ML20107L562
| ML20107L562 | |
| Person / Time | |
|---|---|
| Site: | Wolf Creek  |
| Issue date: | 12/31/1995 |
| From: | WOLF CREEK NUCLEAR OPERATING CORP. |
| To: | |
| Shared Package | |
| ML20107L534 | List: |
| References | |
| NUDOCS 9604290360 | |
| Download: ML20107L562 (151) | |
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l Enclosure 2 l j WO 96-0061 i
I WOLF CREEK NUCLEAR OPERATING CORPORATION
! WOLF CREEK GENERATING STATION i
! 1995 ANNUAL RADIOLOGICAL ,
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ENVIRONMENTAL OPERATING REPORT 1
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APRIL 15,1996 1
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9604290360 960423 2 PDR ADOCK 0500 R
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l TABLE OF CONTENTS List of Tables 11 List of Figures lii Introduction 1 l
I. Program Description 2 i II. Discussion of Results 5
~ll III. Annual Land Use Census Results and Program Revisions 10 IV. Program Deviations 12 V. EPA Interlaboratory Comparison Program Results 13 l l
Tables. 14 Figures 35 l
Appendix A A-1 Appendix B B-1 I
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LIST OF TABLES l
1 1995 Radiological Environmental Monitoring Program Sample Collection 14 l l
2 Sample Location Numbers, Distances, and Directions 19 3 1995 Airborne Particulate Gross Beta Analyses 20 i 1 l 4 1995 Airborne Particulate Quarterly Composite Gamma Isotopic 22 Analyses l I
5 1995 First & Second Quarter TLD Results 23 l t
l 6 1995 Third & Fourth Quarter TLD Results 24 l
l l 7 1995 Drinking Water Radiological Analyses 25 l
l 8 1995 Surface Water Radiological Analyses 26 9 1995 Ground Water Radiological Analyses. 27 10 1995 Aquatic Plants Radiological Analyses <
27 11 1995 Shoreline Sediment Radiological Analyses 28 12 1995 Bottom Sediment Radiological Analyses 28 13 1995 Broadleaf Vegetation Radiological Analyses 29 14 1995 Irrigated Crops Radiological Analyses 29 l
f 15 1995 Milk Radiological Analyses 30 ;
16 1995 Fish Radiological Analyses 31 17 1995 Land Use Census Residence Data 32 18 1995 Land Use Census Milk and Garden Data 33 19 EPA Interlaboratory Comparison Program 1995 34 l
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LIST OF FIGURES 1 Airborne Pathway Sampling Locations 35 2 Direct Radiation Pathway Sampling Locations 36 3 Waterborne Pathway Sampling Locations 37 4 Ingestion Pathway Sampling Locations 38 l 1
5 Distant Sampling Locations 39 l 6 1995 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 12 WCCL Smoothed Surface Water Tritium Data 46 13 Cumulative Liquid Effluent Tritium Data 47 14 Drinking Water Gross Beta, Historical 48 15 Cs-137 in Shoreline Sediment (Location Discharge Cove) 49 16 Tritium in Wolf Creek Cooling Lake Fish 50 1
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l INTRODUCTION i
The 1995 Annual Radiological Environmental Operating Report for Wolf Creek i Generating Station (WCGS) covers the period from January 1 through l December 31, 1995. WCGS is located in Coffey County, Kansas, approximately five miles northeast of Burlington, Kansas.
Fuel loading commenced at WCGS on March 12, 1985. The operational phase of the Radiological Environmental Monitoring Program 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 Radiological Environmental Monitoring Program (REMP) conducted by Wolf Creek Nuclear Operating Corporation (WCNOC), results of sample analyses performed by Teledyne Brown l Engineering Environmental Services and WCNOC Health Physics technicians, a discussion of monitoring program results, a description of revisions to and deviations from the program, and comments on the results of the Environmental Protection Agency (EPA) 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 to the report.
During 1995, activation products were not detected in airborne particulate and radioiodine filters, broadleaf vegetation, crops, milk, ground water, nondomestic meat, terrestrial vegetation or drinking water.
During 1995, activation products were detected in algae, aquatic vegetation, shoreline sediment, bottom sediment, soil, surface water and fish samples.
All nuclides detected in the REMP samples were below applicable NRC reporting levels.
1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 1 of 50
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l I. PRON W DESCRIPTION Radiological environmental samples were collected according to the schedule in Attachment A, Table 5-1 of the WCGS Offsite Dose Calculation Manual (ODCM).
All samples were collected by WCNOC's Environmental Management group. The samples were analyzed by Teledyne Brown Engineering Environmental Services of Westwood, New Jersey or WCGS Health . Physics Technicians. Table 1 lists sampling pathways and frequencies of sampling and analysis. Table 2 lista each sample location's 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 ani analysis program by )
individual pathways. I A. Airborne i
i Low volume air sampling pumps continually collected particulate and l radiciodine samples on 47 mm glass fiber filters and charcoal canisters, i respectively. Weekly, the filters and charcoal canisters were changed out, labeled, and shipped to Teledyne Brown Engineering Environmental Services for l analysis. The volume of air sampled was calculated from the average of l initial and final flow rates and the total time of collection. Each pump is equipped with a time totalizer that is checked weekly against the elapsed '
time.
Gross beta analysis of the air particulate samples was performed approximately 72 hours8.333333e-4 days <br />0.02 hours <br />1.190476e-4 weeks <br />2.7396e-5 months <br /> post collection to allow the radon and thoron daughter products to 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 resulted in analysis of each individual charcoal canister.
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 location. Distances and directions to sampling locations from the plant site are listed in Table 2; locations are shown in Figure 1 (nearby locations) and Figure 5 (distant locations).
B. Direct Radiation Panasonic UD-814-AQ TLDs were used during the 1995 sample year. These TLDs consist of one lithium-borate element and three calcium sulfate elements in a plastic case. Each TLD is annealed and analyzed by Wolf Creek Health Physics technicians on a Panasonic UD-710A TLD reader.
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 TLDs from the elements and 1 tampering. Two TLDs were placed at each designated location. TLD sample locations are illustrated in Figure 2 (nearby locations) and Figure 5 (distant 1995 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 2 of 50 l
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I locations). Table 2 provides the distance and direction of each location from the site.
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 perfomed on drinking water samples. Tritium analysis was performed monthly by liquid scintillation for surf ace water and quarterly for drinking water.
Tritium analysis for ground water was performed quarterly by gas . counting.
All 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 Cooling Lake (WCCL) and the Neosho River. Monthly, composite samples were obtained from automatic composite samplers at each location that pulled approximately 10 ml samples j hourly. I l
Monthly, grab samples were drawn from each surface water location. Surface !
water was sampled at the outfall of John Redmond Reservoir (JRR) as a control (location Make-up Water Screenhouse [ MUSH]) and in the discharge cove and spillway of WCCL for indicator locations.
Ground water samples were collected quarterly from four locations. One ground l 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 I indicator samples. Duplicate samples were obtained from location B-12 and l were labeled F-20. These duplicate samples served as a lab quality check.
Shoreline sediments were sampled semiannually for gamma analysis at the discharge cove (indicator, Figure 3) and at JRR (control, Figure 3).
Shoreline sediment samples were also obtained from location Environmental Education Area (EEA) [ indicator, Figure 3].
Bottom sediments were collected semiannually for gamma analysis at the discharge cove (indicator, Figure 3) and at location WC&1lth RD (indicator, Figure 3). Due to high water, the sample normally collected in the spring at JRR (control, Figure 3) was unobtainable. However, the fall sample was collected.
Algae from the discharge cove (indicator, Figure 3) was collected semiannually for gamma analysis. Aquatic plants were sampled from locations EEA,'DC ALT and Make-up Water Discharge Structure (MUDS) [ indicator, Figure 3] and were also analyzed for gamma emitters.
D. Ingestion Milk samples were collected semimonthly from April through November and monthly from December through March. No sampling locations that produce milk 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 3 of 50
for human consumption were identified within 5 miles of the plant during 1995.
Therefore, only control samples were obtained. Radiochemical I-131 and gamma l 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 four gardens. The three indicator gardens (two regular and one alternate) and a control garden wereisampled (Fig.tre 5) . Gamma isotopic analyses were performed on all samples.
Due to the wet spring, downstream crops were not irrigated. Three samples were obtained from cropland downstream of the confluence of Wolf Creek and the Neosho River (indicator) and two samples were obtained upstream (control).
- Gamma isotopic analysis was performed on each sample.
Fish were sampled from the tail waters of JRR (control) and from WCCL semiannually for gamma isotopic analysis (Figure 4). Several 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.
l Fish entrails were sampled for gamma isotopic analysis from JRR (control, l Figure 4) and WCCL (indicator, Figure 4). The fish entrails were also analyzed for tritium. These samples were a cooperative sampling effort with the Kansas Department of Health and Environment (KDHE).
l Deer and quail were sampled in the immediate vicinity of the plant
- (indicator) . Quail were also sampled from a control location that was remote from the site. Gamma isotopic analysis was performed on boneless meat portions of the game. These samples were a cooperative sampling effort with the KDHE.
Soil was sampled semiannually fro. locations MUDS and EEA for gamma isotopic l analyses. These samples were a cooperative sampling effort with the KDHE.
1 Terrestrial vegetation was also sampled semiannually from locations MUDS and EEA for gamma isotopic analyses. These samples were a cooperative sampling effort with the KDHE.
Sampling locations listed in this section are outlined in Table 2.
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l II. DISCUSSION OF RESULTS Analysis results for all pathways are summarized in Appendix A using the '
format described in NRC Radiological Assessment Branch Technical Position, Revision 1, November 1979. 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 l radioactivity, and effluent releases when applicable. Trends or seasonal l effects are discussed. Associated errors for positive results on data '
contained in Tables 3 through 16 may be obtained in Appendix B.
A. Airborne
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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 1995.
Figure 7 represents the historical smoothed averages of indicator and control gross beta. Figure 8 illustrates the hist'orical indicator and control gross beta ratio. Finally, Figure 9 displays a historical plot of average weekly indicator and control gross beta values since initial criticality.
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 to a low point in the spring months (May or June).
Results from the weekly analysis of charcoal filters for I-131 did not exceed the detection limit during the year.
Results of the quarterly gamma analysis of air particulate filter composites are summarized in Table 4. Naturally occurring Be-7 and K-40 were detected.
Effects of plant operation were not seen via the airborne pathway for the year and no unusual trends were noted.
B. Direct Radiation Quarterly gamma exposures measured at each location for 1995 are shown in Tables 5 and 6. Values are normalized to a standard 90-day quarter.
Results from TLDs located near the plant site (less than approximately three miles distance), which would be most sensitive to changes due to plant operation, were combined into quarterly averages. These nearsite averages, using locations, 1, 2, 7-14, 18, 26-30, 37 and 38, are compared to control (locations 39 and 40) results in Figure 11. In addition, variation of the nearsite averages from the control location results are displayed graphically in Figure 10. These figures also include preoperational data for comparison.
Note that nearsite TLD locations have historically trended higher than the control locations both prior to and after WCGS became operational. Figure 11 also shows that the levels of direct radiation measured by TLDs near Wolf Creek have declined from 1980 to 1993. (For further discussion of this l decline, please see the 1993 WCGS Annual Radiological Environmental Operating Report.)
1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 5 of 50
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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 1995.
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 during 1995 and no unusual trends were noted.
(2) Surface Water Tritium, attributable to WCGS operation, was detected in all surface water samples collected from WCCL in 1995. A total of 1089 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 locations DC and Sp from startup in May 1985 through 1995. The cumulative curies of liquid tritium released to WCCL is illustrated on Figure 13.
During 1995, the annual mean for detected tritium at the discharge cove was 10,275 pCi/ liter. It can be seen in Figure 12 that monthly surface water tritium concentrations appear to be slightly increasing since plant startup.
This is expected until the tritium concentration of the lake reaches equilibrium, which has been estimated at 13,074 pC1/ liter.
There were no other radionuclides detected in surface water for the year, and l no unusual trends were noted.
(3) Ground Water During 1995, the occurrence of radioactivity was not detected in ground water samples.
(4) Shoreline sediment Naturally occurring nuclides (K-40, Ra-226 and Th- 22 8 ) were detected in all indicator locations as well as the control locations. Another naturally occurring nuclide (Be-7) was detected in a control location sample.
In two samples from the discharge cove, Co-60 was detected (115 pCi/kg and 168 pCi/kg). This activity is attributable to plant operation.
1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 6 of 50
i Cs-137 was detected in samples from the indicator locations, as well as in one sample from a control location. Since Cs-134 was not detected in the samples l 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 i that Cs-137 activity was detected preoperationally and is routinely detected at the discharge cove. A linear trendline indicates that the Cs-137 activity i detected in the discharge cove is showing a downward trend. Analysis results are summarized in Table 11.
D. Ingestion (1) Milk No indicator locations for milk existed during 1995 (see Program Deviation section for explanation). A control sample was routinely obtained for analysis. All milk samples analyzed contained K-40. The yearly average K-40 concentration was 1400 pCi/ liter. Table 15 summarizes milk analysis results I for 1995.
No other gamma emitters were detected.
(2) Food and Garden Crops Gamma analyses of broadleaf vegetation samples during 1995 revealed naturally occurring gamma emitters Be-7 and K-4 0. Table 13 shows the results of 1995 analysis. Additional gamma emitters were not detected in broadleaf vegetation samples.
In addition to broadleaf vegetation, crop samples irrigated with water from the Neosho River were collected. Two control samples were obtained from cropland upstream of the confluence of Wolf Creek and the Neosho River, and three indicator samples were obtained downstream. Gamma analysis detected naturally occurring K-40 to be present in all of the samples, with no nuclides detected due to plant operation. Due to the wet spring, downstream crops were not irrigated this year. Results of crop analyses are summarized in Table 14.
(3) Fish Analysis results are illustrated in Table 16. Naturally occurring K-40 was detected in all fish samples.
During 1995, fish were also analyzed for tritium. All fish samples taken from WCCL and from the WCCL 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 l for 1995 (9,100 pCi/kg) would receive a calculated committed dose of 0.012 I
mrem. Figure 16 illustrates the tritium concentrations detected in fish from WCCL.
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I E. Special Samples (not required by the WCGS ODCM)
(1) Nondonestic Meat (Quail & Deer)
Naturally occurring K-40 was detected in all samples. Other radionuclides were not detected and no effects of plant operation were detected in these samples.
(2) . Bottom Sediment Table 12 shows gamma emitters detected during 1995 in bottom sediment samples.
Naturally occurring nuclides detected include Be-7, K-40, Ra-226, and Th-228.
Mn-54 and Co-58 were detected in one WCCL discharge cove sample. This j q activity is attributable to plant operation and is regularly identified in j plant effluents, i-i Co-60 was detected in both samples obtained from the WCCL discharge cove.
Co-60 activity shown in Table 12 is attributable to plant operation and is commonly identified in plant effluents. I Two samples obtained from the discharge cove contained both Cs-134 and Cs-137.
- since both nuclides are present, some of the Cs-137 activity is attributed to plant operations, and all of the Cs-134 is attributed to plant operation.
Cs-137 was also detected in a sample taken from location WC&1lTH RD. Since Cs-134 was not present and Cs-137 activity was also detected from the control
, location sample, this activity is primarily due to fallout, and not to a newly j produced fission product.
No other radionuclides were detected.
I I (3) Aquatic Vegetation Table 10 shows gamma emitters detected during 1995 in aquatic plant samples.
Naturally occurring Be-7, K-40, Ra-226 and Th-228 were detected.
Mn-54 was detected in algae samples collected from the discharge cove. This !
activity is attributed to plant operation and is regularly identified in plant l effluents.
Co-58 and Co-60 were also detected in algae samples collected from the discharge cove. This activity is attributed to plant operation and both nuclides are regularly identified in plant effluents.
Nb-95/Zr-95 were detected in an algae sample obtained from the discharge cove.
This activity is attributed to plant operation and is regularly identified in plant effluents.
Cs-137 was detected in algae samples collected from the discharge cove. )
Cs-137 was also detected in the arrowhead sample collected from the EEA. I Since Cs-134 was not detected in the samples, the Cs-137 activity is primarily j due to fallout, and not due to a newly produced fission product. i 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 8 of 50 l
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i (4) Terrestrial veFatation 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-228 activity was detected. Cs-137 activity was detected in three of the four soil samples. Since Cs-134 was not detected, the Cs-137 activity is primarily due to fallout, and not from a l newly produced fission product.
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1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 9 of 50
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III.
ANNUAL LAND USE CENSUS RESULTS AND PROGRAM REVISIQHS INTRODUCTION The annual Land Use Census of rural residents within five miles of the WCGS I
has been completed for 1995. The results and notable changes are summarized and illustrated in Tables 17 and 18.
BACKGROUND l Section 5.2, Attachment A, of the ODCM procedure (AP 07B-003), directs that "A
! Land Use Census shall be conducted annually during the growing season to identify the nearest (1) milk animal, (2) residence, and (3) garden of greater that 500 square feet producing broadleaf vegetation in each of the 16 j meteorological sections within five miles of the WCGS site." "The results of the Land Use Census shall be included in the Annual Radiological Environmental Operating Report." l l l l Table 5-1, Attachment A, of the ODCM requires that broadleaf vegetation l samples be collected from "two indicator locations with the highest calculated
) annual average D/Q."
Table 5-1, Attachment A, of the ODCM also reqvires that milk samples be collected from "three indicator locations within 5 miles of the site having the highest dose potential."
I METHODOLOGY l Surveys were mailed to rural residents within five miles of WCGS during the l first week of September 1995. A follow-up mailing was sent during the third I week of September to residents who had not responded. The survey excluded the residents of New Strawn, Burlington, and a trailer park just north of l Burlington. These locations are excluded due to the large number of l households and the low likelihood that information gained from these residences would affect the locations chosen for REMP sampling. Of the 168 l surveys mailed to the rural residents, 146 were returned by mail and 16
! responses were obtained through telephone conversations. Six surveys were l partially completed with information obtained by driving by the locations, l since the residents could not be reached by telephone or the surveys were not i returned by mail . This is a response rate of 96.43 percent for the 1995 !
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i RESULTS l
The estimated population for the 1995 Land Use Census is 476 persons. This is an increase from the 1994 Land Use Census which was estimated at 436 persons.
l In 1993, 146 households were surveyed, while 158 households were surveyed in the 1994 Land Use Census.
Comparing the 1994 Land Use Census results to this year's results indicates )
that the nearest residence has changed in sectors A, M, and N. In sector A,
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the nearest residence is located 2.6 miles from the. plant (location A2.6-17TE1520). In sector M, the nearest residence is no longer 2.4 miles from the plant; the new location (M1.6-NARD 1441) is located closer to the plant at 1.6 miles. In sector N, the nearest residence is no longer 2.6 miles from the plant; the new location (N2.1-15ED1350) is located closer to the
, plant at 2.1 miles. In sector L, the closest residence is still located at
' 1339 Native Road,.SE, however, the distance was changed to more accurately reflect this location.
Two changes were noted in the distance to the nearest milk animal. During 1994, no locations were identified as.having milk animals. During 1995, two .
i surveys indicated dairy cattle were kept on the property. Telephone calls I were made to both residences (G3.6-RERD1150 and B4.1-QURD1823) , and neither household is milking the dairy cattle for human consumption.
j Numerous location changes were noted for the nearest garden producing l broadleaf vegetation. In sectors A, B, P, the gardens are closer to the plant than the gardens indicated in 1994. In sector L, the distance is the same, I however, the location is different. I i
SUMMARY
l Considering the data collected in the 1995 Land Use census, a change is required in the REMP regarding broadleaf vegetation. The two locations with the highest calculated . annual average D/0 rankings are A2.61-OXLA1731 and R2.1-NALA1650, respectively. The ODCM specifies that an " alternate location may be used to provide continued monitoring". The garden at G1.6-QURD1384 is third by the D/Q ranking, and is a likely candidate for the alternate garden location. The' residents at A2.61-OXLA1731, R2.1-NALA1650, and G1.6-QURD1384 will be contacted to ask if they will participate in the REMP sampling program. Considering the residents' answers, the REMP will be revised accordingly.
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i 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 11.of 50 l
IV. PROGRAM DEVIATIONS Airborne Location 2 (October 31): While performing the weekly air sample collection, the pump at locatic. 2 (Sharpe) was found to be inoperable. The motor on the l
air sample pump was completely seized-up. The air sample pump was replaced. l Although the motor seized, the installed clock continued to operate. I Therefore the air particulate filter and the charcoal filter were submitted to '
the vendor lab with " unknown" as the volume. (PIR 95-2652) i Direct Radiation Samplers (TLDs)
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Location 42, first quarter: The Health Physics lab reported that an erroneous reading had occurred on TLD E-0000079. The results for this location are based on one TLD instead of two.
Location 43, first quarter: The Health Physics lab reported than an erroneous reading had occurred on TLD E-0000036. The results for this location are based on one TLD instead of two.
Ingestion Milk Indicator sampling locations are still unavailable within five miles of the plant. Refer to Section III, Annual Land Use Census Results and Program Revisions.
Broadleaf Vegetation Broadleaf vegetation is sampled when seasonally available. No broadleaf vegetation deviations occurred during 1995. Listed below are those sample locations and dates when the samples were not collected due to seasonal unavailability, No corrective actions were necessary. Samples were collected at alternate location C-1 when available. Sample locations R-1 and G-1 are the primary sample locations and S-4 is the control location.
G-1 (5/30) Unavailable. All other gardens sampled.
G-1 (6/27) Unavailable. All other gardens sampled R-1 (9/26) Unavailable. All other gardens sampled R-1 (10/31) Unavailable. All other gardens sampled 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 12 of 50
V. EPA INTERLABORATORY COMPARIEON PRON m RESULTS l
Teledyne Brown Engineering Environmental Services is contracted to perform radiological analysis of environmental samples for WCNOC. Teledyne l participated in the EPA Interlaboratory Comparison Program during 1995. I I
Table 19 shows intercomparison test results received during the year. The table lists the sample date, the sample media, the nuclide or analysis type, the known value reported by the EPA, the measured value reported by Teledyne l Brown Engineering Environmental Services (based upon triplicate analysis), and :
the normalized deviation from the known. Results are listed in the table for l sample media and analysis types corresponding to those performed for WCNOC. '
l All of the Teledyne Brown Engineering Environmental Services results were '
within three standard deviations of the known EPA *esults.
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I 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 13 of 50
TABLE 1 1995 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SAMPLE COLLECTION EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHNAY/ AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS AIRBORNE Figures 1 & 5 Radiciodine )
Samples from five Continuous sampler Analyze and locations operation with sample radiciodine Particulates collection weekly, or canister weekly ,
more frequently if for I-131 {
required by dust i loading. I Samples from Analyze l locations near the particulate site boundary in filter weekly three sectors for gross beta having the highest activity; calculated annual perform average D/Q quarterly gamma (Locations 2, 3, isotopic and 37 on Figure 1) analysis composite (by location)
Sample from the vicinity of a j community having !
the highest calculated annual average D/Q (Location 32 on Figure 1, New Strawn)
Sample from a control location 10-20 miles distant in a low D/Q sector (Location 40 on Figure 5) l l
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TABLE 1 (Cont)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND FREQUENCY PATNWAY/ AND SAMPLE LOCATIONS COLLECTION FREQUENCY OF ANALYSIS SAMPLE DIRECT RADIATION Figures 2 & 5 I
40 routine Quarterly Gamma dose i monitoring stations quarter 3y with two or more dosimeters measuring dose '
continuously, placed as follows:
An inner ring of stations, one in each meteorological I sector 0-3 mile range from the site (Locations 1, 7-9, 11-13, 18, 26, 27, 29-31, 37 and 38 on Figure 2) l An outer ring of stations, one in each meteorological sector in the 3-5
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mile range from the site (Locations 4-6, 15-17, 19-25, and 33-36 on Figure 2). Five sectors
[A, B, D, G, and L]
contain an additional station (Locations 2, 3, 10, 14 and 28)
The balance of the stations to be placed in special l
interest areas such l as population centers (Locations 23 and 32), nearby residences 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 15 of 50
TABLE 1 (Cont)
EXPOSURE NUMBER OF SAM.'LES SAMPLING AND TYPE AND PATNWAY/ AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS DIRECT RADIATION (cont) l-(many locations are near a residence),
schools (Location 23), and in one or two areas to serve l as control stations i
10-20 miles distant from the site (Locations 39 and l 40 on Figure 5)
WATERBORNE Figure 3 l
Surface One sample upstream Monthly grab sample Monthly gamma l (Location MUSH on isotopic
- Figure 3) and one analysis and I sample downstream composite for I (Location DC on tritium analysis Figure 3). quarterly Ground Samples from one or Quarterly Quarterly gamma two sources only if isotopic and likely to be tritium analysis affected.
Indicator samples at locations hydrologically downgradient of the I site (Locations C-10, C-49, and D-65 on Figure 3) ;
! Control sample at a l location hydrologically
( upgradient of the site (Location B-12 on Figure 3) '
i f 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 16 of 50 I
t TABLE 1 (Cont) l EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND l PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS l
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 l LW-40 on Figure 5); composite
! control sample from sample.
location upstream Quarterly of the site tritium analysis l (Location BW-15 on of composites.
l Figure 3) l Shoreline one sample from the Semiannually Semiannual gamma sediment vicinity of Wolf isotopic l Creek Cooling Lake analysis l discharge cove; control sample from John Redmond l Reservoir l
(Locations DC and JRR respectively on
- Figure 3) l INGESTION Figures 4 & 5 Milk Samples from semimonthly while Gamma isotopic ,
milking animals at animals are on analysis and 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 (December highest dose to March) potential (currently there l are no locations producing milk for human consumption within five miles of the site); one sample from a control location greater than 10 miles from the site (Location S-3 on
- Figure 5) 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 17 of 50
l l
l TABLE 1 (Cont)
EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF ;
SAMPLE LOCATIONS ANALYSIS l INGESTION (cont)
Fish Indicator samples Semiannually Gamma isotopic of 1-3 analysis on j recreationally edible portions l
important species from Wolf Creek Cooling Lake; control samples of similar species i from John Redmond j Reservoir spillway l l (Figure 4)
! l l Broadleaf samples of Monthly when Gamma isotopic !
Vegetation available broadleaf available analysis on I vegetation from two edible portions I indicator locations with highest I calculated annual l average D/O (Locations R-1 and
! G-1 and alternate l
location C-1 on
! Figure 4); sample l of similar l broadleaf vegetation from a control location greater than 10 miles from the site in a low D/Q sector (Location S-4 on Figure 5)
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 l (Location NR-D1 and NR-D2 on Figure 5)
/
1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 18 of 50
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l TABLE 2 SAMPLE LOCATION NUMBERS, DISTANCES (Miles), AND DIRECTIONS l 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 16 4.2/E 31 3.0/WNW 2 2.7/N 17 3.6/SE 32 3.2/WNW 3 3.0/NNE 18 3.0/SSE 33 3.7/WNW 4 4.0/NNE 19 4.0/SSE 34 4.0/NW 5 4.0/NE 20 3.3/S 35 4.6/NNW 6 4.4/ENE 21 3.8/S 36 4.2/N 7 1.9/NE 22 4.1/SSW 37 2.1/NNW 8 1.6/NNE 23 4.5/SW 38 1.2/NW 9 2.0/ENE 24 4.1/WSW 39 13.0/N 10 2.4/ENE 25 3.6/W 40 >15.0/WNW 11 1.6/E 26 2.6/WSW 41 0.8/NNW 12 1.8/ESE 27 2.1/SW 42 0.8/SSE 13 1.5/SE 28 2.8/SW 43 0.8/WNW 14 2.6/SE 29 2.6/SSW 44 3.0/NNW 15 4.5/ESE 30 2.2/W 45 1.5/WNW Ground water Drinking water Surface water B-12/F-20 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 2.9/SW SP 2.9/S D-65 3.9/S Milk Broadleaf vegetation Irrigated Crops S-3 >15.0/WNW C-1 2.6/NE NR-U1 4.2/SW R-1 2.1/NNW NR-D1 9.2/S G-1 1.6/SE NR-D2 >10.0/S S-4 >15.0/WNW Fish Shoreline Soil Aquatic Vegetation / Algae WCCL 0.6/WNW DC 0.6/WNW DC 0.6/WNW JRR 4.0/W JRR 4.0/W DC ALT 1.5/NW EEA 3.0/NNW EEA 3.0/NNW MUDS 1.5/WNW Game Birds and Animals WCCL General Vicinity - NNW/N LeRoy >10.0/SSE Terrestrial Vegetation & Soil Bottom Sediment EEA 3.0/NNW DC 0.6/WNW MUDS 1.5/WNW JRR 4.0/W WC&11th RD 3.8/S 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 19 of 50
1 TABLE 3 1995 Airborne Particulate Gross Beta Analyses i
(pci/ cubic meter, analysis error reported in Appendix B)
Date Location Beginning Ending 2 3 32 37 40 Control 12/27/94 1/3/95 0.040 0.040 0.043 0.037 0.041 l 1/3/95 1/10/95 0.041 0.037 0.040 0.039 0.037 ;
1/10/95 1/17/95 0.035 0.036 0.037 0.035 0.034 i 1/17/95 1/24/95 0.024 0.024 0.022 0.022 0.024 !
1/24/95 1/31/95 0.040 0.041 0.043 0.045 0.045 j 1/31/95 2/7/95 0.017 0.018 0.019 0.017 0.017 2/7/95 2/14/95 0.021 0.024 0.022 0.020 0.023 1 2/14/95 2/21/95 0.026 0.024 0.024 0.023 0.025 I 2/21/95 2/28/95 0.021 0.019 0.020 0.019 0.019 2/28/95 3/7/95 0.027 0.028 0.029 0.028 0.027 i 3/7/95 3/14/95 0.026 0.023 0.031 0.026 0.028 ~
3/14/95 3/21/95 0.025 0.029 0.029 0.027 0.025 3/21/95 3/28/95 0.020 0.019 0.020 0.019 0.019 l 3/28/95 4/4/95 0.020 0.024 0.026 0.022 0.023 1 4/4/95 4/11/95 0.022 0.024 0.023 0.023 0.025 4/11/95 4/18/95 0.021 0.022 0.021 0.019 0.019 4/18/95 4/25/95 0.013 0.015 0.015 0.020 0.015 l 4/25/95 5/2/95 0.015 0.016 0.016 0.016 0.014 5/2/95 5/9/95 0.012 0.014 0.012 0.013 0.014 5/9/95 5/16/95 0.013. 0.014 0.016 0.016 0 015 5/16/95 5/23/95 0.016 0.020- 0.020 0.018 0.016 5/23/95 5/30/95 0.013 0.011 0.011 0.011 0.011 l
5/30/95 6/6/95 0.014 0.012 0.014 0.014 0.015 6/6/95 6/13/95 0.019 0.017 -0.019 0.017 0.022 6/13/95 6/20/95 0.028 0.027 0.028 0.031 0.029 6/20/95 6/27/95 0.025 0.024 0.029 0.029 0.026 6/27/95 7/5/95 0.021 0.021 0.023 0.022 0.023 i
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l 1995 Annual Radiological Environmental Operating Report f Wolf Creek Generating Station Page 20 of 50
m . - .. .. ._ . _ __ __ _ _.. ..
i TABLE 3 (Cont) 1995 Airborne Particulate Gross Beta Analyses (pci/ cubic meter, analysis error reported in Appendix B)
Date Location Beginning Ending 2 3 32 37 40 Control 7/5/95 7/11/95 0.027 0.023 0.026 0.028 0.027 7/11/95 7/18/95 0.037 0.030 0.035 0.038 0.035 7/18/95 7/25/95 0.024 0.020 0.022 0.023 0.023 7/25/95 8/2/95 0.024 0.020 0.023 0.024 0.024 l 8/2/95 8/8/95 0.017 0.016 0.020 0.017 0.018
{ 8/8/95 8/16/95 0.021 0.024 0.021 0.025 0.023 8/16/95 8/22/95 0.029 0.026 0.029 0.032 0.029 8/22/95 8/29/95 0.043 0.045 0.041 0.046 0.041 8/29/95 9/5/95 0.044 0.043 0.045 0.044 0.039 9/5/95 9/12/95 0.030 0.029 0.029 0.032 0.028 9/12/95 9/19/95 0.037 0.034 0.037 0.039 0.036 9/19/95 9/26/95 0.025 0.022 0.023 0.024 0.021 i 9/26/95 10/3/95 0.044 0.040 0.045 0.043 0.039 10/3/35 10/10/95 0.022 0.019 0.023 0.026 0.025 l 10/10/95 10/16/95 0.035 0.036 0.036 0.040 0.040 i 10/16/95 10/24/95 0.022 0.023 0.020 0.025 0.025 l 10/24/95 10/31/95 *** 0.023 0.021 0.022 0.023 l 10/31/95 11/7/95 0.032 0.036 0.035 0.036 0.032 11/7/95 11/14/95 0.028 0.032 0.035 0.033 0.031 11/14/95 11/21/95 0.036 0.038 0.034 0.038 0.037 11/21/95 11/29/95 0.040 0.036 0.038 0.035 0.034 11/29/95 12/5/95 0.033 0.039 0.043 0.036 0.037 l 12/5/95 12/12/95 0.028 0.031 0.033 0.035 0.033 12/12/95 12/20/95 0.040 0.037 0.040 0.039 0.046 l 12/20/95 12/26/95 0.030 0.034 0.028 0.032 0.037
- 12/26/95 1/3/96 0.040 0.047 0.040 0.043 0.045
- - Unavailable due to pump failure i
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1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 21 of 50
. . . . . - . . . ._ . . . . _ - . . . = . . _ _ . - _ . _ . _ . _ . . . . . . . . . _ . _ _ . _ . . . _ . _.. _ _ . _ . . __ . . . . _ . .
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TABLE 4 1995 Airborne Particulate Quarterly Composite Gamuna Isotopic Analyses (pCi/ cubic meter, analysis error reported in Appendix B)
Location Quarter Be-7 K-40 4
2 1 0.133 3 1 0.157
- 32 1 0.156 l 37 1 0.177 40 1 0.127 0.0130 j 2 2 0.168 4
3 2 0.159 32 2 0.181 0.0087 37 2 0.169
, 40 2 0.180 2 3 0.0855 3 3 0.0680 32 3 0.0900 37 3 0.0941 40 3 0.0727 2 4 0.0611 0.0143
! 3 4 0.0645 1
32 4 0.0590 37 4 0.0648
-40 4 0.0677 4
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1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 22 of 50 i
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I TABLE 5 1995 First and Second Quarter TLD Results (ar/90 day qtr) l 1
First Quarter Second Quarter Location Days 90 Day Error (2 Location Days 90 Day Error (2 Average std dev) Average std dev) 1 92.0 13.4 0.8 1 91.0 18.0 0.6 2 92.1 15.0 1.1 2 90.8 14.3 1.0 3 92.1 14.4 2.3 3 90.9 13.6 1.4 4 92.8 16.1 1.3 4 90.2 14.5 1.6 5 92.8 13.9 1.0 5 90.2 14.3 0.4 6 92.8 16.6 1.1 6 90.2 13.6 0.9 7 92.0 16.5 0.5 7 90.9 13.4 0.9 j 8 92.0 18.1 1.1 8 91.0 17.6 0.6 i 9 92.8 15.6 0.8 9 90.2 15.8 1.3 10 92.8 15.2 3.9 10 90.2 18.2 1.1 11 92.8 18.6 1.3 11 90.2 16.6 0.7 12 92.8 17.0 1.7 12 90.2 16.5 2.1 13 92.8 17.6 0.9 13 90.2 16.5 1.1 l 14 92.8 17.6 2.0 14 90.2 15.4 0.8 15 92.8 18.0 1.7 15 90.2 17.5 3.8 16 92.8 17.5 1.1 16 90.2 15.2 3.2 17 92.8 17.4 1.1 17 90.3 13.5 1.0 1
18 92.8 18.3 1.4 18 91.0 14.5 0.9 19 91.9 17.4 0.4 19 91.0 16.6 1.6 20 91.9 16.3 1.0 20 91.0 16.3 0.8 21 91.9 12.8 1.1 21 91.0 13.6 1.1 22 91.9 15.8 0.6 22 91.0 15.3 0.8 23 91.9 14.9 1.3 23 91.0 14.3 0.4 24 91.9 15.2 0.8 24 90.3 14.2 0.8 25 91.9 12.0 1.4 25 90.3 12.2 0.7 26 91.9 ~ 13.7 2.6 26 90.3 14.4 0.2 27 91.9 14.3 1.4 27 91.0 15.0 2.2 28 92.0 12.4 3.3 28 91.0 12.9 0.8 29 92.0 14.5 3.6 29 90.9 13.1 C.4 30 91.9 15.2 3.3 30 90.3 15.1 0.9 31 31.9 14.0 2.0 31 91.0 14.6 1.0 32 92.0 12.6 0.7 32 90.3 15.5 1.6 33 92.0 16.1 7.0 33 90.3 16.2 1.1 34 91.1 14.9 2.7 34 90.9 15.5 1.6 35 92.1 14.7 2.3 35 90.8 16.3 2.1 36 92.1 15.3 0.8 36 90.8 15.1 0.8 37 92.0 13.2 1.1 37 91.0 14.3 0.5 38 92.0 15.5 2.5 38 91.0 16.0 1.1 39 92.0 14.9 0.9 39 90.9 15.3 0.8 ,
40 91.1 11.6 0.5 40 90.8 13.4 1.2 !
41 92.0 16.4 2.5 41 91.7 17.5 0.8 i
- 42 92.0 10.8 0.6 42 91.0 10.5 3.5
- 43 92.0 9.1 1.1 43 91.0 9.2 0.3 " j 44 92.1 15.8 1.4 44 90.8 15.9 1.0 l
45 91.9 16.0 1.5 45 90.3 18.4 2.3 1
- One TLD 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 23 of 50 l
l 1
__ -. _ _ . - ~ __..___.._m..._ ._-_._ ._._ . _ . _ _ . _ _ - _ _ _ . m - , .__ _ _ _ . . _ _
l TABLE 6 1995 Third and Fourth Quarter TLD Results (ar/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) l- 1 97.9 17.4 0.9 1 84.1 18.7 1.5 l 2 98.0 14.2 1.8 2 84.1 15.8 2.3 I 3 98.1 15.7 1.4 3 84.0 15.2 1.5 4 98.1 18.0 3.9 4 84.0 17.2 3.4 5 98.1 14.6 1.1 5 84.0 15.6 1.6 6 98.1 14.8 2.2 6 84.0 15.5 1.6 l 7 98.9 14.7 0.8 7 83.2 15.6 1.0 8 98.8 18.3 2.8 8 83.2 17.5 2.4 9 98.8 15.6 3.1 9 83.2 15.7 1.5 10 98.8 17.8 3.6 10 83.2 17.2 2.0 l 11 98.8 18.3 2.1 11 03.2 18.0 1.1 5
12 98.1 17.2 2.5 12 84.0 16.2 2.0 13 98.1 16.8 1.8 13 84.0 17.9 3.8 14 98.1 17.8 3.2 14 84.0 16.8 1.4 15 98.1 18.0 4.8 15 84.0 16.0 1.4 i
16 98.1 16.8 0.8 16 84.0 16.7 2.7
! 17 98.8 16.6 1.1 17 84.0- 15.4 1.0 l 18 98.0 18.6 2.9 18 84.0 16.9 1.5 19 98.1 16.8 1.8 19 83.9 16.5 1.9 l 20 98.2 17.4 2.6 20 83.9 18.5 1.4 I 21 98.1 14.2 0.9 21 83.9 15.4 2.1 22 98.0 18.8 3.5 22 83.9 16.2 1.9 l 23 98.0 15.7 3.8 23 83.9 15.4 1.6 24 98.8 15.5 2.4 24 83.9 15.2 1.2 :
25 98.8 13.1 1.4 25 83.9 13.4 1.1 l 26 98.9 14.1 1.4 26 83.9 14.6 1.7 27 98.2 16.2 0.8 27 83.9 18.3 2.0 j 28 98.2 13.4 1.5 28 83.9 13.8 2.0 l 29 98.2 12.8 2.0 29 83.9 13.1 1.4 l 30 98.9 14.7 0.5 30 83.9 15.3 1.3 i 31 79.2 14.7 2.0 31 83.9 15.8 1.7 32 ~38.9 14.2 1.2 32 83.8 15.3 1.2 l 33 98.8 16.4 1.8 33 83.9 18.3 2.8 34 98.1 16.4 1.4 34 84.0 17.8 1.8 35 98.2 16.5 0.7 35 84.0 16.1 1.6 36 98.2 17.4 2.6 36 84.0 16.3 1.6 37 97.8 15.8 1.6 37 84.9 18.0 3.0 38 97.8 19.8 2.1 38 84.9 19.4 2.2 39 98.1 16.9 0.9 39 84.0 17.8 1.6 40 98.2 15.6 1.1 40 84.0 15.5 2.1 41 97.2 16.7 1.3 41 84.1 18.3 1.7
[ 42 97.9 10.2 0.2 42 84.9 12.0 1.3
, 43 97.9 9.7 1.4 43 84.9 11.4 1.4 44 98.0 16.0 1.0 44 84.2 17.4 1.6 45 98.9 15.7 0.6 45 83.9 18.9 1.8 a
i 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 24 of 50
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l 1995 Drinking Water Radiological Analyses (pci/ liter, analysis error reported in Appendix B)
~
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l Location Date Gr-B BW15 1/3/95 6.4 BW15 2/7/95 7.7 BW15 3/7/95 6.6 BW15 4/4/95 5.9 BW15 5/2/95 6.5 BW15 6/6/95 5.8 l BW15 7/5/95 7.9 BW15 8/2/95 7.1 l BW15 9/5/95 8.5 BW15 10/3/95 7.9 BW15 11/7/95 9.4 BW15 12/5/95 9.1 j i LW40 1/3/95 6.3 l LW40 2/7/95 4.8 LW40 3/7/95 7.0 l LW40 4/4/95 6.3
! LW40 5/2/95 4.5 LW40 G/6/95 5.4 LW40 7/5/95 5.1 LW40 8/2/95. 6.8 LW40 9/5/95 7.6 LW40 10/3/95 11 i
LW40 11/7/95 8.6 LW40 12/5/95 7.3 l
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4 1995 Annual Radiological Environmental Operating Report
- Wolf Creek Generating Station Page 25 of 50
, . . . . . . . - - ~ - . . . . . .- . . . . - - _ . . . - . , ~ . - - . - . . . . - . . - . _ . - . , - - . . . _ . . . . . _-
TABLE 8 1995 Surface Water Radiological Analyses (pci/ liter, analysis error reported in Appendix B)
Location Date H-3 DC 1/17/95 9700 DC 2/22/95 11000 DC 3/21/95 9500 DC 4/25/95 12000
, DC 5/16/95 11000 DC 6/20/95 9500 r i
i DC 7/11/95 9700
! DC 8/22/95 8300 DC 9/19/95 9300 DC 10/24/95 12000 l DC 11/21/95 12000 DC 12/20/95 9300 SP 1/17/95 9800 SP 2/22/95 9900 SP 3/21/95 9400 SP 4/25/95 12000 SP 5/16/95 11000 l SP 6/20/95 9600 l
SP 7/11/95 10000 1
SP 8/22/95 8500
I
{
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l 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 26 of 50 l
l TABLE 9 1935 Ground Water Radiological Analyses (pci/ liter, analysis error reported in Appendix B),
1 The occurrence of radioactivity was not detected in 1995 ground water samples.
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TABLE 10 l 1995 Aquatic Plants Radiological Analyses j (pci/kg, wet, analysis error reported in Appendix B)
( Loc Type Date Be-7 K-40 Mn- Co. Co- Nb- Nb- Cs- Ra- Th-54 58 60 95 95/ 137 226 228 zr-l 0 l
DC Algae 5/15 844 2000 16.9 192 118 31.7 20.7 61.9 431 194 l
EEA Arrow- 6/15 183 3700 16.5 243 154 head DC Algae 8/25 570 1430 17.6 68.7 145 47.3 283 154 DC Am 8/25 184 2200 l
ALT Lotus '
I MUDS Pond- 10/11 2190 f weed l
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i 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 27 of 50 t
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TABLE 11 1995 Shoreline Sediment Radiological Analyses (pci/kg, dry, analysis error reported in Appendix B) l l
i Location Date Be-7 K-40 Co-60 Cs-137 Ra-226 Th-228 i DC 5/15/95 8940 115 88.5 1950 1050 l DC 10/18/95 6570 168 207 1340 902 EEA 10/16/95 9140 90.6 1480- 909 JRR 6/23/95 5540 12100 204 1220 507 l
l JRR 10/18/95 8360 4080 1570 l
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l TABLE 12
! 1995 Bottom Sediment Radiological Analyses !
! (pci/kg, dry, analysis error reported in Appendix B) l l
l Loc Date Be-7 K-40 Mn-54 Co-58 Co-60 Cs- Cs- Ra- Th- l 134 137 226 228 l DC 5/15 11100 61.2 220 548 123 400 1720 1020 l
WC&1l 5/30 11000 1750 1090 TH RD WC&1l 10/24 1090 12100 98.1 2510 1200 TH RD DC 10/18 13100 1090 152 623 2080 1540 JRR 10/18 16700 220 2240 1250 i
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I 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 28 of 50
._.___.___.-..._-_..m _ . . - . . _ _ . . ~ - . - . _ _ . _ _ . _ _ _ _ _ _ _ _ _ . _ . _ . _ - - _ . . . _ _ . . . . _
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TABLE 13 1995 Broadleaf Vegetation Radiological Analyses (pci/kg, wet, analysis error reported in Appendix B)
Type Location Date Be-7 K-40 CABBAGE C-1 5/30/95 504 3510 CABBAGE C-1 6/27/95 616 5950 l
CABBAGE C-1 7/25/95 252 4350 CABBAGE C-1 8/29/95 154 3860 CABBAGE C-1 9/26/95 232 3910 i CABBAGE C-1 10/16/95 2600
{ CABBAGE C-1 10/31/95 368 2020 CABBAGE- G-1 7/26/95 546 3120 CABBAGE G-1 8/29/95 310 4760 CABBAGE G-1 9/26/95 318 2750 CABBAGE G-1 10/31/95 154 2740 LETTUCE R-1 -5/30/95 724 4500 LETTUCE R-1 6/27/95 1190 4960 CABBAGE R-1 7/25/95- 217 3970 LETTUCE R-1. 8/29/95 141 6940 CABBAGE S-4 5/30/95 449 .4300 CABBAGE S-4 6/27/95 621 2050 CABBAGE S-4 7/25/95 1050 4910 CABBAGE S-4 8/29/95 569 4520 CABBAGE S-4 9/26/95 484 4310 CABBAGE S-4 10/31/95 258 3160 TABLE 14 1995 Irrigated Crops Radiological Analyses (pci/kg, wet, analysis error reported in Appendix B)
Type Location Date K-40 Comments-SOYBEANS NRD2 10/19/95 15300 CROP WAS NOT IRRIGATED SOYBEANS NRU1 10/26/95 14700 SOYBEANS NRD1 10/26/95 18200 CROP WAS NOT IRRIGATED-CORN NRD2 10/19/95 2710 CROP WAS NOT IRRIGATED CORN NRU1 10/26/95 2800
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4 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 29 of 50 I , .. , , , , _ .. - -.
TABLE 15 1995 Milk Radiological Analyses (pCi/ liter, analysis error reported in Appendix B)
LOC TYPE DATE K-40 S-3 cow- 1/10/95 1570 S-3 cow 2/14/95 1390 i S-3 cow 3/14/95 1310 S-3 cow 4/11/95 1340 S-3 cow 4/22/a5 ,
1400 S-3 cow 5/9/95 1280 S-3 cow 5/23/95 1340 S-3 cow. 6/13/95 1410 S-3 cow 6/27/95 1550 S-3 cow 7/11/95 1360 S cow 7/25/95 1390 S-3 cow 8/9/95 1410 S-3 cow 8/22/95 1420 S-3 cow 9/12/95 1240 S-3 cow 9/26/95 1390 S-3 cow 10/10/95 1460 S-3 cow. 10/24/95 1390 S-3 cov 11/14/95 1460 S-3 cow 11/28/95 1450 S-3 cow 12/12/95 1440 i
i 1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 30 of 50 i
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. , , m, . . . .-. _ _
a wa- y a,.>-L.s,m.1-wen- a wa>-'- - +"
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l TABLE 16 1995 Fish Radiological Analyses l (pci/kg, wet, analysis error reported in Appendix B)
SPECIES LOC DATE K-40 H-3 COMMON CARP JRR 5/10/95 3460 )
CHANNEL CATFISH JRR 5/10/95 3620 CHANNEL CATFISH JRR 10/18/95 3750 i BM BUFFALO JRR 10/18/95 3660 BM BUFFALO UHS 10/11/95 3020 6800 l WALLEYE UHS 10/11/95 3620 7400 l WHITE BASS WCCL-CAUSEWAY 10/11/95 3850 7100 SM BUFFALO WCCL-CAUSEWAY 10/11/95 3430 6300 WHITE CRAPPIE WCCL-DC 4/7/95 3250 9100 COMMON CARP WCCL-DC 5/15/95 3820 7900 FLATHEAD CATFISH WCCL-DC 5/15/95 4820 7300 CHANNEL CATFISH WCCL-DC 10/11/95 3010 6000 WIPER WCCL-DC 10/11/95 4230 6600 SM BASS WCCL-MAIN BODY 5/15/95 3960 5800 CHANNEL CATFISH WCCL-MAIN BODY 5/15/95 3730 7400
- j. FLATHEAD CATFISH WCCL-OUTLET POOL 10/16/95 3400 5100 RIVER CARPSUCKER/SM BUFFALO WCCL-OUTLET POOL 10/16/95 2860 6100 LM BASS WCCL-SE AREA 5/15/95 3970 6900 i
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1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 31 of 50
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TABLE 17 1995 Land Use Census Residence Data TOTAL NO. OF 1994 CLOSEST 1995 CLOSEST POPULATION RESPONSES / RESIDENCE RESIDENCE SECTOR FOR SECTOR HOUSEHOLDS A 12 fl1 A2.6-OXLA1731 A2.6-17TE1520 B 17 7/7 B3.1-QURD1712 B3.1-QURD1712 C 21 11/11 C1.9-16RD1655 C1.9-16RD1655 1
D 12 Eli D2.1-QULA1571 D2.1-QULA1571 E 11 5/5 F1.i-QULA1485 E1.8-QULA1485 l
F 21 13/14 P;.6-14RD1711 F1.6-14RD1711 G 22 10/12 G1.6-QURD1384 G1.6-QURD1384 H 21 6/6 H3.1-12RD1711 H3.1-12RD1711 J 11 All J3.3-OXLA1141 J3.3-OXLA1141 K 1 ill K2 . 6- 12 LA14 39 K2.6-12LA1439 L El 23/23 L2.1-NARD 1339 L2.4-NARD 1339 M AA 16/16 M2.4-14RD1321 M1.6-MARD1441 N 12 li2 N2.6-HW751465 N2.1-15RD1350 P 21 28/28 P2.7-16RD1255 P2.7-16RD1255 Q al 12/12 Q1.4-NALA1574 Q1.4-NALA1574 I R n 3/3 R2.1-NALA1650 R2.1-NALA1650 l
NOTE: Entries underlined indicate changes from the 1994 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. l The number immediately following the first letter designates the distance (in miles) from the powerblock.
l The characters following the dash represent a unique identifier based upon l location address.
The example is in sector A, 1.4 miles from the plant, at 1525 16th Road.
1995 Annual Radiological Environmental Operatjag Report Wolf Creek Generating Station Page 32 of 50
I i
i TABLE 18 1995 Land Use Census Milk and Garden Data 1994 1995 1994 CLOSEST 1995 CLOSEST D/Q MILK MILK GARDEN GARDEN PRODUCING (DEPOSITION ANIMAL ANIMAL PRODUCING BROADLEAF CONSTANT) /
SECTOR BROADLEAF VEGETATION RANKING VEGETATION
, A none none A2.9-17LA1518 A2.61-OXLA1731 1.97E-09/1 1
B none B4.1-OURD1823 B4.2-18RD1758 B3.1-OURD1712 9.05E-10/6 C none none C2.2-16RD1670 C2.2-16RD1670 6.56E-10/8 i
D none none D2.1-QULA1571 D2.1-QULA1571 4.32E-10/15 E none none E1.8-QULA1485 E1.8-QULA1485 7.76E-10/7 F none none F1.8-14RD1730 F1.8-14RD1730 9.39E-10/4 G none G3.6-RERD1150 G1.6-QURD1384 G1.6-QURD13s. 1.55E-09/3 H none none H3.1-12RD1711 H3.1-12RD1711 6.32E-10/9 J none none J3.8-11RD1535 J3.8-11RD1535 4.45E-10/14 K none none K4.1-NARD 1120 K4.1-NARD 1120 3.30E-10/16 L none none L2.6-NARD 1308 L2.6-MARD1309 4.97E-10/13 M none none M2.4-14RD1321 M2.4-14RD1321 6.19E-10/10 N none none N2.6-HW751455 N2.6-HW751455 5.32E-10/12 P none none P4.3-16RD1112 P2.R-MW751534 5.49E-10/11 Q none none Q2.3-MILA1619 Q2.3-MILA1619 9.36E-10/5 R none none R2.1-NALA1650 R2.1-NALA1650 1.94E-09/2 NOTE: Underlined entries indicate changes from the 1994 Land Use Census.
1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 33 of 50
_ .-. . . . . - -. -. ~ .- - _ _ . - ._ _
1 TABLE 19 EPA Interlaboratory Comparison Program 1995 l Environmental Collection Media Nuclide EPA Result (a) Teledyne Brown Deviation Date Engineering (c)
[
Result (b)
! 02-27-95 Water Gr-Beta 5.0 5.0 6.00 t 1.00 0.35 -
l 02-03-95 Water I-131 100.0 10.0 88.33 1 2.31 -2.02 (d) 03-10-95 Water H-3 7435.0 1 744.0 7066.67 1 115.47 -0.86 l 04-18-95 Water Gr-Beta 86.6 10.0 80.33 1 2.52 -1.09 l Co-60 29.0 i 5.0 31.67 1 2.08 0.92 l Cs-134 20.0 1 5.0 19.67 i 1.73 -0.12
[ Cs-137 11.0 1 5.0 11.67 i 1.53 0.23 07-21-95 Water Gr-Beta 19.4 5.0 19.33 i 1.53 -0.02
! 08-04-95 Water H-3 4872.0 1 487.0 4866.67 1 152.75 -0.02 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 d) The normalized deviation marginally exceeded the warning level and an apparent trend in the results appeared. The cause was a probable high bias in the beta counting efficiency. Check source control charts did not indicate any changes in the counting equipment, so the I-131 calibration was suspected. New I-131 calibrations were performed July 3 through 6, i
1995 after receiving a new standard fror the EPA. The intercomparison sample data sheets were recalculated with the new . efficiencies and the average result was in agreement with the EPA (96 pCi/l versus the EPA value l of 100 pCi/1) . The discrepancy in the I-131 efficiency between the current calibration and the previous one (aside from the uncertainty in the standard) appears to be an abnormally low yield in the preparation of the standard for the older calibration which created a high bias in the counter i efficiencies. The bias was less than ten percent, therefore further l- corrective action or revision of previously reported data is not deemed necessary.
l l
l l
1995 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 34 of 50
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1 1 8 i I 1 6 I I I I I I I t 10/11/95 _ l ; ; ; l l l
. , , , , I i ,
I I I t i e i t 6 1 t i 1 e # l 10/11/95 l l , l l l l l t t l l l 4 l l t t i 1 l l l l 1 1 1 I t 4 I i 10/11/95 . l l l , l l l l 1 i 1 . , , , , f I I I e i i e I l i I I I I i 10/11/95 , 9T EMDDIA
l l Appendix A Summary Tables in the format of NRC Radiological Assessment Branch Technical Position Revision 1, November 1979 l I Page A-1
_ _ - - - _ ~ - - . _ - - - _ _ - - - - - - - - _ - _ _ _ _ - - - - - . _ _ _ - _ _ _ _ _ _ q b / $7 2: /-r a G 2 a v s-a J~- ENVIRONMENTAL RADIO 1DGICAL MONfIORING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 Imcation of Facility Coffev County. Kansas Reporting Period Annual 1995 (County, State) Analysis and lower IJmit Number of Medium of Pathway Total Number of All Indicator Locations Imcation with Highesi Annual Mean ControlImcations Nonroutine Sampled ofAnalysis Detection " Mean (f) Name "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measurements" statson No. 40 A1 Particulate Cross (264) 3 27(211/211) 37 2.1 miles NNW 28(53/53) 28(53/53) 0 (X10-3 pCI/Cu.M.) Beta (l1-47) (I l-46) (11-46) I-131 (264) 7 -(0/211) N/A' N/A -(0/53) - y Gamma (20) o.
% Be-7 1 118(16/16) 37 2.1 miles NNW 126(4/4) 112(4/4) 0 (59-181) (65-177) (68-180) rv K-40 24 12(2/16) 2 2.7 miles N 14(1/4) 13(1/4) 0 (8.7-14) -- --
Gamma (4) Sector H Animals K-40 500 3560((3/3) Comp. A & R 3850(1/i) 3700(1/1) 0 (pCl/kg wet) (3060-3850) 1 mile N/NNW -- -- Stations 39 and 40 Extehal TLD (358) 0.013 0.173(342/342) 11 1.6 miles E 0.199(8/8) 0.168(8/8) 0 Radiauon Quarterly (0.109-0.199) (0.183-0.213) (0.127-0.199) (mR/ day) Nominal Lower L.imit of Detection (LLD)
*
- Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parendieses (f)
n, _ . _. - -. ENVIRONMENTAL RADIOLOGICAL MONTIORING PROCRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 Location of Facility Coffer County. Kansas Reporung Period Annual 1995 (County State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator Imcations Incation with Highest Annual Mean ControlImcauens Nonrouune Sampled ofAnalysis Detection " Mean (0 Name "Mean (f) "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measurements"
- 4. Om T _ . :.- ,
Fish Gamma (18) K-40 500 3641(14/14) WCCL - SE Area 3970(1/1) 3623(4/4) 0 (2860-4820) -- (3460-3750 Trinum (18) 300 6843(14/14) WCCIs - DC. 7380(5/5) -(0/4) 0 (5100-9100) (6000-9100) -- u 2 J. Redanomd Reservoir i % Fish Entrails Gamma (2) j 7 (pCl/kg wet) K-40 500 885(1/1) WCCleMain Body 885(1/1) 817(1/1) O
~
ca .. .. ; Triuum (2) 300 7800(1/1) WCCleMain Body 7800(l/1) (0/1) 0 l' l. i s-4 Food and Gamma (21) Garden Crops (pC1/kg wet Be-7 90 409(14/15) S-4 >15 miles WNW 572(6/6) 572(6/6) 0 weight) (141-1190) (258-1050) (258-1050) , K-40 500 4001(15/15) R-12.1 miles NNW 5093(4/4) 3875(6/6) 0 ; (2020-6940) (3970-6940) (2050-4910) 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)
q L, < .; . st s2
.i_T 2 :J 2;; N 1:
ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAIM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.S~IN 50-482 location of Facility Coffev County. Kansas Reporting IYriod Annual 1995 (County, State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator locations Incation with Highest Annual. Mean Control Incations Nonrouune Sampled ofAnalysis Detection " Mean (f) Name "Mean (0 **Mean (f) Reported (Unit of Measurement) Performed (LLD) "Ra nge Distance and Directions " Range " Range Measurements" NRU1 Irrigated Crop Gamma (5) (pC /kg wet weight) K-40 500 12070(3/3) NR-D1 9.2 miles S 18200(1/1) 8750(2/2) 0 (2710-18200) -- (2800-14700) o Os D tD 2n i 4 I l Nominal imwer Limit of Detection (LLD)
' Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
I
.q b . ' g c/ CD G 3 G 13 %
ENVIRONMENTAL RADIOLOGICAL MONflVRING PROGRAM
SUMMARY
Name of Facility Wolf Cneek Ninetaar Docket No.S'IN 50-482 Incation of Facility Coffer County. Kan=== Reporting Period Annual 1995 (County, State) Analysis and lower Limit Number of ! Medium of Pathway Total Number of All Indicator Imcations Imrathn with Hishest Anne ==1 Mean ControlImcations Nonroutine ' Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (0 Reported (Unit of Measurement) Performed (LLD) *
- Ra nge Distance and Directions " Range " Range Measuremente** 3 Station S 3 Milk I-131 (20) 3 -- --
-(0/20) 0 [
(pCl/II Gamma (20) K-40 100 -- -- 1400(20/20) 0 y (1240-1570) as to ro ! I M i u, l r l
?
Nominal Imwer Limit of Detection (11D) f
** Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f) I l
1.
,q x / G u CD - G 2 01; ;;.8 I ENVIRONMEIRAL RADIOLOGICAL MONfIORING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 location of Facility Coffev County. Kansas Reporting Period Annual 1995 (County, State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator Imcations Incation with Hinhest Annual Mean control locations Nonrouune Sampled ofAnalysis Detection ** Mean (f) Name **Mean (0 **Mean (O Reported (Unit of Measurement) Performed (LLD) **Ra nge Distance and Directions ** Range ** Range Measurements ** No Control Soll Gamma (4) (pcs/kg dry weight) He-7 300 1680(1/4) EEA 1680(1/2) -- 0 3.0 miles NNW -- K-40 500 12400(4/4) EEA 12600(2/2) -- 0 (11200-13400) 3.0 miles NNW (l1800-13400)
- EEA Cs- 137 60 185(3/4) 236(2/2) --
0 (82-260) 3.0 miles NNW 7 _- a3 Ra-226 500 1993(4/4) MUDS. 2105(2/2) -- 0 (1520-2340) 1.5 miles WNW (1870-2340)-- Th-228 40 1213(4/4) MUDS 1315(2/2) -- 0 (1060-1350) 1.5 miles WNW (1280-1350) Nominal lower Limit of Detection (LLD) i
' Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
.q rr.,/ 5 D - C G U IG .u.;4 r ENV1RONMEffrAL RADIOIDGICAL MONTIORING PROGRAM
SUMMARY
Name of Facility Wolf Cnek Nuclear Docket No.S'IN 50-482 6 location of Facility CoNew County. Kan=== Reporting Period Annual 1995 (County, State) 1 Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator locations location with liighest Annual Mean Controllocations Nonrouune Sampled ofAnalysis Detection " Mean (0 Name "Mean (f) "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measurements" 1 Station No.JRR Shoreline Soll Gamma (5) (pCl/kg dry weight) Be-7 300 -(0/3) JRR 4 miles W 5540(1/2) 5540(1/2) K-40 500 8217(3/3) JRR 4 miles W 10230(2/2) 10230(2/2) 0 (6570-9140) (8360-12100) (8360-12100) Co-60 30 142(2/3) DC 0.6 miles WNW 142(2/2) -(0/2) 0
* (115-168) (115-168) --
2> O Cs-137 60 129(3/3) DC 0.6 miles WNW 148(2/2) 204(1/2) 0 (89-207) (89-207) -- Ra-226 500 1590(3/3) JRR 4 miles W 2650(2/2) 2650(2/2) 0 (1340-1950) (1220-4080) (1220-4080) Th-228 40 954(3/3) JRR 4 miles W 1039(2/2) 1039(2/2) 0 (902-1050) (507-1570) (507-1570)
- Nominal lower Limit of Detection [11DI
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (0
.q u / 5 D-ta a 3G.d44r -
ENVIRONMElfrAL RADIOIDGICAL MONITORING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 location of Facility Coffey County. Kan- Reporting Period Annual 1995 ; (County. State)
~
{ l Analysis and lower Limit Number of ! Medium of Pathway Total Number of All Indicator Imcations location with Highest Annual Mean ControlImcations Nonroutine a Sampled ofAnalysis Detection Mean (f) Name **Mean (f) **Mean (f) Reported ; (Unit of Measurement) Performed (LLD) **Ra nge Distance and Directions " Range. **Ranste Measurements" ' Station No.JRR ' i Sediment / Silt Gamma (5) ! (pCi/kg i dry weight) Be-7 300 1090(1/4) WC & 1Ith Road 1090(1/2) -(0/1) 0 l 3.8 miles S -- -- K-40 500 .11825(4/4) JRR 4 miles W 16700(1/1) 16700(1/1) 0 (11000-13100) -- -- o . g Co-58 20 220(1/4) DC 0.6 miles WNW 220(1/4)
-(0/1) 0 [
g t 7 Mn-54 30 61(1/4) DC 0.6 miles WNW 61(1/2) -(0/1) 0 [ g -- -- 1 Co-60 20 819(2/4) DC 0.6 miles WNW 819(2/2) -(0/1) 0 l (548-1090) (548-1090) -- Cs-134 60 138(2/4) DC 0.6 miles WNW 138(2/2) -(0/1) O (123-152) (123-152) - l Cs-137 60 374(3/4) DC 0.6 miles WNW 512(2/2) 220(1/1) 0 . (98-623) (400-623) --
- Ra-226 500 2015(4/4) JRR 4 miles W 2240(l/1) 2240(l/1) 0 i (1720-2510) -- --
Th-228 40 1213(4/4) DC 0.6 miles WNW 1280(2/2) 1250(1/1) 0 , (1020-1540) (1020-1540) -- - i l 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 (I) i
)
_m.,___.m___ ____.__________.m .m_ __.m___ __ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ . ,__ - __ _ w
-: L. / 5 W C G .G 2 :' 1; M ;E ;
i ENVIRONMENTAL RADIOLOGICAL MONTIDRING PROGRAM
SUMMARY
Name of Facility Wolf Creek Noclear Docket No.STN 50-482 Location of Facility Coffev County. Kansas Reporting Period Annual 1995 (County, State) I Analysis and lower Limit Number of j Medium of Pathway Total Number of All Indicator locations location with Hiahest Annual. Mean Control Locations Nonrouune i Sampled ofAnalysis Detection " Mean (f) Name "Mean (f) **Mean (f) Reported l (Unit of Measurement) Performed (LLD) "Ra nge Distance and Directions " Range " Range Measurements" ! No Control ; Vegetation Aquatic Gamma (5) , (pC1/kg ; wet weight) Be-7 100 445(4/5) DC 0.6 miles WNW 707(2/2) -- 0 [ (183-844) (570'-844) ' K-40 500 2304(5/5) EEA 3 miles NNW 3700(1/1) -- 0 ! [
~
(1430-3700) -- o en Mn-54 40 17(2/5) DC 0.6 mues WNW 17(2/2) -- 0 { 7 (17-18) (17-18) [ D i Co-58 10 130(2/5) DC 0.6 miles WNW 130(2/2) -- 0 (69-192) (69-192) Co-60 10 132(2/5) DC 0.6 miles WNW 132(2/2) -- O (118-145) (118-145) l t Nb-95 7 32(1/5) DC O.6 miles WNW 32(1/2) -- 0 i Nb-95/Zr-95 10 21(1/5) DC 0.6 miles WNW 21(1/2) O Cs-137 10 42(3/5) DC 0.6 miles WNW 55(2/2) -- 0 - (17-62) (47-62) ! r Ra-226 200 319(3/5) DC 0.6 miles WNW 357(2/2) - 0 (243-431) (283-431) Th-228 20 '167(3/5) DC 0.6 miles WNW 174(2/2) -- 0 (154-194) (154-194) Nominal inwer Limit of Detection (ll.D] k
" Mean and range based upon detectable measurements only. Fraction of detectable measuremems at specified locations is Indicated in parentheses (f) i i - .--.___--.____.__--_.__-___-._______._______-______-_-_-_________-__-_-._-_-___a-
_ - _ _ _ - - - - _ - _ _ _ - - _ _ - - - _ _ - - . r_- - - - - _ a _,
qs;-G.5-cc a 70 u t4 r ENVIRONMElfrAL RADIOLOGICAL MONfIURING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 location of Facility Coffev County. Kansas Reporting Period Annual 1995 (County. State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator locations location with Highest Annual Mean Control locations Nonroutine Sampled oIAnalysis Detection " Mean (f) Name "Mean (f) "Mean (0 Reported (Unit of Measurement) Performed (LLD) "Ra nge Distance and Directions " Range " Range Measurements" No control Vegetation Terrestrial Gamma (4) (pct /kg wet weight) Be-7 100 2270(4/4) MUDS 3080(2/2) -- 0 (1390-3120) 1.5 miles WNW (3040-3120) K-40 500 4943(4/4) EEA 3 miles NNW 5420(2/2) -- 0 2 to (3800-7040) (3800-7040) e a o Nominal Lower Limit of Detection (U D)
' Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (!)
.q ;_, / ; p E n a 30 gia r ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 location of Facility Coffev County. Kansas Reporting Period Annual 1995 (County, State) Analysis and Lower Limit Number of Medium of Pathway Total Number of All Indicator locations location with Highest Annual Mean Control locations Nonrouune S.impled ofAnalysis Detection " Mean (f) Name "Mean (0 "Mean (f) Reported (Unit of Measurement) Performed (LLD) "Ra nge Distance and Directions " Range " Range Measurements" BW-15 , Water I-131 (24) 0.5 -(0/12) NA NA -(0/12) O t Drinking (pCl/l) Gross (24) 2 6.7(12/12) HW-15-3.9 miles SW 7.4(12/12) 7.4(12/12) O ; Beta (4.5- 11) (5.8-9.4) (5.8-9.4) Gamma (24) --
-(0/12) NA NA -(0/12) 0 g Tritium (8) 1000 -(0/4) NA NA -(0/4) 0 o .. .. __
co S B-12/F-20 Water I-131 (20) 0.5 -(0/12) NA NA -(0/8) 0 Ground -- -- (pCl/1) Gamma (20) K-40 100 -(0/12) NA NA -(0/8) 0 Triuum (20) 1000 -(0/12) NA NA -(0/8) O I i Nominal Lower Limit of Detection (11D)
" Mean and range based upon detectable measun ments only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
q 6 - G C: C C G .2 O v L4 : ENVIRONMENTAL RADIOLOGICAL MONTIURING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 location of Facility CoITev County. Kansas Reporting Period Annual 1995 (County, State) Analysts and Lower Limit Number of Medium of Pathway Total Number of All Indicator locations Location with Illahest Annual Mean Control Imcations Nonroutine Sampled ofAnalysis Detection " Mean (f) Name "Mean (0 **Mean (0 Reported (Unit of Measurement) Performed (LLD) "Ra nge Distance and Directions ** Range " Range Measurements" Mush Water Surface Gamma (36) (pCl/l) K-40 60 -(0/24) N/A N/A -(0/12) 0 Tritium (36) 1000 10229(24/24) DC 0.6 miles WNW 10275(12/12) -(0/12) 0 y (8300-12000) (8300-12000) -- to CD t a ru 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)
c l l 4 1 i l l Appendix B l 1995 Individual Sample Results l \ l i 1 I t I 1 l l l l i j i i i 1 l i l i l l I I I Page B-1
4
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/ / / / / / /// / / / / / / / /
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WOLF CREEK NUCLEAR OPERATING CORPORATION AIR PARI 1CUIEIE AND CHARCOAL FIL'IERS STATION NUMBER 02 COLLECTION DNIE MID COUNT A P FILTER MID COUNT CllARCOAL FILTER START STOP TIME GROSS DETA TIME I-131 DATE DATE VOLUME UNITS DA'IE (pC1/Cu.M.) DATE (pCI/Cu.M.) 08/22 08/29 3.20E 08 OC 09/08 4.310.4 E-02 09/02 LT. 2. E-02 08/29 09/05 3.00E 08 OC 09/13 4.4 i 0.4 E-02 09/09 LT. 2. E-02 09/05 09/12 3.00E 08 OC 09/19 3.0 i O.3 E-02 09/16 LT. 2. E-02 09/12 09/19 3.00E 08 OC 09/27 3.7 i O.4 E-02 09/26 LT. 3. E-02 09/19 09/26 3.lOE 08 OC 10/04 2.5 i 0.3 E-02 09/30 LT. 2. E-02 09/26 10/03 2.90E 08 OC 10/11 4.4 i 0.4 E-02 10/10 LT. 3. E-02 10/03 10/10 3.00E 08 OC 10/15 2.2 i 0.3 E-02 10/12 LT. 2. E-02 e 10/10 10/16 2.50E 08 OC 10/21 3.510.4 E-02 10/21 LT. 3. E-02 10/16 10/24 3.40E 08 OC 10/30 2.210.3 E-02 10/28 LT. 1. E-02 10/24 10/31* 4.210.7 E 00 LT. 5. E 00 10/31 11/07 3.00E 08 OC 11/14 3.2 i O.3 E-02 11/11 LT. 2. E-02 11/07 11/14 2.80E 08 OC 11/20 2.810.4 E-02 11/18 LT. 2. E-02 11/14 11/21 3.00E 08 CC 11/29 3.6 i 0.3 E-02 11/28 LT. 3. E-02 11/21 11/29 3.50E 08 OC 12/05 4.010.4 E-02 12/03 LT. 2. E-02 11/29 12/05 2.60E 08 OC 12/10 3.310.4 E-02 12/09 LT. 2. E-02 12/05 12/12 3.00E 08 OC 12/18 2.8 i 0.3 E-02 12/15 LT. 2. E-02 12/12 12/20 3.50E 08 OC 12/28 4.0 i 0.3 E-02 12/27 LT. 2. E-02
- 12/20 13/26 2.70E 08 OC 01/?O 3.010.4 E-02 12/29 LT. 2. E-02 ,
- TOTAL PCI
, t . _ _ .__. ._ _ ._ . . . .
.q s - g c ,.E.a g H G :: M. r WOIE CREEK NUCLEAR OPERATING CORPORATION AIR PAIU1CULATE AND CIIARCOAL FILTERS STATION NUMBFR 02 l
COLLEC110N DATE MID COUNT A P FIL'IER MID COUNT CHARCOAL FIL'IER START STOP TIME GROSS BETA TIME l-131 !
-DATE DATE VOLUME UNITS DATE (pCl/Cu.M.) DATE (pC1/Cu.M.)
12/26 0I/03 3.40E 08 CC 01/13 4.010.4 E-02 01/07 LT. 2. E-02 L i P 7 Cu O (D CD E U1 t t' l I
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/
k T N . q U 6 2 0 7 3 9 6 61 5 71 9 6 3 4 0 6 3 - O EE 0 1 2 2 0 0 2 0 0 1 2 2 3 0 1 CMTA I
/
1
/ 1/ / 1/ / 1 / / / / / / / / / / /
2 2 2 2 2 3 3 3 3 3 3 4 4 DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 MI N O A 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 I T S R ET) . E E E E E E E E E E E E E E E E E A R E T BM. 4 4 4 3 4 3 3 3 3 3 3 3 3 3 3 3 3 R O E T LSu I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 P L FSC i i 1 i i i R 7 O1/ 1 1 i i 1 i i 1 1 1 1 O 1 P RC 0 7 6 4 I. 8 4 2 4 9 8 3 9 8 9 4 4 L A G (p 4 3 3 2 4 1 2 2 2 1 2 2 2 2 2 2 C G O 0 A 3 1 N C T R R _ I A A E R IC MB I E P O D N N U T N R A N U A E ET O I O EE 0 9 6 1 1 2 0 0 1 7 3 1 9 91 8 61 2 0 6 7 21 9 5 2 0 2 2 2 0 0 1 L C L AT A CMTI A / 1
/ /
1
/ /
1
/ /
2 2
/ / / / / / / / / /
2 2 2 2 3 3 3 3 3 4 4 4 U U T DTD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N C S I M _ K U E R E A R P C R - F I L A O S - W T . I N C C C C C C C C C C C C C C C C C O O O O G C O O C O C O O O O O C 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 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 9 0 8 0 9 0 0 0 8 9 9 9 9 0 0 0 - V 3 2 3 2 2 2 3 3 3 2 2 2 2 2 3 3 3 3 0 7 4 1 7 4 4 8 7 4 1 8 4 1 EPE 0 1 1 2 3 0 1 1 1 2 2 0 1 2 2 2 0 1 1 _ TOT ATA / / / / / / / / / / / / / / / / / 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 s DSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 i s y . l a N n O A H
' t e
C *
- a E RE T 7 3 0 7 4 1 7 7 4 1 8 7 4 4 1 8 4 ic l
I 2 0 1 1 2 3 0 0 1 2 2 0 1 1 2 2 0 p LAT / / / / / / / / / / / / / / / / / u OTA 2 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 D CSD 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 * { o'
- q u ," 3 cs- E a :1 a a v w 1-WOIX CREEK NUCLEAR OPERATING CORPOHATION '
AIR PARUCULATE AND CHARCOAL FILTERS STATION NUMBER 03 COllECHON DATE MID COUNT A P FIL'IER MID COUlTI' CHARCOAL MLTER START STOP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS DA~IE (pCl/Cu.M.) DATE (pCl/Cu.M.) 04/11 04/18 2.90E 08 OC 04/23 2.210.3 E-02 04/21 LT. 3. E-02 04/1l' 04/18 2.90E 08 OC 04/23 2.0 i 0.3 E-02 04/22 LT. 2. E-02 ; 04/18 04/25 2.90E 08 OC 05/01 1.5 i 0.3 E-02 04/27 LT. 2. E-02 04/25 05/02 2.90E 08 OC 05/07 1.6 i 0.3 E-02 05/05 LT. 3. E-02 y 05/02 05/09 2.90E 08 OC 05/15 1.4 i 0.3 E-02 05/13 LT. 2. E-02 ! 05/09 05/16 2.90E 08 OC 05/22 1.4 i 0.3 E-02 05/20 LT. 3. E-02 co 05/16 05/23 2.90E 08 OC 05/30 2.010.3 E-02 05/27 LT. 3. E-02
" 2.90E 08 05/23 05/30 OC 06/06 1.1 i 0.2 E-02 06/03 LT. 2. E-02 05/30 06/06 2.90E 08 OC 06/13 1.2 i 0.3 E-02 06/10 LT. 2. E-02 06/06 06/13 3.00E 08 OC 06/19 1.7 i 0.3 E-02 06/17 LT. 2. E-02 06/13 , 06/20 2.90E 08 OC 06/26 2.7 i 0.3 E-02 06/24 LT. 2. E-02 06/20 06/27 2.90E 08 OC 07/06 2.4 i O.3 E-02 07/01 LT. 2. E-02 06/27 07/05 3.50E 08 OC 07/14 2.1 i 0.3 E-02 07/12 LT. 2. E-02 07/05 07/11 2.50E 08 OC 07/20 2.310.3 E-02 07/16 LT. 3. E-02 07/11 07/18 2.90E 08 OC 07/24 3.010.3 E-02 07/20 LT. 2. E-02 07/18 07/25 3.10E 08 OC 08/02 2.0 i 0.3 E-02 07/29 LT. 3. E-02 07/25 08/02 3.40E 08 OC 08/10 2.010.3 E-02 08/08 LT. 1. E-02 08/02 08/08 2.70E 08 OC 08/16 1.6 i 0.3 E-02 08/12 LT. 3. E-02
- Duplicate Analysis
a 6 <- 5 z ,< C;.:i a 2 -J s; ;-.; I WOIF CREEK NUCLEAR OPERATING CORPORATION AIR PARI 1CULA'IE AND CIIARCOAL FIL'IERS STATION NUMBER 03 COLLECIlON DAE MID COUNT A P FIL1ER MID COUNT CHARCOAL FILER START S1DP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS DATE (pCI/Cu.M.) DATE (pC1/Cu.M.) 08/08 08/16 3.40E 08 OC 08/25 2.410.3 E-02 08/21 LT. 3. E-02 08/16 08/22 2.50E 08 OC 08/29 2.6 i 0.4 E-02 08/26 LT. 2. E-02 08/22 08/20 3.00E 08 CC 09/08 4.5 i 0.4 E-02 09/02 LT. 2. E-02 08/29 09/05 2.90E 08 CC 09/13 4.310.4 E-02 09/09 LT. 2. E-02 09/05 09/12 3.00E 08 OC 09/19 2.9 i 0.3 E-02 09/16 LT. 2. E-02 o 09/12 09/19 3.00E 08 OC 09/27 3.4 i 0.3 E-02 09/26 LT. 3. E-02 m 09/19 09/26 3.10E 08 OC 10/04 2.2 i 0.3 E-02 09/30 LT. 2. E-02 09/26 10/03 3.00E 08 OC 10/11 4.010.4 E-02 10/10 LT. 3. E-02 10/03 10/10 3.00E 08 OC 10/15 1.9 i 0.3 E-02 10/12 LT. 2. E-02 10/10 10/16 2.60E 08 CC 10/21 3.610.4 E-02 10/21 LT. 3. E-02 10/16 10/24 3.50E 08 OC 10/30 2.310.3 E-02 10/28 LT. 1. E-02 10/24 10/31 3.10E 08 CC 11/05 2.3 i 0.3 E-02 11/03 LT. 2. E-02 10/24* 10/31 3.10E 08 CC 11/05 2.6 i 0.3 E-02 11/04 LT. 9. E-03 10/31 :I/07 3.00E 08 OC 11/14 3.6 i 0.3 E-02 11/11 LT. 2. E-02 11/07 11/14 2.80E 08 OC 11/20 3.2 i 0.4 E-02 11/18 LT. 2. E-02 11/14 11/21 2.90E 08 OC 11/29 3.8 i 0.4 E-02 11/28 LT. 3. E-02 11/21 11/29 3.30E 08 OC 12/05 3.6 i 0.4 E-02 12/03 LT. 2. E-02 11/29 12/05 2.50E 08 OC 12/10 3.9 i 0.4 E-02 12/09 LT. 2. E-02
- Duplicate Analysis
-Q u / *H C. - E D G20UNr WOIF CREEK NUCI2AR OPERATING CORPORATION AIR PARUCUIATE AND CHARCOAL FILTERS STATION NUMBER 03 COLLEC'IlON DATE MID COUNT A P FILTER MID COUNT CHARCOAL FILTER START STOP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS DA1E (pCl/Cu.M.) DATE (pct /Cu.M.)
12/05 12/12 3.00E 08 OC 12/18 3.1 i 0.3 E-02 12/15 LT. 2. E-02 12/12 12/20 3.40E 08 OC 12/28 3.7 i 0.3 E-02 12/27 LT. 2. E-02 12/20 12/26 2.60E 08 OC 01/10 3.4 i 0.4 E-02 12/29 LT. 2. E-02 12/20 01/03 3.30E 08 OC 01/13 4.7 i 0.4 E-02 01/07 LT. 2. E-02 o D C (D CC) f O _ _ . _ _ _ _ _ _ . . _ _ _ _ . _ _ . _ _ _ . _ _ _ _ _ ._____m __.__ _ _ _ _ _ _ _ _ _ . _ _ . _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _
c7L gC-c0 :7. a ...! :z: 4 a .r WOtX CREEK NUCLEAR OPERATING CORPORATION AIR PARUCULKIE AND CIIARCOAL FIL'IERS STA'I1ON NUMBER 32 COLLECTION DATE MID COUNr A P FIL'IER MID COUNT CHARCOAL FILTER START STOP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS DA~IE (pCi/Cu.M.) DATE (pC1/Cu.M.) 12/27 01/03 3.00E 08 OC 01/10 4.310.4 E-02 01/06 LT. 2. E-02 O1/03 01/10 3.00E 08 OC 01/19 4.010.4 E-02 01/12 LT. 2. E-02 01/10 01/17 3.10E 08 (E O1/26 3.7 i 0.3 E-02 01/20 LT. 1. E-02 01/10* 01/17 3.10E 08 OC 01/20 3.4 i 0.3 E-02 01/21 LT. 1. E-02 01/17 01/24 2.90E 08 OC 02/01 2.2 i 0.3 E-02 01/27 LT. 2. E-02 2 01/24 01/31 3.00E 08 CC 02/07 4.310.4 E-02 02/03 LT. 2. E-02 01/31 02/07 2.90E 08 OC 02/13 1.9 i O.3 E-02 02/09 LT. 2. E-02 m ' 02/14 3.00E 08 L T. 1. E-02 02/07 OC 02/19 2.210.3 E-02 02/16 02/14 02/21 3.00E 08 OC 02/28 2.4 i 0.3 E-02 02/25 LT. 2. E-02 02/21 02/28 3.10E 08 OC 03/06 2.010.3 E-02 03/07 LT. 3. E-02 02/28 03/07 3.10E 08 OC 03/12 2.9 i 0.3 E-02 03/09 LT. 2. E-02 03/07 03/14 3.20E 08 OC 03/20 3.110.3 E-02 03/16 LT. 2. E-02 03/14 03/21 3.00E 08 OC 03/26 2.9 i 0.3 E-02 03/23 LT. 2. E-02 03/21 03/28 3.20E 08 OC 04/02 2.0 i 0.3 E-02 03/30 LT. 2. E-02 03/28 04/04 3.20E 08 OC 04/09 2.6 i 0.3 E-02 04/06 LT. 2. E-02 ~ 04/04 04/11 3.20E 08 OC 04/15 2.3 0.3 E-02 04/13 LT. 2. E-02 04/11 04/18 3.10E 08 OC 04/23 2.1 i 0.3 E-02 04/21 LT. 2. E-02 04/18 0-4/25 3.10E 08 OC 05/01 1.5 i 0.3 E-02 04/27 LT. 2. E-02
*Duplimte Analysis
F! : il !i' ! ! f : ' < i
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G L . 2 0 2 0 2 0 2 0 2 0 2 0 2 0 2 0 2 0 2 0 2 0 2 02 0 2 0 2 0 2 0 2 0 2 I F M. 0 - - - - - - - - - - - - - - - - - L 1 u C A13C E E E E E E E E E E E E E E E E E E C O/ I 3 2 2 3 2 2 2 2 2 2 2 3 2 3
- 1. 3 2 2 C ICp
- R (
T. T. T. T. T. T. T. T. T. T. T. T. T.
.- A T. T. T. T. T.
8 H C L L L L L L L L L L L L L L L L L L 7 . 5
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G T i N t U 5 3 10 7 3 0 7 4 1 2 3 6 10 9 8 2 6 OEE 0 2 2 0 1 1 2 0 1 1 2 2 0 1 1 2 2 CMTA I
/
5 5 5 / / / / /5
/ / / / / /
6 6 6 6 7 7 7 7 7 7 8 8 8 8
/ / / / / /
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 I A 0- 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 . 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 3 2 3 3 2 3 3 3 3 3 3 3 3 3 3 3 3 4 - R O EI LSu 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 0 0 - F SC
' I P L I Oi/ i i i i 1 i i i i i i i i 1 1 i 1 1 R F PRC 6 2 6 0 1 4 9 8 9 3 2 6 5 2 3 0 9 -
O L A G (p 2 1 C A 2 1 1 1 1 1 1 2 2 2 2 2 3 2 2 2 2 2 G O 3 N C T R R I A A E R i l B E C M P O N D U N R A N U A U
~E 0 7 5 1 2 0 6 3 9 6 61 4 14 0 4 2 0 6 5 9 2 I 1 OEE 0 2 3 0 2 0 1 1 2 2 0 1 1 2 2 C LA TA I
CMTI A / / / / / / / / / / / / / / / / / / 5 5 5 5 6 6 6 6 7 7 7 7 7 8 8 8 8 8 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 K 1 I E R E A R P C R X A I I O S W T I N C O OC O CO C O OC OCO CO C O OC OCO C O O C OC C C C E C 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 E E E E E E E E E E E E E E E E E E L 0 O 0 0 0 0 0 01 O 0 0 0 0 0 0 0 0 0 O 9 l. 2 0 0 0 0 O. 4 4 6 0 1 4 7 7 5 V 2 3 3 3 3 3 3 3 3 3 3 2 3 3 3 2 3 2 EPE 2 9 6 3 10 6 3 0 7 5 5 1 8 5 2 8 6 2 0 0 2 3 0 1 2 2 0 0 1 1 2 0 0 1 2 TOT / / / / / / / / / / / / / / / / / / ATA DSD 5 5 5 5 5 6 6 6 6 7 7 7 7 7 8 8 8 8 i s s . 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 - ly a _ N n _ O A - l I t e C a - ET 5 2 9 6 3 0 16 3 0 7 7' 5 8 5 2 8 6 ic LRE 2 0 0 2 3 0 1 2 2 2 0 1 1 1 2 0 0 1 lp LAT / / / / / / / / / / / / / / / / / / u OTA 4 5 5 5 5 5 6 6 6 6 6 7 7 7 7 8 8 8 D CSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ' [* m8 ,-
q c. . - g u c a G J a u y4 r WOtX CREEK NUCLEAR OPERATING CORPORATION AIR PAR 11CUIATE AND CilARCOAL FIL'IERS STATION NUMBER 32 COLLECI1ON DA'IE MID COUNT A P FIL'IER MID COUNT CilARCOAL FILTER START STOP TlME GROSS BETA TIME l-131 DATE DATE VOLUME UNITS DATE (pCl/Cu.M.) DATE (pCl/Cu.M.) 08/22 08/29 3.10E 08 OC 09/08 4.1 i 0.4 E-02 09/02 LT. 2. E-02 08/22* 08/29 3.10E 08 (I' 09/08 4.4 i O.4 E-02 09/06 LT. 2. E-02 08/29 09/05 2.90E 08 OC 09/13 4.5 i 0.4 E-02 09/09 LT. 2. E-02 09/05 09/12 3.00E 08 OC 09/19 2.9 i 0.3 E-02 09/16 LT. 2. E-02 09/12 09/19 3.00E 08 CC 09/27 3.7 i 0.4 E-02 09/26 LT. 3. E-02 2 09/19 09/26 3.10E 08 OC 10/04 2.3 i 0.3 E-02 09/30 LT. 2. E-02 e 09/26 10/03 2.90E 08 OC 10/11 4.5 i 0.4 E-02 10/10 LT. 3. E-02
' 2.3 t o.3 E-02 10/12 10/03 10/10 3.10E 08 OC 10/15 LT. 2. E-02 N
10/10 10/16 2.60E 08 OC 10/21 3.6 i 0.4 E-02 10/21 LT. 3. E-02 10/16 10/24 3.50E 08 OC 10/30 2.010.3 E-02 10/28 LT. 1. E-02 10/24 10/31 3.10E 08 CC 11/05 2.1 i 0.3 E-02 11/03 LT. 2. E-02 10/31 11/07 3.00E 08 (E 11/14 3.5 i 0.3 E-02 11/11 LT. 2. E-02 11/07 11/14 2.80E 08 CC 11/20 3.510.4 E-02 11/18 LT. 2. E-02 11/14 11/21 3.10E 08 OC 11/29 3.410.3 E-02 11/28 LT. 3. E-02 11/21 11/29 3.50E 08 OC 12/05 3.8 i 0.4 E-02 12/03 LT. 2. E-02 11/29 12/05 2.60E 08 (E 12/10 4.3 i 0.4 E-02 12/09 LT. 2. E-02 12/05 12/12 3.00E 08 OC 12/18 3.310.3 E-02 12/15 LT. 2. E-02 12/12 12/20 3.50E 08 OC 12/28 4.010.3 E-02 12/27 LT. 2. E-02
- Duplicate Analysis
- q b / 5.r - C O G H 01) #4.E WOlE CREEK NUCLEAR OPERATING CORPORA 110N AIR PART1CULATE AND CIIARCOAL FILTERS STATION NUMBER 32 COLLEC110N DATE MID COUlVT A P FILTER MID COUNT CHARCOAL FILTER START STOP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS DA'IE (pCl/Cu.M.) DATE (pct /Cu.M.)
12/20 12/26 2.70E 08 OC 01/10 2.8 i 0.4 E-02 12/29 LT. 2. E-02 12/26 01/03 3.40E 08 CC 01/13 4.010.4 E-02 01/07 LT. 2. E-02 o O (Q (D 03 8 e W
! ' l 4
L n J-3 R E a I L'
) .
2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 H1 M. u 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 a L A13C E E E E E E E E E E E E E E E E E E C O/ CIC t 2 2 1 2 2 2 1 2 4 2 2 2 2 2 2 2 2 2 R ( p A T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T.
- r. H C
L L L L L L L L L L L L L L L L L L _ g k r f q: l U O EE 6 0 21 0 272 3 0 09 0 5 7 9 2 00 0 1 3 0 6 3 5 2 3 0 1 7 1 2 2 CMTAl
/
1 / / / 1 1
/1 / / / / / / / / / / / / /
2 2 2 2 3 3 3 3 3 4 1 4 1 4 4 4 DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 M N 2 O I RT). A- 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 - - - - - T S E E E E E E E E E E E E E E E E E E E A R E T B M. 3 4 3 3 4 R 3 3 3 3 3 3 3 3 3 3 3 3 3 O 'E I LSu I FSC 0 0 0 0 0 0 0 O 0 0 0 0 0 0 0 0 0 0 P L R F I Ol/ 1 i i i 1 i 1 i i 1 i 1 i i 1 1 i 1 O PRC 7 9 5 2 5 7 0 3 9 8 6 7 9 2 3 1 9 0 L A G (p 3 3 3 2 4 2 2 2 2 2 C A 7 G O 3 1 1 1 2 2 2 1 2 N C T R R I A A E R I I B E C M P D U O N N T R A N N A E O U 0 9 6 1 7 3 9 81 6 220 0 6 12 9 5 7 3 E I O EE 1 1 2 0 0 1 ALT 2 2 0 0 1 1 1 2 0 L C TA CMT l A / 1
/ 1 / /I / /2 2/ / / / / / / / / / / /
2 2 2 3 3 3 3 4 4 4 4 4 5 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 T I E I E A R P C R X 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 C U O O O O C O O O O O O O O C O O C O 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 0 0 0 0 0 0 0 0 0 0 0 O 0 9 2 9 0 9 0 0 0 0 0 0 0 0 1 1 0 0 V 3 2 3 2 3 2 3 3 3 3 3 3 3 3 3 3 3 3 3 0 7 4 7 8 7 4 EPE 0 1 1 2 3 0 1 4 1 1 2 2 0 1 1 2 8 2 0 4 1 1 1 1 8 5 1 2 TO' I
/ / / / / / / / / / / / / / / / / /
ATA 1 1 1 1 1 2 2 2 2 3 3 3 3 4 4 4 4 4 s DSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 i s y l a N n O A l I t e C a ET LRE 7 3 0 7 4 1 7 4 1 8 7 4 1 8 4 4 1 8 l i c 2 0 1 1 2 3 0 2 2 0 2 2 0 0 p LAT / / 1/ / 1/ / 1/ / I / / 1 / / / / / / / 1
/
1 1 1 u OTA CSD 2 2 2 2 2 3 3 3 3 4 4 4 4 D 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
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m 4 / :Li & :; a a 3 0 ij 5.[ r 1 i
?
WOIX CREEK NUCLEAR OPERATING CORPORATION AIR PARDCULATE AND CilARCOAL FILTERS ' STATION NUMBER 37 ' COLLEC110N DATE MID COUNT A P FILTER MID COUNT CHARCOAL FILTER , START STOP TIME GROSS BETA TIME I-131 i DATE DATE VOLUME UNITS DATE (pct /Cu.M.) DATE (pCI/Cu.M.) 04/25 05/02 3.10E 08 OC 05/07 1.6 i 0.3 E-02 05/05 LT. 2. . E-02 1 05/09 3.10E 08 05/15 1.3 i 0.2 E-02 05/02 OC 05/13 LT. 2. E-02 05/09 05/16 2.90E 08 OC 05/22 1.6 i 0.3 E-02 05/20 LT. 3. E-02 05/16 05/23 3.00E 08 OC 05/30' l.8 i 0.3 E-02 05/27 LT. 3. E-02 i 05/23 05/30 3.10E 08 OC 06/06 1.1 i 0.2 E-02 06/03 LT. 2. E-02 y 05/30 06/06 3.00E 08 OC 06/13 1.410.3 E-02 06/10 LT. 2. E-02 N 06/06 06/13 3.00E 08 OC 06/19 1.7 i 0.3 E-02 06/17 LT. 2. E-02 06/13 06/20 3.00E 08 OC 06/26 3.1 i 0.3 E-02 06/24 LT. 2. E-02 [ 06/20 06/27 3.00E 08 OC 07/06 2.9 i 0.3 E-02 07/01 LT. 2. E-02 06/27 07/05 3.50E 08 OC 07/14 2.210.3 E-02 07/12 LT. 2. E 07/05 07/11 2.60E 08 OC 07/20 2.8 i 0.3 E-02 07/16 LT. 3. E-02 8 07/11 07/18 3.00E 08 OC 07/24 3.8 i 0.4 E-02 07/20 LT. 2. E-02 07/18 07/25 3.10E 08 OC 08/02 2.3 i 0.3 E-02 07/29 LT. 3. E-02 07/25 08/02 3.40E 08 OC 08/10 2.410.3 E-02 08/08 LT. 1. E-02 08/02 08/08 2.60E 08 CC 08/16 1.7 i 0.3 E-02 08/12 LT. 3. E-02 08/08 08/16 3.30E 08 OC 08/25 2.5 i 0.3 E-02 08/21 LT. 3. E-02 ' 08/16 08/22 2.50E 08 OC 08/29 3.2 i 0.4 E-02 08/26 LT. 2. E-02 08/22 08/29 3.00E 08 OC 09/08 4.610.4 E-02 09/02 LT. 2. E-02 08/29 09/05 2.90E 08 OC 09/13 4.4 i 0.4 E-02 09/09 LT. 2. E-02 i L t. h
q x., / 3 %::. a a 3 a u;..; _r WOIE CREEK NUCLEAR OPERATING CORPORATION AIR PAIGCULATE AND CilARCOAL FILTERS STATION NUMBER 37 COLLECIlON DATE MID COUlfr A P FILTER MID COUNT CHARCOAL FILTER START STOP TIME GROSS BETA TIME I-131 l DATE DATE VOLUME UNITS DATE (pct /Cu M.) DATE (pCl/Cu.M.) 09/05 09/12 3.00E 08 OC 09/19 3.2 i 0.3 E-02 09/16 LT. 2. E-02 09/12 09/19 3.10E 08 OC 09/27 3.9 i 0.4 E-02 09/26 LT. 3. E-02 3.00E 08 C 2.4 i O.3 E-02 I 09/19 09/26 10/04 09/30 LT. 2. E-02 09/19* 09/26 3.00E 08 OC 10/04 2.4 i 0.3 E-02 10/03 LT. 7. E-02 09/26 10/03 3.00E 08 OC 10/11 4.3 i 0.4 E-02 10/10 LT. 3. E-02 y 10/03 10/10 3.10E 08 OC 10/15 2.6 0.3 E-02 10/12 LT. 2. E-02
$ 10/10 10/16 2.50E 08 OC 10/21 4.0 i 0.4 E-02 10/21 LT. 3. E-02 10/16 10/24 3.30E 08 OC 10/30 2.510.3 E-02 10/28 LT. 1. E-02 i 10/24 10/31 3.00E 08 OC 11/05 2.210.3 E-02 11/03 LT. 2. E-02 10/3I I1/07 3.00E 08 OC 11/I4 3.6 i 0.3 E-02 11/11 LT. 2. E-02 1I/07 11/I4 2.90E 08 OC 11/20 3.310.4 E-02 11/18 LT. 2. E-02 11/14 11/21 3.00E 08 OC 11/29 3.8 i 0.4 E-02 11/28 LT. 3. E-02 11/21 11/29 3.40E 08 OC 12/05 3.5 i 0.3 E-02 12/03 LT. 2. E-02 1I/29 12/05 2.50E 08 OC 12/10 3.6 i 0.4 E-02 12/09 LT. 2. E-02 12/05 12/12 2.90E 08 OC 12/18 3.510.4 E-02 12/15 LT. 2. E-02 12/12 12/20 3.30E 08 OC 12/29 3.9 i 0.3 E-02 12/27 LT. 2. E-02 12/20 12/26 2.60E 08 CC 01/10 3.2 i 0.4 E-02 12/29 LT. 2. E-02 12/26 01/03 3.40E 08 OC 01/13 4.310.4 E-02 01/07 LT. 2. E-02
- Duplicate Analysis
E M 4 2 _ I R
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L L L L L L L L L L L L L L L L L LT. LT. C H C
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k T _ i N U OEE 6 0 2 0 272 3 1 0 09 6 5 17 92 0 6 03 0 61 3 2 3 0 1 7 5 3 CMTA 1 2 2 0 1 - l
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/ / / 3 / 3/ /4 4 4 5 5 DTD I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 _
M N 2 2 2 2 2 2 2 2 0 0 0 0 0 0 0 0 0 0 02 02 20 202 02 02 20 202 02 O I A . T S R ET) . E E E E E E E E E E E E E E E E E E E - A R EBM. R 4 4 3 3 4 3 3 3 3 3 3 3 3 3 3 3 3 3 3 O E 1 . I L Su 0 O 0 0 0 0 O 0 0 0 0 0 0 0 0 0 0 0 0 _ F SC I P L' 1 i i i R F I Ol/ 1 i i 1 i 1 i 1 i i 1 i i 1 1 _ PRC O 1 7 4 4 5 71 3 5 9 7 8 5 9 3 5 9 5 4 4 L A G (p 4 3 3 2 4 2 2 2 2 2 C G OA 0 4 1 1 2 2 1 1 1 1 N C T R R I A A EB R I I E C M . P D U _ O N N T N _ R A N U A E E O I O EE 0 9 6 1 1 2 0 0 1 7 3 9 8 6 220 0 6 12 9 5 3 1 7 5 AT AT 2 2 0 0 1 1 1 2 0 0 1 L C L CMT I A / /1/ 1
/1 / 2/ /2 / / / / / / / / / / / /
2 2 2 3 3 3 3 4 4 4 4 5 5 5 DTD U U TS N C I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 _ - K U 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 C . _ U O O O O O O O O O O O O O O O O O C O _ E 8 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 0 U E E E 0E E E0 E 0E0 E E 0 E 0E 0 E E 0 E E E E E L 0 0 0 0 0 0 0 0 0 0 0 O 0 9 1 9 0 9 9 0 9 1 3 0 0 0 9 9 9 9 0 V 3 2 3 2 3 2 2 3 2 3 3 3 3 3 2 2 2 2 3 3 0 7 4 7 4 8 7 8 8 5 2 9 EPE 0 1 1 2 1 3 0 1 1 2 2 0 4 1 1 2 2 0 4 1 1 1 2 0 0 TOT / / / / / / / / / / / / / / / / / / / ATA i 1 1 1 1 2 2 2 2 3 3 3 3 4 4 4 4 5 5 DSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N O I T C ET LRE 7 3 0 71 4 1 7 4 1 8 7 4 1 8 4 1 8 5 2 2 0 1 2 3 0 1 2 2 0 1 2 2 0 1 1 2 0 LAT / / / / / / / / / / / / / / / / / / / OTA 2 1 1 1 1 1 2 2 2 2 3 3 3 3 4 4 4 4 5 CSD 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 iy
q d .. g ,r - r a LT JC :.: w; r WOIX CREEK NUCLEAR OPERATING CORPORATION AIR PARIlCULA'IE AND CHARCOAL FIL'IERS 1 STATION NUMBER 40 COLLECTION DATE MID COUlTT A P FIL'IER MID COUlTT CIIARCOAL FIL'IER START STOP TIME GROSS BETA TIME I-131 DATE DA'IE VOLUME UNITS DATE (pCl/Cu.M.) DATE (pCl/Cu.M.) 05/09 05/16 3.00E 08 OC 05/22 1.510.3 E-02 05/20 LT. 2. E-02 05/16 05/23 2.80E 08 OC 05/30 1.6 i 0.3 E-02 05/27 LT. 2. E-02 05/23 05/30 3.20E 08 OC 06/06 1.1 i 0.2 E-02 06/03 LT. 1. E-02 05/30 06/06 3.10E 08 OC 06/13 1.510.3 E-02 06/10 LT. 1. E-02 05/30* 06/06 3.10E 08 CC 06/13 1.4 i O.3 E-02 06/13 LT. 2. E-02 06/06 06/I3 3.00E 08 CC 06/19 2.210.3 E-02 06/17 LT. 1. E-02
- 3.10E 08 06/13 06/20 CC 06/26 2.9 i 0.3 E-02 06/24 LT. 1. E-02 co i 06/20 06/27 3.10E 08 CC 07/06 2.6 i 0.3 E-02 07/01 LT. 1. E-02 06/27 07/05 3.50E 08 CC 07/14 2.3 i 0.3 E-02 07/12 LT. 1. E-02 07/05 07/11 2.60E 08 OC 07/20 2.710.3 E-02 07/16 LT. 2. E-02 07/11 07/18 3.00E 08 OC 07/24 3.5 i 0.3 E-02 07/20 L T. 1. E-02 07/18 07/25 3.10E 08 CC 08/02 2.310.3 E-02 07/29 LT. 2. E-02 07/25 08/02 3.30E 08 CC 08/10 2.410.3 E-02 08/08 LT. 1. E-02 08/02 08/08 2.50E 08 OC 08/16 1.8 i 0.3 E-02 08/12 LT. 2. E-02 08/08 08/16 3.50E 08 OC 08/25 2.310.3 E-02 08/21 LT. 2. E-02 08/16 08/22 2.60E 08 CC 08/29 2.9 i 0.4 E-02 08/26 LT. 1. E-02 08/22 08/29 3.10E 08 CC 09/08 4.1 i 0.4 E-02 09/02 LT. 9. E-03 08/29 09/05 3.00E 08 CC 09/13 3.910.4 E-02 09/09 L T. 1. E-02
- Duplicate Analysis
q r,/ g.r q g tr 2 :3 :) ut r WOIE CREEK NUCLEAR OPERATING CORPORATION AIR PARDCULATE AND CilARCOAL FILTERS STATION NUMBER 40 COLLECHON DATE MID COUNT A P FIL1ER MID COUNT CHARCOAL FILTER START STOP TIME GROSS BETA TIME l-131 DATE DATE VOLUME UNITS DATE (pCi/Cu.M.) DATE (pCI/Cu.M.) 09/05 09/12 2.90E 08 OC 09/19 2.8 i 0.3 E-02 09/16 LT. 1. E-02 09/12 09/19 3.00E 08 OC 09/27 3.6 i 0.3 E-02 09/26 LT. 1. E-02 09/19 09/26 3.10E 08 CC 10/04 2.110.3 E-02 09/30 LT. 1. E-02 09/26 10/03 2.90E 08 OC 10/11 3.9 i 0.4 E-02 10/10 LT. 2. E-02 10/03 10/10 3.00E 08 OC 10/15 2.5 i 0.3 E-02 10/12 LT. 1. E-02 10/10 10/16 2.60E 08 OC 10/21 4.010.4 E-02 10/21 LT. 1. E-02 10/lo 10/24 3.50E 08 CC 10/30 2.5 i O.3 E-02 10/28 LT. 9. E-03 10/24 10/31 3.10E 08 OC 11/05 2.3 i 0.3 E-02 11/03 LT. 1. E-02 e 10/31 11/07 3.00E 08 OC 11/14 3.2 i 0.3 E-02 11/11 LT. 8. E-03 11/07 11/14 2.90E 08 OC 11/20 3.1 i 0.4 E-02 1I/18 LT. 1. E-02 11/14 11/21 3.10E 08 OC 11/29 3.7 i O.3 E-02 11/28 LT. 2. E-02 11/21 11/29 3.50E 08 OC 12/05 3.4 i 0.3 E-02 12/03 LT. 1. E-02 11/29 12/05 2.50E 08 OC 12/10 3.710.4 E-02 12/09 LT. 1. E-02 11/29* 12/05 2.50E 08 OC 12/10 4.9 i 0.5 E-02 12/12 LT. 2. E-02 12/05 12/12 3.00E 08 OC 12/18 3.3 i 0.3 E-02 12/15 LT. 1. E-02 12/12 12/20 3.50E 08 OC 12/28 4.6 i 0.4 E-02 12/27 LT. 1. E-02 12/20 12/26 2.70E 08 OC 01/10 3.7 i O.4 E-02 12/29 LT. 1. E-02 12/26 01/03 3.50E 08 OC 01/I3 4.5 i 0.4 E-02 01/07 LT. 1. E-02
- Duplicate Analysis
a v/-auZG G J C :lw r WOIE CREEK NUC12AR OPERATING CORPORATION AIR PARTICULATE FILTERS EXPOSURE PA'IIIWAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARTERLY COMi* 3rIE (pCl/Cu.M.) STAT 10N NUMBER 02 - DATE COLLECTED: 01/03 04/04 04/04-07/05 07/05-10/03 10/03-01/03 GAMMA SPEC 1' RUM ANALYSIS: BE-7 1.3310.13 E-01 1.6810.17 E-01 8.5510.85 E-02 6.1110.64 E-02 K-40 LT. 1. E-02 LT.7. E-03 LT.7. E-03 1.4310.52 E-02 MN-54 LT.4. E-04 LT.5. E-04 LT.3. E-04 LT.5. E-04 m CO-58 LT.6. E-04 LT. 6. E-04 LT.5. E-04 LT. 6. E-04
$ FE-59 LT.2. E-03 LT.2. E-03 LT.9. E-04 LT. 1. E-03 CO-60 LT.4. E-04 LT.4. E-04 LT. 6. E-04 LT.6. E-04 7 ZN-65 LT. 1. E-03 LT. 1. E-03 LT. 9. E-04 LT. 1. E-03
$ NB-95/ZR-95 LT.8. E-04 LT.8. E-04 LT. 5. E-04 LT.5. E-04 RU-103 LT. 1. E-03 LT. 1. E-03 LT.5. E-04 LT.6. E-04 RU-106 LT.4. E-03 LT.4. E-03 LT. 3. E-03 LT.4. E-03 1-131 LT. 6. E-02 LT.7. E-02 LT.2. E-03 LT. 2- E.03 CS- 1",4 LT.4. E-04 LT. 5. E-04 LT.5. E-04 LT. 4. E-04 CS-137 LT.4. E-04 LT.5. E-04 LT.4. E-04 LT. 5. E-04 LA-140/BA-140 LT. 1. E-02 LT. 1. E-02 LT.2. E-03 LT. 1. E-03 CE-141 LT. 2- E-03 LT.2. E-03 LT.7. E-04 LT.9. E-04 CE-144 LT.2. E-03 LT.3. E-03 LT.2. E-03 LT.3. E-03 RA-226 LT.6. E-03 LT.9. E-03 LT. 7. E-03 LT. 1. E-02 TII-228 LT. 6. E-04 LT.8. E-04 LT. 7. E-04 LT.9. E-04
m x, 5 c nr.a a 3 a na r I WOis CREEK NUCIEAR OPERATING CORPORA'I10N AIR PAR 11CULA'IE FIL'IERS EXPOSURE PA'I11WAY - AIRBORNE [ ISOTOPIC ANALYSIS ON QUARIERLY COMPOSI'IE l (pCI/Cu.M.) f STA'I1ON NUMBER 03 [ DATE COLLECIED: 01/03-04/04 04/04-07/05 07/05-10/03 10/03-01/03 l GAMMA SPECTRUM ANALYSIS: t BE-7 1.5710.16 E-01 1.5910.16 E-01 6.8010.68 E-02 6.4510.64 E-02 j K-40 LT.9. E-03 LT. 1. E-02 LT.6. E-03 LT. 1. E l MN-54 LT.5. E-04 LT.5. E-04 LT.3. E-04 LT.4. E-04 o CO-58 LT.7. E-04 LT. 8. E-04 LT.4. E-04 LT.5. E-04 r$ FE-59 LT.2. E-03 LT.2. E-03 LT. 1. E-03 LT. 1. E-03
- E-04 CO-60 LT.4. E-04 LT.5. E-04 LT.5. E-04 LT.3.
7 ZN-65 LT. 1. E-03 LT. 1. E-03 LT. 8. E-04 LT.9. E-04 !
$ NB-95/ZR-95 LT.9. E-04 LT.8. E-04 LT. 4. E-04 LT.5. E-04 l RU-103 LT. 1. E-03 LT. 1. E-03 LT.4. E-04 LT. 5. E-04 l RU-106 LT.5. E-03 LT.4. E-03 LT. 3. E-03 LT.4. E-03 I-131 LT.8. E-02 LT.7. E-02 LT. 1. E-03 LT.2. E-03 CS-134 LT.5. E-04 LT.5. E-04 LT. 4. E-04 LT. 5. E-04 CS-137 LT.5. E-04 LT.4. E-04 LT.4. E-04 LT.5. E-04 LA-140/BA-140 LT. 1. E-02 LT. 1. E-02 LT.2. E-03 LT. 1. E-03 CE-141 LT.2. E-03 LT.2. E-03 LT.5. E-04 LT.8. E-04 CE-144 LT.3. E-03 LT.3. E-03 LT.2. E-03 LT.2. E-03 RA-226 LT. 1. E-02 LT.8. E-03 LT.5. E-03 LT.8. E-03 TH-228 LT.9. E-04 LT. 8. E-04 LT.5. E-04 LT.8. E-04 ;
i
n m t - cu a ac :;u r WOIX CREEK NUCIZAR OPERATING CORPORATION AIR PART1CULATE FIL'IERS EXPOSURE PATHWAY - AIRBORNE ISOIUPIC ANALYSIS ON QUARTERLY COMPOSITE D (pCl/Cu.M.) STAT 10N NUMBER 32 DATE COLLECTED: 01/03-04/04 04/04-07/05 07/05-10/03 10/03-01/03
- GAMMA SPECTRUM ANALYSIS:
BE-7 1.5610.16 E-01 1.8110.18 E.01 9.0010.90 E-02 5.9010.59 E-02 K-4 0 LT. 8. E-03 8.7013.80 E-03 LT. 8. E-03 LT. 1. E-02 MN-54 LT. 5. E-04 LT. 5. E-04 LT.3. E-04 LT.4. E-04 ; u CO-58 LT.7. E-04 LT.7. E-04 LT. 3. E-04 LT. 5. E-04
$ FE-59 E-03 E-04 E-03 LT. 2. LT.2. E-03 LT. 8. LT. 1.
- CO-60 E-04 E-04 E-04 LT.4. LT.5. LT. 3. LT. 5. E-04
" ZN-65 L T. 1. E-03 E-03 LT. 1. LT.8. E-04 LT. 1. E-03 ,
[ NB-95/ZR-95 LT.9. E-04 LT.9. E-04 LT.4. E-04 LT.5. E-04 RU-103 LT. 1. E-03 LT. 1. E-03 LT.4. 3-04 LT. 5. E-04 ' RU-106 LT. 4. E-03 LT. 5. E-03 LT. 3. E-03 LT.4. E-03 I-131 LT. 7. E-02 LT.6. E-02 LT. 1. E-03 LT. 1. E-03 y CS-134 LT.5. E-04 LT.4. E-04 LT. 4. E-04 LT.5. E-04 CS-137 LT.5. E-04 LT.5. E-04 LT. 3. E-04 LT. 5. E-04 LA-140/BA-140 LT. 1. E-02 LT. 1. E-02 LT. 8. E-04 LT. 1. E-03 CE-141 LT.2. E-03 LT.2. E-03 LT. 6. E-04 LT. 6. E-04 CE-144 LT.3. E-03 LT. 2. .E-03 LT.2. E-03 LT.2. E-03 i RA-226 LT.8. E-03 LT.6. E-03 LT.6. E-03 LT.6. E-03 TII-228 LT.8. E-04 LT.6. E-04 LT.6. E-04 LT.6. E-04 _ _ _ . _ _ _ _ _ _ _ _ _ _ ~ ___ -
g n .- s .y r a a .; a ou .c WOIX CREEK NUCtJtAR OPERATING CORPORATION AIR PARI 1CULATE FILTERS EXPOSURE PA'IEWAY - AIRBORNE ISO'IUPIC ANALYSIS ON QUARTERLY COMPOSTIE (pCl/Cu.M.) STATION NUMBER 37 4 1 DA'IE COLLECIED: 01/03-04/04 04/04-07/05 07/05-10/03 10/03-01/03 GAMMA SPECTRUM ANALYSIS: BE-7 1.7710.18 E-01 1.6910.17 E-01 9.4110.94 E-02 6.4810.65 E-02 K-40 LT. 1. E-02 LT. 2. E-02 LT.2. E-02 LT.2. E-02 IVN-54 LT.7. E-04 LT.6. E-04 LT. 5. E-04 LT.5. E-04 u ( '9 LT. 1. E-03 LT. 8. E-04 LT.6. E-04 LT. 5. E-04
$ FE-69 LT.3. E-03 LT.3. E-03 LT. 1. E-03 LT. 1. E-03
- CO-60 LT.5. E-04 LT. 6. E-04 LT.6. E-04 LT. 5. E-04 7 ZN-65 LT. 1. E-03 LT. 1. E-03 LT. l.. E-03 LT. 1. E-03
[ NB-95/ZR-95 LT. 1. E-03 LT.9. E-04 LT. 6. E-04 LT.6. E-04 RU-103 LT.2. E-03 LT. 1. E-03 LT.6. E-04 LT.6. E-04 RU-106 LT.5. E-03 LT. 5. E-03 LT.5. E-03 LT.5. E-03 I-131 LT. 1. E-01 LT.7. E-02 LT. 2. E-03 LT.2. E-03 CS-134 LT.7. E-04 LT.6. E-04 LT. 5. E-04 LT.6. E-04 CS-137 LT.6. E-04 LT.5. E-04 LT. 6. E-04 LT.6. E-04 LA-140/BA-140 LT. 1. E-02 LT. 1. E-02 LT. 1. E-03 LT. 1. E-03 CE-141 LT.3. E-03 LT.2. E-03 LT.7. E-04 LT.8. E-04 CE-144 LT.5. E-03 LT.3. E-03 LT.2. E-03 LT.3. E-03 RA-226 LT. 1. E-02 LT.8. E-03 LT.8. E-03 LT.8. E-03 TH-228 LT. 1. E-03 LT. 7. E-04 LT.7. E-04 LT.7. E-04 _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - - _ - _ _ _ _ _ _ _ - _ _ _ - _ _ - - _ _ _ _ _ _ - - _ _ _ _ _ _ _ _ - _ _ _ _ - _ - _ _ _ - _ _ _ = _ _ - _ _ _ _ _ - _ _ - _ _ _ - _ _ _ - _ _ _ _ _ - _ - _ _ - - _ _ _ - _ - _ _ _ _ - - - - _ _ . - - - -
a # r # a1 -8 l l WOIF CREEK NUCIEAR OPERATING CORPORAMON l AIR PARI 1CULATE FILTERS EXPOSURE PAT 11WAY - AIRBORNE l ISOrIOPIC ANALYSIS ON QUARIERLY COMPOSTIE l (pC1/Cu.M.) STATION NUMBER 40 l l [ l DATE COLLECTED: 01/03-04/04 04/04-07/05 07/05-10/03 10/03-01/03 GAMMA SPECI' RUM ANALYSIS: BE-7 1.2710.13 E-01 1.8010.18 E-01 7.2710.73 E-02 6.7710.68 E-02 K-40 1.3010.47 E-02 LT.6. E-03 LT. 1. E-02 LT.6. E-03 MN-54 LT.5. E LT.4. E-04 LT. 5. E-04 LT.3. E-04
.o CO-58 LT.8. E-04 LT. 5. E-04 LT.5. E-04 LT. 3. E-04
$ FE-59 LT.3. E-03 LT. 2. E-03 LT. 1. E-03 LT.8. E-04
- CO-60 LT.6. E-04 LT.4. E-04 LT.4. E-04 LT. 5. E-04 LT. 1. E-03 LT.9. E-04 LT. 9. E-04 LT.7. E-04 7 ZN-65 N NB-95/ZR-95 LT. 1. E-03 LT.7. E-04 LT.5. E-04 LT.4. E-04 RU-103 LT. 1. E-03 LT. 1. E-03 LT.5. E-04 LT. 5. E.04 RU-106 LT.5. E-03 LT. 3. E-03 LT. 4. E-03 LT.3. E-03 I-131 LT.8. E-02 LT.5. E-02 LT. 2. E-03 LT. 1. E-03 CS-134 LT.5. E-04 LT.3. E-04 LT.5. E-04 LT.4. E-04 CS- 137 LT.5. E-04 LT.4. E-04 LT.4. E-04 LT.4. E-04 LA-140/BA- 140 LT.2. E-02 LT. 1. E-02 LT. 1. E-03 LT. 1. E-03 CE-141 LT.2. E-03 LT.2. E-03 LT.5. E-04 LT.7. E-04 CE-144 LT.2. E-03 LT.2. E-03 LT.2. E-03 LT.2. E-03 RA-226 LT.8. E-03 LT.7. E-03 LT.7. E-03 LT.7. E-03 TII-228 LT.8. E-04 LT. 7. E-04 LT.6. E-04 LT.7. E-04
<-i k / 2? -D ~ C U a .5T O U a-2 E WOfE CREEK NUCIEAR OPERATING CORPORA 110N EXPOSURE PATHWAY - INGES110N ANIMAIS/ GAME (pCi/KG WET) i STA110N NUMBER SECTOR A (INDICATOR)
I DATE COLLECIED: 12/15 DEER GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 K-40 3.0610.31 E 03 MN-54 LT.4. E 00 CO-58 LT.4. E 00 y FE-59 LT. 1. E 01 occ CO-60 LT.4. E 00 ZN-65 LT. 1. E 01 E NH-95/ZR-95 LT.4. E 00
$ RU-103 LT.5. E 00 RU- 106 LT.3. E 01 I-131 LT. 1. E 01 CS-134 LT.4. E 00 ;
CS-137 LT.4. E 00 LA-140/BA-140 LT.8. E 00 CE-141 LT.6. E 00 CE-144 LT. 2. E 01 RA-226 LT.6. E 01 . Til-228 LT.6. E 00 4
.q x., / g y:t z's ~ g _=. 0 y M r WOLF CREEK NUCIZAR OPERATING CORPORA 110N EXPOSURE PKIIIWAY - INGESTON ANIMALS / GAME (pCl/KG WET)
STA'I1ON NUMBER SECTORS A&R (INDICATOR) DATE COLLECIED: 12/29 COMP. QUAIL GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 K-40 3.8510.38 E 03 MN-54 LT.2. E 01 o CO-58 LT. 1. E 01
$ FE-59 LT.3. E 01 CO-60 LT.2. E 01 7 ZN-65 LT. 3. E 01
$ NB-95/ZR-95 LT.2. E 01 RU-lO3 LT.2. E 01 RU-106 LT. 1. E O2 I-131 LT. 3. E 01 CS-134 LT. 2. 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.3. E 02 TII-228 LT. 2. E 01
- 4 6 , 5 z' - E G a 3a1 La r WOLF CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PATIIWAY - INGESTION ANIMALS / GAME (pC1/KG WE1)
STA110N NUMBER SECTOR R (INDICATOR) I DATE COLLECTED: 02/08 DEER GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 K-40 3.7710.38 E 03 MN-54 LT.4. E 00 CO-58 LT.5. E 00 y FE-59 LT. 1. E 01 c CO-60 LT.5. E 00 ZN-65 LT. 1. E 01 i NB-95/ZR-95 LT.5. E 00 U RU-103 LT.5. E 00 RU-lO6 LT.4. E 01 1-131 LT. 1. E 01 CS-134 LT.5. E 00 CS-137 LT. 5. E 00 LA-140/BA-140 LT. G. E 00 CE-141 LT. 8. E 00 CE 144 LT.3. E 01 RA-226 LT.9. E 01 Til-228 LT.8. E 00
g x, / G::<< E O G ;ai; v4 r e WOIF CREEK NUCIEAR OPERATING CORPORATION EXPOSURE PA'n{WAY - INGESTION ANIMAIS/ GAME (pCl/KG WEll STA~IlON NUMBER SECTOR II (CONTROL) DA'IE COLLECTED: 12/15 QUAIL GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 K-40 3.7010.37 E 03 MN-54 LT. 1. E 01 t CO-58 LT. 1. E 01
- [ FE-59 LT.3. E 01 C CO-60 LT. 1. E 01 ZN-65 LT.3. E 01 E 01 ro NB-95/ZR-95 LT. 1.
co RU-103 L T. 1. E 01 RU- 106 L T. 1. E 02 I-131 LT.4. E 01 CS-134 LT. 1. E 01 E O1 l CS-137 LT. 1. LA-140/BA-140 LT.2. E 01 CE-141 LT.3. E 01 CE-144 LT.9. E 01 RA-226 LT.3. E 02 TH-228 LT.2. E 01
q :z, , 3 ,_ 2 -3 g .=_ :3 O M ;- WOtX CREEE NUCIEAR OPERATING CORPORATION EXPOSURE PA111WAY - INGESTION FEED & FORAGE (pCl/KG WET) STATION NUMBER NR.U1 DAIE COLLECTED- 10/26 10/26 CORN SOYBEANS GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 LT.5. E 01 K-40 2.8010.28 E 03 1.4710.15 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 2 CO-60 LT.4. E 00 LT.8. E 00 ZN-65 LT. 1. E 01 LT.2. E 01 m NB-95/ZR-95 LT.4. E 00 LT. 7. E 00 RU-103 LT.5. E 00 LT.7. E 00
$ RU- 106 LT.4. E 01 LT.6. E 01 1-131 LT. 8. E 00 LT. 1. E 01 CS-134 LT.4. E 00 LT.7. E 00 CS-137 LT.5. E 00 LT.7. E 00 LA-140/BA-140 LT.6. E 00 LT.6. E 00 CE-141 LT. 7. E 00 LT.9. E 00 CE-144 LT.3. E 01 LT.3. E 01 RA-226 LT.8. E 01 LT.9. E 01 TH-228 LT.7. E 00 LT.9. E 00 i
.q 6 / 5 C. 'E G -G 3 G:; t4 Y t WOEX NN NUCIZAR OPERATING CORPORATION EXPOSURE PK111WAY - INGESTION FEED & FORAGE (pCl/KG WEI) ,
STKI1ON NUMBER NR-D1 DA1E COLLECTED: 10/26 SOYBEANS GAMMA SPECTRUM ANALYSIS: BE-7 LT.6. E 01 K-40 1.8210.18 E 04 MN-54 LT.6. E 00 CO-58 LT. 6. E 00 FE-59 LT.2. E 01 o o, CO-60 LT.7. E 00
$ ZN-65 LT.2. E 01 co NB-95/ZR-95 LT.7. E 00 b RU-103 LT.6. E 00 0 E 01 RU-106 LT.5.
1-131 LT. 1. E 01 CS-134 LT.7. E 00 CS-137 LT.7. E 00 LA-140/BA-140 LT.7. E 00 CE-141 LT. 9. E 00 CE-144 LT.4. E 01 RA-226 LT. 1. E O2 TH-228 LT. 1. E 01 ! 6
9 a / 5 d - C LT u 3 G t; w .c WOIX CREEE NUCIEAR OPERATING CORPORATION EXPOSURE PK111WAY - INGES~nON FEED & FORAGE (pct /KG WET) STKHON NUMBER NR-D2 DA'IE COLLECIED: 10/19 10/19 CORN SOYBEANS GAMMA SPEC 1' RUM ANALYSIS: BE-7 LT.4. E 01 LT.6. E 01 K-40 2.7110.27 E 03 1.5310.15 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
- o. CO-60 LT.5. E 00 LT. 8. E 00 m ZN.65 LT. 1. E 01 LT.2. E 01 m NB-95/ZR-95 LT.4. E 00 LT.7. E 00 b RU-103 LT. 5. E 00 LT.7. E 00 RU-106 LT.4. E 01 LT.6. E 01 I-131 LT.8. E 00 LT. 1. E 01 CS-134 LT.5. E 00 LT.7. E 00 CS-137 LT.4. E 00 LT.7. E 00 LA.140/BA-140 LT.6. E 00 LT.8. E 00 CE-141 LT.7. E 00 LT. 1. E 01 CE-144 LT.3. E 01 LT.4. E 01 RA-226 LT. 7. E 01 LT. 1. E 02 TH-228 LT.6. E 00 LT.9. E 00 i
l l
WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PARIWAY - INGES' HON FISH (pCl/KG WE'Il STATION NUMBER WCCL DC DA'IE COLLECTED: 04/07 05/15 05/15 10/11 10/11 WHUE CRAPPIE FLAHIEAD CATFISH COMMON CARP CHANNEL CATFISH WIPER GAMMA SPECIRUM ANALYSIS: BE-7 LT. 1. E 02 LT.2. E 02 LT.2. E 02 LT. 1. E 02 LT. 1. E O2 K-40 3.2510.32 E 03 4.8210.48 E 03 3.8210.38 E 03 3.0110.30 E 03 4.2310.42 E 03 MN-54 LT. 1. E 01 LT.3. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 CO-58 L T. 1. E 01 LT.3. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 FE-59 LT.3. E 01 LT. 5. E 01 LT.5. E 01 LT. 3. E 01 LT.4. E 01 o', CO-60 LT.2. E 01 LT. 3. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01
$ ZN-65 LT.3. E 01 LT. 6. E 01 LT. 5. E 01 LT.3. E 01 LT.4. E 01 m NB-95/ZR-95 LT. 1. E 01 LT.3. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 L, RU-103 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 N RU-106 LT. 1. E 02 LT.3. E 02 LT.2. E 02 LT. 1. E O2 LT. 1. E O2 I-131 LT.2. E 01 LT. 5. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 CS-134 LT. 1. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 CS-137 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LA-140/BA-140 LT.2. E 01 LT.4. E 01 LT.3. E 01 LT.2. E 01 LT.3. E 01 CE-141 LT.3. E 01 LT.4. E 01 LT.4. E 01 LT.2. E 01 LT.2. E 01 CE-144 LT. 1. E 02 LT. 1. E 02 LT. 1. E O2 LT.8. E 01 LT.8. E 01 RA-226 LT.3. E 02 LT.5. E O2 LT.5. E 02 LT.3. E 02 LT.2. E 02 TH-228 LT.3. E 01 LT.5. E 01 LT.4. E 01 LT.2. E 01 LT.2. E 01 TRITIUM ANALYSIS:
H-3 0.1 i 0.5 E 03 7.3 1 0.3 E 03 7.9 i 0.3 E 03 6.0 i 0.2 E 03 6.6 1 0.2 E 03
9OMUCG G :.T C U M r l WOLF CREEK NUCl2AR OPERATING CORPORATION EXPOSURE PA111WAY. - INGESTION ; I j FISli [ (pCl/KG WEll [ STA'110N NUMBER JRR DATE COLLECTED- 05/10 05/10 10/18 10/18 10/18* COMMON CARP CilANNEL CATFISH CHANNEL CATFISH BM BUFFAID BM BUFFAID CAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 02 LT.2. E 02 LT. 1. E 02 LT. 1. E 02 LT. 9. E 01 t K-4 0 3.4610.35 E 03 3.6210.36 E 03 3.7510.37 E 03 3.6610.37 E 03 4.0510.41 E 03
- MN.54 LT.2. E 01 LT.3. 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. 1. E 01 LT. 1. E 01 LT. 1. E 01
{ o, o FE-59 LT.5. E 01 LT.5. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 to CO-60 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 ZN-65 LT.4. E 01 LT. 5. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 Y NB-95/ZR-95 LT. 2. E 01 LT.3. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 - U RU-103 LT. 2. E 01 LT.3. E 01 LT.2. E 01 LT. 2. E 01 LT. 1. E 01 RU-106 LT.2. E 02 LT.2. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 ! l-131 LT.6. E 01 LT.7. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 CS-134 LT.2. E 01 LT.3. E 01 LT. 2. E 01 LT.2. E 01 LT. 1. E 01 , CS-137 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LA-140/BA-140 LT.4. E 01 LT.4. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 CE-141 LT.3. E 01 LT.4. E 01 LT.2. E 01 LT.2. E 01 LT. 2. E 01 ! i CE-144 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. S. E 01 LT.8. E 01 r RA-226 LT.4. E 02 LT.5. E 02 E 02 LT.3. E 02 ' LT. 3. LT.2. E 02 TII-228 LT.4. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 j i TRITIUM ANALYSIS: . i H-3 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT 1. E 02 LT. 1. E 02 l
- Duplicate Analysis ,
I t
.9 6 / JuC0 GJGUWr WOIX CREEK NUCIJCAR OPERATING CORPORATION EXPOSURE PA~IRWAY - INGESTION FISH (pCl/KG WET)
STATION NUMBER WCCL - MAIN BODY DATE COLLEC1ED- 05/15 05/15 SM BASS CilANNEL CATFISH GAMMA SPECIRUM ANALYSIS: BE-7 LT.2. E 02 LT.2. E 02 K-40 3.9610.40 E 03 3.7310.37 E 03 MN-54 LT.3. E 01 LT.2. E 01 y CO-58 LT.2. E 01 LT.2. E 01 g FE-59 LT,6. E 01 LT.4. E 01 (D CO-60 LT. 3. E 01 LT.2. E 01 tn ZN-65 LT.6. E 01 LT. 5. E 01 b NB-95/ZR-95 LT.3. E 01 LT.2. E 01 RU-103 LT.3. E 01 LT. 2. E 01 RU-lO6 LT.3. E O2 LT.2. E 02 I-131 LT. 5. E 01 LT.4. E 01 CS-134 LT.3. E 01 LT.2. E 01 CS-137 LT.3. E 01 LT.2. E 01 LA-140/BA-140 LT.3. E 01 LT.2. E 01 CE-141 LT.4. E 01 LT.4. E 01 CE-144 LT.2. E 02 LT. 1. E 02 I RA-226 LT.5. E 02 LT.4. E 02 TII-228 LT. 5. E 01 LT.4. E 01 j TRITIUM ANALYSIS: 11- 3 5.8 1 0.3 E 03 7.4 1 0.3 E 03 i __s..-. --.___. _ . _ _ __ _ - _ . - _ - _ - -. - _ _ _ _ . _ _ - _ _ _ . - -_._-_- - _ _ , -
.q n / g .r/: .0 . : ;; a :s t4 r WOLF CREEK NUCIE.AR OPERATING CORPORATION EXPOSURE PKIIIWAY - INGESTION FISH (pC1/KG WET)
STATION NUMBER WCCL - SE AREA DA'IE COLLECIED: 05/15 LM BASS GAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 02 K-4 0 3.9710.40 E 03 MN-54 LT.3. E 01 CO-58 LT.3. E 01 2 FE-59 LT. 5. E 01
% CO-60 LT.3. E 01 m ZN-65 LT. 5. E 01 8
NB-95/ZR-95 LT.3. E 01 m RU-103 LT.3. E 01 RU-106 LT.3. E 02 1-131 LT.5. E 01 CS-134 LT.3. E 01 CS-137 LT.3. E 01 LA-140/BA-140 LT.4. E 01 CE-141 LT.3. E 01 CE-144 LT. L E 02 RA-226 LT. 5. E 02 TH-228 LT.5. E 01 TRrl1UM ANALYSIS: H-3 6.9 i O.3 E 03
q s ,- ; & , - E a G 27.: 2; M .: WOIE CREEK NUCIJCAR OPERATING CORPORATION EXPOSURE PA11IWAY - INGESTION FISil (pC1/KG WEI) STA110N NUMBER UHS DATE COLLECIED: 10/11 10/11 BM BUFFALO WALTYE . GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT. 1. E 02 K-4 0 3.0210.30 E 03 3.6210.36 E 03 MN-54 LT. 1. E 01 LT. 1. E 01 CO-58 LT. 1. E 01 LT. 1. E 01 y FE-59 LT.3. E 01 LT.3. E 01 o CO-60 LT. 1. E 01 LT.2. E 01 ZN-65 LT.3. E 01 LT.3. E 01 NB-95/ZR-95 LT. 1. E 01 LT.2. E 01
$ RU-103 LT.2. E 01 LT.2. E 01 RU- 106 LT. 1. E 02 LT. 1. E 02 I-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 LA-140/BA-140 LT.2. E 01 LT.2. E 01 CE-141 LT.3. E 01 LT.3. E 01 CE-144 LT. 1. E 02 LT. 1. E 02 RA-226 LT.3. E 02 LT.3. E 02 TH-228 LT.3. E 01 LT.3. E 01 TRI11UM ANALYSIS:
H-3 6.8 i 0.2 E 03 7.4 i 0.3 E 03
?z h , ; . .-g a a 3 01; M r WOIE CREEK NUCIJI:AR OPERATING CORPORATION EXPOSURE PATIIWAY - INGE5 HON FISil (pCl/KG WEI)
STA110N NUMBER WCCL CAUSEWAY DATE COLLECTED: 10/11 10/I1* 10/11 WHrl'E BASS WIIITE BASS SM BUFFALO GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT.2. E 02 LT. ' 2. E 02 K-40 3.8510.39 E 03 3.0210.30 E 03 3.4310.34 E 03 MN.54 LT. 1. E 01 LT.2. E 01 LT. 2. E 01 CO-58 LT. 1. E 01 LT. 2. E 01 LT. 2. E 01 o FE-59 LT. 3. E 01 LT.5. E 01 LT.5. E 01
$ CO-60 LT. 1. E 01 LT.2. E 01 LT.2. E 01 ZN-65 LT.3. E 01 LT.5. E 01 LT. 4. E 01
? NB-95/ZR-95 LT. 1. E 01 LT.2. E 01 LT.2. E 01
$ RU-103 LT.2. E 01 LT. 3. E 01 LT.2. E 01 RU-106 LT. 1. E 02 LT.2. E 02 LT.2. E 02 1-131 LT.3. E 01 LT.5. E 01 LT.4. E 01 CS- 134 LT. 1. E 01 LT.2. E 01 LT.2. E 01 CS-137 LT.2. E 01 LT.3. E 01 LT. 2. E 01 LA-140/BA-140 LT. 2. E 01 LT.3. E 01 LT. 3. E 01 CE-141 LT.3. E 01 LT.3. E 01 LT. 3. E 01 CE.144 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 RA-226 LT.3. E 02 LT.4. E 02 LT. 4. E 02 TH-228 LT.3. E 01 LT.4. E 01 LT. 3. E 01 TRIT 1UM ANALYSIS:
11-3 7.1 1 0.2 E 03 7.5 1 0.3 E 03 6.3 1 0.2 E 03
- Duplicate Analysis
_ _ _ _ - . ... . _ _ _ - - _ _ _ _ _ - - _ _ _ _ _ - _ _ _ - - = _ - _ _ _ - _ _ _ _ _ - _ _ - - _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - - - _ - _ - - - - _ - _ - - - _ - _ - _ _ _ - _ _ _ _ _ _ - _ - _ -
.q y ,q c; c a a yG :;u.t .
WOEF CREEK NUCIEAR OPERATING CORPORATION EXPOSURE PA111WAY - INGES110N FISH IPC1/KG WET) STA'I1ON NUMBER WCCL - OITILET POOL DA1E COLLECTED: 10/16 10/16 Fl>LTilEAD CA'ITISH SM BUFFALO / RIVER CARPSUCKER GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT.2. E 02 - K-40 3.4010.34 E 03 2.8610.29 E 03 MN-54 LT. 1. E 01 LT.2. E 01 y CO-58 LT.2. E 01 LT. 2. E 01
$ FE-59 LT.3. E 01 LT. 5. E 01
- CO-60 LT.2. E 01 LT.2. E 01 7 ZN-65 LT.4. E 01 LT. 5. E 01 g NB-95/ZR-95 LT.2. E 01 LT. 2. E 01 RU-103 LT.2. E 01 LT.2. E 01 RU-106 LT. 1. E 02 LT. 2. E 02 1-131 LT.2. E 01 LT.3. E 01 CS-134 LT.2. E 01 LT.2. E 01 CS-137 LT.2. E 01 LT.2. E 01 LA-140/BA-140 LT. 2. E 01 LT. 3. E 01 CE-141 LT.3. E 01 LT. 3. E 01 CE-144 LT. 1. E 02 LT. 1. E 02 RA-226 LT.3. E 02 LT.4. E 02 TH-228 LT. 3. E 01 LT.3. E 01 TRIT 1UM ANALYSIS:
11-3 5.1 1 0.3 E 03 6.1 i O.3 E 03 _ - - - - - _ _ _ _ _ _ _ _ - _ _ _ _ _ - _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - - _ _ _ _ _ _ _ - _ _ _ . _ _ _ _ _ _ - _ _ _ _ . - _ . _ . - _ . . - . . . _ ~
q x, ,- 5 ._p - C a G 23 c: W E WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PATTIWAY - INGES'IlON FISil EffrRAILS (pC1/KG WET) STAT 10N NUMBER JRR DATE COLLECTED: 05/10 CilANNEL CATFISH GAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 02 K-4 0 8.17tl.77 E 02 MN-54 LT.2. E 01 CO-58 LT.2. E 01 g FE-59 LT.5. E 01 C CO-60 LT.2. E 01 ZN-65 LT.4. E 01 cn e NB-95/ZR-95 LT.3. E 01 e" RU-103 LT. 3. E 01 RU- 106 LT.2. E 02 I-131 LT.7. E 01 CS-134 LT.2. E 01 CS-137 LT.3. E 01 LA-140/BA-140 LT. 5. E 01 CE-141 LT.4. E 01 CE-144 LT. 1. E 02 , RA-226 LT.5. E 02 Til-228 LT.5. E 01 TRITIUM ANALYSIS: 11- 3 LT.2. E 02
q u - : U 5' G G 3 0 2; M .E WOLF CREEK NUCIJ!lAR OPERATING CORPORATION EXPOSURE PATHWAY - INGESDON FISil ENTRAILS (pCl/KG WE'Il STKI1ON NUMBER WCCL - MAIN BODY DA1E COLLEC1ED: 05/15 CIIANNEL CKIFISH GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E 02 K-40 8.8512.03 E O2 MN-54 LT.3. E 01 CO-58 LT.3. E 01 y FE-59 LT. 5. E 01 e CO-60 LT.3. E 01 ZN-65 LT.4. E 01 NB-95/ZR-95 LT.3. E 01
$ RU-103 LT.3. E 01 RU-106 LT.3. E 02 1-131 LT. 5. E 01 CS-134 LT.3. E 01 CS-137 LT.3. E 01 LA-140/BA-140 LT.4. E 01 CE-141 LT. 4. E 01 CE-144 LT. 1. E 02 RA-226 LT. 5. E O2 TH-228 LT.5. E 01 TRITIUM ANALYSIS:
11- 3 7.8 i 0.3 E 03
qs.gc/ca a z:';U N r wOrs CREEK NUCLEAR OPERATMG CORPORATION EXPOSURE PATHWAY - INGESBON FOOD /CARDEN CROPS (PCI/KG WE'll STABON NUMBER R-1 DATE COLLECTED: 05/30 06/27 07/25 08/29 - LETTUCE LETTUCE CABBAGE LETTUCE GAMMA SPECTRUM ANALYSIS: BE-7 7.2410.87 E 02 1.1910.12 E 03 2.1710.81 E 02 1.41i0.80 E 02 K-40 4.5010.45 E 03 4.9610.50 E 03 3.9710.40 E 03 6.9410.69 E 03 MN.54 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 L T. 1. E 01 CO-58 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 . LT. 1. E 01 [ FE-59 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 i j CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 m ZN-65 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.3. E 01 g NB-95/ZR-95 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 RU-103 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 RU-106 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 I-131 LT.2. E 01 LT. 2. E O1 LT.2. E 01 LT.2. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 . CS-137 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LA-140/BA-140 LT.2. E 01 LT. 2. E 01 LT. 1. E 01 LT. 1. E 01 CE.141 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 CE-144 LT.7. E 01 LT.8. E 01 LT.7. E 01 LT.9. E 01 RA-226 LT.2. E 02 LT.3. E 02 LT.2. E 02 LT.3. E 02 i TH.228 LT.2. E 01 LT. 2. E 01 LT. 2. - E 01 LT.2. E 01 i 1
q y ,- a u C D .a 2 0 U 6E.E WOIE CREEK NUC1JtAR OPERATING CORPORATION EXPOSURE PATilWAY - INCESTION FOOD / GARDEN CROPS (PCI/KG WE11 STATION NUMBER C-1 DATE COllECIED: 05/30 06/27 06/27* 07/25 08/29 CABBAGE CABBAGE CABBAGE CABBAGE CABBAGE GAMMA SPECTRUM ANALYSIS: BE-7 5.0410.64 E 02 6.1611.05 E 02 5.8910.77 E 02 2.5210.70 E 02 1.5410.63 E 02 K-4 0 3.5910.36 E 03 5.9510.60 E 03 5.1110.51 E 03 4.3510.43 E 03 3.8610.39 E 03 MN-54 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT.9. E OC LT.8. E 00 CO-58 LT. 9. E 00 LT. 1. E 01 LT. 1. E 01 LT.8. E 00 LT.9. E 00 2 FE-59 LT. 2. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT. 2. E 01 $ CO-60 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 m ZN-65 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 LT.9. E 00 i NB-95/ZR-95 N RU-103 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT. 9. E 00 LT.9. E 00 RU-106 LT.9. E 01 LT. 1. E 02 LT. 1. E 02 LT.7. E 01 LT.8. E 01 I-131 LT. 1. E 01 LT.2. E 01 LT.2. 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. 1. E 01 LT.9. E 00 CS-137 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 LT. 1. E 01 LA-140/BA-140 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 CE-141 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 CE- 144 LT.5. E 01 LT.7. E 01 LT.6. E 01 LT.5. E 01 LT.5. E 01 RA-226 LT.2. E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02 TII-228 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 "Dupikate Analysis
q c. / 5 t, - .c a G 2 01.; m .T. WOLF CREEK NUCLEAR OPERATTNG CORPOPA'I10N EXPOSURE PA"11IWAY - INGES110N FOOD / GARDEN CROPS (PCI/KG WE'll STATION NUMBER C-1 DKIE CollECIED- 09/26 10/16 10/31 CABBAGE CABBAGE CABBAGE GAMMA SPECTRUM ANALYSIS: BE-7 2.3210.79 E 02 LT. 1. E 02 3.6810.84 E 02
- K-40 3.9110.39 E 03 2.6010.26 E 03 2.0210.20 E 03 A MN-54 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01
$ CO-58 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 m FE-59 LT. 2. E 01 LT.3. E 01 LT.2. E 01 '
[ CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 W ZN-65 LT.3. E 01 LT. 3. E 01 LT.2. E 01 NB-95/ZR-95 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 RU-103 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 RU-106 LT. 1. E 02 LT. 1. E 02 LT. 1. E O2 i 1-131 LT. 2. E 01 LT. 1. E 01 LT. 1. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CS-137 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 , LA-140/BA-140 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CE-141 LT.2. E 01 LT.2. E 01 LT.2. E 01 CE-144 LT.7. E 01 LT.7. E 01 LT.7. E 01 RA-226 LT.? E 02 LT.2. E 02 LT.2. E 02 TH-228 LT.2. E 01 LT.2. E 01 LT.2. E 01
c o-sr-ca c r o u w .I , WOtX CREEK NUCI2AR OPERATING CORPORA'E10N EXPOSURE PKI11WAY - INGES'I1ON FOOD / GARDEN CROPS (PCI/KG WET) STA*I1ON NUMBER G-1 DKIE COLLECIED: 07/26 08/29 C9/26 10/31 CABBAGE CABBAGE CABBAGE CABBACE CAMMA SPECTRUM ANALYSIS: BE-7 5.4610.88 E 02 3.1010.78 E 02 3.1811.05 E 02 1.5410.56 E 02 K-4 0 3.1210.31 E 03 4.7610.48 E 03 2.7510.27 E 03 2.7410.27 E 03 MN-54 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT. 7. E 00 7 CO.58 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.8. E 00
$ FE-59 LT.2. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.8. E 00 8
ZN-65 LT.2. E 01 LT. 2. E 01 LT.3. E 01 LT.2. E 01
$ NB-95/ZR-95 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT.8. E 00 RU-103 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT.9. E 00 RU-106 LT. 1. E O2 LT. 9. E 01 LT. 1. E 02 LT.8. E 01 1-131 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT. 2. E 01 LT.8. E 00 CS-137 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT.9. E 00 LA-140/BA-140 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LT.9. E 00 CE-141 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LT.2. E 01 ,
CE 144 LT.6. E 01 LT. 6. E 01 LT. 1. E 02 LT.7. E 01 RA-226 LT.2. E 02 LT. 2. E 02 LT.3. E 02 LT.2. E 02 TH-228 LT.2. E 01 LT. 2. E 01 LT. 2. E 01 LT.2. E 01
e
& z** -$ N ! k,s Y - Y --
WOW CREEE NUCLEAR OPERAMNO CORPORATION ! EXPOSURE PKillWAY - INGES~l10N r FOOD /CARDEN CROPS j (PCl/KG WEll l STA'110N NUMBER S-4 DATE COLLEC'IED: 05/30 06/27 07/25 08/29 09/26 : CABBAGE CABBAGE CABBAGE CABBAGE CABBAGE GAMMA SPECTRUM ANALYSIS: BE-7 4.4910.94 E 02 6.2110.62 E 02 1.0510.10 E 03 5.6910.80 E 02 4.8411.00 E 02 K-40 4.3010.43 E 03 2.0510.21 E 03 4.9110.49 E 03 4.5210.45 E 03 4.3110.43 E 03 MN-54 LT. 1. E 01 LT.7. E 00 LT.8. E 00 LT.9. E 00 LT. 1. E 01 o CO-58 LT. 1. E O1 LT.7. E 00 LT.8. E 00 LT.8. E 00 LT. 1. E OI
$ FE-59 LT. 3. E O1 LT.2. E O1 LT.2. E O1 LT.2. E 01 LT.3. E Oi
- E 01 LT.7. E 00 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 CO-60 LT. 1.
7 ZN-65 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.3. E 01
$ NB-95/ZR-95 LT. 1. E 01 LT.7. E 00 LT.9. E 00 LT.9. E 00 LT. 1. E 01 RU-103 LT. 1. E 01 LT.8. E 00 LT. 1. E 01 LT. 8. E 00 LT. 1. E 01 RU-106 LT. 1. E 02 LT. 6. E 01 LT.8. E 01 LT.8. E 01 LT. 1. E 02 I-131 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 CS-134 LT. 2. E 01 LT.8. E 00 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 CS-137 LT.2. E 01 LT.8. E 00 LT.9. E 00 LT.9. E 00 LT. 1. E 01 LA-140/BA-140 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 CE-141 LT.2. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 CE-144 LT.8. E 01 LT.4. E O1 LT.5. E 01 LT.5. E 01 LT.8. E 01 RA-226 LT.3. E 02 LT. 1. E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02 TH-228 LT. 3. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01
;T k. / 5 :/ E G G 3 G :;t4 r WOIX CREEE NUCl2AR OPERA 11NG CORPORATION EXPOSURE PATHWAY - INGESTION FOOD / GARDEN CROPS (PCI/KG WET)
STKI1ON NUMBER S-4 DKIE COLLECIED: 10/31 CABBAGE GAMMA SPECTRUM ANALYSIS: BE-7 2.5810.87 E 02 K-40 3.1610.32 E 03 MN-54 LT. 1. E 01 y CO-58 LT. 1. E 01 o FE-59 LT.3. E 01 CO-60 LT. 1. E 01 ZN-65 LT.3. E 01
$ NM5/ZR-95 LT. 1. E 01 RU-103 LT. 1. E 01 RU-106 LT. 1. E 02 1-131 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
M b / G U a~ D G 2 G;;+.4E WOEX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PK111WAY - INGES'110N MILK (PCI/ LITER) STA'llON NUMBER S-3 DATE COLLECIED: 01/10 02/14 03/14 04/11 04/25 RADIOCIIEMICAL ANALYSIS: I-131 LT.2 E-01 LT.2. E-01 LT. 1. E-01 LT. I. E-01 LT. 2. E-01 i GAMMA SPECI' RUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT. 3. E 01 C
] K-40 1.5710.16 E 03 1.3910.14 E 03 1.3110.13 E 03 1.3410.13 E 03 1.40iO.14 E 03 MN-54 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT. 3. E 00 CO-53 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00
' FE-59 LT.9. E 00 LT.7. E 00 LT.8. E 00 LT.9. E 00 LT.6. E 00 t D CO-60 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 ZN-65 LT. 1. E 01 LT. 9. E 00 LT.9. E 00 LT.9. E 00 LT.8. E 00 NB-95/ZR-95 LT.4. E 00 LT.3. 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.4. E 00 LT.4. E 00 LT.3. E 00 i 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.5. E 00 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.4. 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.4. E 00 LT.4. E 00 LT.4. E 00 LT.5. E 00 LA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 CE-141 LT.7. E 00 LT.5. E 00 LT.6. E 00 LT.7. E 00 LT. 6. E 00 CE-144 LT. 3. E 01 LT.2. E 01 LT. 3. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.8. E 01 LT.6. E 01 LT.8. E 01 LT.9. E 01 LT.7. E 01 TH-228 LT.8. E 00 LT.6. E 00 LT.7. E 00 LT.7. E 00 LT.6. E 00
=- . . -
a u / g ._n .E a a 3 :J u M .:.r WOIE CREEK NUCLEAR OPERA'I1NG CORPORATION EXPOSURE PATTIWAY - INGEST 10N MILK (PCI/ LITER) STA"I1ON NUMBER S-3 DATE COLLECTED: 05/09 05/23 06/13 06/27 06/27* RADIOCilEMICAL ANALYSIS: 1-131 LT.2. E-01 LT.2. E-01 LT.2. E-01 LT.5. E-01 LT. 5. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.6. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 y K-40 1.2810.13 E 03 1.3410.13 E 03 1.4110.14 E 03 1.5510.16 E 03 1.3610.14 E 03 o MN-54 LT.5. E 00 LT.4. E 00 LT. 3. E 00 LT.4. E 00 LT.3. E 00 CO-58 LT. 6. E 00 LT.3. E 00 LT.4. E 00 LT. 4. E 00 LT.3. E 00 FE-59 LT. 1. E OI LT.8. E 00 LT.8. E 00 LT.9. E 00 LT.7. E 00 $ CO-60 LT. 5. E 00 LT. 4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 ZN.65 LT. 1. E 01 LT. 1. E 01 LT.8. E 00 LT.9. E 00 LT. 7. E 00 NB-95/ZR-95 LT.6. E 00 LT.4. E 00 LT.4. E 00 LT. 4. E 00 LT.3. E 00 RU-103 LT.7. E 00 LT.4. E 00 LT. 4. E 00 LT.4. E 00 LT.4. E 00 RU-106 LT.6. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 I-131 LT. 1. E 01 LT.5. E 00 LT.6. E 00 LT.9. E 00 LT. 1. E 01 CS-134 LT.6. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.6. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT.8. E 00 LT.5. E 00 LT.4. E 00 LT.6. E 00 LT.7. E 00 CE-141 LT. 1. E 01 LT.7. E 00 LT.5. E 00 LT. 6. E 00 LT. 7. E 00 CE-144 LT.5. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT. 1. E 02 LT. 9. E 01 LT.7. E 01 LT.8. E 01 LT.7. E 01 TH.228 LT. 1. E 01 LT.7. E 00 LT.6. E 00 LT.7. E 00 LT.6. E 00
- Duplicate Analysis
-q .., n .3 - cc a y a 1y H r WOIX CREEK NUCIE.AR OPERA'11NG CORPORATION EXPOSURE PA'IEWAY - INGESTION MILK (PCl/ LITER)
STKI1ON NUMBER S-3 DA'IE COLLECIED: 07/11 07/25 08/09 08/22 09/12 RADIOCHEMICAL ANALYSIS: I-131 LT.2. E-01 LT.2. E-01 LT.3. E-01 LT.4. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 2 K-40 1.3610.14 E 03 1.3910.14 E 03 1.4110.14 E 03 1.4210.14 E 03 1.2410.12 E 03 MN-54 LT.4. E 00 LT.3. E 00 LT. 4. E 00 LT.4. E 00 LT.3. E 00
, CO-58 LT.5. E 00 LT.3. E 00 LT.4. E 00 L.T. 3. E 00 LT.3. E 00 g FE-59 LT. 1. E 01 LT. 8. E 00 LT.8. E 00 LT.8. E 00 LT.8. E 00 e CO-60 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 ZN-65 LT. 1. E 01 LT.9. E 00 LT.9. E 00 LT.8. E 00 LT.8. E 00 NB-95/ZR 95 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 RU-103 LT.5. E 00 LT.4. E 00 LT.4. E 00 L.T. 4. E 00 LT.4. E 00 RU-106 LT.4 E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 1-131 LT. 1. E 01 LT.7. E 00 LT.6. E 00 LT.4. E 00 LT.5. E 00 CS-134 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT. 5. E 00 LT.4. E 00 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 LT.4. E 00 - LT. 4. E 00 CE-141 LT. 1. E 01 LT.7. E 00- LT.6. E 00 LT.6. E 00 LT.6. E 00 CE-144 LT.4. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT. 1. E 02 LT.7. E 01 LT.7. E 01 LT.7. E 01 LT.7. E 01 TH-228 LT.9. E 00 LT.6. E 00 LT.7. E 00 LT.7. E 00 LT. 6. E 00
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WOtX CREEK NUCIZAR OPERATING CORPORATION EXPOSURE PA'IEWAY - INGESTION MILK (PCI/ LITER) STATION NUMBER S-3 DA'IE COLLECIED: 12/12 RADIOCHEMICAL ANALYSIS: , 1-131 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 g K-40 1.4410.14 E 03 & C MN.54 LT.4. E 00 CO-58 LT.4. E 00 LT.9. E 00 u's FE-59
- CO-60 LT.4. E 00 ZN-65 LT.9. E 00 NB-95/ZR-95 LT.4. E 00 RU-103 LT.4. E 00 ,
RU-106 LT.4. E 01 I-131 LT.5. 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.6. E 00 l
9 6 .-- G C/ i~ G G si G u C i r WOIX CREEK NUCIEAR OPERATING CORPORATTON EXPOSURE PATHWAY - AQUA 11C SEDIMENT SILT (pCi/KG DRY) STA110N NUMBER JRR DA'IE COILECTED: 10/18 . GAMMA SPECTRUM ANALYSIS: l BE-7 LT.4. E 02 K-40 1.67i0.17 E 04 MN-54 LT. 4. E 01 CO-58 LT.4. E 01 FE-59 LT. 1. E 02 cu CO-60 LT.4. E 01
$ ZN-65 LT. 1. E 02 co NB-95/ZR-95 LT.5. E 01 E RU-103 LT. 5. E 01
" RU-106 LT. 4. E 02 1-131 LT. 1. E 02 CS-134 LT.5. E O1 CS-137 2.2010.44 E 02 LA-140/BA-140 LT.7. E 01 CE-141 LT.8. E 01 CE-144 LT.3. E 02 RA-226 2.24i0.71 E 03 TH-228 1.2510.13 E 03
m t,.s 5 z^; E a :15 C11; H r WOIE CRERK NUCI2AR OPERATING CORPORA'I10N EXPOSURE PKIEWAY - AQUARC SEDIMENT / SILT (pC1/KG DRY) STAVON NUMBER DC r DA'IE COLLECIED: 05/15 10/18 GAMMA SPECIRUM ANALYSIS: BE-7 LT.4. E 02 LT.3. E 02 K-40 1.1110.11 E 04 1.3110.13 E 04 MN-54 6.1212.35 E 01 LT.4. E 01 CO.58 2.2010.38 E 02 LT.3. E 01 FE-59 LT.9. E 01 LT.7. E 01 o', CO-60 5.4810.55 E 02 1.0910.11 E 03
$ ZN-65 LT. 1. E 02 LT.8. E 01 m NB-95/ZR-95 LT. 5. E 01 LT.4. E 01
$ RU-103 LT.4. E 01 LT.4. E 01 W RU.106 LT.4. E 02 LT.3. E 02 I-131 LT. 8. E 01 LT 8. E 01 CS-134 1.2310.40 E 02 1.5210.32 E 02 CS-137 4.0010.46 E 02 6.2310.62 E 02 LA-140/BA-140 LT.7. E 01 LT.5. E 01 ;
CE-141 LT.6. E 01 LT.5. E 01 CE-144 LT.2. E 02 LT.2. E 02 RA-226 1.7210.63 E 03 2.0810.48 E 03 TH-228 1.0210.10 E 03 1.5410.15 E 03 i
qL,/; _ :CG G .;; O ll14. WOtX CREEK NUCIZAR OPERATING CORPORA 110N EXPOSURE PKIEWAY - AQUKI1C SEDIMENT / SILT (pCI/KG DRY) STK110N NUMBER WC & 1Ith ROAD DATE COLLECTED: 05/30 10/24 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 1.0910.37 E 03 K-40 1.1010.11 E 04 1.2110.12 E 04 MN-54 LT.3. E 01 LT.4. E 01 CO-58 LT.3. E 01 LT.4. E 01 y FE-59 LT.8. E 01 LT. 1. E 02 y CO-60 LT.4. E 01 LT.4. E 01 ! S ZN-65 LT 8. E 01 LT. 1. E 02 to NB-95/ZR-95 LT.4. E 01 LT.6. E 01 m RU-103 LT.4. E 01 LT.5. E 01 RU-106 LT.3. E 02 LT.4. E 02 I-133 LT.7. E 01 LT. 1. E 02 CS-134 LT.4. E 01 LT.5. E 01 CS-137 LT.5. E 01 9.8112.93 E 01 LA-140/BA-140 LT.5. E 01 LT.8. E 01 CE-141 LT. 6. E 01 LT.9. E 01 CE-144 LT.2. E 02 LT.3. E 02 RA-226 1.7510.52 E 03 2.51i0.70 E 03 e TH-228 1.09 0.11 E 03 1.2010.12 E 03 v
q s, ,-- s c./ c0 a 2 :J u i.; r WOIX CREEK NUCIZAR OPERATING CORPORATION EXPOSURE PADIWAY - WKIERBORNE SilORELINE SOIL (pC1/KG DRY) STA110N NUMBER DC DATE COLLECTED: 05/15 10/18 CAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 LT. ' 3. E 02 K-4 0 8.9410.89 E 03 6.5710.66 E 03 MN-54 LT.3. E 01 LT.3. E 01 CO-58 LT. 4. E 01 LT.4. E 01 FE-59 LT.8. E 01 LT.7. E 01 '
.j CO-60 1.1510.36 E 02 1.6810.30 E 02 y ZN-65 LT.9. E 01 LT.8. E 01 g NB-95/ZR-95 LT.5. E 01 LT.4. E 01 8
RU-103 LT.4. E 01 LT.4. E 01 ; m RU-106 LT.3. E 02 LT.3. E 02 I-131 LT.7. E 01 LT.8. E 01 CS-134 LT.5. E 01 LT.4. E 01 , CS-137 8.8514.00 E 01 2.0710.35 E 02 LA-140/BA- 140 LT.6. E 01 LT.6. E 01 CE-141 LT.7. E 01 LT.5. E 01 - CE-144 LT. 3. E O2 LT.2. E 02 RA-226 1.9510.64 E 03 1.3410.49 E 03 Til-228 1.0510.11 E 03 9.0210.90 E 02
-q u , g z,- E D c 2 0 :; a r WolE CREEK NUC1JtAR OPERATING CORPORATION EXPOSURE PAT 11WAY - WATERBORNE SIIORELINE SOIL (pCl/KG DRY)
STATION NUMBER EEA DATE COLLECIED: 10/16 CAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 K-40 9.1410.91 E 03 MN-54 LT. 3. E 01 CO-58 LT.3. E 01 FE-59 LT.6. E 01 A CO-60 LT.3. E 01 $ ZN-65 LT. 6. E 01 m NB-95/ZR-95 LT.3. E 01 & RU-103 LT.3. E 01
- RU- 106 LT. 2. E 02 1-131 LT.7. E 01 CS-134 LT.3. E 01 CS-137 9.0612.69 E O1 LA-140/BA-140 LT.5. E 01 CE-141 LT.5. E 01 CE-144 LT.2. E 02 RA-226 1.4810.46 E 03 TII-228 9.0910.91 E 02
9 6 / 5 . y .; Cr a _Ta .z; g.i r WOlJ CREEK NUClJtAR OPERATING CORPORATION EXPOSURE PAT 1IWAY - WATERBORNE SIIORELINE SOIL (pCl/KG DRY) STA'I1ON NUMBER JRR DATE COLLECTED: 06/23 10/18 GAMMA SPECTRUM ANALYSIS: BE-7 5.5410.55 E 03 LT.4. E 02 K-40 1.2110.12 E 04 8.3610.84 E 03 MN-54 LT.3. E 01 LT.4. E 01 CO-58 LT.3. E 01 LT.3. E 01 FE-59 LT. 9. E 01 LT.8. E 01 2 CO-60 LT.3. E 01 LT.4. E 01
$ ZN.65 LT.8. E 01 LT. 9. E 01 m NB-95/ZR-95 LT.4. E 01 LT.5. E 01
' RU-103 LT.4. E 01 LT.4. E 01
'8 RU- 106 LT.3. E 02 LT.3. E O2 I-131 LT. 1. E 02 LT. 1. E 02 CS-134 LT.4. E 01 LT.5. E 01 CS-137 2.0410.35 E 02 LT.4. E 01 LA-140/BA-140 LT.8. E 01 LT.7. E 01 CE-141 LT.7. E U1 LT.7. E 01 CE-144 LT.2. E 02 LT.3. E 02 RA-226 1.2210.53 E 03 4.0810.68 E 03 Til-228 5.0710.51 E 02 1.5710.16 E 03
q s ,~::: cv c c a J L; n w r r WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PKIEWAY 'IERRESTRIAL SOIL (pCl/KG DRY) STA110N NUMBER MUDS DATE COLIECIED: 06/15 10/16 GAMMA SPECI' RUM ANALYSIS: BE-7 LT.4. E 02 LT.4. E 02 K-40 1.3210.13 E 04 ).1210.11 E 04 MN-54 LT.4. E 01 LT.4. E 01 CO-58 LT.3. E 01 LT.4. E 01 FE-59 LT.8. E 01 LT.8. E 01 A CO-60 LT.4. E 01 LT.4. E 01 m ZN-65 LT.9. E 01 LT.9. E 01 m NB-95/ZR-95 LT.5. E 01 LT.5. E 01 5 RU-103 LT.4. E 01 LT.5. E 01
- RU-106 LT.3. E 02 LT.3. E 02 1-131 LT.9. E 01 LT. 1. E 02 CS-134 LT.5. E 01 LT.5. E 01 CS-137 8.20i3.45 E O1 LT.5. E O1 LA-140/BA-140 LT.6. E 01 LT.7. E 01 CE-141 LT.7. E 01 LT.8. E 01 CE-144 LT.2. E 02 LT.3. E 02 RA-226 1.87i0.61 E 03 2.3410.71 E 03 TH-228 1.3510.13 E 03 1.2810.13 E 03
--_____ _ _ ___-__m 2_._m__ __ ____
qn a gcv-r g ..g .a G #1,-! _r_ WOIX CREEK NUCIEAR OPERATING CORPORATION EXPOSURE PA"IllWAY "IERRESTRIAL SOIL (pCl/KG DRY) I STA110N NUMBER EEA DATE COLLECIED: 06/15 10/16 GAMMA SPECTRUM ANALYSIS: BE-7 1.68 i 0.36E 03 LT.3. E 02 K-40 1.1810.12 E 04 1.3410.13 E 04 - MN-54 LT.4. E 01 LT.3. E 01 CO-58 LT.4. E 01 LT.4. E 01 FE-59 LT.9. E 01 LT.9. E 01 2 CO-60 LT.4. E 01 LT.3. E 01 ZN-65 LT. 1. E 02 LT. 8. E 01 m NB-95/ZR-95 LT.5. E 01 LT.5. E 01
& RU-103 LT.4. E 01 LT.4. E 01
- RU-106 LT.4. E 02 LT.3. E 02 1 1-131 LT. 1. E 02 LT. 1. E 02 CS-134 LT.5. E 01 LT. 4. E 01 CS-137 2.6010.45 E 02 2.1210.39 E 02 LA-140/BA-140 LT.6. E 01 LT.8. E 01 CE-141 LT.7. E 01 LT. 6. E 01 CE-144 LT.3. E 02 LT.2. E O2 RA-226 1.5210.65 E 03 2.2410.52 E 03 TH-228 1.0610.11 E 03 1.1610.12 E 03
(
!; k / 5 G - E x7 G _='G U y~[ r WOLF CREEK NUCIZAR OPERATING CORPORATION EXPOSURE PAT 1IWAY - AQUATIC VEGETATION - AQUATIC (pCl/KG WET)
STAT 10N NUMBER DC DATE COLLECTED: 05/15 08/25 AIDAE AIDAE GAMMA SPECTRUM ANALYSIS: BE-7 8.4410.84 E 02 5.7010.57 E 02 K-4 0 2.0010.20 E 03 1.4310.14 E 03 MN-54 1.6910.38 E 01 1.7610.34 E 01 CO-58 1.9210.19 E 02 6.8710.69 E 01 y FE-59 LT. 1. E 01 LT.9. E 00 o CO 60 1.1810.12 E 02 1.4510.15 E 02 ZN-65 LT. 1. E 01 LT.9. E 00 NB-95/ZR-95 2.0710.74 E 01 LT.5. E 00
$ RU-103 LT.5. E 00 L T. 5. E 00 RU-106 LT.4. E 01 LT.4. E 01 1-131 LT.7. E 00 LT.8. E 00 CS-134 LT.7. E 00 LT. 6. E 00 CS-137 6.1910.62 E O1 4.7310.48 E O1 LA-140/BA-140 LT. 6. E 00 LT.6. E 00 CE-141 LT.8. E 00 LT.8. E 00 CE-144 LT.3. E 01 LT.3. E 01 RA-226 4.3110.83 E O2 2.8310.66 E 02 Til-228 1.9410.19 E 02 1.5410.15 E 02 NB-95 3.1710.36 E 01 4
qs/ 3 D-CC G ;.10 :)ME WOIX CREEK NUCIE.AR OPERATING CORPORATION EXPOSURE PAT 11WAY - AQUATIC VEGETAT10N - AQUATIC (pCl/KG WE'll STATION NUMBER ALT DC DATE COLLECIED: 08/25 AM LUITJS GAMMA SPECTRUM ANALYSIS: BE-7 1.8410.77 E 02 + K-4 0 2.2010.22 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 y FE-59 LT.3. E 01 C CO-60 LT. 1. E 01 ZN-65 LT.3. E 01
- NB-95/ZR-95 LT. 1. E 01
$ RU-103 LT. 1. E 01 RU-10G LT. 1. E 02 1 131 LT. 2. 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.6. E 01 RA-22G LT.2. E 02 Til-228 LT.2. E 01 ,
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WOIE CREEK NUCLEAR OPERATE 40 CORPORATION y EXPOSURE PAT 11WAY - AQUAVC VEGETADON - AQUABC (pC1/KG WE'O STABON NUMBER EEA DATE COLLECTED: 06/15 ARROWIIEAD CAMMA SPECTRUM ANALYSIS: BE-7 1.8310.68 E 02 K-40 3.7010.37 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 A FE-59 LT.2. E 01
$ CO-60 LT. 1. E 01 m ZN-65 LT.2. E 01 k NB-95/ZR-95 LT. 1. E 01 N 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 1.6510.84 E O1 LA-140/BA-140 LT.2. E 01 CE-141 LT.2. E 01 CE-144 LT.6. E 01 RA-226 2.4311.25 E 02 TII-228 1.5410.15 E 02
.q 1, ,-' s .5 - E a .a 2 ;2 a 64 r WOIF CREEE NUCIRAR OPERATING CORPORATION EXPOSURE PAlifWAY- AQUA 11C VEGETA110N - AQUA 11C (pCl/KG WET)
STA110N NUMBER MUDS DATE COLLECTED: 10/11 PONDWEED GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 K-4 0 2.1910.22 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 g FE-59 LT.2. E 01 C CO-60 LT. 1. E 01 , ZN-65 LT.2. E 01 8 NB-95/ZR-95 LT. 1. E 01 cn w RU-103 LT. 1. E 01 RU- 106 LT. 1. E 02 I-131 LT.2. E 01 CS-134 LT. 1. E 01 CS-137
- L T. 1. E 01 LA-140/BA- 140 LT.2. E 01 CE-141 LT.2. E 01 CE-144 LT.7. E 01 RA-226 LT.2. E 02 TII-228 LT.2. E 01
q u / ~_: .3./ cc c 2::J 1;p r ' WOIX CREEK NUCIZAR OPERATING CORPORATION EXPOSURE PA'IIIWAY 'IERRESTR'AL VEGETA'110N 'IERRESTRIAL (pCl/KG WEB STATION NUMBER MUDS DA'IE COLLECIED: 06/15 10/16 TERRESTRIAL TERRESTRIAL GAMMA SPECTRUM ANALYSIS: BE-7 3.0410.30 E 03 3.1210.35 E 03 K-40 4.1610.42 E 03 4.7710.48 E 03 MN-54 LT. 2. E 01 LT.4. E 01 CO-58 LT.2. E 01 LT.4. E 01 o FE.59 LT.4. E 01 LT.9. E 01
$ CO-60 LT.2. E 01 LT.4. E 01
- E 01 ZN-65 LT.4. E 01 LT.9.
7 NB-95/ZR-95 LT.2. E 01 LT.4. E 01
$ RU-103 LT. 2. E 01 LT. 4. E 01 ,
RU-106 LT.2. E O2 LT.3. E 02 I-131 LT.4. E 01 LT.8. E 01 CS-134 LT.2. E 01 LT.4. E 01 CS-137 LT. 2. E 01 LT.4. E 01 LA-140/BA-140 LT. 3. E 01 LT.6. E 01 CE-141 LT.3. 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 TII-228 LT.4. E 01 LT. 6. E 01
9 k.r ." 15 C/ ~ U _ G J *~ia:M I WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PA'111WAY "IERRESTRIAL VEGETA~i10N - TERPESTRIAL (pCl/KG WET) STATION NUMBER EEA DATE COLLECTED: 06/15 10/16 TERRESTRIAL TERRESTRIAL GAMMA SPECTRUM ANALYSIS: BE-7 1.5310.16 E 03 1.3910.15 E 03 K-4 0 3.8010.38 E 03 7.0410.70 E 03 MN-54 LT.2. E 01 LT.2. E 01 CO-58 LT. 2. E 01 LT.2. E 01 y FE-59 LT.4. E 01 LT.4. E 01 u3 CO-60 LT. 2. E 01 LT.2. E 01 ZN-65 LT.4. E 01 LT.4. E 01 U NB-95/ZR-95 LT.2. E 01 LT.2. E 01
$ RU-103 LT.2. E 01 LT.2. E 01 RU-106 LT.2. E 02 LT. 1. E 02 I-131 LT.4. E 01 LT.3. E 01 CS-134 LT.2. E 01 LT.2. E 01 CS-137 LT.2. E 01 LT.2. E 01 1A-140/BA-140 LT.3. E 01 LT.2. E 01 CE-141 LT.3. E 01 LT.2. E 01 CE- 144 LT. 1. E 02 LT.9. E 01 RA-226 LT.3. E 02 LT. 3. E 02 Til-228 LT.3. E 01 LT.3. E 01
m L.:/.57C:/ E C G HLTz; 5..t E WOIE CREEK NUCLEAR OPERATING CORPORATION EXIOSURE PN11IWAY - WKIERBORNE DRINKING WATER (PCl/ LITER) STATION NUMBER BW15 DATE COLLECTED: 01/03-02/07 02/07-03/07 03/07-04/04 04/04-05/02 04/04-05/02* RADIOCllEMICAL ANALYSIS: GR-B 6.4 1 1.3 E 00 7.7 i 1.4 E 00 6.6 i 1.2 E 00 5.9 i 1.7 E 00 6.7 i 1.8 E 00 1-131 LT.6. E-Ol LT.3. E-01 LT. 5. E-01 LT. 1. E 00 LT. 1. E 00 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 3. E 01 LT.3. E OI LT.3. E O1 LT.5. E O1 LT.2. E 01 2 K-40 LT.8. E 01 LT.9. E 01 LT.9. E 01 LT.7. E 01 LT.5. E 01
- MN-54 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 m CO-58 LT. 3. E 00 LT.3. E 00 LT. 3. E 00 LT.4. E 00 LT.3. E 00 g FE-59 LT.7. E 00 LT.7. E 00 LT.7. E 00 LT. 1. E O1 LT.6. E 00 cn CO-60 LT.3. E 00 LT. 3. E 00 LT. 4. E 00 LT.5. E 00 LT.3. E 00 ZN-65 LT.8. E 00 LT.7. E 00 LT. 7. E 00 LT.9. E 00 LT.5. E 00 NB-95/ZR-95 LT. 3. E 00 LT.3. E 00 LT. 3. E 00 LT.5. E 00 LT.3. E 00 RU-103 LT.4. E 00 LT.4. E 00 LT. 4. E 00 LT.6. E 00 LT.3. E 00 RU 106 LT.3. E O1 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.2. E 01 1-131 LT.5. E 00 LT.5. E 00 LT.5. E 00 LT. 1. E 01 LT.7. E 00 CS-134 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT. 1. E 01 LT. 5. E 00 CE-141 LT.7. E 00 LT. 5. E 00 LT.6. E 00 LT. 1. E 01 LT. 6. E 00 CE-144 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.8. E 01 LT.7. E 01 LT.7. E 01 LT. I. E 02 LT.6. E 01 TH-228 LT.6. E 00 LT.6. E 00 LT.6. E 00 LT.9. E 00 LT. 5. E 00 TRI'I1UM ANALYSIS: 0I/03-04/04 11-3 LT.3. E 02
- Duplicate analysis
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q u . - su ra a an wr i wots CREEK NUCLEAR OPERAMNG CORPORAMON EXPOSURE PATrIWAY - WA~IERBORNE DRINKING WA'IER (PCI/ LITER) STA'110N NUMBER BW15 DATE COLLEC'IED: 05/02-06/06 05/02 06/06* 06/06-07/05 07/05-08/02 08/02-09/05 RADIOCHEMICAL ANALYSIS: GR-B 6.5 i 1.7 E 00 4.3 i 1.6 E 00 5.8 i 1.2 E 00 7.9 i 1.3 E 00 7.1 i 1.3 E 00 I-131 LT.8. E-01 LT. 1. E 00 LT. 1. E-01 LT. 5. E-01 LT.8. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 2. E 01 y K-40 LT. 5. E 01 LT.5. E 01 LT.8. E 01 LT.8. E 01 LT.5. E 01 .
$ MN-54 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT. 3. E 00
- CO-58 LT.3. E 00 LT.3. E 00 LT.4. 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.6. E 00 LT.5. 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 ZN-65 LT.6. E 00 LT.7. E 00 LT.7. E 00 LT. 7. E 00 LT.5. E 00 NB-95/ZR-95 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 RU-103 LT.4. E 00 LT.4. E 00 LT.4. 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.3. E 01 LT.3. E 01 1-131 LT.8. E 00 LT. 1. E 01 LT.7. E 00 LT.5. 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 l CS-137 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 i LA-140/BA-140 LT.5. E 00 LT.8. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.7. E 00 LT.7. E 00 LT.5. E 00 LT.6. E 00 LT. 5. E 00 t CE-144 LT.3. E 01 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.7. E 01 LT.6. E 01 TH-228 LT.6. E 00 LT.6. E 00 LT.7. E 00 LT. 6. E 00 LT.5. E 00 ,
TRrI1UM ANALYSIS: 04/04-07/05 07/08-10/03 H-3 LT.2. E 02 LT. 2. E 02
- Duplicate analysis e
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q t, n u CU c 2 GT o p.i E WOLF CREEK NUCLEAR OPERA 11NG CORPORATION EXPOSURE PA111WAY- WATERBORNE DRINKING WATER (PCl/ LITER) STA110N NUMBER LW40 DA'IE COLLECTED: 01/03-02/07 02/07-03/07 03/07-04/04 04/04-05/02 05/02-06/06 RADIOCilEMICAL ANALYSIS: GR-B 6.3 i 1.4 E 00 4.8 i 1.3 E 00 7.0 i 1.3 E 00 6.3 i 1.9 E 00 4.5 i 1.6 E 00 1-131 LT.8. E.01 LT.5. E-01 LT.5. E-01 LT.6. E-01 LT. 5. E-01 GAMMA SPECTRUM ANALTSIS: n BE-7 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT. 2. E 01 LT. 3. E 01 e K-40 LT.6. E 01 LT.5. E 01 LT. 1. E 02 LT. 5. E 01 LT.9. E 01
*' MN-54 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 m CO-58 LT.3. E 00 LT. 3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 b FE-59 LT.6. E 00 LT.6. E 00 LT.9. E 00 LT.5. E 00 LT.8. E 00 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.7. E 00 LT.6. E 00 LT. 1. E 01 LT.5. E 00 LT.7. E 00 NB-95/ZR-95 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 RU- 103 LT.4. E 00 LT.3. E 00 LT.5. E 00 LT.3. E 00 LT.4. E 00 RU-106 LT. 3. E 01 LT.3. E 01 LT.4. E 01 LT. 2. E 01 LT.3. E 01 1-131 LT.5. E 00 LT.6. E 00 LT.6. E 00 LT.7. E 00 LT.8. E 00 CS-134 LT.3. E 00 LT.3. E 00 LT.5. E 00 LT.3. E 00 LT.4. E 00 CS-137 LT.4. E 00 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. 5. E 00 LT.5. E 00 LT. 5. E 00 CE-141 LT.6. E 00 LT.6. E 00 LT.8. E 00 LT.6. E 00 LT.6. E 00 CE-144 LT.3. 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.7. E 01 LT.9. E 01 LT.6. E 01 LT.7. E 01 Til-228 LT.6. E 00 LT.7. E 00 LT.8. E 00 LT.5. E 00 LT.7. E 00 TR111UM ANALYSIS: 01/03-04/04 04/04-07/05 11-3 LT.3. E 02 LT.2. E 02
i
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- WORE Ceter NUCLRAR OPERA'I1NG CORPORATTON t EXPOSURE PA1MWAY - WATERBORNE i
DRINKING WA*IER i (PCI/ LITER) ; STA*110N NUMBER LW40 I , DATE COLLECIED: 06/06-07/05 07/05-08/02 08/02-09/05 09/05-10/03 10/03-11/07 RADIOCHEMICAL ANALYSIS: , GR-B 5.4 i 1.2 E 00 5.1 i 1.1 E 00 6.8 i 1.4 E 00 7.6 i 1.4 E 00 1.1 1 0.2 E 01 : 1-131 LT.2. E-01 LT.5. E-01 LT.7. E-01 LT.4. E-01 LT.2. E-01 GAMMA SPECIRUM ANALYSIS: o BE-7 LT. 3. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.3. E 01
$* K-40 LT.8. E 01 LT.6. E 01 LT.5. E 01 LT.5. E 01 LT.5. E 01 l MN.54 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 7 CO-58 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.3. E 00 y FE.59 LT.7. E 00 LT.6. E 00 LT.6. E 00 LT.5. E 00 LT.6. E 00 CO-60 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 ZN-65 LT.7. E 00 LT.7. E 00 LT.6. E 00 LT.6. E 00 LT. 6. E 00 NB-95/ZR-95 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 RU-103 LT.4. 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 I-131 LT.7. E 00 LT. 6. E 00 LT.4. E 00 LT.5. E 00 LT.4. E'00 CS-134 LT.4. E 00 LT.4. E 00 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 LT.3. E 00 LT.3. E 00 LA-140/BA-140 LT.5. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 CE-141 LT. 6. E 00 LT. 6. E 00 LT.6. E 00 LT.6. E 00 LT.6. E 00 CE-144 LT.2. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.3. E 01 RA-226 LT.7. E 01 LT.7. E 01 LT.7. E 01 LT. 6. E 01 LT.8. E 01 ; TH-228 LT.7. E 00 LT.6. E 00 LT.6. E 00 LT.5. E 00 LT.6. E 00 TRITIUM ANALYSIS: 07/08-10/03 , H-3 LT.2. E 02
. . _ . _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ . _ . . _ _ _ . _ _ . _ _ _ . _ _ _ _ _ ___ _ _ m _ ___._____ __ _ _ _ _ _ _ . _ . _ _ _
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WOIF CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA~HlWAY - WATERBORNE DRINKING WATER (PCI/ LITER) STA'I1ON NUMBER LW40 DATE COLLECIED: 11/07-12/05 12/05-01/03 RADIOCIIEMICAL ANALYSIS: GR-B 8.6 i 1.G E 00 7.3 i 1.5 E 00 I-131 LT. 5. E-01 LT.5. E-01 GAMMA SPECTRUM ANALYSIS: o BE-7 LT.2. E 01 LT.3. E 01
$ K-40 LT.4. E 01 LT. 5. E 01
- MN-54 E 00 LT. 2. LT.3. E 00 7 CO-58 LT.2. E 00 LT. 3. E 00 j FE-59 LT.4. E 00 LT.7. E 00 CO-60 LT.3. E 00 LT.3. E 00 ZN-65 LT.5. E 00 LT.7. E 00 NB-95/ZR-95 LT.3. E 00 LT.3. E 00 RU-103 LT.3. E 00 LT.3. E 00 RU-106 LT.2. E 01 LT. 3. E 01 I-131 LT.3. E 00 LT.6. E 00 CS-134 LT.2. E 00 LT.3. E 00 CS-137 LT.3. E 00 LT.4. E 00 LA-140/BA-140 LT.3. E 00 LT.6. E 00 CE-141 LT.5. E 00 LT.7. E 00 CE-144 LT.2. E 01 LT.3. E 01 RA-226 LT.5. E 01 LT. 7. E 01 Til-228 LT.4. E GO - LT. 7. E 00 -
TRIT 1UM ANALYSIS: 10/03-01/03 11- 3 LT.2. E O2
sq u <:G u r a G2 CUM: WOIX CREEK NUCl2AR OPERATfMG CORPORATION EXPOSURE PATTIWAY - WA'IERBORNE CROUND WATER (PCI/ LITER) STAT 10N NUMBER B-12 DATE COLLECTED: 02/22 05/16 08/22 11/21 RADIOCIIEMICAL ANALYSIS: I-131 LT.2. E-01 LT.2. E-01 LT.3. E-01 LT.2. E-01 GAMMA SPECIRUM ANALYSIS: DE-7 LT.3. E 01 LT.3. E 01 LT. 3.- E 01 LT.3. E 01 K-4 0 LT.5. E 01 LT. 1. E 02 LT.6. E 01 LT.8. E 01 y MN-54 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 g CO-58 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00
- FE-59 LT.7. E 00 LT. 8. E 00 LT.6. E 00 LT. 6. E 00 y CO-60 LT.3. E 00 LT. 4. E 00 LT.3. E 00 LT. 3. E 00 N ZN-65 LT. 7. E 00 LT.7. 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.3. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.4. E OI LT.3. E 01 LT.3. E O1 I-131 LT.4. E 00 LT. 7. E 00 LT.4. E 00 LT.6. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT.4. E 00 LT.6. E 00 LT.5. E 00 LT.4. E 00 CE-14 I LT.5. E 00 LT. 6. E 00 LT.6. E 00 LT.5. 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.8. E 01 LT.8. E 01 LT.6. E 01 Til-228 LT.6. E 00 LT.8. E 00 LT.7. E 00 LT.6. E 00 TRIT 1UM ANALYSIS: i 11-3 LT.2. E 02 LT.3. E 02 LT.3. E 02 LT. 2. E 02 l r
n s / g t/ c a . a z:J u u r woss enEEE NUCLEAR OPERA 1 MEG COMPORADON EXPOSURE PA11tWAY - WKIERBORNE GROUND WATER i (PCI/ LITER) STATION NUMBER C-10 DKIE COLLECIED: 02/22 05/16 08/22 11/21 r .i RADIOCHEMICAL ANALYSIS: 1-131 LT.2. E-01 LT.2. E-01 LT.4. 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 i K-40 LT. 9. E 01 LT. 1. E 02 LT.6. E 01 LT.6. E 01 l 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 to to FE-59 LT.7. E 00 LT. 8. E 00 LT.6. E 00 LT.8. E 00 to CO-60 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 '
b ZN-65 LT.7. E 00 LT.7. E 00 LT.7. E 00 LT.7. E 00 NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 t RU-103 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT. 4. E 00 i RU-106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 I I-131 LT.4. E 00 LT.7. E 00 LT.5. E 00 LT.7. E 00
, CS-134 LT.4. E 00 LT.4. 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 LA-140/BA-140 LT.4. E 00 LT.6. E 00 LT.4. E 00 LT.7. E 00 CE-141 LT.5. E 00 LT.7. E 00 LT.7. E 00 LT.8. E 00 CE-144 LT.2. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 RA-226 LT.7. E 01 LT.8. E 01 LT.9. E 01 LT.8. E 01 TH-228 LT.6. E 00 LT.7. E 00 LT.8. E 00 LT.8. E 00 TR111UM ANALYSIS:
H-3 LT.2. E 02 LT.3. E 02 LT.3. E 02 LT.2. E 02
s r g 2.:.: ca a . a v si r WOIE CREEK NUCLEAR OPERAT1NG CORPORATION EXPOSURE PATHWAY - WATERBORNE GROUND WKIER (PCI/ LITER) STA~ITON NUMBER C-49 DATE Coll.ECTED: 02/22 05/16 08/22 11/21 RADIOCHEMICAL ANALYSIS: I-131 LT.2. E-01 LT. 2. E-01 LT.3. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 o K-40 LT. 1. E 02 LT.9. E 01 LT. 5. E 01 LT.8. E 01 $ MN-54 LT.4. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00
- CO-58 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT. 3. E 00 7 FE-59 LT. 9. E 00 LT.7. E 00 LT.6. E 00 LT. 7. E 00
% CO-60 LT.5. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 ZN-65 LT. 1. E 01 LT,7. E 00 LT.6. E 00 LT.8. E 00 NB-95/ZR-95 LT.6. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 RU- 103 LT.5. E 00 LT.4. E 00 LT 3. E 00 LT.4. E 00 RU-106 LT.4. E 01 LT.4. E 01 LT.3. E 01 LT. 3. E 01 I-131 LT. 6. E 00 LT.7. E 00 LT.4. E 00 LT.6. E 00 CS-134 LT. 5. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.5. E 00 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.4. E 00 LT.4. E 00 CE-141 LT.7. E 00 LT.7. E 00 LT. 6. E 00 LT.6. E 00 CE-144 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.9. E 01 LT.9. E 01 LT.7. E 01 LT.7. E 01 TH.228 LT.9. E 00 LT.7. E 00 LT.7. E 00 LT.6. E 00 TRITIUM ANALYSIS: 11-3 LT.2. E 02 LT.3. E 02 LT.2. E 02 LT. 2. E 02 _ _ - _ _ _ _ _ _ . __ _ __________ -____ - _________ - -_____________ _ _____ -______-- _ - -__ -__ - --__ - _ _ _ - _ _ _ ~
s s / s;r/ cc a2anur WORF CREEE NUCLEAR OPERATEGO CORPORATION EXPOSURE PA'nIWAY - WATERBORNE GROUND WATER i (PCI/ LITER) STATION NUMBER D-65 DA'IE COI1EC'IED: 02/22 05/16 08/22 11/21 RADIOCHEMICAL ANALYSIS: I-131 LT. 2. E-01 LT. 2. E-01 LT.4. E-01 LT.2. E-01 GAMMA SPEC'IRUM ANALYSIS: BE-7 LT.3. E 01 LT.4. E 01 LT.2. E 01 LT.3. E 01 o K-40 LT. 5. E 01 LT. 1. E 02 LT.5. E 01 LT.5. E 01
$ MN-54 LT.3. E 00 LT.4. E 00 LT.2. E 00 LT.3. E 00
- E 00 E 00 CO-58 LT.3. E 00 LT.4. LT.2. LT.2. E 00 7 FE-59 LT.7. E 00 LT.8. E 00 LT.5. E 00 LT.5. E 00 y CO-60 LT 4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 03 ZN-65 LT.8. E 00 LT.9. E 00 LT.5. E 00 LT.6. 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.4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 RU-106 LT. 3. E 01 LT.4. E 01 LT.2. E 01 LT. 3. E 01 1-131 LT.6. E 00 LT.7. E 00 LT.4. E 00 LT.5. E 00 CS-134 LT.4. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 CS-137 L'r. 4. E 00 LT.5. E 00 LT.4. E 00 LT.3. E 00 LA-140/BA-140 LT.5. E 00 LT.6. E 00 LT.3. E 00 LT.4. E 00 CE-141 LT.8. E 00 LT.7. E 00 LT. 5. E 00 LT.6. E 00 CE-144 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT.9. E 01 LT.9. E 01 LT.6. E 01 LT.7. E 01 TH-228 LT.7. E 00 LT.8. E 00 LT. 5. E 00 LT.6. E 00
. TRn1UM ANALYSIS: H-3 LT.2. E 02 LT.3. E 02 LT.3. E 02 LT.2. E 02
q t , / s ;n.m a a 2 ., :p w .r WOIE CREEK NUCLEAR OPERATING CORPORATION ' EXPOSURE PATIIWAY - WATERBORNE GROUND WATER (PCI/ LITER) STATION NUMBER F-20 (DUPLICATE SAMPLES FROM STA110N NUMBER B-12) DATE COLLECIED: 02/22 05/16 08/22 11/21 11/21* RADIOCIIEMICAL ANALYSIS: I l-131 LT.2. E-01 LT.2. E-01 LT.4. E-01 LT.4. E-01 LT. 4. E-01 CAMMA SPECI' RUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.5. E 01 y K-4 0 LT.7. E 01 LT.8. E 01 LT.5. E 01 LT. 1. E 02 LT.2. E 02 l g MN-54 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.5. E 00 to CO-58 LT.4. E 00 LT.4. E 00 LT.2. E 00 LT.4. E 00 LT.5. E 00 ' cn FE-59 LT.8. E 00 LT.7. E 00 LT.6. E 00 LT.8. E 00 LT. 1. E 01 ! b CO-60 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.5. E 00 2N-65 LT.8. E 00 LT.7. E 00 LT. 6. E 00 LT.8. E 00 LT. 1. E 01 NB-95/ZR-95 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT. 5. E 00 RU-103 LT.5. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT. 6. E 00 RU- 106 LT. 4. E 01 LT.3. E 01 LT.2. E 01 LT.4. E 01 LT.5. E 01 I-131 LT.7. E 00 LT.7. E 00 LT.5. E 00 LT. 7. E 00 LT. 1. E 01 CS-134 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.5. E 00 LT.6. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT. 6. E 00 l IA-140/BA- 140 LT.6. E 00 LT.5. E 00 LT.4. E 00 LT. 6. E 00 LT. 7. E 00 i CE-141 LT.9. E 00 LT. 6. E 00 LT.6. E 00 LT.6. E 00 LT.9. E 00 CE-144 LT.4. E 01 LT.2. E 01 LT. 3. E 01 LT.2. E 01 LT.4. E 01 RA-226 LT. 1. E 02 LT.8. E 01 LT. 7. E 01 LT.7. E 01 LT. 1. E 02 Til-228 LT.9. E 00 LT.7. E 00 LT.6. E 00 LT.6. E 00 LT. 8. E 00 TRI11UM ANALYSIS: 11-3 LT.2. E 02 LT. 3. E 02 LT.2. E 02 LT.2. E 02 LT.2. E 02
- Duplicate Analysis
q s- 2pra a _m v : : .r WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA111WAY - WATERBORNE SURFACE WATER (PCI/ LITER) STATION NUMBER MUSII DATE COLLECTEC 01/17 02/22 02/22* 03/21 04/25 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 K-40 LT.5. E 01 LT. 1. E 02 LT. 7. E 01 LT.7. E 01 LT.9. E 01 MN-54 LT.3. E 00 LT. 4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 y CO-58 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT. 3. E 00 g FE-59 LT.7. E 00 LT.8. E 00 LT.G. E 00 LT.7. E 00 LT.7. E 00 (D CO-60 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 tn ZN-65 LT.7. E 00 LT. 8. E 00 LT.7. E 00 LT.7. E 00 LT.7. E 00 b NB-95/ZR-05 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU-103 LT.3. E 00 LT.4. E 00 LT.4. 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.6. E 00 LT. 6. E 00 LT. 5. E 00 LT.5. E 00 CS-134 LT.4. E 00 LT.4. E 00 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 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.S. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.6. E 00 LT. 6. E 00 LT.8. E 00 LT.6. E 00 CE-144 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.4. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.7. E 01 LT.7. E 01 LT. 1. E 02 LT.7. E 01 T11-228 LT.7. E 00 LT. 6. E 00 LT.6. E 00 LT.9. E 00 LT.6. E 00 TRrl1UM ANALYSIS: H-3 LT.2. E 02 LT.2. E 02 LT.2. E 02 LT.2. E C2 LT.2. E 02
- Duplicate analysis
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9 k , " 5 C. - C U G :1 G 13 H E 4 WOlE CREEK NUCl2AR OPERATEUG CORPORATION EXPOSURE PATHWAY - WATERBORNE SURFACE WA1ER (PCI/ LITER) STATION NUMBER MUSH DATE COLLEC'IED: 10/24 11/21 12/20 GAMMA SPEC 1' RUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 K-4 0 LT. 5. E 01 LT.6. E 01 LT.9. E 01 MN-54 LT.3. E 00 LT.4. E 00 LT.3. E 00 y CO-58 LT.3. E 00 LT. 3. E 00 LT.3. E 00 g FE-59 LT.6. E 00 LT.8. E 00 LT.6. E 00 ! o CO-60 LT.3. E 00 LT.3. E 00 LT.3. E 00 - m ZN-65 LT.7. E 00 LT.8. E 00 LT.6. E 00 b NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU-103 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 I-131 LT.4. E 00 LT.7. E 00 LT.5. E 00 CS-134 LT.3. E 00 LT.4. E 00 LT.3. E 00 , CS-137 LT.3. E 00 LT.4. E 00 LT.3. E 00 LA-140/BA-140 LT.4. E 00 LT.7. E 00 LT.4. E 00 CE-141 LT. 5. E 00 LT.7. E 00 LT.5. E 00 CE-144 LT.2. E 01 LT.3. E 01 LT.2. E 01 i RA-226 LT. 7. E 01 LT.8. E 01 LT.6. E 01 TH-228 LT. 6. E 00 LT.7. E 00 LT.5. E 00 TRIT 1UM ANALYSIS: , H-3 LT.2. E 02 LT.2. E O2 LT.2. E 02
. - - . . . . . . .. . . .. ~- . _ _ . . ~ .
9 6 / & :". e- C G G I! O U i-1.E WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PAT 11WAY - WATERBORNE SURFACE WATER (PCI/ LITER) STA'I1ON NUMBER DC DATE COLLEC1ED: 01/17 02/22 03/21 04/25 05/16 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E O1 LT.3. E O1 LT.3. E O1 LT.3. E O1 LT. 3. E O1 K-40 LT.9. E O1 LT.5. E OI LT. 1. E 02 LT.5. E O1 LT.8. E O1 cu MN-54 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT. 3. E 00
$ CO-58 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 m FE-59 LT.7. E 00 LT. 6. E 00 LT.8. E 00 LT.7. E 00 LT.7. E 00 $ CO-60 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 O
ZN-65 LT. 8. E 00 LT.6. E 00 LT.8. E 00 LT. 6. E 00 LT.6. E 00 NB-95/ZR-95 LT.4. E 00 LT.3. E 00 LT. 4. E 00 LT.3. E 00 LT. 3. E 00 RU-103 LT.4. E 00 LT.3. E 00 LT.4. 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 I-131 LT.5. E 00 LT.5. E 00 LT. 5. E 00 LT.5. E 00 LT.7. E 00 CS-134 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 CS-137 LT.4. 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. 5. E 00 LT.5. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.6. 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.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.8. E 01 LT. 8. E 01 Til-228 LT.6. E 00 LT. 6. E 00 LT.6. E 00 LT.7. E 00 LT.7. E 00 TRITIUM ANALYSIS: 11-3 9.7 i O.3 E 03 1.1 i O.1 E 04 9.5 i 0.3 E 03 1.2 i 0.1 E 04 1.1 1 0.1 E 04
a y- 2c ca a g .a o g; _r WOIX CREEK NUCIJtAR OPERATING CORPORATION EXPOSURE PKI11WAY - WATERBORNE SURFACE WATER (PCI/ LITER) STKi1ON NUMBER DC DATE COLLECTED: 06/20 07/11 08/22 09/19 10/24 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 4. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 K-4 0 LT. 1. E 02 LT. 1. E 02 LT.9. E 01 LT.6. E 01 LT.8. E 01 2 MN-54 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 y CO-58 LT.5. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 FE-59 LT. 1. E 01 LT. 1. E 01 LT.7. E 00 LT.6. E 00 LT.7. E 00
- CO-60 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 3 ZN-65 LT. 1. E 01 LT. 1. E 01 LT.7. E 00 LT.7. E 00 LT.8. E 00 NB-95/ZR-95 LT.5. E 00 LT.5. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU.103 LT.5. E 00 LT. 5. E 00 LT.3. E 00 LT. 4. E 00 LT.4. E 00 RU-106 LT.4. E 01 LT.4. E 01 LT. 3. E 01 LT.3. E 01 LT.3. E 01 1-131 LT.9. E 00 LT. 1. E 01 LT.5. E 00 LT.5. E 00 LT.5. E 00 CS-134 LT.5. E 00 LT. 5. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 CS-137 LT.5. E 00 LT.5. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 IA-140/BA-140 LT.7. E 00 LT.7. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.9. E 00 LT.8. E 00 LT.5. E 00 LT.7. E 00 LT.6. E 00 CE-144 LT.3. E 01 LT.3. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 RA-226 LT.9. E 01 LT.8. E 01 LT.6. E 01 LT.8. E 01 LT.7. E 01 TH-228 LT.8. E 00 LT.7. E 00 LT.6. E 00 LT. 7. E 00 LT.6. E 00 TRI11UM ANALYSIS:
H-3 9.5 1 0.4 E 03 9.7 1 0.4 E 03 8.3 1 0.3 E 03 9.3 i 0.4 E 03 1.2 1 0.1 E 04
a 3, .. - -3 c <- c : i .>] ' :. ;p a . WOfE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA111WAY - WATERBORNE SURFACE WATER (PCI/ LITER) STATION NUMBER DC DATE COLLECIED: 11/21 12/20 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 5. E 01 LT.3. E 01 K-40 LT.9. E 01 LT.6. E 01 cm MN-54 LT.4. E 00 LT.3. E 00 $ CO-58 LT.5. E 00 LT.3. E 00 cn FE-59 LT.9. E 00 LT. 6. E 00 $ CO-60 LT.5. E 00 LT.4. E 00 N ZN-65 LT. 1. E 01 LT.6. E 00 NB-95/ZR-95 LT.5. E 00 LT.4. E 00 RU-103 LT.6. E 00 LT.4. E 00 RU-106 LT.4. E 01 LT.3. E 01 I-131 LT. 1. E 01 LT. 7. E 00 CS-134 LT.5. E 00 LT.4. E 00 CS-137 LT.5. E 00 LT.4. E 00 IA-140/BA-140 LT. 8. E 00 LT.6. E 00 CE-141 LT. 1. E 01 LT.8. E 00 CE-144 LT.5. E 01 LT.3. E 01 RA-226 LT. 1. E 02 LT. 1. E 02 TH-228 LT. 1. E 01 LT.8. E 00 TRIT 1UM ANALYSIS: 11- 3 1.2 1 0.1 E 04 9.3 1 0.3 E 03
a O / 3 u DG :: 3 a y m WOIE CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA'IIIWAY - WATERBORNE SURFACE WATER (PCI/ LITER) STATION NUMBER SP DATE COLLECTED: 01/17 02/22 03/21 04/25 05/16 GAMMA SPECTRUM ANALYSIS: BE.7 LT. 4. E O1 LT. 2. E O1 LT. 3. E O1 LT.3. E O1 LT.4. E 01 K-4 0 LT. 1. E O2 LT. 5. E 01 LT. 6. E 01 LT. 9. E 01 LT. 1. E O2 MN-54 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.3. E OO LT.4. E 00 y CO-58 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 o FE-59 L.T. 9. E 00 LT.5. E 00 LT.6. E 00 LT.7. E 00 LT.8. E 00 CO-60 LT. 4. E 00 LT.3. E 00 LT.3. E 00 LT.3. E OO LT.4. E OO ZN.65 LT. 1. E 01 LT. 6. E 00 LT. 6. E OO LT.7. E 00 LT.8. E 00
$ NB-95/ZR-95 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E OO LT.4. E 00 RU- 103 LT.5. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 RU- 106 LT. 4. E 01 LT.2. E 01 LT. 3. E 01 LT. 3. E 01 LT.4. E 01 I-131 LT.6. E 00 LT.5. E OO LT.4. E OO LT. 5. E 00 LT.8. E OO CS- 134 LT. 5. E 00 LT.3. E 00 LT.3. E OO LT. 3. E 00 LT.5. E 00 CS- 137 LT.5. E 00 LT.4. E OO LT.4. E 00 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT. 5. E 00 LT. 4. E OO LT.4. E 00 LT.4. E 00 LT.6. E 00 CE-141 LT.7. E 00 LT.5. E 00 LT.6. E 00 LT.5. E 00 LT.7. E 00 CE-144 LT.3. E O1 LT.2. E 01 LT.2. E O1 LT. 2. E O1 LT.3. E O1 RA-226 LT.9. E 01 LT. 6. E 01 LT.7. E 01 LT. 6. E 01 LT.8. E 01 Til-228 LT.7. E 00 LT.5. E OO LT.6. E 00 LT.6. E 00 LT.7. E 00 TRrIlUM ANALYSIS:
11-3 9.8 i 0.3 E 03 9.9 i 0.3 E 03 9.4 i 0.3 E 03 1.2 1 0.1 E 04 1.1 1 0.1 E 04
q t. - c ;r. - c o e a o t; w .r WOIX CREEK NUCIJtAR OPERATING CORPORATION EXPOSURE PA11IWAY - WATERBORNE SURFACE WA'IER (PCI/ LITER) STA'I1ON NUMBER SP DATE COLLECTED: 06/20 07/11 08/22 09/19 09/19* CAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E O1 LT.2. E O1 LT.3. E 01 LT.3. E 01 K-40 LT. 1. E O2 LT.7. E 01 LT. 5. E 01 LT.6. E 01 LT. 1. E O2 MN-54 LT.4. E OO LT.3. E OO .T. 2. E 00 LT.3. E OO LT.3. E 00
- 2 CO-58 LT.3. E 00 LT.3. E 00 LT.2. E 00 LT.4. E 00 LT.4. E OO -
$ FE-59 LT.8. E 00 LT.7. E 00 LT.5. E 00 LT.7. E 00 LT.7. E 00 m CO-60 LT.3. E 00 LT.3. E OO LT.3. E 00 LT.4. E 00 LT.4. E OO ,
E ZN-65 LT.7. E 00 LT.6. E 00 LT. 5. E OO LT.6. E OO LT.8. E OO ' NB-95/ZR-95 LT.4. E OO LT.4. E 00 LT.2. E 00 LT.4. E 00 LT.4. E OO RU-103 LT.4. E OO LT.4. E 00 LT.3. E OO LT.4. E 00 LT.4. E 00 : RU-106 LT.3. E 01 LT.3. E 01 LT.2. E O1 LT.3. E 01 LT.3. E 01 I-131 LT.7. E 00 LT.8. E 00 LT.4. E 00 LT.6. E 00 LT. 5. E 00 CS-134 LT.4. E 00 LT.3. E OO LT.3. E 00 LT.4. E OO LT.4. E 00 CS-137 LT.4. E OO LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 , LA-140/BA-140 LT.5. E OO LT.5. E 00 LT.4. E 00 LT.5. E 00 LT. 5. E 00 CE-141 LT.6. E 00 LT.6. E 00 LT.5. E 00 LT.8. E 00 LT. 6. E 00 CE-144 LT.2. E 01 LT.2. E 01 LT.2. E OI LT.3. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT.6. E 01 LT.6. E 01 LT. 1. E O2 LT.7. E 01 TH-228 LT.7. E OO LT.5. E 00 LT.6. E OO LT. 8. E OO LT. 6. E OO TRI11UM ANAIXSIS: H-3 9.6 i 0.4 E 03 1.0 1 0.1 E 04 8.5 i O.3 E 03 9.6 i 0.4 E 03 9.5
- 0.4 E 03
- Duplicate Analysts
.q u ds c / r>J .a 1:3 a;;;.11 r
WOtX CREEK NUCI2AR OPERATING CORPORATION - EXPOSURE PATHWAY - WATERBORNE SURFACE WATER (PCI/ LITER) STA~I1ON NUMBER SP i a DATE COLLECTED: 10/24 11/21 12/20 GAMMA SPECTRUM ANALYSIS: . BE-7 LT.3. E 01 LT.4. E 01 LT.3. E 01 K-4 0 LT.9. E 01 LT. 1. E O2 LT. 1. E O2 MN-54 LT.4. E 00 LT.4. E 00 LT.3. E 00 2 CO-58 LT.4. E 00 LT.4. E OO LT.4. E OO f
$ FE-59 LT.8. E OO LT.9. E 00 LT.8. E OO m CO-60 LT.3. E 00 LT.4. E OO LT.4. E OO
$ ZN.65 LT.8. E OO LT.9. E OO LT. 8. E OO i
- NB-95/ZR-95 LT.4. E OO LT.4. E 00 LT.4. E OO RU-103 LT.4. E 00 LT.5. E 00 LT.4. E 00 RU- 106 LT.4. E O1 LT.4. E O1 LT.3. E 01 i l I-131 LT.4. E 00 LT.8. E 00 LT.7. E 00 ;
CS-134 LT.4. E 00 LT. 5. E 00 LT. 4. E OO CS-137 LT.4. E 00 LT.4. E 00 LT. 4. E 00 1 1A-140/BA-140 LT.4. E 00 LT.6. E 00 LT.5. E 00 CE-141 LT.5. E 00 LT.7. E 00 LT.6. E OO t CE-144 LT.2. E O1 LT.3. E O1 LT.2. E 01 e RA-226 LT. 8. E O1 LT.8. E 01 LT. 7. E 01 . TII-228 LT. 7. E OO LT.7. E OO LT.6. E 00 TRIT 1UM ANALYSIS: I 11-3 1.1 i O.1 E 04 1.2 1 0.1 E 04 9.4 1 0.3 E 03 i
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