1.9 i 0.3 E-02 07/19 LT. 1. E-02 07/09 07/16 2.90E 08 07/30 2.010.3 E-02 07/26 LT. 1. E-02 07/16 07/23 2.90E 08 OC 08/05 2.1 i 0.3 E-02 08/03 LT. 2. E-02 07/23 07/30 3.00E 08 OC OC 08/11 2.4 i 0.3 E-02 08/10 LT. 2. E-02 07/30 08/06 3.00E 08 08/18 3.010.4 E-02 08/17 LT. 1. E-02 08/06 08/13 2.90E 08 OC 08/25 2.7 i 0.3 E-02 08/22 LT. 1. E-02 08/13 08/20 3.00E 08 OC 09/03 2.2 i 0.3 E-02 08/31 LT. 2. E-02 08/20 08/27 3.10E 08 OC
' Duplicate Analysis
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s s s s s s s s s s s s s s s s s s s = e o o o a O O O O O - - - - - N N N N a. Y.o ama O O O O O - - - - - - - - - - - - - - Page B-11 L -
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e t ) L . 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 M 1 M. 0- 0 0- 0 0 0 - 0 0- 0 0 0 0 0 0 0 0 0- 0 L 3Cu E E E E E E E E E E E E E E E E E E A1/ . . . . . . . . . . . . . . . . . . OC C R l t p 2 2 2 2 2 3 1 2 2 1 1 2 2 2 2 1 2 1 ( T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. A L L L L L L L L L L L L L L L L L L H C _ r r P U 2 0 6 2 9 7 3 1 8 9 5 31 9 5 3 9 6 3 O EE 1 2 2 0 0 1 2 0 0 0 2 2 0 1 1 2 0 CMT I A / / / / / / / / / / / / / / / / / / 1 I 1 2 2 2 2 3 3 3 3 3 3 4 4 4 4 5 DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 M N 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 O A 0- 0 0 - 0 - 0 0- 0 0- 0 -0 0 0 0- 0 0 0 0 0 - - - - - - - - I T S R ET) . E E E E E E E E E E E E E E E E E E A R EBM. T 4 4 4 4 4 3 4 3 3 3 4 3 3 3 3 3 3 3 R E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ O T F Ot I SC P L I / i i i 1 i 1 1 1 i i i i 1 i i 1 i i R F P RC 1 3 8 2 8 5 8 1 7 6 6 5 5 9 1 2 8 4 O L A G (p 4 3 3 3 3 2 2 3 2 2 3 2 2 2 3 2 1 1 C A G O 3 7 l C U T R R A R A H E B E C M P O D U N N r f R A N f U A 2 E 01 I O EE 6 3 9 1 2 2 0 4 1 1 0 6 3 2 2 0 1 1 1 1 8 6 I 2 0 0 1 9 4 1 3 9 5 2 2 0 C E A I 1 CMT I A / / / / / / / / / / / / / / / / / / 1 1 1 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 I U U TS DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N C1 I M K I E R E A R P C R E A l I O S W T I N C O C C CC OC CC OC OC OCOCO CO CO CO CO CO C O C O C : I C U E 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 U E 0 0 E E E E E E E E 0 0 05 0 10 0 0 0 EC E E E 0 000 00 E 0E 0E 0E E 0 L 2 0 0 O 5 1 4 8 9 1 2 1 1 1 V 2 3 3 2 3 2 2 3 3 3 3 3 3 3 3 3 3 3
- PE 9 6 4 0 6 3 10 7 5 5 2 9 06 21 9 1 6 32 00 0 1 2 3 0 1 2 3 0 2 2 0 OT TA
/
1
/ 1 / /1 / 1/ / / / / / / / / / / / /
2 2 2 2 3 3 3 3 3 4 4 4 4 4 i s
- SD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 s y
l a n _ N A 0 1 t e 7 a ic mTRE s AT 3 9 6 4
/ / / / /2 3/0 / 2/ 2 /2 /
0 0 1 0 6 3 01 7 2 2 2 0 7' 5 2 1 9 61 2 9 6 3
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p OTA 1 1 1 1 1 2 4 4 4 D CSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
- y [ro
i WOIX CREEK NUCLEAR OPERAT1NG CORPORATION AIR PARI 1CULATE AND CIIARCOAL FIL"IERS STATION NUMBER 37 COLIECIlON MID COUNT A P FILTER MID COUNT CHARCOAL FILat.n START STOP TIME GROSS BETA TIME I.131 DATE DATE VOLUME UNITS DATE (pCl/Cu.M.) DATE (pCI/Cu.M.) 04/30 05/08 3.20E 08 OC 05/15 1.9 i 0.3 E-02 05/11 LT. 1. E-02 05/08 05/14 2.70E 08 CC 05/20 2.010.3 E-02 05/18 LT. 2. E-02 05/14 05/21 2.90E 08 OC 05/26 2.2 i 0.3 E-02 05/24 LT. 2. E-02 05/21 05/28 2.90E 08 OC 06/03 1.9 i 0.3 E-02 05/31 LT. 1. E-02 , 05/28 06/04 3.00E 08 OC 06/10 1.7 i 0.3 E-02 06/07 LT. 1. E-02 u t$ 06/04 06/I1 2.90E 08 OC 06/17 2.2 i 0.3 E-02 06/14 LT. 2. E-02 m 06/11 06/18 2.80E 08 OC 06/24 2.7 i 0.4 E-02 06/21 LT. 2. E-02 36/18 06/25 2.90E 08 OC 06/30 2.010.3 E-02 06/28 LT. 2. E-02 06/25 07/02 2.90E 08 OC 07/10 2.4 i 0.4 E-02 07/09 LT. 3. E-02 07/02 07/09 2.80E 08 OC 07/14 3.010.4 E-02 07/12 LT. 1. E-02 07/09 07/16 3.00E 08 CC 07/20 1.7 i 0.3 E-02 07/19 LT. 1. E-02 07/16 07/23 3.00E 08 G: 07/30 1.7 i 0.3 E-02 07/26 LT. 1. E-02 07/16' 07/23 3.00E 08 G: 07/30 1.5 i 0.3 E-02 07/27 LT. 7. E-03 07/23 07/30 2.90E 08 OC 08/05 2.8 i 0.3 E-02 08/03 LT. 2. E-02 07/30 08/06 1.80E 08 OC 08/11 2.110.4 E-02 08/10 LT. 3. E-02 ; 08/13 3.00E 08 02 08/18 2.7 i 0.3 E-02 08/17 LT. 1. E-02 08/06 08/20 2.90E 08 OC 08/25 2.4 i 0.3 E-02 08/22 LT. 1. E-02 08/13 08/27 3.10E 08 OC 09/03 2.3 i 0.3 E-02 08/31 LT. 2. E-02 08/20
' Duplicate Analysis 'l l
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1 CMTA I
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0 0 1 DTD I 0 0 0 0 1 1 I 1 1 1 M N 0 A 2 0 2 0 2 0 2 0 2 0 2 0 2 0 - 2 0 - 2 0 - 2 0 2 - 0 - 2 0 - 2 0 2 - 0 2 - 0 2- 0 2 - 0 2 - 0 2 - 0 - 1 1 S RT) E. E - E - E - E E E E E E E E E E E E E E E E _ A R R E E T BM. 4 4 3 3 3 3 3 3 3 3 3 4 4 3 3 4 3 3 4 O T LSu I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 P L F Ol SC / i i 1 1 i 1 1 i 10 i i i i 1 i7 7t 810 1 i R F I PRC 9 5 2 5 4 1 6 1 9 2 6 1 1 9 O L A G (p 3 4 2 2 2 3 2 2 2 2 2 2 3 3 1 3 2 3 4 C G O 3 A 7 N C - I R R T A A E ER C H M B P D U O N N T N - R A N U 8 713 9 7 4 1 8 4 0 1 8 4I 42 30 5 1 2 2 8 - A E. ET 01 O EE 0
/ 2 2 0 1
/ / / / / / / / / / / / 2/ 2 /2 2/ / / / 2 2 0 1 1 3 0 0 0 t
C L A T A CMT I A 9 9 9 9 0 0 0 0 1 1 I 1 1 1 1 1 1 1 0 0 0 1 I U T DTD 0 0 0 0 1 1 1 1 1 1 1 N CU S _ I M _ K IT _ E R _ E A - R P C R F A E I _ O S W T C C O C O C O C O C O C O C O C O C O CO CO CO CO CO CO CO CO C OO I N U E 8 0 80 8 0 8 0 80 8 0 8 0 8 0 8 0 80 80 8 0 8 0 8 0 8 0 8 0 8 0 8 0 8 0 M U E 0 E0 E0 E0 E0 E00 E E E E E E E E E E E E E L O 1 0 5 7 1 400 0 7 00 0 0 1 08 807 0 01 08 909 0 0 0 V 3 3 3 2 3 3 3 3 2 3 3 2 2 3 2 2 2 2 3 1 PE 3 0 18 41 2 0 0 1 8 6 32 290 5 2 9 6 250 0 7 4 42 1 1 1 1 1 2 3 0 O *I
.TA
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9 9 9 9 0 0 0 0 0 1 1 1 1 1 1 2 2/2 / 1 1 2 2/ 2/ / 1 1 1 i s s 1 1 1 1 1 y _ .SD 0 0 0 0 1 1 1 l a n . N A e O t _ I T
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- CSD 0 0 0 0 0 1 1 1 1 1 1 2
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2 0 0 2 2 0 0 1 1 2 0 CMIK I 1 1 1 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ M - N 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 02 02 0 O A 0- 0 0- - 0 0 0- 0 0- 0 0-0- 0 0- 0 0- - - I T S RT). E E E E E E E E E E E E E E E E E E A R EE T B M. 4 4 3 4 4 3 4 3 4 3 3 3 3 3 3 3 3 3 R E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O T F SC I P L I OI/ i i 1 1 i i i i i i i i i i i 1 1 i R F PRC 4 8 3 1 8 6 7 9 8 3 5 5 4 3 6 9 0 5 _ _ O L A G (p 4 2 3 3 3 2 2 2 2 3 2 2 2 2 2 1 2 1 C GO A 04 _ N C T R R I _ A R A H MEB E C P D U O N N T N _ R A N U A E 'E O I I OEE 6 3 9 1 2 2 0 4 1 1 0 6 3 2 2 0 1 1 8 6 1 1 2 0 0 0 9 9 4 1 3 9 5 2 2 0 L / / / / / / / / / / / / / / / / / / C LA T A CMIN 2 2 2 2 3 3 3 3 4 4 4 4 4 4 5 _ I 1 1 1 T DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 U N CU S I K U M E R E A R P C R X A I I O S _ W T - I N I I C C C C C C C C C C C C C C C C _ ( ( O O O O O O O O O O O O C O O O U E 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 M 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ U E E E E E E 0 E 0E 0E 0E0 E0 E0 E E E E E E 0 0 0 0 0 0 0 _ L 0 0 O 0 - O 6 0 4 6 2 9 0 9 0 1 9 7 0 0 0 8 0 0 V 2 3 3 2 3 2 3 2 3 3 2 2 3 3 3 2 3 3 PE 9 6 4 0 6 3 0 7 5 2 9 6 12 21 9 26 03 0 0 0 2 3 0 1 2 3 0 1 2 2 0 1 DT IA /1
/ 1/ /1 / /1 / / / / / / / / / / / /
2 2 2 2 3 3 3 3 4 4 4 4 4 4 i s S~D 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 s y l a N n O A e _ H t a C
- c ET LRE 3 9 6 4 0 6 3 0 7 5 2 9 16 6 1 2 9 6 3 i 2 l
p 0 0 1 2 3 0 1 2 2 0 2 2 0 0 1 LAT / / 1 / /1 / / / / / / / / / / / / / / 3u 3 3 4 OTA 1 1 1 2 2 2 2 3 3 4 4 4 D CSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
- y
l i" WOIX CREEK NUCLEAR OPERA 11NG OORPORATION AIR PARI 1CULATE AND CHARCOAL FILTERS STATION NUMBER 40 l MID COUNT A P FIL'IER MID COUlU CHARCOAL filar.n COIAECI1ON . TIME GROSS BETA TIME I-131 START STOP - (pC1/Cu M.) DA~IE (pC1/Cu.M.) DATE VOLUME UNITS DA~IE DATE 05/15 1.8 i 0.3 E-02 05/11 LT. 9. E-03 04/30 05/08 3.30E 08 CE OC 05/20 1.7 i 0.3 E-02 05/18 LT. 1. E-02 05/08 05/14 2.60E 08 OC 05/26 1.9 i 0.3 E-02 05/24 LT. 9. E-03 05/14 05/21 3.00E 08 OC 06/03 1.9 i 0.3 E-02 05/31 LT. 9. E-03 05/21 05/28 2.90E 08 CC 06/10 2.0 i 0.3 E-02 06/07 LT. 1. E-02 05/28 06/04 2.80E 08 OC 06/17 1.7 i 0.3 E-02 06/14 LT. 1. E-02 06/04 06/11 2.90E 08 OC 06/24 2.4 i 0.3 E-02 06/21 LT. 1. E-02 06/11 06/18 3.10E 08 CC 06/30 2.2 i 0.3 E-02 06/28 LT. 9. E-03 cu 06/18 06/25 2.90E 08 07/10 2.7 i 0.4 E-02 07/09 LT. 2. E-02 06/25 07/02 3.20E 08 CC OC 07/14 2.7 i 0.3 E-02 07/12 LT. 7. E-03 07/02 07/09 3.00E 08 OC 07/20 2.210.3 E-02 07/19 LT. 8. E-03 07/09 07/16 3.00E 08 OC 07/30 1.6 i 0.3 E-02 07/26 LT. 8. E-03 07/16 07/23 3.00E 08 OC 08/05 2.310.3 E-02 08/03 LT. 1. E-02 i 07/23 07/30 3.10E 08 08/11 2.6 i 0.3 E-02 08/10 LT. 8. E-03 07/30 08/06 3.00E 08 CE i 08/18 2.7 i 0.3 E-02 08/17 LT. 7. E-03 1 08/06 08/13 2.90E 08 OC OC 08/25 2.610.3 E-02 08/22 LT. 7. E-03 j 08/13 08/20 3.20E 08 2.310.3 E-02 08/31 LT. 1. E-02 i 08/20 08/27 3.00E 08 OC 09/03 j 09/04 2.6 i 0.3 E-02 09/04 LT. 3. E-02 08/20' 08/27 3.00E 08 OC
- *Dupilante Analysis i
i ' d
- WOEF CREEK NUCLRAR OPERATING CORPORATION AIR PARTICULATE AND CilARCOAL FILTERS STATION NUMBER 40 .
A P FIL'IER MID COUNT CHARCOAL F1Lar n COLLEC110N MID COUKF I.131 TIME GROSS BETA TIME START STOP (pCl/Cu.M.) DATE (pCI/Cu.M.) DATE VOLUME UNITS DATE DATE 4.1 10.4 E-02 09/07 LT. 1. E-02 08/27 09/03 3.00E 08 OC 09/08 3.9 i 0.4 E-02 09/13 LT. 1. E-02 09/03 09/10 3.00E 08 OC 09/17 2.4 i 0.3 E-02 09/21 LT. 5. E-03 09/10 09/18 3.40E 08 OC 09/23 2.010.3 E-02 09/27 LT. 1. E-02 09/18 09/24 2.60E 08 CE 09/29 2.8 i 0.3 E-02 10/04 LT. 8. E-03 10/01 3.00E 08 OC 10/07 y 09/24 2.9 i 0.3 E-02 10/11 LT. 9. E-03 0 10/08 2.90E 08 OC 10/14 10/01 3.4 i 0.4 E-02 10/19 LT. 8. E-03 10/16 3.20E 08 OC 10/21 10/08 2.110.3 E-02 10/26 LT. 1. E-02 10/23 2.80E 08 OC 10/28 10/16 2.310.3 E-02 11/02 LT. 1. E-02 10/29 2.60E 08 CC 11/04 10/23 2.8 i 0.3 E-02 11/09 LT. 1. E-02 10/29 11/05 2.90E 08 OC I1/10 2.4 i 0.3 E-02 11/16 LT. 1. E-02 11/05 11/12 3.00E 08 OC 11/18 2.6 i 0.3 E-02 11/23- LT. 9. E-03 11/19 3.00E 08 OC 11/24 1I/12 LT. 1. E-02 OC 12/04 3.010.3 E-02 12/03 11/19 11/26 3.00E 08 3.1 10.3 E-02 12/11 LT. 8. E-03 11/26 12/05 3.90E 08 OC 12/13 1.7 i 0.3 E-02 12/14 LT. 1. E-02 12/05 12/10 2.10E 08 OC 12/15 3.9 i 0.4 E-02 12/24 LT. 1. E-02 12/31 4 12/10 12/17 3.00E 08 OC 3.110.3 E-02 12/31 LT. 1. E-02 12/17 12/24 2.90E 08 CC 01/02 5.210.4 E-02 01/04 LT. 8. E-03 12/24 12/31 2.90E G8 OC 01/08 i
WOIX CREEK NUCLEAR OPERATING CORPORATION AIR PARI 1CULATE FIL'IERS EXPOSURE PA11tWAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARIERLY COMPOSITE (pCl/elu.M.) STAT 10N NUMBER 02 1 07/02-10/01 10/01-12/31 01/03-04/02 04/02-07/02 DATE COLLECIED: GAMMA SPECTRUM ANALYSIS: 9.9811.00 E-02 6.8210.68 E-02 7.7210.77 E-02 8.9410.89 E-02 BE-7 LT.9. E-03 LT.8. E-03 ; LT. 1. E-02 LT.9. E-03 K-40 LT.5. E-04 LT. 6. E-04 ) LT.5. E-04 LT.3. E-04 o MN-54 LT. 5. E-04 LT.5. E-04 [ LT. 5. E-04 LT.4. E-04 h CO-58 LT. 1. E-03 LT. 1. E-03 { LT. 1. E-03 LT.9. E-04 m FE-59 LT.4. E-04 LT.6. E-04 LT. 5. E-04 L T. 5. E-04 1 CO-60 E-04 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT. 9. E-04 ZN-65 LT. 5. E-04 LT. 5. E-04 LT. 5. LT.5. E-04 E-04 NB-95/ZR-95 E-04 LT.5. E-04 LT.6. LT.5. E-04 LT. 5. RU-103 LT.4. E-03 LT.4. E-03 LT.4. E-03 LT.3. E-03 RU-106 E-03 LT. 2. E-03 LT. 1. E-03 LT. 1. E-03 LT. 1. 1-131 LT. 5. E-04 LT.6. E-04 LT.5. E-04 LT.4. E-04 CS-134 LT.7. E-04 LT.6. E-04 LT.5. E-04 LT.4. E-04 ! CS-137 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT.9. E-04 LA-140/BA-140 E-04 LT. 9. E-04 LT.7. E-04 LT. 8. E-04 LT. 8. CE-141 LT.3. E-03 LT.3. E-03 LT.2. E-03 LT.2. E-03 CE-144 LT.8. E-03 LT.9. E-03 LT.7. E-03 LT.8. E-03 RA-226 LT.7. E-04 LT.9. E-04 LT.7. E-04 LT.7. E-04 TH-228 , b _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ .________________._-_____.__m____ ________m
WOLF CREEK NUCI2AR OPERATING CORPORA 110N i . AIR PART1CULATE FIL'IERS EXPOSURE PATIIWAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARIERLY COMPOSITE , (pC1/Cu.M.) , STAT 10N NUMBER 03 DATE COLLECIED: 01/03-04/02 04/02-07/02 07/02-10/01 10/01-12/31 GAMMA SPECTRUM ANALYSIS: 4 BE-7 9.5810.96 E-02 9.6510.07 E-02 8.5510.86 E-02 5.9410.59 E-02 K-40 7.3113.84 E-03 LT. 1. E-02 7.1313.35 E-03 LT. 1. E.02 MN-54 LT. 5. E-04 LT.6. E-04 LT.4. E-04 LT.4. E-04 y CO-58 LT.3. E-04 LT.5. E-04 LT.4. E-04 LT.5. E-04 FE-59 E-03 E-03 LT. 9. E-04 LT. 1. E-03
% LT. 1. LT. 1.
c3 CO-60 LT. 5. E-04 LT.6. E-04 LT.4. E-04 LT.5. E-04 5 ZN-65 LT. 1. E-03 LT. 1. E-03 LT. 9. E-04 LT.9. E-04 NB-95/ZR-95 LT.6. E-04 LT.6. E-04 LT. 5. E-04 LT.5. E-04 RU-103 LT.6. E-04 LT. 6. E-04 LT. 5. E-04 LT.5. E-04 RU-106 LT.4. E-03 LT.4. E-03 LT.4. E-03 LT.4. E-03 1-131 LT. 1. E-03 LT. 2 E-03 LT. 1. E-03 L T. 1. E-03 CS-134 LT.5. E-04 L7'. 5. E-04 LT.4. E-04 LT.5. E-04 i CS-137 LT.4. E-04 L'I, 5. E-04 LT. 5. E-04 LT.5. E-04 LA-140/BA-140 LT. 1. E-03 LT. 1. E-03 LT.9. E-04 LT. 1. E-03 : CE-141 LT.8. E-04 LT. 1. E-03 LT. 5. E-04 LT. 6. E-04 CE-144 LT.3. E-03 LT.4. E-03 LT.2. E-03 LT.2. E-03 RA-226 LT.9. E-03 LT. 1. E-02 LT.6. E-03 LT.6. E-03 TH-228 LT.9. E-04 LT. 1. E-03 LT.6. E-04 LT. 6. E-04 , i
. _ _ _ _ _ - _ -_..__-_-_m.__r -- --- - _ _ _
WOLF CREEK NUCIEAR OPERATING CORPORAT10N AIR PARI 1CULATE FIL'IERS { EXPOSURE PATHWAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARIERLY COMPOSTIE t (pCI/Cu.M.) STATION NUMBER 32 04/02 07/02 07/02-10/01 10/01-12/31 DATE COLLECTED: 01/03-04/02 GAMMA SPECTRUM ANALYSIS: 9.5310.95 E-02 1.0010.10 E-01 6.9110.69 E-02 BE-7 8.4710.85 E-02 LT.8. E-03 LT.8. E-03 LT.2. E-02 K-40 5.6212.88 E-03 LT.4. E-04 LT.4. E-04 LT.6. E-04 MN-54 LT.5. E-04 LT.4. E-04 LT.4. E-04 LT.6. E-04 y CO-58 LT.4. E-04 E-03 LT.9. E-04 LT. 1. E-03 FE-59 LT. 1. E-03 LT. 1.
% LT.5. E-04 LT. 5. E-04 LT.5. E-04 CO-60 LT.6. E-04 7 LT. 1. E-03 LT.9. E-04 LT. 1. E-03 LT. 1. E-03 y ZN-65 LT.7. E-04 LT.5. E-04 LT.4. E-04 LT.4. E-04 NB-95/ZR-95 LT.7. E-04 LT.5. E-04 LT.5. E-04 LT. 4. E-04 RU-103 LT.5. E-03 LT.4. E-03 LT.4. E-03 LT.4. E-03 RU- 106 LT.2. E-03 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 I-131 LT.6. E-04 LT. 5. E-04 LT.4. E-04 LT.4. E-04 CS- 134 E-04 LT.6. E-04 LT.5. E-04 LT.6.
CS-137 LT.4. E-04 E-03 LT.7. E-04 LT. 1. E-03 IA-140/BA-140 LT.8. E-04 LT. 1. LT.7. E-04 LT.6. E-04 LT.9. E-04 CE-141 LT.7. E-04 LT.2. E-03 LT. 2. E-03 LT.3. E-03 CE-144 LT. 3. E-03 LT.8. E-03 LT.6. E-03 LT.9. E-03 RA-226 LT.8. E.03 LT.7. E-04 LT.6. E-04 LT.8. E-04 TH-228 LT.8. E-04
t WOIF CREEK NUCI2AR OPERATING CORPORATION + AIR PARI 1CULATE FIL1ERS , EXPOSURE PA11(WAY - AIRBORNE ' ISOIDPIC ANALYSIS ON QUARIERLY COMPOSITE (pCl/Cu.M.) 1 STATION NUMBER 37 ., 01/03 04/02 04/02-07/02 07/02-10/01 10/01-12/31 DA1E COLLECIED: GAMMA SPECTRUM ANALYSIS: 8.3710.84 E-02 9.8710.99 E-02 7.8010.78 E-02 ! l BE-7 8.6810.87 E-02 E-02 LT.2. E-02 LT.7. E-03 K-40 8.4513.49 E.03 LT. 1.
- LT.4. E-04 LT.6. E-04 LT.4. E-04 MN-54 LT. 3. E-04 E-04 LT.5. E-04 LT.6. E.04 LT. 5. E-04 u CO-58 LT.3.
E-03 LT. 1. E-03 LT. 1. E-03 ,j LT.8. E-04 LT. 1. { FE-59 LT.4. E-04 LT.4. E-04 LT.7. E-04 LT.6. E-04 t co CO-60 E-04 LT.8. E-04 LT. 1. E-03 LT. 1. E-03 LT.9. h ZN-65 E-04 E-04 LT.7. E-04 LT.4. E-04 LT. 3. LT. 5. NB-95/ZR-95 RU-103 LT.4. E-04 LT.5. E-04 LT. 7. E-04 LT.4. E-04 ll II LT.4. E-03 LT.6. E-03 LT.4. E-03 RU-106 LT.3. E-03 ' LT. 1. E-03 LT.2. E-03 LT. 2. E-03 I-131 LT. 1. E-03 E-04 LT.7. E-04 LT.3. E-04 CS-134 LT.4. E-04 LT.4. E-04 LT. 6. E-04 LT.4. E-04 CS-137 LT.3. E-04 LT.4. E-03 LT. 1. E-03 LT. 1. E-03 LA-140/BA-140 LT.6. E-04 LT. 1. LT. 5. E-04 LT.9. E-04 LT.8. E-04 CE-141 LT.6. E-04 E-03 LT.3. E-03 LT.2. E-03 CE-144 LT.2. E-03 LT.2. E-03 LT.9. E-03 LT.8. E-03 ! RA-226 LT.6. E-03 LT.6. I' LT.6. E-04 LT.9. E-04 LT. 7. E-04 TH-228 LT.6. E-04 l. 8
wots CREEK NUCl2AR OPERATING CORPORATION AIR PART1CULATE FILTERS EXPOSURE PA'IHWAY - AIRBORNE , t ISOTOPIC ANALYSIS ON QUAR 1ERLY COMPOSITE (pCl/Cu.M.) STATION NUMBER 40 01/03-04/02 04/02-07/02 07/02-10/01 10/01-12/31 DATE COLLEC1ED-GAMMA SPECIRUM ANALYSIS: 8.3710.84 E-02 8.3210.83 E-02 1.1010.11 E-01 6.1410.61 E-02 BE-7 E-02 LT.8. E-03 LT.8. E-03 L.T. 1. E-02 K-4 0 LT.2. E-04 LT. 5.- E-04 LT.4. E-04 LT.4. E-04 MN-54 LT.6. E-04 LT.5. E-04 LT.4. E-04 LT.4. E-04 CO-58 LT.5. E-03 LT. 1. E-03 LT. 1. 'E-03 LT. I. E-03 FE-59 LT. 1. E-04 LT.5. E-04 LT.6. E-04 LT.5. E-04 LT.5. [CO-60 LT. 1. E-03 LT. 1. E-03 LT. 1. E.03 LT.9. E-04 (0 ZN.65 LT.4. E-04 LT.5. E-04 LT.5. E-04 TNB-95/ZR-95 LT. 6. E-04 ' E-04 LT. 5. R na LT. 5. E 04 LT. S. E-04
$RU-103 LT.6.
E-03 LT.4. E-03 LT.4. E-03 LT.4. E-03 , RU- 106 LT.5. E-03 LT. 1. E-03 LT. 1. E-03 I-131 LT. 1. E-03 LT. 1. LT. 5. E-04 LT. 5. E-04 LT.5. E-04 CS-134 LT.6. E-04 LT.4. E-04 LT. 5. E-04 LT.4. E-04 [ CS-137 LT.5. E-04 f E-03 LT.9. E-04 LT.9. E-04 1A-140/BA-140 LT. 1. E-03 LT. 1. LT.6. E-04 LT. 8. E-04 LT.5. E-04 CE-141 LT.7. E-04 ' E-03 LT. 2. E-03 LT.3. E-03 LT.2. E.03 CE-144 LT.2. LT.6. E-03 LT.8. E-03 LT.6. E-03 RA-226 LT.7. E-03 LT.6. E-04 LT.8. E.04 LT.6. E-04 TH-228 LT.7. E-04
WOtX CREEK NUCIZAR OPEIPATING CORPORATION EXPOSURE PATHWAY - INGES110N ANIMAIS/ GAME i (pCf/KG WET) STA110N NUMBER SECTOR Q l i DATE COLLECTED: 12/20 ' W111TETAIL DEER j GAMMA SPECIRUM ANALYSIS: BE-7 LT.5. E 01 K-40 3.7710.38 E 03 MN.54 LT.5. E 00 ~ CO-58 LT.6. E 00 FE-59 LT. 1. E 01 CO-60 LT.6. E 00 i 2 ZN-65 LT. 1. E 01 S NB-95/ZR-95 LT.6. E 00 LT.7. E 00 ? RU-103 E$ RU-106 LT. 5. E 01 I-131 LT. 1. E 01 I CS-134 LT.6. E 00 E 00 l CS-137 LT.7. LA-140/BA-140 LT.9. E 00 CE-141 LT. I. E 01 CE-144 LT.3. E 01 RA-226 LT. I. E 02 TH-228 LT. 9. E 00 t
WOlE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE Pall {WAY - INGEST 10N FEED & FDRAGE (pCl/KG WET) STATION NUMBER NR-D1 DATE COLLECIED: 10/21 CORN GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 K-40 3.0610.31 E 03 MN-54 LT.4. E 00 CO-58 LT.4. E 00 FE-59 LT. 1. E 01 CO-60 LT.4. E 00 o ZN-65 LT. 1. E 01 LT.4. E 00 f NB-95/ZR-95 m RU-103 LT.4. E 00 5 RU-106 LT.3. E 01 I-131 LT.6. E 00 CS-134 LT.4. E 00 , CS-137 LT.4. E 00 LA-140/BA-140 LT.4. E 00 CE-141 LT.7. E 00 j CE-144 LT.3. E 01 RA-226 LT.9. E 01 TH-228 LT.7. E 00 l t I t i h l
I WOLF CREEK NUCLEAR OPERATING CORPORAT10N EXPOSURE PATHWAY - INGESTION FEED & FORAGE ! (pCl/KG WET) STAT 10N NUMBER NR-D2 DATE COLLECTED: 10/21 CORN GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 K-40 3.4510.34 E 03 MN-54 LT.4. E 00 CO-58 LT.3. E 00 FE-59 LT.9. E 00 CO-60 LT.4. E 00 LT.9. E 00 [ ZN-65 LT.4. E 00 m NB-95/ZR-95
? RU-103 LT.4. E 00
$ RU-106 LT.3. E 01 1-131 LT.5. E 00 CS-134 LT.4. E 00 CS-137 LT.4. E 00 LA-140/BA-140 LT.4. E 00 CE 141 LT.5. E 00 CE-144 LT.2. E 01 RA-226 LT.7. E 01 TH-228 LT. 6. E 00
WOIE CREEK NUCI2AR OPE 3tATING CORPORA 110N
- EXPOSURE PA~IIIWAY - INGEST 10N FEED & FORAGE (pCl/KG WET)
STAT 10N NUldBER NR-UI l DA'IE COLLECIED: 10/21 10/2i CORN SOYBEANS GAMMA SPEC 1' RUM ANALYSIS: DE-7 LT.4. E O1 LT.6. E O1 K-40 2.8410.28 E 03 1.7910.18 E 04 MN-54 LT.4. E 00 LT. 7. E 00 CO-58 LT.4. E 00 LT. 7. E 00 FE-59 LT. 1. E 01 LT.2. E 01 CO-60 LT.5. E 00 LT.8. E 00 u ZN-65 LT. 1. E 01 LT.2. E 01 NB-95/ZR-95 LT.4. E 00 LT.7. E 00
- h. E 00 m RU-103 LT.4. E 00 LT.7.
d> RU-106 LT.4. E 01 LT.6. E 01
- E 00 LT.9. E 00 l-131 LT.6.
CS-134 LT.4. E 00 LT.8. E 00 CS-137 LT. 5. E 00 LT.7. E 00 IA-140/BA-140 LT.5. E 00 LT.7. E 00 CE-141 LT. 6. E 00 LT.9. E 00 CE-144 LT.3. E 01 LT.4. E 01 RA-226 LT.7. E 01 LT. 1. E 02 ! TH-228 LT.7. E 00 LT. 1. E 01 i ________m___ _ _ _ __ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ - __ _ _ _ _ _ _ _ _ ___- -
i WOIX CREEK N11CIJCAR OPERATING CORPORATION EXPOSURE PA'ITIWAY - INGES110N l'Isil (pCI/KG WEll STATION NUMBER JRR 05/01 05/01 10/25 10/25/96 DATE COLLECTED: CilANNEL CATFISil COMMON CARP COMMON CARP CIIANNEL CATFISil GAMMA SPECTRUM ANALYSIS: E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 BE-7 LT. 1. 3.8210.38 E 03 3.4910.35 E 03 3.5210.35 E 03 3.3310.33 E 03 K-40 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 MN-54 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CO-58 E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 FE-59 LT.2. LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 y CO-60 LT.3. E 01 LT.3. E 01 , LT.2. E 01 LT. 3. E 01
$ ZN.65 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 cu NB-95/ZR-95 LT. 1. E 01 E 01 LT. 1. E 01 LT.I. E 01 LT. 1. E 01 LT. 1.
- h RU-103 LT.9. E 01 LT. 1. E 02 LT. 1. E 02 L T. 1. E O2 RU- 106 E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 I-131 LT.2. '
L T. 1. E 01 LT. 1. E 01 LT. 1. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 , CS-137 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 IA.140/BA-140 E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. CE-141 E 01 LT.7. E 01 LT.8. E 01 LT.6. E 01 > CE-144 LT.7. E 02 LT.2. E 02 LT.3. E 02 LT.2. E 02 .
< RA-226 LT.2. I E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 ,
TH-228 LT.2. TR111UM ANALYSIS: E 02 LT.2. E 02 LT.3. E 02 LT. 1. E 02 H-3 LT.2.
l WOtF CREEK NUCIEAR OPERATING CORPORATION
^
EXPOSURE PA111WAY - INGES'110N FISit (pCl/KG WE'Il STA~I1ON NUMBER UllS DA1E COLLECTED: 04/16 10/16 WALLEYE WALLEYE GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT.2. E 02 K-40 3.8710.39 E 03 4.7110.47 E 03 MN-54 LT. 1. E 01 LT.2. E 01 CO-58 LT. 1. E 01 LT.2. E 01 FE-59 LT.3. E 01 . LT. 5. E 01 CO-60 LT. 1. E 01 LT.2. E 01 LT.3. E 01 LT.5. E 01 2 ZN-65
?> NB-95/ZR-95 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01
? RU-103 E 02
@ RU-100 LT. 1. E 02 LT.2.
1-131 LT.3. E 01 LT.3. E 01 CS-134 LT. 1. E 01 LT.2. E 01 CS-137 LT.2. E 01 LT.2. E 01 IA-140/BA-140 LT.2. E 01 LT.2. E 01 CE-141 LT.2. E 01 LT.3. E 01 CE-144 LT.7. E 01 LT. 1. E 02 RA-226 LT.2. E 02 LT.4. E 02 TH-228 LT.2. E 01 LT. 3. E 01 , TRITIUM ANALYSIS: H-3 8.9 i 0.3 E 03 6.0 i 0.3 E 03 L I
WOtX CREEK NUCIJtAR OPERATING CORPORAT10N EXPOSURE PATHWAY - INGES110N F1SH (pCl/KG WEll STATION NUMBER WCCL CAUSEWAY DATE COLLECTED: 04/16 BM BUITAID GAMMA SPECIRUM ANALYSIS: BE-7 LT. 1. E 02 K-40 3.0510.30 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 FE-59 LT.3. E 01 u CO-60 LT. 1. E 01 LT.3. E 01 f ZN-65 LT. 1. E 01 m NB-95/ZR-95 k RU-103 LT. 1. E 01
- LT. 1. E 02 RU-106 I-131 LT.3. E 01 CS-134 LT. 1. E 01 CS-137 LT.2. E 01 -
LA-140/BA-140 LT.2. E 01 , CE-141 LT.2. E 01 CE-144 LT.8. E 01 RA-226 LT. 2. E 02 TH-228 LT.2. E 01 , TRI11UM ANALYSIS: 11-3 7.6 1 0.2 E 03 .
' WOLF CREEK NUCIEAR C?ERATING CORPORAT10N EXPOSURE PATHWAY - INGESTION FISil ,
(pCI/KG WTI) STA110N NUMBER WCCL DC DATE COLLECIED: 04/16 04/16 04/16 10/16/96 10/16/96 WilrIE CRAPPIE CHANNEL CATFISH COMMON CARP CHANNEL CA1T1SH COMMON CARP GAMMA SPECTRUM ANALYSIS: E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 BE-7 LT. 1. E 02 LT. 1. 3.4410.34 E 03 3.4410.34 E 03 3.0710.31 E 03 3.9010.39 E 03 3.3010.33 E 03 K-40 E 01 E 01 LT. 1. E 01 LT. 1. E 01 MN-54 LT. 1. E 01 LT. 1. LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CO-58 LT.2. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 LT. 2. E 01 FE-59 LT.4. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 2 CO-60 LT.2. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 LT. 2. E 01 E ZN.65 LT.3. E 01 L T. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 i' NB.95/ZR-95 LT.2. , E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 i
$ RU-103 LT.2.
L T. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 L.T. 1. E 02 RU-106 I E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT. 1. E 01 1-131 LT.3. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 L.T. 1. E 01 CS-134 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 L T. 1. E 01 i CS-137 LT. 2. LT.2. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 IA-140/BA-140 ' E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 CE-141 LT.2 E 01 L T. 1. E 02 LT. 1. E 02 LT.7. E 01 LT. 6. E 01 CE-144 LT.8. E 02 E 02 LT.3. E 02 LT.2. E 02 LT. 2. E 02 i RA-226 LT. 3. LT.3. I E 01 LT.3. E 01 LT. 3. E 01 LT.2. E 01 LT.2. E 01 TH-228 LT.2. TRI11UM ANALYSIS: ! 9.4 1 0.3 E 03 9.3 i 0.3 E 03 5.9 i 0.2 E 03 6.3 i 0.3 E 03 H.3 9.2 i 0.3 E 03 f _ . _ _- _ . _ _ _ . - - . . . . . - - . _ . . . - - . ~ . - - . . . - _ _ - - _ . _ . - - . - _ _ _ _ _ _ _ _ - _ _ . - . - - - _ - _ _ . _ - - - _ - - _ _ _ _ _ - __.--- ----
---w. ---- - 4a_, :s ,,A,_ >e.m44_+--e-
---- - - - - - - - - - - - - - - - - - - - ' - - - - - - - - - ' - - - - - - - ' - - - - - ' - - - - - - ' - - ' - ' ' ' - - - - - - - - - - - - - " - - - - - - - - - - - - - - - - - r------- --- - - - - - - ' ' - - ----m-- ------T WOtX CREEE NUCEEAR OPERATING CORPORATION EXPOSURE PAlifWAY - INGES110N FISH (pCl/KG WET)
STATION NUMBER WCCL DC DATE CO11ECTED: 10/16 SM BUFFALO GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 K-40 3.0210.30 E 03 MN.54 LT. 1. E 01 CO-58 LT. 1. E 01 FE-59 LT.2. E 01 o CO-60 L T. 1. E 01 y ZN-65 LT.2. E 01 m NB-95/ZR-95 LT. 1. E 01 O RU-103 LT. 1. E 01
~
RU-106 LT. 1. E 02 I-131 LT. 1. E 01 CS-134 LT. 1. E 01 CS-137 LT. 1. E 01 LA-140/BA-140 LT. 1. E 01 CE-141 LT.2. E 01 CE-144 LT.7. E 01 RA-226 LT.2. E 02 TH-228 LT.2. E 01 TRIT 1UM ANALYSIS: H-3 6.2 i 0.2 E 03
1 WOlE CREEK NUCIEAR OPERATING CORPORATION EXPOSURE PA~niWAY - INGES110N FISH (pCl/KG WEll STA110N NUMBER WCCL - MAIN BODY DATE COLLECTED: 10/16 WIPER GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 K-40 3.4510.34 E 03 MN-54 LT. 1. E 01 I CO-58 LT. 1. E 01 o FE-59 LT.2. E 01 y CO-60 LT. 1. E 01 LT.3. E 01 m ZN-65 E3 NB-95/ZR 95 LT. 1. E 01
" LT. 1. E 01 RU-103 RU- 106 LT. 1. E 02 l-131 LT.2. E 01 CS-134 LT. 1. E 01 CS-137 LT.2. E 01 LA-140/BA-140 LT. I- E 01 ,
CE-141 LT. 2. E 01 . CE-144 LT.8. E 01 RA-226 LT.3. E 02 TH-228 LT.2. E 01 y TR111UM ANALYSIS: H-3 6.5 i 0.3 E 03 [
" WOfE CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PA111WAY - INGESTION FISH (pct /KG WET)
STA110N NUMBER WCCL - OUILET POOL 06/12 DATE COLLECTED: FLA111EAD CATT1Sil/ SM BUFFAID . GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 , K-40 3.1110.31 E 03 MN-54 LT. 1. E 01 y CO-58 LT. 1. E 01
$ FE-59 LT.3. E 01 CO-60 LT. 1. E 01 d, ZN-65 LT.3. E 01
" NB-95/ZR-95 LT. 1. E 01 RU-103 LT. 1. E 01 RU- 106 LT. 1. E 02 1-131 LT.3. E 01 CS-134 LT. 1. E 01 CS-137 LT. 1. E 01 LA-140/BA-140 LT.2. E 01 CE-141 LT. 2. E 01 CE-144 LT.9. E 01 RA-226 LT. 3. E 02 TH-228 LT. 2. E 01 TRIT 1UM ANALYSIS:
H-3 6.4 i 0.3 E 03
- WOIE CREEK NUCIEAR OPERATING CORPORATION !
EXPOSURE PAT 1tWAY - INGESTION FISH (pct /KG WET) , STATION NUMBER WCCL - SP l DATE COLLECIED: 10/16 BM BUFFAID . GAMMA SPECTRUM ANALYSIS: BE-7 LT.8. E 01 i K-40 3.2010.32 E 03 f MN-54 LT.8. E 00 CO-58 LT.G. E 00 FE-59 LT.2. E O1 y g CO-60 LT. 1. E 01 E 01
- ZN-65 LT.2.
E NB-95/ZR-95 LT.8. E 00
$RU-103 LT. 1. E 01 RU- 106 LT. 8. E 01 1-131 LT. 1. E 01 I
CS-134 LT.9. E 00 CS-137 LT. 1. E 01 1A-140/BA-140 LT.9. E 00 i CE-141 LT.2. E 01 i CE-144 LT.7. E 01 RA-226 LT.2. E 02 TH-228 LT. 2. E 01 t TRIT 1UM ANALYSIS: H-3 6.0 i 0.2 E 03 f
- - ~ - -_. .
WOlE CREEK NUCLEAR OPERAT1NG CORPORATION EXPOSURE PATTIWAY - INGESTION FOOD / GARDEN CROPS (PCI/KG WET) STAT 10N NUMBER G-1 06/25 07/30 08/27 08/27* DATE CO11ECIED: 05/28 CABBAGE BROCCOilLVS BROCCOll LVS CABBAGE CABBAGE GAMMA SPECIRUM ANALYSIS: LT. 1. E 02 4.3210.57 E 02 7.4610.75 E 02 7.40i0.86 E 02 BE-7 LT.8. E 01 2.8910 29 E 03 2.07i0.21 E 03 3.55t0.36 E 03 3.9710.40 E 03 K-40 4.5010.45 E 03 LT. 1. E 01 LT.7. E 00 LT. 1. E 01 LT. 1. E 01 MN-54 LT.9. E 00 E 01 LT.7. E 00 LT. 1. E 01 LT. 1. E 01 CO-58 LT.8. E 00 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. g FE-59 E 00 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 LT.9. E 00 LT.7.
$ CO-60 E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 cn ZN-65 LT.2. E 01 LT.2.
E 01 LT.7. E 00 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 LT. 1. h NB-95/ZR-95 E 00 LT. 1. E 01 LT. 7. E 00 LT. 1. E 01 LT. 1. E 01 RU-103 LT.9. E 01 LT.6. E 01 LT.9. E 01 LT.9. E 01 RU-106 LT.8. E 01 LT.9. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 1-131 L T. 1. E 01 LT.2. LT.7. E 00 L T. 1. E 01 LT. 1. E 01 LT.9. E 00 LT. 1. E 01 CS-134 E 01 LT. 1. E 01 LT. 1. E 01 LT.8. E 00 LT. 1. E 01 LT. 1. CS-137 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 LT. 1. E 01 1A-140/BA-140 E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. CE-141 E 01 LT.6. E 01 L T. 5. E 01 LT.6. E 01 LT.4. E 01 LT.7. CE-144 E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02 LT. 1. E 02 LT.2. RA-226 E 01 LT.2. E 01 4.1510.87 E 01 LT.2. E 01 LT. 1. E 01 LT.2. TH-228
- Duplicate Analysis
- WO1F CREEK NUCIZAR OPERATB40 CORPORATION EXPOSURE PATHWAY - INGESTION FOOD / GARDEN CROPS i
(PCI/KG WET STATION NUMBER R-1 DKIE COLIECTED: 06/25 CABBAGE GAMMA SPECIRUM ANALYSIS: BE-7 3.5910.72 E 02 K-40 4.7310.47 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 FE-59 LT. 2- E 01 2 CO-60 LT. 1. E 01
% ZN-65 LT.2. E 01 to NB-95/ZR-95 LT. 1. E 01 g RU-103 LT. 1. E 01 RU-106 LT.9. E 01 1-131 LT.2. E 01 CS-134 LT. 1. E 01 CS-137 - LT. 1. E 01 IA-140/BA-140 LT. 1. E 01 CE-141 LT. 1. E 01 CE-144 LT.5. E 01 RA-226 LT.2. E 02 TH-228 LT.2. E 01
WOIF CREEK NUC12AR OPERA 11NG CORPORA'ItON EXPOSURE PAMIWAY - INGES110N FOOD / GARDEN CROPS , (PCI/KG WE'Il STA~I1ON NUMBER S.4 DATE cot 1ECIED: 05/28 06/25 07/30 08/27 CABBAGE CABBAGE CABBAGE CABBAGE GAMMA SPECIRUM ANALYSIS: 1.8710.82 E 02 3.0410.96 E 02 5.6510.93 E 02 8.1710.86 E 02 BE.7 3.9010.39 E 03 4.2310.42 E 03 4.39iO.44 E 03 3.8410.38 5 03 K-40 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E Cl MN-54 LT. 1. E 01 LT.2. E 01 L T. 1. E 01 LT. 1. E 01 CO-58 LT.3. E 01 LT.4. E 01 LT.2. E 01 LT.2. E 01 m FE-59 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 L T. 1. E 01 f CO-60 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 2. E 01 m ZN.65 E 01 d, NB-95/ZR-95 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. , LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01
" RU-103 E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1.
RU-106 ' LT.2. E 01 LT.3. E 01 LT.2. E 01 LT. 1. E 01 I-131 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 l CS-134 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 CS-137 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LA-140/BA-140 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 CE-141 LT.8. E 01 LT. 1. E 02 LT.9. E 01 LT. 6. E 01 CE-144 LT.2. E 02 LT.2. E 02 LT. 3. E 02 LT.2. E 02 RA-226 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 . TH-228 s 1 t
I WOEF CREEK NUCIJtAR OPERA 11100 CORPORA 110N : EXPOSURE PATHWAY - INGESTION , MILK (PCI/ LITER) STKnON NUMBER S-3 i DATE COllECIED: 01/09 02/13 03/12 04/09 04/23 RADIOCHEMICAL ANALYSIS: E-01 LT.3. E-01 LT.2. E-01 LT.3. E-01 1-131 LT.2 E-01 LT.2. GAMMA SPECIRUM ANALYSIS: E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 BE-7 LT.3. 1.4010.14 E 03 1.1910.12 E 03 1.2710.13 E 03 1.36fo.14 E 03 1.40i0.14 E 03 K-40 E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3.~ E 00 y MN-54 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3.
$ CO-58 E 00 E 00 i cn FE-59 LT.7. E 00 LT.9. E 00 LT.9. E 00 LT.8. LT. 6.
E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00' LT.3. E 00 LT.3. h CO-60 E 00 LT. 1. E 01 LT.9. E 00 LT.7. E 00 ZN-65 LT.8. E 00 LT.9. LT.3 E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 NB-95/ZR.95 E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. RU-103 E 01 LT.3. E 01 LT.4. E 01 LT.4. E 01 LT.3. E 01 RU-106 LT. ' 3. LT.4. E 00 LT.5. E 00 LT.5. E 00 LT.5. E 00 LT.4. E 00 1-131 E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.3. E 00 CS-134 LT.3. E 00 LT.5. E 00 LT. 5. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.3. E 00 1A.140/BA-140 LT.4. E 00 LT.6. E 00 LT.7. E 00 LT.6. E 00 LT.6. E 00 CE-141 LT.5. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 CE-144 LT.2. E 01 LT.7. E 01 LT.9. E 01 LT.7. E 01 LT. 7. E 01 RA-226 LT.6. ' E 00 LT.8. E 00 LT.7. E 00 LT.6. E 00 ' TH-228 LT. 6. E 00 LT.6.
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WOlE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA'111WAY - INCES110N MILK (PCI/ LITER) STA110N NUMBER S-3 I DA'IE COLLECIED: 07/09' 07/23 08/13 08/27 09/10 RADIOCHEMICAL ANALYSIS: E-01 LT.2. E-01 LT.2. E-01 LT.2. E-01 LT.2. E-01 I-131 LT.4. GAMMA SPECTRUM ANALYSIS: , E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 l , BE-7 LT.3. 1.3710.14 E 03 1.4710.15 E 03 1.3310.13 E 03 1.1610.12 E 03 1.3010.13 E 03 s K-40 E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 2 MN.54 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 l
% CO-58 LT. 3.
E 00 LT.6. E 00 LT.7. E 00 LT. 1. E 01 LT.9. E 00 LT.9. ; 7 FE-59 E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 g CO-60 LT.4. LT.7. E 00 LT.8. E 00 LT.9. E 00 LT.9. E 00 LT.7. E 00 ZN-65 E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT. 3. E 00 NB-95/ZR-95 LT.3. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 RU-103 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 RU-106 LT.3. E 00 LT.2. E 01 LT.7. E 00 LT.7. E 00 LT.4. E 00 I-131 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 CS-134 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT.4. E 00 LT. 1. E 01 LT. 5. E 00 LT.6. E 00 LT.3. E 00 l IA-140/BA-140 LT.4. E 00 LT.8. E 00 LT.6. E 00 LT.5. E 00 i CE-141 LT. 5. E 00 LT.8. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 CE-144 LT.2. E 01 LT.7. E 01 LT.8. E 01 LT.7. E 01 LT.6. E 01 '[' RA-226 LT.6. LT. 6. E 00 LT.7. E 00 LT.7. E 00 LT.5. E 00 TH-228 LT. 5. E 00 ;
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WOtX CREEK NUCtJ.AR OPERATING CORPORATION EXPOSURE PA111WAY - INCEST 10N MILK iPCI/ LITER) STATION NUMBER S 3 DA'TE COLLECTED: 12/10 RADIOCHEMICAL ANALYSIS: 1-131 LT.3. E.01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 K-40 1.1910.12 E 03 MN-54 LT.3. E 00 LT.3. E 00 [mCO-58 LT.8. E 00 FE-59
? CO-60 LT.4. E 00
$ ZN-65 LT.9. E 00 NB-95/ZR-95 LT.3. E 00 RU-103 LT.3. E 00 RU-106 LT.3. E 01 1-131 LT.4. E 00 CS-134 LT.4. E 00 CS-137 LT.4. E 00 IA-140/BA-140 LT.4. E 00 CE-141 LT.6. E 00 CE-144 LT. 2. E 01 RA-226 LT.7. E 01 TH-228 LT.7. E 00 t
WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA'111WAY - AQUATIC SEDIMENT / SILT (pCl/KG DRY) STA~ DON NUMBER DC DATE COLLECIED: 05/01 10/25 GAMMA SPECTRUM ANALYSIS: ! BE-7 LT.3. E 02 LT.4. E 02 K-40 1.1910.12 E 04 1.2610.13 E 04 r MN-54 6.7412.58 E O1 8.0913.38 E O1 , CO-58 1.6810.29 E 02 1.0010.38 E 02 FE-59 LT.8. E 01 LT. 1. E 02 CO-60 1.2410.12 E 03 1.6010.16 E 03 I ZN-65 LT. 8. E 01 LT. 1. E O2 . g NB-95/ZR-95 LT.4. E 01 LT.5. E 01 RU-103 LT.4. E 01 LT.4. E 01 ! E RU-106 LT.3. E 02 LT.4. E 02
$ I-131 LT.8. E 01 LT.8. E 01 CS-134 LT. 5. E 01 LT.5. E 01 :
CS-137 4.8510.48 E 02 4.9110.49 E 02 ; LA-140/BA-140 LT. 5. E 01 LT.5. E 01 i CE-141 LT. 5. E 01 LT.6. E 01 i CE-144 LT. 2. E 02 LT.2. E 02 RA-226 2.2510.49 E 03 2.6910.58 E 03 i TH-228 9.9911.00 E 02 1.1310.11 E 03 1 _ - _ _ . - _._ - _ _ - _ _. __ _ . . _ . . . - _ . . J
WOIX CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PATHWAY - AQUATIC SEDIMENT / SILT (pCl/KG DRY) STA~I1ON NUMBER JRR 6 DATE COI.LECIED: 05/01 10/25 GAMMA SPECIRUM ANALYSIS: BE-7 LT.4. E 02 LT.3. E 02 K-40 1.5810.16 E 04 1.7810.18 E 04 MN-54 LT.4. E 01 LT.4. E 01 CO-58 LT.4. E O1 LT.4. E OI ! FE-59 LT.9. E 01 LT.8. E 01 CO-60 LT.4. E 01 LT.4. E 01 y ZN-65 LT. 1. E 02 LT. 1. E 02
$ NB-95/ZR-95 LT.5. E 01 LT.4. E 01
- RU-103 LT.5. E 01 LT.4. E 01 7 RU-106 LT.4. E O2 LT.3. E 02 I -131 I LT. 1. E 02 LT.8. E 01 I CS-134 LT. 5. E 01 LT.4. E 01 <
CS-137 1.8610.45 E 02 2.3910.38 E 02 l IA-140/BA-140 LT. 1. E 02 LT.5. E 01 l CE-141 LT. 8.~ E 01 LT.6. E 01 CE-144 LT. 3. E 02 LT.2. E 02 RA-226 1.9510.75 E 03 2.1510.53 E 03 TH-228 1.5310.15 E 03 1.2910.13 E 03 F 4 4 l
WOLF CREEK NUCIE.AR OPERATING CORPORA 110N EXPOSURE PAT 11WAY - AQUAllC SEDIMENT / SILT (pCI/KG DRY) STATION NUMBER llc & lith Rd DATE COLLECTED: 05/24 10/23 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 LT.2. E 02 K-40 1.0310.10 E 04 1.1910.12 E 04 MN-54 LT.3. E 01 LT.2. E 01 CO-58 LT.3. E 01 LT.2. E 01 FE-59 LT.7. E 01 LT.5. E 01 CO-60 LT.3. E 01 LT 2. E 01 ZN-65 LT.7. E 01 LT.7. E 01 LT. 5. E 01 LT.3. E 01 [ NB-95/ZR-95
- RU-103 LT. 4. E 01 LT.3. E 01 i
? RU-106 LT.3. E 02 LT.2. E 02
$ I-131 LT.8. E 01 LT.5. E 01 !
CS-134 LT.4. E 01 LT. 3. E 01 CS-137 LT.4. E 01 4.8812.30 E 01 LA-140/BA-140 LT.7. E 01 LT.3. E 01 CE-141 LT.7. E 01 LT.5. E 01 CE-144 LT.2. E 02 LT.2. E 02 RA-226 2.1410.59 E 03 2.2210.46 E 03 TH-228 9.7810SS E 02 1.0110.10 E 03 , i i i
WOIE CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PA111WAY - WATERBORNE SHORELINE SOIL [pCl/KG DRY) STATION NUMBER DC DATE COLLECIED: 05/01 10/25 GAMMA SPECTRUM ANALYSIS: BE-7 4.6012.60 E 02 LT.3. E 02 K-40 1.0310.10 E 04 9.0310.90 E 03 ' MN-54 LT.4. E 01 LT.4. E 01 CO-58 2.6310.36 E 02 LT.4. E 01 , FE-59 LT.8. E 01 LT.8. E 01 CO-60 2.5810.34 E 02 8.2213.16 E O1 m ZN-65 LT.7. E 01 LT.9. E 01 i $ NB-95/ZR-95 LT.4. E 01 LT.4. E 01 RU-103 LT.4. E 01 LT. 4. E 01 i RU-106 LT.3. E 02 LT. 3. E 02
- I-131 LT.9. E 01 LT.8. E 01 CS-134 LT.4. E 01 LT.4. E 01 CS-137 1.6110.26 E 02 LT.4. E 01 IA-140/BA-140 LT. 6. E 01 LT. 5. E 01 CE-141 LT.6. E 01 LT. 6. E 01 CE-144 LT.2. E 02 LT.2. E 02 RA-226 1.4710.48 E 03 1.2310.55 E 03 TH-228 1.0110.10 E 03 8.3110.83 E 02 4
+
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WOLF CREEK NUCIJCAR OPERATING CORPORATION EXPOSURE PATHWAY - WATERBORNE SHORELINE SOIL (pCl/KG DRY) , STATION NUMBER EEA DATE COLLECIED: 06/25 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 K-40 1.0310.10 E 04 MN-54 LT.4. E 01 CO-58 LT.3. E 01 FE-59 LT.8. E 01 CO-60 LT.4. E 01 y ZN-65 LT.9. E 01
$ NB-95/ZR-95 LT.4. E 01 RU-103 LT.4. E 01 g RU-106 LT.3. E 02 N I-131 LT. 6. E 01 CS-134 LT. 5. E 01 CS-137 LT.4. E 01 LA-140/BA-140 LT. 5. E 01 CE-141 LT.7. E 01 CE-144 LT. 3. E 02 RA-226 1.8110.62 E 03 TH-228 1.1410.11 E 03 i
WOIX CREEK NUCIE.AR OPERATING CORPORAT10N EXPOSURE PAT 11WAY - WATERBORNE SIIORELINE SOIL (pCl/KG DRY) STA110N NUMBER JRR DATE COLLECIED: 05/01 10/25 CAMMA SPECI' RUM ANALYSIS: BE-7 LT.3. E 02 LT.3. E 02 K-40 6.3010.63 E 03' l.1910.12 E 04 MN-54 LT.3. E 01 LT.3. E 01 CO-58 LT. 3. E 01 LT.2. E 01 FE-59 LT.5. E 01 LT. 5. E 01 CO-60 LT.3. E 01 LT.2. E 01 y ZN-65 LT. 6. E 01 LT.5. E 01
$* NB-95/ZR-95 LT.4. E 01 LT.3. E 01 RU-103 LT.3. E 01 LT.3. E 01 7 RU-106 LT. 2. E O2 LT.2. E 02
$ I-131 LT. 8. E 01 LT.6. E 01 CS-134 LT.4. E 01 LT.3. E 01 CS-137 LT.3. E 01 LT.3. E 01 LA-140/BA-140 LT.6. E 01 LT.4. E 01 CE-141 LT.6. E 01 LT. 5. E 01 CE-144 LT.2. E 02 LT.2. E 02 RA-226 2.9910.49 E 03 2.0710.40 E 03 TH-228 1.3510.14 E 03 1.4010.14 E 03
WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA111WAY - AQUATIC SHORELINE SOIL (pct /KG DRY) STKnON NUMBER MUDS DATE COILECTED: 05/08 10/28 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 LT.3. E 02 K-40 1.1610.12 E 04 1.0310.10 E 04 MN-54 LT.4. E 01 LT.4. E 01 . CO-58 LT.4. E 01 LT.4. E 01 FE-59 LT.8. E 01 LT.8. E 01 CO-60 LT.4. E 01 LT.4. E 01 u ZN-65 LT. 1. E 02 LT.9. E 01 y NB-95/ZR-95 LT. 5. E 01 LT.5. E 01 m RU-103 LT.4. E 01 LT.4. E 01 1, RU-106 LT.4. E 02 LT.3. E 02
- l-131 LT.6. E 01 LT.7. E 01 CS-134 LT.5. E 01 LT.5. E 01 CS-137 1.4310.41 E 02 LT.4. E O1 LA-140/BA-140 LT.5. E 01 LT. 6. E 01 CE-141 LT.6. E 01 LT.7. E 01 ,
CE-144 LT.3. E 02 LT. 3. E 02 RA-226 2.2610.66 E 03 2.8510.69 E 03 TH-228 1.2110.12 E 03 1.3410.13 E 03 b
WOLF CREEK NUCIJtAR OPERATING CORPORATION EXPOSURE PATHWAY 'IERRESTRIAL SOIL (pCl/KG DRY) , STAllON NUMBER EEA DA'IE COLLECIED: 06/19 10/28 GAMMA SPECTRUM ANALYSIS: , BE-7 LT.5. E 02 LT.4. E 02 K-40 1.0310.10 E 04 1.2210.12 E 04 ' MN-54 LT.4. E 01 LT.4. E 01 CO-58 LT.4. E 01 LT.3. E 01 FE-59 LT. 1. E 02 LT.9. E 01 ! CO-60 LT. 4. E 01 LT.4. E 01 y ZN-65 LT. 1. E 02 LT. 1. E 02 ; $ NB-95/ZR-95 LT. 5. E 01 LT.5. E 01 RU-103 LT. 5. E 01 LT.5. E 01 RU-106 LT.3. E 02 LT.4. E 02 : O I-131 LT. 1. E 02 LT.7. E 01 CS-134 LT.5. E 01 LT.6. E 01 i CS-137 1.6410.37 E 02 2.0910.47 E 02 1A-140/BA-140 LT.8. E 01 LT.6. E 01 CE-141 LT.7. E 01 LT.7. E 01
- CE-144 LT.3. E 02 LT.3. E 02 &
RA-226 2.2710.71 E 03 2.4510.79 E 03 TH-228 1.0710.11 E 03 1.4010.14 E 03
-~, - ,- - . . _ _ - - _ _ _ _ _ _ - _ _ _ - -
1 WOIX CREEK NUCI2AR OPERATING CORPORAT10N EXPOSURE PA111WAY "IERRESTRIAL , SOIL (pCl/KG DRY) ' STA~IlON NUMBER MUDS l DATE COLLECTED: 06/19 10/28 GAMMA SPECTRUM ANALYSIS: BE-7 1.1610.26 E 03 LT.4. E 02 i K-40 1.2810.13 E 04 1.2310.12 E 04 MN-54 LT.3. E 01 LT.5. E 01 CO-58 LT.3. E 01 LT 4. E 01 FE-59 LT.7. E 01 LT. 1. E 02 CO-60 LT.3. E 01 LT. 5. E 01 ZN-65 LT.7. E 01 LT. 1. E 02 LT.4. E 01 LT.5. E 01 [NB-95/ZR-95 S RU- 103 LT.3. E 01 LT. 5. E 01 TRU-106 LT.3. E 02 LT.4. E 02 D-131 LT.8. E 01 LT.8. E 01 ; CS-134 LT.4. E 01 LT.5. E 01 CS-137 LT.4. E 01 4.4210.58 E 02 LA-140/BA-140 LT.6. E 01 LT.7. E 01 CE-141 LT.5. E 01 LT.7. E 01 CE-144 LT. 2. E 02 LT.3. E 02 j RA-226 1.2710.48 E 03 2.0010.74 E 03 TH-228 8.70iO.87 E 02 1.4010.14 E 03 I L L I t . _ . _ . _ _ _ _ _ . . _ _ _ . _ _ _ . . _ _ _ _ _ _ . _ _ _ _ . _ _ _ _ _ _ _ _ . _ _ . _ _ _ _ _ _ _ _ _ _ . _ . _ _ . _ _ _ . _ _ . _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ . _ _ . _ _ _ _ _ _ _ _ _ . _ _ _ _ _--m- -- .. _- . _ -
WOtX CREEK NUCIEAR OPERATING CORPORATION EXPOSURE PAT 11WAY - AQUAT1C VECETATION - AQUA ~I1C (pCl/KG WET) STATION NUMBER DC DATE COllECIED: 05/01 AIEAE GAMMA SPECIRUM ANALYSIS: BE-7 4.3410.56 E 02 K-40 2.6610.27 E 03 MN-54 8.0110.80 E 01 CO-58 8.5710.86 E 02 FE-59 1.4010.15 E 02 CO-60 5.2710.53 E 02 2 ZN-65 LT.2. E 01 EO NB-95/ZR-95 6.4110.97 E 01
? RU-103 LT.9. E 00
$ RU-106 LT.7. E 01 I-131 LT.2. E O1 CS-134 2.4510.56 E O1 CS-137 5.82 0.58 E 01 LA-140/BA-140 LT. 1. E 01 CE-141 LT. 1. E 01 CE-144 LT.4. E 01 RA-226 6.7010.95 E 02 TH-228 2.8210.28 E 02 CR-51 2.4010.52 E 02 SB-125 1.3110.14 E 02 NB-95 1.4510.15 E 02
A WOtX CREEK NUCIZAR OPERATING CORPORATION EXPOSURE PAT 11WAY "IERRESTRIAL VEGETATION "IERRESTRIAL (pCl/KG WET) STATION NUMBER EEA DATE COLLEC'IED: 06/19 10/28 PASTURACE PASTURAGE GAMMA SPECTRUM ANALYSIS: BE-7 2.8510.28 E 03 3.4910.35 E 03 K-40 3.5510.36 E 03 4.4310.44 E 03 MN-54 LT.3. E 01 LT.3. E 01 CO-58 LT.2. E 01 LT.2. E 01 FE-59 LT. 6. E 01 LT.5. E 01 CO-60 LT. 2. E 01 LT.3. E 01 2 ZN-65 LT. 5. E 01 LT.6. E 01 E NB-95/ZR-95 LT.3. E 01 LT. 3. E 01 y RU-103 LT.3. E 01 LT.3. E 01
$ RU-106 LT. 2. E 02 LT.3. E 02 I-131 LT. 7. E 01 LT.4. E 01 ,
CS-134 LT.3. E 01 LT.3. E 01 CS-137 LT. 3. E 01 LT.3. E 01 LA-140/BA-140 LT.4. E 01 LT.3. E 01 CE-141 LT.4. E 01 LT.4. E 01 CE-144 LT.2. E 02 LT.2. E 02 RA-226 LT.5. E 02 LT.5. E 02 TH-228 LT.4. E 01 LT.5. E 01 1 I
WOIX CREEK NUCLEAR OPERATING CORPORAT10N EXPOSURE Pall {WAY 'IERRESTRIAL VEGETA110N 'IERRESTRIAL (pC1/KG WET STATION NUMBER MUDS DATE COLLECIED: 06/19 10/28 PASTURAGE PAS 113 RAGE GAMMA SPECTRUM ANALYSIS: , e BE-7 2.3610.24 E 03 4.1310.41 E 03 K-40 5.1210.51 E 03 2.5510.38 E 03 MN-54 LT.2. E 01 LT.4. E 01 CO-58 LT.2. E 01 LT.4. E 01 FE-59 LT.5. E 01 LT.8. E 01 CO-60 LT.2. E 01 LT.4. E 01 u ZN-65 LT.5. E 01 LT.9. E 01 4 I h NB-95/ZR-95 LT.2. E 01 LT.4. E 01 m RU-103 LT.3. E 01 LT.4. E 01 LT.2. E 02 LT.3. E 02 h RU-106 I-131 LT.6. E 01 LT.7. E 01 CS-134 LT.2. E 01 LT.4. F 01 CS-137 LT.2. E 01 LT.4. E 01 IA-140/BA-140 LT.4. E 01 LT.5. E 01 CE-141 LT.4. E 01 LT.6. E 01 CE-144 LT. 1. E 02 LT.2. E 02 RA-226 LT.4. E 02 LT.7. E 02 TH-228 LT.3. E 01 LT.7. E 01
WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PATHWAY - WATERBORNE DRINKING WATER 4 (PCI/LTI'ER) STKI1ON NUMBER BW15 DATE COLLECTED: 01/03-02/06 02/06-03/05 03/05-03/19 04/02 04/02-05/08
. RADIOCHEMICAL ANALYSIS:
GR-B 9.7 i 1.6 E 00 8.7 i 1.5 E 00 8.1 1 2.1 E 00 7.9 i 1.5 E 00 8.1 i 1.5 E 00 I-131 LT.6. E-01 LT.5. E-01 LT.7. E-01 LT. 3. E-01 LT. 2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 3. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 K-40 LT.9. E 01 LT.7. E 01 LT.6. E 01 LT. 1. E 02 LT. 1. E 02
- MN-54 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00
, CO-58 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 $ FE-59 LT. 7. E 00 LT. 7. E 00 LT. 8. E 00 LT.8. E 00 LT. 8. E 00 CO-6; LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 & ZN-65 LT.7. E 00 LT.7. E 00 LT.7. E 00 LT.7. E 00 LT.8. E 00
- NB.95/ZR-95 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4.
E 00 LT.4. E 00 RU-103 LT.3. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 1-131 LT.4. E 00 LT. 5. E 00 LT.2. E 01 LT. 5. E 00 LT.5. E 00 CS-134 LT.3 E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT. 3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.9. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.5. E 00 LT.8. E 00 LT. 1. E 01 LT.5. E 00 LT.6. E 00 CE-144 LT.2. E 01 LT.3. E 01 LT.4. E 01 LT.2. E 01 LT.3. E 01 RA-226 LT.6. E 01 LT. 1. E 02 LT. 1. E 02 LT.7. E 01 LT.7. E 01 Til-228 LT.5. E 00 LT.8. E 00 LT.8. E 00 LT.7. E 00 LT.6. E 00 TRTI1UM ANALYSIS: 01/03 04/02 11-3 LT.2. E 02
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WOtX CREEK NUCLEAR OPERA 11NG CORPORA 110N EXPOSURE PATHWAY - WATERBORNE DRINKING WATER (PCI/ LITER) . STA110N NUMBER BW15 DATE COLLECTED: 05/08-06/04 06/04-07/03 06/04-07/03* 07/03-08/06 08/06-09/03 RADIOCHEMICAL ANALYSIS: GR-B 6.2 i 1.3 E 00 6.1 i 1.8 E 00 5.1 i 1.8 E 00 6.3 i 1.4 E 00 6.8 i 1.3 E 00 1 131 LT.2. E-01 LT.6. E-01 LT. 5. E-01 LT.2. E-01 LT.3. E-01 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT. 3. E 01 LT. 3. E 01 LT. 3. E 01 K-4 0 LT.8. E 01 LT.6. E 01 LT. 7. E 01 LT. 5. E 01 LT.9. E 01 MN-54 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 LT.3. E 00 y CO-58 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 LT.3. E 00 I y FE-59 LT.6. E 00 LT. 8. E 00 LT.6. E 00 LT.6. E 00 LT. 7. E 00 cn CO-60 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 h ZN-65 LT. 6. E 00 LT.7. E 00 LT.6. E 00 LT.6. E 00 LT.8. E 00 NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT.3. E 00 RU-103 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT. 3. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 1-131 LT.4. E 00 LT.8. E 00 LT.6. E 00 LT.4. E 00 LT.5. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT.4. E 00 i CS-137 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT.4. E 00 LA-140/BA-140 LT.3. E 00 LT.6. E 00 LT. 5. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.4. E 00 LT.6. E 00 LT. 5. E 00 LT.5. E 00 LT.5. E 00 CE-144 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 , RA-226 LT. 6. E 01 LT. 7. E 01 LT.6. E 01 LT. 6. E 01 LT. 7. E 01 . TH-228 LT. 5. E 00 LT.6. E 00 LT. 5. E 00 LT.6. E 00 LT.6. E 00 TRTI1UM ANALYSIS: 04/02-07/03 07/03-10/01 H-3 LT.2. E O2 LT.2. E 02
- Duplicate Analysis i
I WOtX CREEE NUCLEAR OPERATING CORPORAT10N EXPOSURE PKIHWAY - WKIERBORNE , i DRINKING WATER (PCI/ LITER) - STA110N NUMBER BW15 DATE COLLECTED: 09/03-10/01 10/0l-11/05 11/05-12/04 12/04-01/06 < i RADIOCHEMICAL ANALYSIS: GR-B 6.2 i 1.3 E 00 8.2 i 1.4 E 00 7.5 i 1.3 E 00 - 7.1 1 1.5 E 00 i 1-131 E-01 E 00 E-01 E-01 LT.6. LT. 1. LT.7. LT.6. GAMMA SPECIRUM ANALYSIS: ; BE-7 LT.4. E 01 LT. 3. E 01 LT.3. E 01 LT.' 4. E 01 K-40 L T. 1. E 02 LT. 6. E 01 LT.5. E 01 LT. 1. E 02 MN-54 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 o CO-58 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 . f FE-59 LT.9. E 00 LT.6. E 00 LT.5. E 00 LT. 1. E 01
; m CO-60 LT.4. E 00. LT. 3. E 00 LT.3. E 00 LT.4. E 00 E ZN.65 LT. 1. E O1 LT. 7. E 00 LT. 6. E 00 LT.9. E 00
" NB-95/ZR-95 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.5. E 00 RU-103 LT. 5. E 00 LT. 4. E 00 LT.3. E 00 LT.5. E 00 RU-106 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT.4. E 01 !
l I-131 LT. 6. E 00 LT. 5. E 00 LT. 5. E 00 LT. 1. E 01 I CS-134 LT. 5. E 00 LT.4. E 00 LT.3. E 00 LT.5. E 00 - CS-137 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT 5. E 00 IA-140/BA-140 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.8. E 00 CE-141 LT. 7. E 00 LT.8. E 00 LT.6. E 00 LT.8. E 00 CE-144 LT. 3. E 01 LT.3. E 01 LT.2. E 01 LT. 3. E 01 RA-226 E 02 LT.8. E 01 LT. 1. LT. 7. E 01 LT 9. 2 01 i TH-228 LT. 7. E 00 LT.8. E 00 LT.6. E 00 LT.8. E 00 ! TRTI1UM AFALYSIS: 10/01-01/06 j H-3 LT. 1. E 02 ,
-5
WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PA'niWAY - WATERBORNE DRINKING WATER (PCI/ LITER) STATION NUMBER LW40 DA'IE COllICIED: 01/03-02/06 02/06-03/05 03/05-04/02 04/02-05/08 05/08-06/04 RADIOCHEMICAL ANALYSIS: GR-B 8.5 i 1.6 E 00 7.1 i 1.5 E 00 7.2 1 1.5 E 00 7.9 i 1.6 E 00 6.6 i 1.4 E 00 I-13 LT.6. E-Ol LT.5. E-01 LT.3. E-01 LT. 3. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 2. E 01 K-40 LT.4. E 01 LT.5. E 01 LT.6. E 01 LT.5. E 01 LT.4. E 01 y MN-54 LT.2. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 LT.2. E 00 y CO-58 LT.2. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT. 2. E 00 m FE-59 LT.4. E 00 LT.7. E 00 LT.6. E 00 LT. 7. E 00 LT.4. E 00 b CO-60 LT.2. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.2. E 00 ZN-65 LT. 5. E 00 LT.7. E 00 LT.7. E 00 LT. 6. E 00 LT.5. E 00 NB-95/ZR-95 LT. 2. E 00 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.2. E 00 RU-103 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.2. E 00 RU-106 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 1-131 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.6. E 00 LT.3. E 00 CS-134 LT.2. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.2. E 00 CS-137 LT.2. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 IA-140/BA-140 LT. 3. E 00 LT. 4. E 00 LT.5. E 00 LT. 5. E 00 LT. 3. E 00 CE-141 LT.5. E 00 LT.7. E 00 LT. 7. E 00 LT. 7. E 00 LT.4. E 00 CE-144 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 LT. 2. E 01 RA-226 LT. 5. E 01 LT.8. E 01 LT.8. E 01 LT. 8. E 01 LT. 5. E 01 TH-228 LT. 5. E 00 LT.7. E 00 LT.7. E 00 LT.7. E 00 LT.4. E 00 TRITIUM ANALYSIS: 01/03-04/02 H-3 LT.2. E 02 i
WOIX CREEE NUC12AR OPERATING CORPORATION EXPOSURE PA111WAY - WA'IERBORNE DRINKING WATER (PCI/ LITER) STA110N NUMBER LW40 . DATE COLLECTED: 06/04-07/03 07/03-08/06 08/06-09/03 09/03-10/01 10/I8 RADIOCHEMICAL ANALYSIS: GR-B 6.9 i 1.9 E 00 6.1 i 1.3 E 00 6.6 i 1.2 E 00 6.9 i 1.3 E 00 7.5 i 1.4 E 00 1-131 LT.3. E-01 LT.2. E.01 LT.3. E-01 LT.5. E-01 LT.3. E-01 GAMMA SPECTRUM ANALYSIS: . I BE-7 LT. 3. E 01 LT.2. E O1 LT.3. E O1 LT.3. E O1 LT. 3. E 01 K-40 LT.7. E 01 LT.4. E 01 LT.5. E 01 LT.9. E 01 LT.8. E 01 2 MN.54 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.4. E 00 LT.3. E 00 ' S CO-58 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.3. E 00 LT. 3. E 00 . LT.6. E 00 LT.5. E 00 LT.5. E 00 LT.7. E 00 LT.7. E 00 7 FE-59 E 00
$ CO-60 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.4. E 00 LT. 3.
ZN-65 LT.7. E 00 LT.6. E 00 LT.5. E 00 LT.8. E 00 LT.6. E 00 NB-95/ZR-95 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU-103 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT. 4. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.3. E 01 LT.3. E 01 I-131 LT.6. E 00 LT.4. E 00 LT. 4. E 00 LT.4. E 00 LT.8. E 00 CS-134 LT. 3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LA-140/BA-140 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT. 6. E 00 CE-141 LT.5. E 00 LT.5. E 00 LT.5. E 00 LT. 5. E 00 LT.6. E 00 CE-144 LT.2. E O1 LT.2. E 01 LT.2. E O1 LT.2. E G1 LT.2. E 01 RA-226 LT.6. E 01 LT.6. E 01 LT.7. E 01 LT.7. E 01 LT. 6. E 01 TH-228 LT.6. E 00 LT. 5. E 00 LT.6. E 00 LT. 6. E 00 LT.5. E 00 TRITIUM ANALYSIS: 04/02-07/03 07/03-10/01 H.3 LT.2. E 02 LT.2. E 02
- - - - - -- _ _ _ _ .________m__.__.. __ _ ___ _ _ ______ _ _ _ ___ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ , _ _____ _ _ _ _ ___ _ _ _ _ __ _ _
- m. __ .. _ . . . . _ . .
_ _ . _ - . . _ - - . . . . . . ~ . . _ . . _ . . . = __ ...m . _ WOlE CREEK NUCIJtAR OPERATING CORPORATION EXPOSURE PATHWAY - WATERBORNE DRINKING WATER (PCI/ LITER) STATION NUMBER LW40 DATE COLLECIED: 10/18-11/05 11/05-12/04 12/04-01/06 RADIOCHEMICAL ANALYSIS: G R-B 5.1 1 2.0 E 00 6.6 i 1.2 E 00 9.9 i 1.6 E 00 I-131 LT.9. E-O1 LT.7. E-01 LT. 6. E-01 GAMMA SPECTRUM ANALYSIS: i BE-7 LT.3. E 01 LT.2. E 01 LT.3. E 01 K-4 0 LT.5. E 01 LT.4. E 01 LT. 5. E 01 y MN-54 LT.3. E 00 LT.2. E 00 LT. 3. E 00
$ CO-58 LT. 3. E 00 LT.3. E 00 LT.3. E 00 p FE-59 LT.6. E 00 LT.5. E 00 LT. 5. E 00 g CO-60 LT. 3. E 00 LT.3. E 00 LT. 3. E 00 ZN-65 LT.6. E 00 LT.6. E 00 LT.6. E 00 NB-95/ZR-95 LT.3. E 00 LT.3. E 00 LT. 3. E 00 RU-103 LT.4. E 00 LT.3. E 00 LT. 3. E 00 RU-106 LT.3. E 01 LT.2. E 01 LT. 2. E 01 I-131 LT.4. E 00 LT.4. E 00 LT.6. E 00 CS-134 LT.3. E 00 LT. 3. E 00 LT. 3. E 00 CS-137 LT.4. E 00 LT. 3. E 00 LT.4. E 00 IA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.4. E 00 j CE-141 LT.7. E 00 LT.4. E 00 LT. 5. E 00 CE-144 LT.3. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT.8. E 01 LT. 5. E 01 LT.6. E 01 TH-228 LT.7. E 00 LT.5. E 00 LT. 5. E 00 TRI11UM ANALYSIS: 10/18-01/06 i H-3 LT. 1. E 02 s
f WOtX CREEE NUCUuut OPERATING CORPORATION , EXPOSURE PATHWAY - WATERBORNE CROUND WATER l (PCI/ LITER) l STA110N NUMBER B.12 DATE COLIECIED: 02/20 05/21 08/22 11/27 RADIOCHEMICAL ANALYSIS: , I-131 LT. 1. E-01 LT. 3. E.01 LT. 2. E-01 LT. 3. E-01 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E O1 LT.3. E O1 LT. 3. E O1 LT.3. E O1 K-40 LT.6. E 01 LT. 1. E 02 LT.6. E 01 LT.5. E 01 MN.54 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 [*CO-58 E 00 E 00 FE-59 LT.7. E 00 LT.8. E 00 LT.7. LT.6. I CO-60 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00
$ ZN-65 LT.7. E 00 LT.8. E 00 LT.7. E 00 LT.7. E 00 NB-95/ZR-95 LT. 3. E 00 ' LT. 4. E 00 LT. 3. E 00 LT.3. E 00
< RU-103 LT. 3. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 ; RU-106 LT. 3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 1-131 LT.4. E 00 LT.5. E 00 LT. 6. E 00 LT.5. E 00 , CS-134 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 - CS-137 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 '! LA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 CE-141 LT.5. E 00 LT.5. E 00 LT.6. E 00 LT. 6. E 00 CE-144 LT.2. E 01 LT.2. E 01 LT.3. E 01 LT. 2. E 01 RA-226 LT.7. E 01 LT.7. E 01 LT.8. E 01- LT.7. E 01 TH-228 LT.6. E 00 LT.6. E 00 LT.6. . E 00 LT.6. E 00
@ LUM ANALYSIS:
H-3 LT.2. E 02 LT. 1. E 02 LT 2. E 02 LT.2. E 02
WOIX CREEK NUCLEAR OPERATING CORPORA 110N EXPOSURE PAT 11WAY - WATERBORNE GROUND WATER (PCI/ LITER) STAT 10N NUMBER C-10 DATE COLLECIED: 02/20 05/21 08/22 12/10 RADIOCHEMICAL ANALYSIS: 1-131 LT.2. E-01 LT.2. E-Ol LT. 2. E.01 LT. 1. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E O1 LT.3. E 01 K-40 LT.9. E 01 LT.6. E 01 LT.6. E 01 LT.9. E 01 MN-54 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 CO-58 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E 00 y FE-59 LT.7. E 00 LT.7. E 00 LT.7. E 00 LT.7. E 00 $ CO-60 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 ZN-65 LT.8. E 00 LT.7. E 00 LT.7. E 00 LT.8. E 00 g NB-95/ZR-95 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 f' N RU-103 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 RU-lO6 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 l I-131 LT.5. E 00 LT.4. E 00 LT.6. E 00 LT.5. E 00 I CS-134 LT.4. E 00 LT. 3. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT.4. E 00 LT.5. E 00 LT.6. E 00 LT.4. E 00 CE-141 LT. 6. E 00 LT.6. E 00 LT.8. E 00 LT.5. E 00 CE-144 LT. 2. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.8. E 01 LT. 1. E 02 LT.7. E 01 Til-228 LT. 6. E 00 LT. 7. E 00 LT.8. E 00 LT.6. E 00 TRIT 1UM ANALYSIS: H-3 LT.2. E 02 LT. 1. E 02 LT. 2. E 02 LT.2. E O2 _. - .__ _ _ _ - _ _ _-_-__ _ _ -__. _ - __-_____- - . - . - - - - , = , - .
wols CREEE NUCLEAR OPERAMNG CORPORAMON EXPOSURE PKIIIWAY - WATERBORNE GROUND WA'IER (PCI/ LITER) STKnON NUMBER C-49 DATE COILEC'IED: 02/20 05/21 08/22 11/27 RADIOCHEMICAL ANALYSIS: 1-131 LT.2. E-01 LT.2. E-01 LT.2. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 3. E 01 LT.3. E O1 LT.3. E 01 LT. 2. E O1 K-40 LT.8. E 01 LT.5. E 01 LT.9. E 01 LT.4. E 01 MN.54 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E 00 y CO-58 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 g FE-59 LT. 6. E 00 LT.6. E 00 LT.7. E 00 LT.6. E 00 m CO-60 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00
!:n ZN-65 LT.8. E 00 LT.6. E 00 LT.7. E 00 LT.6. E 00 NB-95/ZR-95 LT.4. E 00 LT.4. E 00 L.T. 4. E 00 LT.3. E 00 RU-103 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 2. - E 01 1-131 LT.5. E 00 LT.4. E 00 LT.5. E 00 LT.5. E 00 CS-134 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 LA.140/BA-140 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.5. E 00 CE-141 LT. 5. E 00 LT.6. E 00 LT.6. E 00 LT.4. E 00 CE-144 LT.2. E 01 LT. 3. E 01 LT.2. E 01 LT. 2. E 01 RA-226 LT.7. E 01 LT.7. E 01 LT.7. E 01 LT.5. E 01 TH-228 LT.6. E 00 LT. 7. E 00 LT.6. E 00 LT. 5. E 00 TRrnUM ANALYSIS:
H-3 LT. 2. E 02 LT. 1. E 02 LT.2. E 02 LT.2. E 02 _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ ___ _ _____ ____ _ _ _ _ _ . _ _ _ _ _ . _ _ ~.
WOIX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PAT 11WAY - WATERBORNE GROUND WATER (PCI/IIIER) STAT 10N NUMBER D-65 DATE COLLECIED: 02/20 05/21 08/22 11/27 RADIOCHEMICAL ANALYSIS: I-131 LT.2. E-01 LT.2. E-01 LT.2. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 K-40 LT. 5. E 01 LT.4. E 01 LT.5. E 01 LT.5. E 01 MN-54 LT. 3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 l
,o CO-58 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 $ FE-59 LT.6. E 00 LT. 5. E 00 LT.6. E 00 LT.5. E 00 ;
a, CO-60 LT.3. E CO LT.3. E 00 LT.3. E 00 LT.3. E 00 ' LT. 7. E 00 LT. 6. E 00 LT.7. E 00 LT.6. E 00 e[n ZN-65 NB-95/ZR-95 LT.3. E 00 LT. 3. . E 00 LT.3. E 00 LT.3. E 00 RU- 103 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 ! RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 ! I-131 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.5. E OO CS-134 LT.3. E OO LT.3. E 00 LT.3. E 00 LT.3. E OO CS-137 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT. 4. E 00 IA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT. 6. E 00 LT.6. E 00 LT.5. E 00 CE-144 LT. 3. E 01 LT.2. E 01 LT. 2. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.7. E 01 LT.7. E 01 LT.6. E 01 TH-228 LT.7. E 00 LT. 6. E 00 LT.6. E 00 LT.5. E 00 TRI'l1UM ANALYSIS: H-3 LT.2. E 02 - LT. 1. E 02 LT.2. E 02 LT.2. E 02
t WOIE CREEK NUC12AR OPERATING CORPORATION EXPOSURE Pall {WAY - WATERBORNE GROUND WA'IER ; i (PCI/L11ER) srATION NUMBER L-49 DATE COLIECIED: 02/20 05/21 08/22 11/27 11/27* j RADIOCHEMICAL ANALYSIS: 1-131 LT.2. E-01 LT. 3. E-01 LT.2. E LT.3. E-01 LT. 3. E-01 GAMMA SPECTRUM ANALYSIS: i BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT. 3. E 01 K-4 0 LT.8. E 01 LT. 6. E 01 LT.7. E 01 LT. 1. E 02 LT.9. E 01 , MN.54 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT. 5. E 00 LT. 3. E 00 '
,o CO-58 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.5. E 00 LT.4. E 00 l
g FE-59 LT.6. E 00 LT.7. E 00 LT.7. E 00 LT. 1. E 01 LT.8. E 00 E 00 E 00 E 00 i m CO-60 LT.3. E 00 LT.4. E 00 LT.3. LT.5. LT.4. E ZN-65 LT.9. E 00 LT.8. E 00 LT.7. E 00 LT. 1. E 01 LT.8. E 00 , NB-95/ZR-95 LT.4. T 00 LT. 5. E 00 LT.3. E 00 LT. 5. E 00 L.T. 4. E 00 RU-103 L T. 3. E 00 LT.4. E 00 LT.3. E 00 LT 5. E 00 LT.4. E 00 RU-106 LT. 0. E 01 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 I-131 LT.4. E 00 LT. 5. E 00 LT.5. E 00 LT.8. E 00 LT.6. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT. 5. E 00 LT.4. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT. 5. E 00 LT.4. E 00 LA-140/BA-140 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.6. E 00 LT.5. E 00 CE-141 LT. 5. E 00 LT. 7. E 00 LT.5. E 00 LT.8. E 00 LT.6. E 00
- CE-144 LT.2. E 01 LT.3. E 01 LT.2. E 01 - LT. 3. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.8. E 01 LT.6. E 01 LT.9. E 01 LT.7. E 01 ,
TH-228 LT.7. E 00 LT. 8. E 00 LT.5. E 00 LT.9. E 00 LT.7. E 00 + t TRrl1UM ANALYSIS: , t H-3 LT.2. E 02 LT. 1. E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02
- Duplicate Analysis !
, - -.. a -c ,
WOIE CREEK NUC12AR OPERATING CORPORATION EXPOSURE PA*HIWAY - WA~IERBORNE SURFACE WA~IER (PCI/LTIER) STATION NUMBER DC DATE COI1ECIED: 01/16 02/20 03/26 04/23 05/21 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 3. E O1 LT.3. E O1 LT.2. E O1 LT.3. E O1 LT.3. E O1 K-40 LT.8. E 01 LT.5. E 01 LT.4. E 01 LT.6. E 01 LT. 1. E 02 MN-54 LT.3. E 00 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 CO-58 LT.3. E 00 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 FE-59 LT.6. E 00 LT. 6. E 00 LT.4. E 00 LT. 7. E 00 LT. 8. E 00 ,
- CO-60 E 00 7.2413.17 E 00 E 00 LT.3. LT.2. LT.3. E 00 LT.4. E 00
? ZN-65 LT. 6. E 00 LT. 7. E 00 LT. 5. E 00 LT.7. E 00 LT.8. E 00 $ NB-95/ZR-95 LT. 3. E 00 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 RU-103 LT. 3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT. 3. E 01 LT.4. E 01 1-131 LT.4. E 00 LT. 5. E 00 LT.3. E 00 LT.4. E 00 LT.5. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 IA-140/BA-140 LT.4. E 00 LT. 5. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 ! CE-141 LT.5. E 00 LT.7. E 00 LT.4. E 00 LT.7. E 00 LT. 5. E 00 CE-144 LT. 2. E 01 LT.3. E 01 LT.2. E 01 LT. 3. E 01 LT.2. E 01 RA-226 LT.6. E 01 LT.8. E 01 LT.5. E 01 LT. 8. E 01 LT.7. E 01 TII-228 LT. 5. E 00 LT.7. E 00 LT.4. E 00 LT. 7. E 00 LT.6. E 00 TRTIlUM ANALYSIS: H.3 9.3 1 0.3 E 03 1.4 1 0.1 E 04 1.3 1 0.1 E 04 1.2 1 0.1 E 04 1.1 1 0.1 E 04
WOIF CREEK NUCI2AR OPERATING CORPORAT10N EXPOSURE PKIEWAY - WA"IERBORNE SURFACE WATER (PCI/IIIER) STATION NUMBER DC DATE COILECTED: 05/21' 06/18 07/16 08/22 09/24 GAMMA SPECIRUM ANALYSIS: BE.7 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.4. E 01 LT. 3. E 01 K-40 LT.9. E 01 LT.5. E 01 LT.5. E 01 LT. 1. E 02 LT. 5. E 01 MN.54 LT.3. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 ,o CO-58 LT. 3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 $ FE-59 LT.6. E 00 LT. 5. E 00 LT.5. E 00 LT.9. E 00 LT.6. E 00 to CO-60 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.7. E 00 LT.6. E 00 LT.5. E 00 LT. 1. E 01 LT.6. E 00 h ZN-65 E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 NB-95/ZR-95 LT.3. RU-103 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.5. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 4. E 01 LT.3. E 01 1-131 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.7. E 00 LT.6. E 00 CS-134 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT. 5. E 00 LT.4. E 00 CS-137 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT. 5. E 00 LT.3. E 00 1A-140/BA-140 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.6. E 00 LT.6. E 00 CE-141 LT.5. E 00 LT.5. E 00 LT.6. E 00 LT.7. E 00 LT.6. E 00 CE-144 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.3. E 01 LT. 2. E 01 RA-226 LT.6. E 01 LT.6. E 01 LT.7. E 01 LT.9. E 01 LT. 7. E 01 TH-228 LT.5. E 00 LT. 5. E 00 LT.6. E 00 LT.8. E 00 LT. 6. E 00 TRI11UM ANALYSIS: H-3 1.0
- 0.1 E 04 1.4 i 0.1 E 04 9.7 i O.3 E 03 8.9 i O.3 E 03 9.3 1 0.3 E 03
- Duplicate Analysis
WOIX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PAT 11WAY - WATERBORNE SURFACE WATER (PCl/ LITER) STAT 10N NUMBER DC DATE COLLECTED: 10/23 11/27 12/19 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 K-4 0 LT.5. E 01 LT.7. E 01 LT.5. E 01 i MN-54 LT.2. E 00 LT.3. E 00 LT.3. E 00 CO-58 LT.2. E 00 LT. 3. E oC LT. 3. E 00 FE-59 E 00 E 00 E 00 LT.5. LT. 7. LT. 6.
- CO-60 LT.3. E 00 LT. T3. E 00 LT. 3. E 00
? ZN.65 LT.6. E 00 LT. 7. E 00 LT. 7. E 00 $ NB-95/ZR-95 LT.3. E 00 LT.3. E 00 LT. 3. E 00 RU-103 LT.3. E 00 LT.3. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 1-131 LT.4. E 00 LT.5. E 00 LT.5. E 00 i CS-134 LT.3. E 00 L.T. 3. E 00 LT.3. E 00
- CS-137 LT.3. E 00 LT.3. E 00 LT.4. E 00 ;
LA-140/BA-140 LT.3. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.5. E 00 LT.6. E 00 f CE-144 LT.2. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.6. E 01 LT.7. E 01 [ TH-228 LT.6. E 00 LT. 6. E 00 LT.7. E 00 ; TRITIUM ANALYSIS: H-3 8.8 i 0.3 E 03 9.1 1 0.4 E 03 8.8 i 0.4 E 03
WOtF CREEK NUCIZAR OPERAT1NG CORPORATION EXPOSURE PATHWAY - WATERBORNE SURFACE WATER (PCI/ LITER) STAllON NUMBER MUSH DATE COLLECIED: 01/16 02/20 03/26 04/23 05/21 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E O1 LT.3. E O1 LT. 2. E 01 LT.3. E 01 LT.3. E O1 K-40 LT. 6. E O1 LT. 7. E O1 LT.4. E O1 LT.6. E O1 LT. 8. E O1 MN-54 LT.3. E 00 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.3. E 00 CO-58 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.3. E 00 LT.3. E 00 FE-59 LT.6. E 00 LT. 7. E 00 LT. 5. E 00 LT.7. E 00 LT.6. E 00 y CO-60 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00
$* ZN-65 LT.6. E 00 LT.6. E 00 LT. 5. E 00 LT.8. E 00 LT.7. E 00 NB-95/ZR-95 LT. 3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00
[ RU-103 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00
- RU-106 LT.3. E 01 LT. 3. E 01 LT. 2. E 01 LT. 3. E 01 LT.3. E 01 1-131 LT.6. E 00 LT. 5. E 00 LT.4. E 00 LT. 5. E 00 LT.4. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT.2. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 LA-140/BA-140 LT.4. E 00 LT.5. E 00 LT.3. E 00 LT.4. E 00 LT 3. E 00 CE-141 LT.6. E 00 LT.6. E 00 LT. 5. E 00 LT. 6. E 00 LT. 5. E 00 CE-144 LT. 2. E 01 LT. 3. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.8. E 01 LT.6. E 01 LT. 8. E 01 LT.6. E 01 TH-228 LT.7. E 00 LT.7. E 00 LT. 5. E 00 LT. 8. E 00 LT.5. E 00 i TRIllUM ANALYSIS:
H-3 LT.2. E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02 LT. 1. E 02
i WOlE CREEK NUCLEAR OPERATING CORPORAT10N i EXPOSURE PA111WAY - WATERBORNE SURFACE WNIER (PCI/ LITER) STATION NUMBER MUSH DATE COLLECIED: 06/18 07/16 08/22 09/24 10/23 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT. 2. E 01 LT.4. E 01 LT. 2. E 01 LT.3. E 01 K-4 0 LT.5. E 01 LT.4. E 01 LT. 1. E 02 LT.4. E 01 LT. 5. E 01 MN-54 LT.3. E 00 LT.2. E 00 LT.4. E 00 LT. 3. E 00 LT. 3. E 00 CO-58 LT.3. E 00 LT.2. E 00 LT.4. E 00 LT. 2. E 00 LT. 3. E 00 FE-59 LT.6. E 00 LT.5. E 00 LT.9. E 00 LT. 5. E 00 LT. 6. E 00 m CO-60 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00
$ ZN.65 LT.6. E 00 LT.6. E 00 LT.9. E 00 LT.6. E 00 LT.6. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 h NB-95/ZR-95 L RU-103 LT.3. E 00 LT.3. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 0 RU-106 LT.3. E 01 LT.2. E 01 LT.4. E 01 LT.2. E 01 LT.3. E 01 1-131 LT.4. E 00 LT.3. E 00 LT.7. E 00 LT.4. E 00 LT.4. E 00 CS-134 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.3. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 l LA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.4. E 00 LT.6. E 00 LT.5. E 00 LT.5. E 00 CE-144 LT.2. E 01 LT. 2. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT. 5. E 01 LT.8. E 01 LT.6. E 01 LT.7. E 01 TH-228 LT.6. E 00 LT.5. E 00 LT.7. E 00 LT. 5. E 00 LT.6. E 00 ,
k TRI'11UM ANALYSIS: H-3 LT. 1. E 02 LT.2. E 02 LT. 2. E 02 LT. 1. E 02 LT.2. E 02 ; t [ i
WOlX CREEK NUCLEAR OPERATING CORPORATION EXIVSURE PA11IWAY - WATERBORNE SURFACE WA~IER (PCI/ LITER) STATION NUMBER MUSli DATE COLLECIED- 11/27 12/24 12/24' GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 K.40 LT.6. E 01 LT. 5. E 01 LT. 1. 6 02 MN-54 LT.3. E 00 LT.3. E 00 LT.4. E 00 CO-58 LT.3. E 00 LT.3. E 00 LT.4. E 00 FE-59 LT.6. E 00 LT.7. E 00 LT.8. E 00 ; y CO-60 LT.3. E 00 LT.3. E 00 LT.4. E 00 $* ZN-65 LT.7. E 00 LT.7. E 00 LT.8. E 00 ' NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT.4. E 00 RU-103 LT.4. E 00 LT.4. E 00 LT.4. E 00 j RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 ! I-131 LT.6. E 00 LT. 6. E 00 LT.7. E 00 ; CS-134 LT.3. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.4. E 00 ; LA-140/BA-140 LT.5. E 00 LT. 5. E 00 LT.5. E 00 CE-141 LT.7. E 00 LT. 6. E 00 LT.6. E 00 . CE-144 LT.3. E 01 LT.2. E 01 LT.2. E 01 , RA-226 LT.8. E 01 LT. 7. E 01 LT.7. E 01 TH-228 LT.7. E 00 LT.7. E 00 LT.7. E 00 TRrl1UM ANALYSIS: H-3 LT.2. E 02 2.1 i 1.1 E 02 LT.2. E 02
- Duplicate Analysis
l b WOIX CREEK NUCI2AR OPERAT1NG CORPORATION EXPOSURE PA111WAY - WATERBORNE SURFACE WATER (PCI/ LITER) ; STA110N NUMBER PSBR i DATE COLLECIED: 12/16 CAMMA SPECI' RUM ANALYSIS: BE-7 LT.4. E O1 K-40 L T. 1. E 02 MN-54 LT.4. E 00 y CO-58 LT.4. E 00 ,
$ FE-59 L T. 1. E 01 CO-60 LT.5. E 00 4 ZN-65 LT. 1. E 01 N E 00 NB-95/ZR-95 LT.5.
RU-103 LT.5. E 00 RU-106 LT.4. E 01 I-131 LT.9. E 00 CS-134 LT.5. E 00 CS-137 LT.5. E 00 LA-140/BA-140 LT. 7. E 00 CE-141 LT 8. E 00 CE-144 LT.3. E 01 RA-226 LT.9. E 01 TH-228 LT.7. E 00 TRIT 1UM ANALYSIS: , i H-3 8.6 i 0.3 E 03
-. ._ -re _~ . _ _ _ _ _ _ - - - _ _ _ -- -
' __ _ _ . - - _ . _ _ _ _ - - ___m -
u ___ __ __ _ ___m - --___._ _.__:--
WOtX CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PA~nIWAY - WATERBORNE SURFACE WATER (PCI/ LITER) STATION NUMBER SP DATE COLLECTED: 01/16 02/27 02/20* 03/26 04/23 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.2. E 01 LT. 3. E 01 LT.3. E 01 K.40 LT. 1. E 02 LT.4. E 01 LT.8. E 01 LT. 7. E 01 MN-54 LT.4. E 00 LT. 2. E 00 LT. 3. E 00 LT. 3. E 00 CO-58 LT.3. E 00 LT. 2. E 00 LT. 3. E 00 LT.3. E 00 FE-59 LT.7. E 00 LT.4. E 00 LT. 6. E 00 LT.7. E 00 2 CO-60 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 $ ZN-65 LT.8. E 00 LT. 5. E 00 LT.6. E 00 LT.8. E 00 ? NB-95/ZR-95 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT. 3. E 00 d RU-103 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 RU-106 LT. 3. E 01 LT.2. E 01 LT.3. E 01 LT. 3. E 01 1-131 LT. 5. E 00 LT. 3. E 00 LT.4. E 00 LT. 5. E 00 CS-134 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 CS-137 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.4. E 00 1A-140/BA-140 LT.5. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.5. E 00 LT.4. E 00 LT. 8. E 00 CE-144 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT. 3. E 01 RA-226 LT.7. E 01 LT.6. E 01 LT.6. E 01 LT. 1. E 02 TH-228 LT.6. ' E 00 LT.5. E 00 LT. 5. E 00 LT.8. E 00 TRI11UM ANALYSIS: 11- 3 9.4 i O.3 E 03 1.2 1 0.1 E 04 1.3 1 0.1 E 04 1.3 i 0.1 E 04
- Sample Not Collected /lce.
WOEF CREEK NUCI2AR OPERAT1NG CORPORAT10N EXPOSURE PKDIWAY - WATERBORNE SURFACE WKIER (PCI/ LITER) STATION NUMBER SP DATE COILECIED: 05/21 06/18 07/16 08/22 09/24 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 K-40 LT.6. E 01 LT. 1. E 02 LT.4. E 01 LT.4. E 01 LT. 8. E 01 MN.54 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.2. E 00 LT. 3. E 00 CO-58 LT.2. E 00 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.3. E 00 FE-59 LT.6. E 00 LT.7. E 00 LT.5. E 00 LT. 5. E 00 LT.6. E 00 ['DCO-60 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT. 2. E 00 LT. 3. E 00 ZN-65 LT.6. E 00 LT.8. E 00 LT.6. E 00 LT. 5. E 00 LT. G. E 00
? NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT.3. E 00 % RU-lO3 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT.3. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.3. E 01 1-131 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 IA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.7. E 00 LT.5. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 CE-144 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT.8. E 01 LT.7. E 01 LT.6. E 01 LT.5. E 01 LT.6. E 01 TH-228 LT.7. E 00 LT.6. E 00 LT. 5. E 00 LT.5. E 00 LT.5. E 00 TRTI1UM ANALYSIS:
H-3 1.0 1 0.1 E 04 1.1 1 0.1 E 04 9.8 1 0.3 E 03 9.2 1 0.3 E 03 9.5 1 0.3 E 03
i WOtX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PATIIWAY - WATERBORNE SURFACE WA'IER (PCI/ LITER) STAT 10N NUMBER SP DATE COLLECTED: 10/23 11/27 12/19 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 3. E 01 LT.3. E 01 LT.3. E 01 K-40 LT. 5. E 01 LT. 5. E 01 LT. 7. E 01 MN-54 LT.3. E 00 LT.3. E 00 LT.3. E 00 CO-58 LT.3. E 00 LT.3. E 00 LT.3. E 00 FE-59 LT. 5. E 00 LT.7. E 00 LT.6. E 00 y CO-60 LT.3. E 00 LT.4. E 00 LT.3. E 00 g ZN-65 LT.5. E 00 LT.6. E 00 LT.7. E 00 m NB-95/ZR-95 LT.3. E 00 LT. 3. E 00 LT.3. E 00 0 RU-103 LT.3. E 00 LT 3. E 00 LT.3. E 00
- RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 I-131 LT.4. E 00 LT. 5. E 00 LT.5. E 00 CS-134 LT.3. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.3. E 00 LT. 3. E 00 LT.3. E 00 LA-140/BA-140 LT.4. E 00 LT. 5. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.6. E 00 LT. 5. E 00 CE- 144 LT.3. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.8. E 01 LT.8. E 01 LT.6. E 01 Til-228 LT.7. E 00 LT.7. E 00 LT. 5. E 00 TRIT 1UM ANALYSIS:
11-3 9.3 1 0.3 E 03 8.4 1 0.3 E 03 8.0 i O.3 E 03
- - - - . - . -- , --. . . . - -}}