ML20082T706
| ML20082T706 | |
| Person / Time | |
|---|---|
| Site: | Wolf Creek  |
| Issue date: | 12/31/1994 |
| From: | WOLF CREEK NUCLEAR OPERATING CORP. |
| To: | |
| Shared Package | |
| ML20082T694 | List: |
| References | |
| NUDOCS 9505040139 | |
| Download: ML20082T706 (166) | |
Text
{{#Wiki_filter:. _ _ _ _ . . _ _ _ _ _ l l'l,, '. l l l WOLF CREEK NUCLEAR OPERATING CORPORATION WOLF CREEK GENERATING STATION , 1994 ANNUAL RADIOLOGICAL l ENVIRONMENTAL OPERATING REPORT
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TABLE OF CONTENTS List of Tables 11 List of Figures iii Introduction 1 I. Program Description 2 II. Discussion of Results 5 III. Annual Land Use Census Results and Program Revisions 10 IV. Program Deviations 12 V. EPA Interlaboratory Comparison Results 15 e 1
LIST OF TABLES 1 1994 Radiological Environmental Monitoring Program Sample Collection 16 2 Sample Location Numbers, Distances, and Direct?.ons 23 3 1994 Airborne Particulate Gross Beta Analyses 24 4 Airborne Particulate Quarterly Composite Gamma Isotopic Analyses 26 5 1994 First & Second Quarter TLD Results 27 6 1994 Third & Fourth Quarter TLD Results 28 7 1994 Drinking Water Radiological Analyses 29 8 1994 Surface Water Radiological Analyses 30 9 1994 Ground Water Radiological Analyses 31 10 1994 Aquatic Plants Radiological Analyses 31 11 1994 Shoreline Sediment Radiological Analyses 32 12 1994 Bottom Sediment Radiological Analyses 32 13 1994 Broadleaf Vegetation Radiological Analyses 33 14 1994 Irrigated Crops Radiological Analyses 33 15 1994 Milk Radiological Analyses 34 16 1994 Fish Radiological Analyses 35 i 17 1994 Land Use Census Residence Data 36 l 18 1994 Land Use Census Milk and Garden Data 37 19 1994 US EPA Interlaboratory Comparison Program 38 l [ ii l l
i l[ LIST OF FIGURES .t 1 Airborne Pathway Sampling Locations .41 2 Direct Radiation Pathway Sampling Locations 42 l 3 ' Waterborne Pathway Sampling Locations 43 [
-i 4 Ingestion Pathway Sampling Locations 44
{ f 5 Distant Sampling Locations 45 l i 6 1994 Airborne Gross Beta Weekly Results 46 7 Historical Airborne Smoothed. Indicator and Control Gross Beta '47 j 8 Airborne Particulate Gross Beta Indichcor Weekly Average t o Control 48 i Ratio Historical. j 9 Historical Airborne Gross Beta Control and Indicator Location 49 i
-Average I 10 Variation of Nearsite TLD Averages Expressed as a Ratio to Control 50 _!
Values , 11 TLD Nearsite Locations, Control Locations, and Neart,ite D,dicator to 51 ,t Control Ratios j l 12 WCCL Smoothed Surface Water Tritium Data 52 13 Cumulative Liquid Effluent Tritium Data 53 14 Drinking Water Gross Beta (Historical) 54 7
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i I J INTRODUCTION The 1994 Annual Radiological Environmental Operating Report for Wolf Creek I Generating Station (WCGS) covers the period from January 1 through December 31, 1994. 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 7CNOC), results of sample analyses performed by Teledyne Brown 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. Radiological effects of plant operations were not detected in airborne particulate and radiciodine filters, broadleaf vegetation, irrigated crops, milk, ground water, nondomestic meat or drinking water. During 1994, activation products were detected in algae, shoreline sediment, bottom sediment, surface water and fish samples. All nuclides detected in the Radiological Environmental Monitoring samples were below applicable NRC reporting le,rels. 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 1 of 54
r I. PROGRAM DESCRIPTION Radiological environmental samples were collected according to the schedule in Section 5.0 and 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 lists each sample location's distance and direction from the plant. Samples in addition to those required by the WCGS ODCM were obtained in conjunction with the Kansas Department of Health and Environment (KDHE) and to monitor additional parameters. The following is a description of the sampling and analysis program by individual pathways. A. Airborne Low volume air sampling pumps continually collected particulate and radioiodine samples on 47 mm glass fiber filters and charcoal canit. cers , respectively. Weekly, the filters and charcoal canisters are changed out, labeled, and shipped to Teledyne Brown Engineering Environmental Services for analysis. The volume of air sampled was calculated from the average of initial and final flow rates and the total time of collection. Each pump 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 hours post collection to allow the radon and thoron daughter products to decay. Each filter was mounted on a stainless steel planchette and counted on an automatic alpha-beta counter. Weekly air particulate filters were combined into quarterly composites for each location and analyzed for gamma emitting isotopes on a Ge(Li) detector. Charcoal canisters were re>utinely 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 u mpling locations from the plant site are listed in Table 2; locations are rhuwn in Figure 1 (nearby locations) and Figure 5 (distant locations). B. Direct Radiation During the first quarter of 1994, the thermoluminescent dosimeters (TLDs) used were provided by Teledyne Brown Engineering Environmental Services. The TLDs consisted of rectangular Teflon wafers impregnated with CaSO4 :Dy. Prior to placement in the field, the dosimeters were annealed for at least one hour at 250 to 260 degrees Centigrade. The TLDs were then placed in polyethylene pouches and holders containing 0.093 inch thick copper shields to filter out low energy radiation. Freshly annealed dosimeters were exchanged with exposed 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 2 of 54
dosimeters and the exposed dosimeters were shipped to Teledyne Brown Engineering Environmental Services for analysis. Four freshly annealed TLDs were shipped as controls with the exposed TLDs to record any exposure received in transit. Gamma exposures were measured on a Teledyne TLD reader. Individual dosimeters were then exposed to a Cs-137 source to determine each dosimeter's calibration factor. Panasonic UD-814-AQ TLDs were used during the second, third and fourth quarters of 1994. 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. In general, TLDs were positioned roughly 3 to 4 feet above the ground. They were contained in either plastic thermostat boxes or fiberglass air sample pump housings. The boxes and housings protect them from the elements and tampering. Two TLDs were placed at each designated location. TLD sample locations are illustrated in Figure 2 (nearby locations) and Figure 5 (distant locations). Table 2 provides the distance and direction of each location from the site. C. waterborne All water samples were analyzed ca a Ge (Li) detector 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 performed on drinking water samples. Tritium analysis was performed monthly by liquid scintillation for surface 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. l 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 are obtained from automatic composite samplers at each location that draw approximately 10 m1 samples hourly. Monthly, s a) 1amples were drawn from each surface water location. Surface water war ampled at the outfall of John Redmond Reservoir as a control (location MUSH) and in the discharge cove and spillway of WCCL for indicator 1 locations. Per a KDHE request, special samples were collected due to the potential opening of the cooling lake to public access. Ground water samples were collected quarterly from four locations. One ground water well is hydrologically upgradient from the site (location B-12) and is used as a control location. Three additional samples (C-10, C-49, and D-65) were obtained from wells hydrologically downgradient from the site as indicator samples. 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 3 of 54 ;
Shoreline sediments were sampled semiannually for gamma analysis at the discharge cove (indicator, Figure 3) and at JRR (control, Figure 3). Per a KDHE request, special samples were collected due to the potential opening of the cooling lake to public access. Bottom sediments were also collected semiannually. Samples were obtained for gamma analysis at the discharge cove (indicator, Figure 3) and at JRR (control, Figure 3). Per a KDHE request, special samples were collected due to the potential opening of the cooling lake to public access. Semiannual aquatic plant and algae samples were obtained for gamma analysis , from the discharge cove area or from an alternate location near the discharge cove (DC and DC ALT, respectively on Figure 3). D. Ingestion Milk samples are collected semimonthly from April through November (while the ! animals are feeding on pasture grass) and monthly from December through March (while the animals are on stored feed). Sampling locations were not identified within 5 miles of the plant that produced milk for human consumption during 1994. Therefore, only control samples were obtained. Radiochemical I-131 and gamma isotopic analyses were performed on each sample. The control location 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 were sampled (Figure 5). Gamma isotopic t analysis was performed on all samples. Irrigated crops (soybeans and corn) were also sampled. Three samples were ' obtained from cropland downstream of the confluence of WCCL effluents and the Neosho River (indicator) and two samples were obtained upstream (control). Gamma isotopic analysis was performed on each sample. An alfalfa sample was also obtained from a downstream indicator location. Fish are sampled from the tail waters of aRR (control) and from WCCL semiannually for gamma isotopic analysis ('.< igure 4). Several species of gamefish and roughfish are sampled. Gamma isotopic analysis is performed on boneless meat portions of the fish. During the second half of 1994, fish were also analyzed for tritium. Game are sampled annually in th:. immediate vicinity of the plant and at a control location that is remote frota the site. Gamma isotopic analysis is performed on boneless meat portions of the game. All sampling locations listed in this section are outlined in Table 2. I 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 4 of 54
l l l l 1 II. DISCUSEION OF REEULTS 2-Analysis results for all pathways are summarized in Appendix A using the format described in NRC Radiological Assessment Branch Technical Position, i Revision 1, November 1979. Results for individual samples are listed in l Appendix B. t In this section, results are discussed by pathway and analysis type. ; operational results are related to controls, preoperational values, sources of radioactivity, and effluent releases when applicable. Trends or seasonal effects are discussed. Tables 3 through 16 illustrate results of interest for 1994. Associated errors for positive results may be obtained in Appendix B. A. Airborne , i Results of the weekly gross beta analysis are summarized in Table 3. In i addition, Figure 6 illustrates a graph of weekly gross beta results for 1994. Figure 7 represents the historical smoothed averages of indicator and control i gross beta. Figure 8 illustrates a historical plot of the gross beta indicator to control ratios and includes a smoothed average trend. Finally, Figure 9 displays a historical plot of average weekly indicator and control gross beta values during plant operations. 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) . No unusual tunds were noted. Results from the weekly analysis of charcoal filters for I-131 did not show ' concentrations above 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, K-40 and Th-228 were detected. Effects of plant operation were not seen via the airborne pathway for the year and no unusual trends were noted. j B. Direct Radiation l Quarterly gamma exposureo measured at each location for 1994 are shown in l Tables 5 and 6. Values are normalized to a 90-day standard quarter. l l 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 l (locations 39 and 40) results in Figure 11. In addition, variation of the ; nearsite averages from the control location results are displayed graphically l in Figure 10. These figures also include preoperational data for comparison. ; Note that nearsite TLD locations have historically trended higher than the l 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 i 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 5 of 54 l
i Creek have declined from 1980 to 1993. (For further discussion on this decline, please see the 1993 WCUS Annual Radiological Environmental Operating ' Report.) The transfer from Teledyne to Panasonic TLDs has been completed. A study was , conducted in 1994 which compared the two types of TLDs. The conclusion from i that study was that it was statistically valid to replace the Teledyne TLDs I with Panasonic TLDs. Teledyne TLDs were used during the first quarter of > 1994. For the remainder of the year, Panasonic TLDs were used. 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. f Figure 14 illustrates the historical drinking water gross beta data through ; 1994. [ 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 except that during March the ; indicator gross beta activity level was 13 +/- 2 pCi/ liter while the control , location gross beta activity level was 4.6 +/- 1.7 pci/ liter. The vendor lab ; recalculated the gross beta activity and confirmed the reported values. This ! activity is not attributable to plant operation since tritium was not detected (which would be expected if the activity was from water that came from WCCL). : Activity due to plant operations was not evident in drinking water samples ; during 1994 and no unusual trends were noted. ) i (2) Surface water ! l T-itium, attributable to WCGS operation, was detected in all surface water samples collected from WCCL in 1994. A total of 974 curies of liquid tritium were 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 1994. The cumulative curies of liquid tritium released to WCCL is illustrated on Figure 13. 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 lake concentration reaches equilibrium. A peak concentration of 14,000 pCi/ liter was detected at location DC in July when the monthly grab sample was obtained a few hours after a batch release. Since the sample point is close to the discharge structure, complete mixing j had not occurred. (The tritium concentration for the same time frame at l location SP was 9,200 pCi/ liter.) ) l l 1994 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 6 of 54 l a
I Naturally occurring K-40 was detected in a sample obtained from the discharge cove on May 17. No unusual trends were noted. (3) Ground Water The only radionuclide detected in ground water samples was the naturally occurring K-40. Other gamma emitters or tritium were not detected in ground water samples during 1994. A sungnary of results is included in Table 9. ; (4) Shoreline Sediment Naturally occurring nuclides K-40, Ra-226 and Th-228 were detected in shoreline sediment samples during 1994. These nuclides were the only activity detected in the control samples from location JRR. In one sample from the discharge cove (October 26), Co-58 was detected. This activity is attributable to plant operations. In two samples from the discharge cove (May 31 and October 26) , Co-60 was detected. This activity is attributable to plant operations. One sample from the discharge cove (May 31) had both Cs-134 and Cs-137 activity detected. The Cs-137 detected activity was 122 pCi/kg, well below the preoperational range. The Cs-134 is attributable to plant operations, as l well as some of the Cs-137 activity. (The preoperational range for Cs-137 > detected activity at location DC was 224 pCi/kg to 437 pCi/kg.) Three other WCCL locations also detected Cs-137, however, Cs-134 was not detected at these locations. The EEA sample obtained October 14, had a Cs-137 concentration of 93 pCi/kg. Cs-137 was also detected in two WCCL samples obtained October 26. The t',ischarge cove concentration of Cs-137 was 44 pCi/kg and was below the range e s f preoperational data. A sample taken from Sector R had Cs-137 activity of 50 pCi/kg. The presence of Cs-134 would be expected if the occurrence of Cs-137 was related to plant operation (Cs-134 decays with a shorter half-life than Cs-137; detection of Cs-137 alone may indicate older fallout as opposed to newly produced fission products) . Analysis results are summarized in Table 11. D. Ingestion (1) Milk No indicator locations for milk existed during 1994 (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 1419 pCi/ liter. Table 15 summarizes milk analysis results for 1994. No other gamma emitters were detected. 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 7 of 54
(2) Food and Garden Crops Gamma analyses of broadleaf vegetation samples during 1994 revealed naturally occurring gamma emitters Be-7 and K-40. Table 13 shows the results of 1994 analysis. An indicator location sample obtained June 28 from location R-1 had a Cs-137 concentration of 17.1 pCi/kg which is in the range of fallout seen in preoperational samples. Cs-134 was not detected in the June 28 sample, which would be expected if this was attributable to plant operations, thus the Cs-137 was not a tributable to plant operation. Additional gamma emitters were not detected in broadleaf vegetation samples during the remainder of the year. 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 WCCL discharge and the Neosho River, and three indicator samples were obtained downstream. Gamma analysis only detected naturally occurring Be-7 and K-40 to be present in the samples, with no nuclides detected due to plant operation. 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. In a white crappie sample collected April 22 from the WCCL, Cs-137 was detected with a concentration of 24 pCi/kg. Although fallout Cs-137 is regularly measured in other er-'Aronmental media and is probably reflected in these values, it is assumed that these concentrations are attributable to WCGS operational releases. A dose calculation for an adult consuming 21 kilograms at the maximum measured Cs-137 concentration for 1994 (24 pCi/kg) results in an annual dose of 0.02 mrem / year. During the second half of 1994, fish were analyzed for tritium. Six fish samples taken from WCCL, and two samples from the WCCL outlet pool all , contained tritium. The detected tritium activity is attributable to plant j operation. A dose calculation for an adult consuming 21 kilograms at tne j maximum measured tritium concentration for 1994 (7,600 pCi/kg) results in an annual dose of 0.01 mrem / year. E. Special Samples (not required by the WCGS ODCM) (1) Nondomestic Meat (Quail) ] l Naturally occurring K-40 was detected in all quail samples. Other radionuclides were not detected and no effects of plar'. operations were detected in these samples. 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 8 of 54 j
i L (2) Bottom Sediment Table 12 shows gamma emitters detected during 1994 in bottom Sediment samples. , Naturally occurring nuclides detected include Be-7, K-40, Ra-226, and Th-228. Co-60 was detected in seven samples obtained from WCCL. Co-60 activity shown in Table 12 is attributable to plant operation and is regularly identified in plant effluents. Two samples obtained from the discharge cove contained both Cs-134 and Cs-137. Since both are present, some of this activity is attributed to plant operations. Cs-137 was detected in both control samples as well as six other WCCL locations. Since Cs-134 is not present and the control samples contained Cs-137 as well, this activity is primarily due to fallout, and not to a newly produced fission product. No other radionuclides were detected. (3) Aquatic Vegetation Table 10 shows gamma emitters detected during 1994 in aquatic plant samples. Naturally occurring Be-7, K-40, Ra-226 and Th-228 were detected. Mn-54 was detected in an algae sample collected from the discharge cove. This activity is attributed to plant operation and is regularly identified in plant effluents. Co-58 and Co-60 were detected in an algae sample collected from the discharge cove. This activity is attributed to plant operation and both nuclides are regularly identified in plant effluents. Cs-134 and Cs-137 were detected in an algae sample collected from the discharge cove. Since both radionuclides were detected, a portion of this activity is attributable to plant operation. (4) Terrestrial Vegetation Pasturage samples were obtained from two locations: Environmental Education Area (EEA) and Makeup Discharge Structure (MUDS). Both samples had naturally occurring Be-7 and K-40 activity detected. (5) Soil i l Soil samples were obtained from three locations: A-1, EEA and MUDS. , Naturally occurring Be-7, K-40, Ra-226 and Th-228 activity were detected. l Cs-137 activity was detected in all three soil samples. The Cs-137 activity is attributable to fallout since Cs-134 activity was not detected and the activity levels for Cs-137 are well within the preoperational range (255 to 2160 pCi/kg). 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 9 of 54
III. ANNUAL L1MD USE crMMUS RESULTS AND Prot: RAM REVISIONS INTRODUCTION The annual Land Use Census of rural residents within five miles of the Wolf Creek Generating St: ation has been completed for 1994. The results and notable changes are summar.'. zed and illustrated in Tables 17 and 18. BACKGROUND Section 5.2 of ADM 04-019, Offsite Dose Calculation Manual (ODCM) 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 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." Table 5-1 of the ODCM lists the number of samples and sample locations for food products as: " Samples of available broadleaf vegetation from two indicator locations with highest calculated annual average D/Q." (D/Q = relative deposition) Table 5-1 of the ODCM lists the number of samples and sample locations for milk as: " Samples from milking animals at three indicator locations within 5 miles of the site having the highest dose potential." METHODOLOGY Surveys were mailed to the rural residents within five miles of WCGS during the first week of September 1994. A follow-up mailing was sent during the fourth week of September to residents that had not responded. The survey excluded the residents of New Strawn, Burlington, and a trailer park just north of Burlington. These locations are excluded because of the large number of households and the low likelihood that information gained from these residences would affect the locations chosen for REMP sampling. Of the 158 surveys mailed to the rural residents, 115 were returned by mail, 35 responses were obtained through telephone solicitations and I response was obtained via an interview. Seven surveys had to be completed by driving by the locations, since the residents could not be reached by telephone or the surveys were not returned by mail. This is a response rate of 95.57 percent for the 1994 census. RESULTS The estimated population for the 1994 Land Use Census is 436 persons. This is - an increase from the 1993 Land Use Census which was estimated at 384 persons. In 1993, 146 households were sent surveys, while in the 1994 Land Use Census, 158 households were sent surveys. Comparing the 1993 Land Use census results to this year the nearest resident has changed in Sectors A, M, N, and P. In. Sector A, the nearest residence is no longer 1.4 miles from the plant; the new location (A2.6-OXLA1731) is further from the plant at 2.6 miles. In Sector M, the nearest residence is no longer 1.6 miles from the plant; the new location (M2.4-14RD1321) is further 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 10 of 54
from the plant at 2.4 miles. In Sector N, the nearest residence is no longer 2.1 miles from the plant; the new location (N2.6-HW751465) is further from the plant at 2.6 miles. In Sector P, the nearest residence is no longer 2.8 miles-from the plant; the new location (P2.7-16RD1255) is closer to the plant at 2.7 miles. , Several changes were noted in the distance to the nearest milk animal. During 1993, four sectors were listed as having milk animals: B, F, G and H. During the 1994 survey, four rural residences returned positive responses concerning dairy cattle and or goats. Each residence was contacted by telephone. Two residents stated that they had filled out their survey incorrectly, and the other two residents stated that they no longer owned the animals. Thus, no locations were identified in 1994 as having milk animals. Numerous location changes were noted for the nearest garden producing broadleaf vegetation. In Sectors C, H, J and Q, the gardens are closer to the plant than the ones in 1993. In Sector A, the closest garden is no longer 1.4 miles from the plant. The new location in Sector A is 2.9 miles from the plant (A2.9-17LA1518).
SUMMARY
Based upon the data collected in the 1994 Land Use Census, a change is required in the Radiological Environmental Monitoring Program for 1995 regarding broadleaf vegetation. The house located at garden sampling site A-1 , is vacant, and will likely remain that way. Location A-1 is listed in the ODCM Table 5-1 as an indicator sampling location. The D/O ranking from the 1994 Land Use Census lists the two highest ranking indicator sampling locations for broadleaf vegetation as R2.1-NALA1650 and G1.6-QURD1384, 1 respectively. The garden with the third highest D/O ranking is A2.9-17LA1518 and should become the alternate location. These changes have been incorporated into the ODCM. , I l l 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 11 of 54
I IV. PROGRAM DEVIATIONS Airborne All locations (March 15): Air sample pumps were one day past their ; calibration expiration date when removed from service. The pumps were left in service for the additional day because a replacement set was not calibrated in time. The replacement set was not calibrated because the mass flowmeter used to check the pumps would not function properly. The backup mass flowmeter was unavailable because it was at the contract lab. A rush order was placed and the flowmeter was returned on March 14. The replacement pumps were calibrated on March 14 and put into service March 15. To prevent this from happening again, the defective mass flowmeter was replaced to ensure a backup is available. No air particulate data were lost due to this incident. Location 37 (July 26) : The air particulate filter was found to be ripped. The rip allowed air to directly enter the charcoal filter. Upon evaluation, the glue holding the " honey comb" shaped metal in place had cracked away, allowing the metal filter to be sucked into the head of the sampler, thus causing the filter to :cip. Spare sample heads were evaluated and none were found to be defective. The collection procedure was revised to help caution personnel of this potential problem. The mean of the indicator locations for the sampling period 7-19-95 through 7-26-94 was 0.032. The analysis results for location 37 for the same time period was 0.018, thus this ripped filter had some impact on the analysis results. Drinking Water Location LW-40 (June 7) : The drinking water sampler located at LeRoy was unavailable from 3:30 p.m. on June 7 until 9:20 a.m. on June 8 due to a liquid sensor probe breaking. The broken probe was discovered during routine i maintenance of the sampler. Approximately 170 milliliters of the 7,200 milliliter monthly composite sample were not collected. The broken part was replaced on June 8, and the drinking water sampler was returned to service. Location LW-40 (June 20 - July 6) : The drinking water sampler located at LeRoy missed approximately 1,430 milliliters of the 7,200 milliliter monthly composite sample. The missed samples were due to the sampler getting clogged with carbon from backflushing of the water system. A grab sample was taken. The gross beta activity detected for the grab sample was 5.2 pCi/ liter while , the gross beta activity detected for the composite sample was 6.1 pCi/ liter. l The procedure on water collection was revised to ensure the intake tube is in the correct section of the water tank. Location LW-40 (August 2 - September 6): The drinking water sampler located at LeRoy missed approximately 4,590 milliliters of the 7,200 milliliter monthly composite sample. The sampler lines were opened and the small pump hose was replaced. The tube housing was cleaned., The sampler was returned to service. A grab sample was taken. The gross beta activity detected for the grab sample was 5.9 pCi/ liter while the gross beta activity detected for the composite sample was B.3 pCi/ liter. The procedure on water collection was 1994 Annual Radiological Environmental Operating Report 1 Wolf Creek Generating Station Page 12 of 54
revised to add requirements for the intake hose and pump. tubes to be replaced on a regular basis. l Direct' Radiation Samplers (TLDs) Location 5, second Quarter: Both TLDs at this location were missing, along with the small housing used to protect them from environmental conditions. J Apparently the utility pole had been replaced during the quarter. A new l station was attached. l l Location 10, Second Quarter: Both TLDs at this location were missing, along l with the small housing used to protect them from environmental conditions. i Apparently the utility pole had been replaced during the quarter. A new station was attached. l Ingestion Milk i Location S-3 (2nd April Sample) : The milk sample at S-3 was not collected for ! the second half of April. This sample was inadvertently omitted from the ! i yearly working sampling schedule. To keep the problem from reoccurring, the procedure was revised to add the requirement that the working schedule must be , verified against the ODCM sample requirements by a person, other than the ~ originator, who is qualified to obtain samples, i There are still no indicator sampling locations available within five miles of the plant. Refer to Section III, Annual Land Use Census Results and Program [ Revisions, i Broadleaf Vegetation f Broadleaf vegetation is sampled when seasonably available. No broadleaf ! vegetation deviations occurred during 1994. 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 G-1 when available. Sample locations A-1 and R-1 are the primary sample locations and S-4 is the control location. , i l ( l l I i 1 1 1994 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 13 of 54 l
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.' A- 1 (5/31) Unavailable. All'other gardens sampled.
A-1 : (6/28) Unavailable. All other gardens sampled l A-1 (7/26) Unavailable. All other gardens sampled f i
' A-1, R (8/23) Unavailable. 'All other gardens sampled -
A-1, R-1 ' (9/27) Unavailable. All other. gardens sampled ! A-1,'R-1 (10/25) Unavailable. All other gardens sampled .f i i i l i i I
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l l 1 i l 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 14 of 54
1 V. EPA INTERLABORATORY COMPARISON REBin.TB 'j i Teledyne Brown Engineering Environmental Services is contracted to perform I radiological analysis of environmental samples for WCNOC. Teledyne J
. participated in the EPA Interlaboratory Comparison Program during 1994.
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 Brown Engineering Environmental Services (based upon triplicate analysis), and the normali::ed deviation from the known. Results are listed in the table for , sample media and analysis types corresponding to those performed for WCNOC. Except for one sample for gamma analysis all of the Teledyne Brown Engineering Environmental Services results were within three standard deviations of the , known EPA results. Only results exceeding three standard deviations require corrective action. The footnotes of Table 19 describe the results of the [ investigations. t [ h l i I t t I I t I I 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 15 of 54 1 I
i l TABLE 1 ; 1994 RADIOLOGICAL ENVIRONNENTAL MONITORING PROGRAM SAMPLE COLLECTION EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATENAY/ AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SANPLE LOCATIONS ANALYSIS AIRBORNE Radioiodine Samples from five Continuous sampler Analyze and locations operation with sample radioiodine Particulates collection weekly, or canister weekly more frequently if for I-131 required by dust loading. Samples from Analyze 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 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 1994 Annual Radiological Environmental Operating Report l Wolf Creek Generating Station Page 16 of 54
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TABLE 1 (Cont) l EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND FREQUENCY
.PATEWAY/ AND SAMPLE LOCATIONS COLLECTION FREQUENCY OF ANALYSIS l SAMPLE DIRECT RADIATION [
40 routine Quarterly Gamma dose , monitoring stations' quarterly ; with two or more ; dosimeters ! measuring dose continuously, placed as follows: An inner ring of . stations, one in t each meteorological 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) An outer ring of < stations, one in each meteorological ! sector in the 3-5 mile range from the site (Locations 4- I 6, 15-17, 19-25, - and 33-36 on Figure 2). Five sectors l B, D, G, and L) [A, contain an , additional station (Locations 2, 3, 10, 14 and 28) The balance of the stations to be placed in special interest areas such as population i centers (Locations 23 and 32), nearby ; residences 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 17 of 54
p [. TABLE 1 (Cont) EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATENAY/ AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS-DIRECT RADIATION (cont) (many locations are
'near a residence),
schools (Location 23), and in one or two areas to serve as control stations 10-20 miles distant from the site (Locations 39 and 40 on Figure 5) Locations 41-45 are not required by the ODCM as sampling stations but have been added as special interest sampling locations WATERBORNE Surface One sample upstream Monthly grab sample Monthly gamma (Location MUSH on isoccpic Figure 3) and two analysis and samples downstream. composite-for (Locations DC and tritium analysis SP on Figure 3). quarterly Special samples were taken from WCCL in 1994. Ground Samples from one or Quarterly Quarterly gamma two sources only if isotopic and likely to be tritium analysis affected. 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 18 of 54
h e TABLE 1 (Cont) EXPOSURE- MIBGBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY / AND SAMPLE COLLECTION FREQUINCY FREQUENCY OF SAMPLE LOCATIONS- ANALYSIS WATERBORNE (cont) Ground (cont) Indicator samples at locations hydrologically downgradient of the site (Locations C-10, C-49, and D-65 on Figure 3); Control sample at a location hydrologically upgradient of the site (Location B-12 on Figure 3) Drinking Sample of municipal Monthly Composite Monthly gamma water suppl / at an isotopic indicator location analysis and downstream of the gross beta site (Location LW- analysis of 40 on Figure 5); composite control sample from sample. location upstream Quarterly of the site tritium analysis (Location BW-15 on of composites. Figure 3) Shoreline one sample from the Semiannually Semiannual gamma sediment vicinity of Wolf isotopic Creek Cooling Lake analysis discharge cove; control sample from John Redmond Reservoir (Locations DC and JRR respectively on Figure 3). Special samples were obtained from WCCL during 1994. J994 Annual Radiological Environmental Operating Report Wod' Creek Generating Station Page 19 of 54
3 TABLE 1 (Cont) EXPOSURE- NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS WATERBORNE (cont) Bottom One sample from the Semiannuslly Semiannual gamma sediment vicinity of Wolf isotopic Creek Cooling Lake analysis discharge cove; control sample from John Redmond Reservoir (Locations DC and 6 JRR respectively on Figure 3). Special samples were obtained from WCCL during 1994. Rooted One sample from the Semiannually Semiannual gamma Aquatics or vicinity of Wolf isotopic Algae Creek Cooling Lake analysis (Location DC on ; Figure 3). INGESTION . Milk Samples from Semimonthly while Gamma isotopic ; milking animals at animals are on analysis and I- l three indicator pasture (April to 131 analysis of locations within November) and monthly 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) l 1 1 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Etation Page 20 of 54 i l 1
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..V.
TABLE 1 (Cont) t EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATNNAY/ AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS INGESTION (cont) Fish Indicator samples Semiannually Gamma isotopic of 1-3 . _ analysis on y recreationally edible portions j important species i from Wolf Creek Cooling Lake; control samples of similar species from John Redmond Reservoir spillway (Figure 4) Broadleaf Samples of Monthly when Gamma isotopic Vegetation available broadleaf available analysis on vegetation from two edible portions indicator locations with highest calculated annual average D/Q (Locations A-1 and . R-1 and alternate ; location G-1 on Figure 4); sample of similar - broadleaf . vegetation from a ; control location greater than 10 2 miles from the site in a low D/O sector ' (Location S-4 on Figure 5) t 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 21 of 54 i i
l l TABLE 1 (Cont) EXPOSURE NUMBER OF SAMPLES SAMPLING AND TYPE AND PATHWAY / AND SAMPLE COLLECTION FREQUENCY FREQUENCY OF SAMPLE LOCATIONS ANALYSIS INGESTION (cont) , 1 Irrigated Sample of crops At time of harvest Gamma isotopic l Crops irrigated with analysis on - l water from the edible portions Neosho River downstream of the i Neosho River - Wolf Creek confluence (Location NR-D1 and NR-D2 on Figure 5); control sample irrigated with water from the Neosho River upstream of the , Neosho River - Wolf ; Creek confluence (Location NR-U1 on Figure 5) l Game birds Indic tor samples Annually Gamma isotopic of region specific analysis on , recreationally edible portions important species from the vicinity of Wolf Creek Cooling Lake; control samples'of similar species from locations >10 miles SSE of WCGS. i i 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 22 of 54 i I
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1 TABLE 2 SAMPLE LOCATION NUNBERS, DISTANCES (Miles), AND DIRECTIONS Location Distance / Location Distance / Location Number Distance / Number Direction Ntamber Direction Direction TLD and Air Particulates and Radiciodines 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 3.2/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 42 0.8/WNW 14 2.6/SE 29 2.6/SSW 44 3.0/NNW 15 4.5/PSE 30 2.2/W 45 1.5/WNW Ground water Drinking water Surface water B-12 2.2/NNE BW-15 3.9/SW MUSH 3.6/W C-10 2.8/W LW-40 >10.0/SSE DC 0.6/WNW C-49 2.9/SW SP 2.9/S D-65 3.9/S Milk Broadleaf vegetation Irrigatad crops S-3 >15.0/WNW A-1 1.4/N 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 and Bottom Aquatic Vegetation / Algae sediments 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 WC&1lth RD 3.8/S EEA 3.0/NNW EEA 3.0/NNW WCCL Outlet Pool 3.3/S Game Birds and Animals WCCL General Vicinity LeRoy >10.0/SSE Special Samples of Surface Mater, Shoreline and Bottom Sediments from WCCL UHS-Sec G 0.6/SE Bemis Cove-Sec H 1.5/SSE Saddle Dam 4-Sec K 2.0/SSW S Reinker Road-Sec L 1.3/SW MUDS-Sec P 1.5/WNW N Housers-Sec R 1.7/NNW 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 23 of 54
. j TABLE 3 1994 Airborne Particulate Gross Beta Analyses (pci/ cubic meter, analysis error reported in Appendix B)
Date Location l Beginning Ending 2 3 32 37 40 Control 12/28/93 1/4/94 0.031 0.030 0.030 0.031 0.024 1/4/94 1/11/94 0.039 0.036 0.043 0.045 0.031 1/11/94 1/18/94 0.035 0.039 0.044 0.038 0.024 ; 1/18/94 1/25/94 0.030 0.029 0.022 0.035 0.029 1/25/94 2/1/94 0.033 0.032 0.035 0.032 0.030 2/1/94 2/8/94 0.028 0.026 0.027 0.029 0.028 2/8/94 2/15/94 0.030 0.028 0.027 0.026 0.023 , 2/15/94 2/22/94 0.025 0.019 0.027 0.021 0.017 . 2/22/94 3/1/94 0.023 0.022 0.031 0.023 0.020 3/1/94 3/8/94 0.025 0.021 0.026
~~
0.022 0.021 3/8/94 3/15/94 0.020 0.023 0.023 0.033 0.020 3/15/94 3/22/94 0.016 0.017 0.021 0.020 0.016 3/22/94 3/29/94 0.019 C.019 0.022 0.020 0.019 , 3/29/94 4/5/94 0.022 0.020 0.023 0.025 0.022 4/5/94 4/12/94 0.020 0.020 0.020 0.020 0.020 4/12/94 4/19/94 0.027 0.026 0.025 0.026 0.027 l 4/19/94 4/26/94 0.025 0.017 0.022 0.019 0.016 4/26/94 5/3/94 0.014 0.011 0.030 0.011 0.013 5/3/94 5/10/94 0.020 0.020 0.022 0.020 0.020 I 5/10/94 5/17/94 0.025 0.022 0.021 0.022 0.024 l 5/17/94 5/24/94 0.025 0.024 0.028 0.023 0.023 l
, 5/24/94 5/31/94 0.025 0.021 0.023 0.021 0.024 5/31/94 6/7/94 0.025 0.023 0.022 0.022 0.019 j 6/7/94 6/14/94 0.021 0.021 0.019 0.020 0.022 6/14/94 6/21/94 0.024 0.027 0.025 0.025 0.027 6/21/94 6/28/94 0.035 0.036 0.036 0.032 0.035 6/28/34 7/5/94 0.023 0.025 0.027 0.026 0.026 l
l l l s I 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 24 of 54 i
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TABLE 3 (Cont) 1994 Airborne Particulate Gross Beta Analyses ; (pci/ cubic meter, analysis error reported in Appendix B) Date Location i Beginning Ending 2 3 32 37 40 Control 7/5/94 7/12/94 0.028 0.027 0.027 0.025 0.026 [ 7/12/94 7/19/94 0.027 0.023 0.027 0.027 0.028 ! 7/19/94 7/26/94 0.027 0.038 0.031 0.018 0.034 [ 7/26/94 8/2/94 0.030 0.029 0.028 0.030 0.029 8/2/94 8/9/94 0.030 0.031 0.027 0.026 0.028 8/9/94 8/16/94 0.028 0.029 0.031 0.032 0.032 8/16/94 8/23/94 0.032 0.036 0.033 0.034 0.031 8/23/94 8/30/94 0.029 0.028 0.031 0.030 0.027 8/30/94 9/6/94 0.029 0.027 0.030 0.028 0.026 l 9/6/94 9/13/94 0.040 0.041 0.043 0.043 0.041 9/13/94 9/20/94 0.020 0.026 0.020 0.024 0.023 9/20/94 9/27/94 0.024 0.024 0.024 0.025 0.025 9/27/94 10/4/94 - 0.048 0.042 0.044 0.045 0.045 10/4/94 10/11/94 0.035 0.037 0.035 0.034 0.035 t 10/11/94 10/18/94 0.023 0.024 0.022 0.023 0.023 10/18/94 10/25/94 0.025 0.033 0.028 0.029 0.028 10/25/94 11/1/94 0.027 0.028 0.031 0.034 0.031 , 11/1/94 11/8/94 0.035 0.039 0.031 0.040 0.034 [ 11/8/94 11/15/94 0.026 0.026 0.024 0.027 0.022 l 11/15/94 11/22/94 0.024 0.027 0.028 0.022 0.026 , 11/22/94 11/29/94 0.030 0.028 0.026 0.030 0.029 l
-11/29/94 12/6/94 0.028 0.025 0.026 0.030 0.029 i 12/6/94 12/13/94 0.035 0.030 0.033 0.032 0.035 !
12/13/94 12/20/94 0.040 0.042 0.043 0.047 0.037 j 12/20/94 12/27/94 0.030 0.032 0.033 0.033 0.034 12/27/94 1/03/95 0.040 0.040 0.043 0.037 0.041 l 1 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 25 of 54 l
1 l TABLE 4 1994 Airborne Particulate Quarterly Composite Gamma Isotopic Analyses l (pci/ cubic meter, analysis error reported in Appendix B) l LOCATION QTR Be-7 K-40 I-131 Cs-134 Cs-137 Th-228 l 1 2 1 0.08 <0.008 <0.001 < 0.0004 < 0.0003 l 2 2 0.09 <0.008 < 0.002 < 0.0005 <0.0005 2 3 0.09 <0.010 < 0. 0 01 < 0.0006 < 0.0006 l 2 4 0.10 <0.020 < 0. 2 4 0.0007 <0.0006 3 1 0.07 0.0478 < 0 . 0 01 < 0.0005 <0.0005 0.00109 l 3 2 0.09 <0.020 < 0.002 < 0.0005 < 0.0006 l 3 3 0.09 <0.010 < 0.0009 < 0.0005 <0.0005 3 4 0.10 <0.009 < 0. 2 < 0.0006 <0.0005 , 32 1 0.09 <0.010 < 0.002 < 0.0004 <0.0005 32 2 0, " < 0.020 < 0.003 < 0.0006 < 0.0006 32 3 0.1o < 0.020 < 0. 001 < 0.0007 <0.0006 32 4 0.12 <0.010 < 0.1 < 0.0005 <0.0005 37 1 0.08 < 0.020 < 0.002 < 0.0006 <0.0006 37 2 0.10 0.00705 <0.002 < 0.0004 <0.0005 37 3 0.09 <0.009 <0.0009 < 0.0004 < 0.0004 f 37 4 0.11 <0.02 < 0.2 < 0.0006 <0.0005 i 40 1 0.07 < 0.007 < 0 . 0 01 < 0.0004 < 0.0003 40 2 0.09 <0.01 < 0.002 < 0.0005 < 0.0004 ' 40 3 0.09 0.0196 < 0.0008 < 0.0004 < 0.0004 i 40 4 0.13 <0.008 < 0 .1 < 0.0004 <0.0005 f B 4 l i 4 l I 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 26 of 54
i l l TABLE 5 , 1994 First and Second Quarter TLD Results l (mr/90 day qtr) l l First Quarter (Teledyne) Second Quarter (Panasonic) l Location Days 90 Day Error (2 Location Days 90 Day Error (2 ] Average std dev) Average std dev) 1 95.2 14.1 1.2 1 89.8 16.4 2.8 2 95.1 12.9 1.6 2 90.0 17.9 2.7 3 95.1 13.5 1.1 3 89.9 16.3 2.2 4 95.1 13.9 2.0 4 89.9 17.5 2.0 5 95.1 13.0 1.4 5 ** 6 95.1 13.4 1.1 6 90.0 17.9 3.1 7 95 12.7 0.8 7 90.0 17.6 2.5 8 95.1 14.1 1.1 8 90.0 19.4 3.3 9 95 12.9 0.9 9 89.9 16.9 2.4 10 95 14.4 1.3 10 ** 11 95 15.2 1.2 11 89.9 20.0 3.5 12 95.1 14.1 2.1 12 89.9 18.6 2.9 13 95.1 13.9 2.2 13 89.9 19.3 3.6 14 95.1 14.6 0.9 ~4 4 89.9 18.9 3.6 15 95.1 14.0 1.8 15 89.9 18.2 2.7 16 95.1 13.4 0.9 16 89.9 18.9 3.9 17 95.1 14.0 1.6 17 89.9 19.0 2.4 18 95.1 14.7 1.9 18 89.9 20.1 3.7
.9 95.1 14.6 1.1 19 89.9 19.7 4.2
[G 95.1 14.4 1.9 20 89.9 18.0 2.9 21 95.1 13.0 2.9 21 89.9 14.3 2.8
'. 2 95.1 15.0 1.7 22 89.9 16.4 2.4 23 95.1 14.2 2.8 23 89.9 16.4 2.7 24 95.1 14.2 1.6 24 89.8 16.0 2.5 25 95.1 11.9 0.5 25 89.8 12.8 1.8 26 95.1 13.2 1.5 26 89.8 14.6 1.7 27 95.1 14.1 1.3 27 89.8 15.8 2.8 ,
28 95.1 12.6 1.4 28 89.8 14.2 2.3 29 95.1 12.1 0.9 29 89.8 13.9 2.6 30 95.1 14.5 1.2 30 89.8 15 4 2.0 31 95.1 13.6 0.8 31 89.8 16.2 2.5 32 95.2 13.5 0.9 32 89.8 16.1 2.8 33 95.1 13.9 2.7 33 89.8 17.1 2.7 34 95.2 14.5 0.6 34 89.7 17.0 2.6 35 95 14.6 1.0 35 90.0 16.2 2.2 36 95 13.9 1.3 36 90.0 15.9 1.2 37 95 14.0 3.1 37 89.8 15.2 1.9 38 95.1 15.5 1.7 38 89.8 18.6 4.4 39 95 14.2 1.0 39 89.8 15.5 1.9 40 95.2 12.6 1.3 40 89.8 14.3 1.9 41 95.1 14.4 1.0 41 89.8 13.7 2.0 42 95.1 9.7 0.9 42 89.8 9.5 1.4 43 95.1 9.5 1.0 43 89.8 9.6 0.9
- TLDs disappeared while in the field i
I 1994 Annual Radiological Environmental Operating Report j Wolf Creek Generating Station Page 27 of 54
TABLE 6 1994 Third and Fourth Quarter TLD Results (mr/90 day qtr) Third Quarter (Panasonic) Fourth Quarter (Panasonic) Location Days 90 Day Error (2 Location Days 90 Day Error (2 Average std dev) Average std dev) 1 90.0 17.1 3.2 1 90.2 15.8 0.8 2 89.7 14.6 2.4 2 90.2 14.1 2.1 3 89.7 16.1 3.0 3 90.2 15.4 0.9 4 89.7 18.1 4.5 4 90.2 16.5 0.7 5 84.8 15.6 2.6 5 90.2 15.0 0.8 ~ 6 89.7 14.9 2.1 6 90.2 14.4 1.0 7 89.8 15.1 3.0 7 90.2 14.8 0.9 8 89.8 18.2 4.6 8 90.2 16.9 0.5 9 89.8 15.1 2.3 9 90.2 14.2 0.6 10 85.0 18.7 5.0 10 90.2 16.4 0.8 11 89.8 18.4 2.9 11 90.2 17.6 1.0 12 89.8 16.8 3.3 12 90.2 15.2 1.3 13 89.8 16.8 2.7 13 90 2 17.7 2.7 14 89.8 16.9 2.6 14 90.2 16.4 1.3 15 89.7 17.0 3.5 15 90.2 15.4 1.0 16 89.7 17.0 2.7 16 90.2 14.7 1.3 17 89.8 17.1 3.8 17 90.2 15.3 0.6 18 89.8 17.7 3.1 18 90.2 16.2 2.1 19 89.9 16.7 2.7 19 91.0 19.5 0.7 20 89.9 17.7 4.0 20 91.0 17.9 1.0 21 89.9 14.3 2.2 21 91.0 13.6 0.5 22 89.9 17.8 4.1 22 91.0 16.5 2.7 23 89.9 15.5 2.6 23 91.0 15.1 3.4 24 89.8 15.7 3.2 24 91.0 15.6 2.8 25 89.9 12.7 1.8 25 91.0 12.7 1.8 26 90.0 14.6 2.4 26 91.0 16.5 1.2 27 90.0 16.2 3.5 27 91.0 16.1 1.2 28 89.9 13.9 2.3 28 91.0 12.6 1.1 29 89.9 12.8 1.3 29 91.0 12.5 0.7 30 90.0 14.6 2.2 30 91.0 14.6 1.2 31 90.0 15.5 3.8 31 91.0 15.0 0.7 32 89.9 15.1 3.1 32 91.0 14.1 0.9 33 89.9 15.6 0.9 33 91.0 18.1 1.0 34 90.0 17.0 2.4 34 91.0 18.4 1.4 35 89.7 16.4 1.7 35 90.2 17.0 , 2.7 36 89.7 17.4 3.1 36 90.2 15.0 1.5 37 90.0 16.0 3.5 37 90.2 16.4 2.6 38 90.0 19.4 3.5 38 90.2 17.6 1.1 39 89.8 16.9 2.8 39 90.2 15.0 1.0 40 90.8 15.7 3.1 40 90.1 16.0 3.3 41 90.0 17.1 3.0 41 90.2 15.4 2.8 42 90.0 10.4 1.5 "~~ 42 90.2 9.7 0.8 43 90.0 9.1 1.7 43 90.2 8.9 0.7 44 90.0 15.9 3.9 44 90.0 16.0 1.0 45 90.0 16.8 2.4 45 91.0 17.2 2.2 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 28 of 54
I r E l TABLE 7 ; 1994 Drinking Water Radiological Analyssa ; (pci/litar, analysis error reported in Appendix B) , Loc Data GR-B E-3 Mn-54 Fe-59 co-58 co-60 Bn-65 Br-Mb-95 1-131 Co-134 co-137 Ba-La-140 comants BW15 5-Jan 6.4 <2 c5 <2 <3 c5 <3 <0.5 <3 <3 <3 BW15 1-Feb 6.4 <3 <7 c4 <4 <7 c4 <0.7 <4- <4 <6 i BW15 1-Mar 4.6 <3 <7 <3 <3 <7 <4 <0.8 <4 <4 c6 i BW15 5-Apr 5.9 c4 <7 c4 c4 <7 c4 <0.2 <3 <4 <6 BW15 3-May 5.9 <3 c6 <3 <3 <6 <3 <0.2 <3 <3 <3 l BW15 8-Jun 5.4 c2 c5 <2 <3 c5 <3 <0.5 <3 <3 - <3 , BW15 7-Jul 7.9 <4 <8 <4 <3 <7 <4 ' <0.1 c4 <4 <6 l BW15 2-Aug 8.2 c3 c5 <3 <3 c6 <3 <0.2 <3 <4 <3 l BW15 6-Sep 7.4 <3 <6 <3 <3 <6 <3 <0.4 <3 c4 <4 i BW15 4-Oct 5.8 <3- <5 <3 <3 <6 <3 <0.6 <3 <3 c4 BW15 2-Nov 7 <3 <8 <3 <3 c6 <3 c0.7 <3 <3 c5 l BW15 6-Dec 5.6 <3 <6 <3 <3 <6 c3 c0.2 <3 <3 c4 i BW15 1 QTR c500 i BW15 2 QTR <500 i BW15 3 QTR <500 l BW15 4 QTR <200 f LW40 5-Jan 5.8 <3 c5 <2 <3 <6 <3 <0.4 <3 <3 <4 i LW40 1-Feb 5.6 <3 <6 c3 <4 c7 <3 <0.6 <3 <3 <6 f LW40 1-Mar 13 <3 <6 <3 <3 c6 <3 <0.9 c3 c4 <4 i LW40 5-Apr 3.3 <3 c6 <3 <3 <7 <3 <0.2 <3 <3 <4 f LW40 3-May 7.4 <3 c5 <3 <3 c6 <3 <0.2 <3 <3 c4 LW40 7-Jun 6.1 <3 c5 <3 <3 c6 <3 <0.4 <3 <3 c4
*W40 6-Jul
., 5.2 <3 c5 c3 <3 <6 <3 <0.1 <3 <3 <4 Grab I Sample }
LW40 6-Jul 8.3 <3 <7 <3 <3 <7 <3 <0.1 <3 <4 <5 ! LW40 2-Aug 8.3 <3 <6 <3 <3 <6 <3 <0.6 <3 c5 <4 LW40 6-Sep 5.9 <4 <B <4 <# <9 <4 <0.2 c4 c4 c4 Grab l Sample i LW40 6-Sep 6.5 c3 <6 <3 c3 c5 <3 <0.5 <3 c4 c5 , LW40 4-Oct 6.4 <9 <20 <9 <9 <20 <9 <0.5 c10 <10 <10 I LW40 2-Nov 7.1 <3 <7 <4 <4 <8 <3 <0.6 <4 <4 c5 J LW40 6-Dec 4.5 c4 <7 <3 c4 <8 <4 <0.2 c4 <4 c4 [ LW40 1 QTR c500 f LW40 2 QTR c500
-f LW40 3 QTR c500 LW40 4 QTR <200 i i
i f
)
L i 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 29 of 54
- ~ _ . . . _ _ , _ . _ , ,
i
I l l TABLE 8 i 1994 Surface Water Radiological Analyses I (pci/ liter, analysis error reported in Appendix B)- Location DATE H-3 K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-Nb- I-131 Cs-134 Cs-137 Ba-La- p 95 140 MUSH JAN 18 <400 <50 <3 c5 <3 <3 c6 <3 c5 <3 c4 <4 . MUSH FEB 15 c400 <50 <3' <7 <3 c4 <7 <3 c6- <3 <3 c5 MUSH MAR 15 <400'c100 <4 <8 c4 c4 48 <4 <7 c4 c4 c6 ; MUSM APR 19 <400 <70 c3 c6 <3 <3 c6 <3 <4 <3 <3 c4 g; MUSH MAY 17 <400 <60 <3 <B c4' <4 <7 <3 <7 <4 e4 <6 ? MUSH JUN 21 <400 c40 <3 c5 <3 . <3 <6 <3 <4 <3 <3 <4 l MUSH JUL 19 <400 <60 <3 c7 <3 <3 <7 <3 <6 c4 <4 <5 MUSH AUG 16 <500 c40 <3 c5 <3 <3 c6 <3 c4 <3 c3 c4 MUSH SEP 20 <500 <90 <3 <7 <3 <4 <7 <3 <4 <4 c4 c4 MUSH OCT 18 c400 c50 c3 <6 <3 <3 <7 <3 <4 <3 c4 c4 MUSH NOV 15 <200 <40 <2 <4 <2 <2 <4 <2 <3 <2 <3 <3 l MUSH DEC 22 <200 c50 <3 <7 <3 <4 <7 <3 c5 c4 <4 <6 DC JAN 18 7500 <100 <4 c9 <4 <4 c10 c5 <8 c5 c5 c6 DC FEB 15 9600 <50 <3 <5 ,<3 <3 ~<5 <3 <6 <3 <3 c4 DC MAR 151M00 <100 c4 <10 <5 45 clo <5 <8 <5 <5 <7 DC APR 1911000 c40 c3 <6 <3 <4 c8 c3 <4 <3 -<3 <4 DC
- APR 19 20000 <50 <3 c5 <3 <3 <5 <3 <4 <3 c3 <3 DC MAY 17 9600 51.3 c4 <9 <4 <4 <9 ce <7 c4 <4 c6-DC JUN 21 9500 c40 <3 c5 <2 c2 <5 <3 <4 <3 <3 <3 l
DC JUL 1914000 <70 <3 c7 <3 <4 <7 ce <6 c4 c4 c6 ; DC AUG 16 8800 <B0 <3 <6 <3 <3 <6 <3 c4 <3 <3 <4
- DC SEP 2011000 c50 <3 c5 <3 <3 <6 <3 <4 <4 c4 <4 i DC OCT 1810000 470 <3 c6 <3 <3 <6 <3 <4 <3 <3 <4 DC
- OCT 1811000 <80 <3 <7 <3 <3 <7 <3 c5 <3 <3 <4 DC NOV 15 9600 <80 <3 c6 <3 <3 <6 <3 c4 <3 <3 <4 DC DEC 22 9400 <60 <3 c6 c4 cf <8 c4 c6 c4 <4 c6 ?
SP ** JAN SP FEB 15 9800 <100 <4 <8 c3 c4 <8 <4 <7 44 <4 <6 L SP MAR 1511000 <80 <3 <6 <3 <3 c6 <3 c5 <3 <3 <4 ! SP APR 1910000 <100 c4 <7 <3 'c3 c8 <4 <4 <4 c4- c4 SP MAY 17 9400 <50 <3 c6 <3 <3 <6 <3 c5 c3 <4 c4 ' SP JUN 21 9400 <50 <3 <6 <3 <3 46 <3 <4 <3 ' 43 <4 [ SP JUL 19 9200 <50 c3 <6 <3 <3 c6 c3 c6 <3 c4 <4 j SP AUG 16 9700 <50 <3 <6 <3 <4 c6 <3 <6 <3 <3 <4 i SP SEP 20 9700 <70 <3 <6 <3 <3 <7 <3 <4 <3 <3 <3 SP OCT 1811000 <100 c3 c7 <3 <3 <7 s3 c5 <3 <3 c4 [ SP NOV 15 9400 <90 <3 <6 <3 c3 <6 <3 <4 <3 <3 <3 r SP DF.C 22 9500 c50 <3 <7 <3 <3 <8 <3 c6 c4 c4 c5 UHS-SEC G-WCCL OCT 26 9700 c50 <3 <6 <3 <3 <6 <3 c5 <3 c4 <4 j BEMIS COVE-SEC H-WCCL OCT 26 9200 <60 <4 <7 <3 c4 <8 c4 <6 c4 <4 c5 ,7 SADDLE DAM 4-SEC K- OCT 26 9600 <50 <3 <6 c3 <3 <6 <3 c4 <3 .<4 c4 - WCCL REINKER RD-SEC L-WCCL OCT 26 9200 <50 c3 <7 <3 <4 <7 <3 <5 c4 <4 <4 , MUDS-SEC P-WCCL OCT 26 2700 c50 <3 c7 <3 <3 <6 <3 <6 <3 <3 c6 ; N HOUSERS-SEC R-WCCL OCT 26 9300 <70 c4 <8 c4 c4 <p <4 47 <4 <4 c6 i
- Duplicate Analysis :
** Unavailable due to ice cover 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 30 of 54
i I I TABLE 9 1994 Ground Water Radiological Analyses (pci/ liter, analysis error reported in Appendix B) Loc Date H-3 K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-Nb- I-131 Cs-134 Cs-137 Ba-La-95 140 B-12 15-Feb-94 <100 <50 <3 <7 <3 <3 <7 <4 < 0.1 <3 4 5 B-12 17-May-94 c400 64.5 < 4 <8 <4 c4 <8 c4 <02 c4 4 6 B-12 16-Aug-94 c500 <50<3 c6 <3 <3 <6 <3 < 0. 3 <3 3 4 B-12* 16-Aug-94 <500 <50 < 3 c5 <3 <3 <5 <3 < 0.2 <3 4 4 B-12 15-Nov-94 <200 <40 < 3 <5 <3 <3 <6 <3 < 0.2 <3 3 4 C-10 15-Feb-94 <100 <60<4 <7 <4 c4 <8 <4 < 0 .1 <4 4 7 C-10 17-May-94 <400 <100 <4 < 10 c4 c4 < 10 c5 < 0.2 c5 5 8 C-10 16-Aug-94 c500 c50 < 3 <6 <3 <3 <6 <3 < 0.2 <3 3 4 C-10 22-Nov-94 < 200 59.5<3 <7 <3 <3 <7 c4 < 0.2 <3 4 5 C-49 15-Feb-94 <100 <60 < 3 c6 <3 c4 <7 <3 < 0.1 <3 4 6 C-49 17-May-94 c 400 <50 < 3 c6 <3 <4 <7 <3 < 0.2 <3 4 5 C-49 16-Aug-94 <500 c60<4 <8 c4 c5 < 10 <5 < 0 .1 c4 5 6 C-49 15-Nov-94 <200 <90 < 3 <7 <3 <3 <7 <3 < 0.2 <3 4 4 D-65 15-Feb-94 <100 <60 < 3 <7 <3 <3 c6 <3 < 0.2 <3 3 4 D-65 17-May-94 c400 <80 < 3 <7 <3 <3 <7 <3 < 0.2 <3 3 5 D-65 16- Aug-94 < 500 <50<3 <6 <3 <3 c6 <3 < 0.1 <3 4 3 D-65 15-Nov-94 <200 440<2 <S <2 <3 <5 <2 40.2 <3 4 4 F-20** 15-Nov-94 <200 <60<3 c6 <2 <3 <6 <3 < 0.2 <3 3 4
- Duplicate Analysis
- Duplicate Sample from Location B-12 (15-Nov-94)
TABLE 10 1994 Aquatic Plants Radiological Analyses (pci/kg, wet, analysis error reported in Appendix B) LOC TYPE DATE BE-7 K-40 MN-54 CO- 5 8 CO- 6 0 CS-13 4 CS -13 7 RA- 22 6 TH- 22 8 DC ALGAE APR 22 721 1680 8 11 100 21 50 417 221 DC
- ALGAE APR 22 719 1730 <5 9 95 c5 46 411 185 DC ALT AM LOTUS MAY 31 255 3000 <20 <20 <20 <20 <20 <300 <30 DC ALT AM LOTUS JULY 19 755 4170 <20 <20 <20 <20 <20 <300 <30 WCCL OUTLET POOL ALGAE OCT 14 859 3080 c6 c6 <B <7 <70 <100 59 EEA PONDWEED OCT 14 294 1560 <8 <8 <9 <10 <10 <200 <20
- Duplicate Analysis l
i 1 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 31 of 54 l
i i TABLE 11 I
)
1994 shoreline sediment Radiological Analyses ; (pci/kg, dry, analysis error reported in Appendix B) LOC DATE BE-7 K-40 CO-58 CO-60 CS-134 CS-137 RA-226 TH-228 , DC 5/31/94 c400 11100 c40 71 89 122 2430 1430 l JRR 5/31/94 <200 9180 <20 ' < 20 <30 < 30 2550 1190 -{ EEA '10/14/94 <400 12100 c40 < 30 c50 93 2050 1240 JRR 10/26/94 <300 6550 <30 < 30 c40 < 40 1510 877 DC' 10/26/94 <300 ' 8400 41 209 c40 44 1130 708 UHS-SEC G-WCCL 10/26/94 <300 8530 <30 < 30 c40 < 40- 1820 1170 , BBMIS COVE-SEC H-WCCL 10/26/94 c500 12000 <50 < 50 c60 < 60 9280 1460 SADDLE DAM 4-SEC K-WCCL 10/26/94 <300 7860 <30 < 30 <30 < 30 1810 1150 j S REINKER ROAD-SEC L-WCCL10/26/94 <300 7820 <30 < 30 <30 < 30 1570 974 MUDS-SEC P-WCCL 10/26/94 <300 12200 <30 < 40 <50 < 40 2470 1430 N HOUSERS-SEC R-WCCL 10/26/94 <300 11300 < 3 0 < 40 c40 50 2640 1410 JRR
- 10/26/94 <300 7050 <30 < 30 c40 < 40 1300 917
- Duplicate Analysis TABLE 12 f 1994 Bottom sediment Radiological Analyses I (pci/kg, dry, analysis error reported in Appendix B) :
Location DATE BE-7 K-40 MN-54 CO-58 CO-60 CS-134 CS-137 RA-226 TM-228 I JRR 5/31/94 c400 17000 < 50 < 40 < 40 < 60 301 2160 1490 DC 5/31/94 <300 12900 < 40 < 40 1100 210 723 1470 1460 DC 10/26/94 < 400 114 00 < 40 < 50 897 168 540 2600 1120 JRR 10/26/94 < 300 16400 < 30 < 30 <- 30 < 40 241 2230 1290 i UHS 10/26/94 <400 12000 < 40 < 40 127 < 40 260 1880 1110 l BP4IS COVE-SEC H-WCCL 10/26/94 c400 10900 < 40 < 40 87.5 < 50 378 1820 1110 , SADDLE DAM 4-SEC K-WCCL 10/26/94 <300 7180 < 40 < 30 < 40 < 40 77.7 1350 863 i S REINKER RD-SEC L-WCCL 10/26/94 <200 4820 < 20 < 30 73.8 < 30 130 1450 707 .l MUDS-SEC P-WC% 10/26/94 <400 10400 < 40 < 40 129 < 40 132 2520 1050 } N HOUSERS-SEC R-WCCL 10/26/94 < 300 11200 < 30 < 30 203 < 40 270 2260 1180 l DC
- 10/26/94 <300 14 000 < - 40 < 40 942 187 678 1870 1170 j WC f 11TH ROAD 11/30/94 632 89*0 < 30 < 30 < 40 < 40 < 40 1980 928 t
- Duplicate Analysis l e
l t l l t
?
i t r 1994 Annual Radiological Environmental Operating Report , Wolf Creek Generating Station Page 32 of 54 !
TABLE 13
'1994 Broadleaf vegetation Radiological Analyses (pci/kg, wet, analysis error reported in Appendix B)-
DATE TYPE LOC RE-7 K-40 RU-103 I-131 CS-134 CS-137 RA-226 TE-228 31-May-94 CABBAGE G-1 < 100 5030 < 10 < 20 < 10 c 10 < 300 < 30 31-May-94 CABBAGE S-4 < 80 4400 < 10 < 10 < 10 < 10 < 200 < 20 31-May LETTUCE R-1 232 4950 < 10 < 10 < 10 < 10 < 200 < 20 28-Jun-94 CABBAGE G-1 146 3700 <9 < 10 < 10 < 10 < 200 < 20 f- 28-Jun-94 CABBAGE S-4 197 4330 <8 < 10 <9 < 8 < 200 < 20 28-Jun-94 CABBAGE R-1 320 4030 <9 < 10 < 10 17.1 < 200 < 20 26-Jul-94 CABBAGE G-1 397 2690 < 10 < 20 < 10 < 10 < 200 < 20 26-Jul-94 CABBAGE S-4 638 3170 < 20 < 30 < 20 < 20 < 300 < 20 26-Jul-94 LETTUCE R-1 464 5670 < 20 < 30 < 20 < 20 < 300 < 30 23-Aug-94 CABBAGE G-1' 417 4030 < 10 < 20 < 10 < 10 < 200 < 10 23-Aug-94 CABBAGE S-4 565 4100 < 20 < 30 < 20 < 20 < 300 < 20 - 27-Sep-94 CABBAGE G-1 589 2470 < 10 < 10 < 10 < 10 < 200 < 20 27-Sep-94 CABBAGE S-4 787 2260 < 10 < 20 < 20 < 20 < 300 < 20 '(
'15-Oct-94 , CABBAGE G-1 223 3220 < 10 < 10 < 10 < 10 < 200 < 20 ,
23-Oct-94 CABBAGE S-4 530 2400 < 10 < 20 < 10 < 10 < 200 < 20
==
TABLE 14 l 1994 Irrigated Crops Radiological Analyses (pci/kg, wet, analysis error reported in Appendix B) ; DATE TYPE LOC BE-7 K-40 R0-103 2-131 CS-134 CS-137 RA-226 TR-228 27-Sep-94 CORN NRD1 c 40 2830 c 4 c 5 c 4 c 4 c 80 <7 17-Oct-94 SOYBEANS NRU1 < 50 16400 <6 c 10 c6 <6 c 90 <9 , r 17-Oct-94 CORN NRU1 < 40 2550 <5 c 10 <5 e5 c 90 c 8 17-Oct-94 CORN NRD2 < 40 3240 <5 c 10 <4 c4 c 80 < 7 j 17-Oct-94 ALFALFA NRD2 804 16500 c 60 < 60 < 50 < 50 c 1000 < 100 17-Oct-94* SOYBEANS NRU1 c 60 16300 c7 c 10 <7 <6 c 100 < 10 i, I
- Duplicate Analysis t t
i l t i
' ;l 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 33 of 54
i TABLE 15 1994 Milk Radiological Analyses (pci/ liter, analysis error reported in Appendix B) , LOC 7YPE DATE I-131 K-40 CS-134 CS-137 BA-LA-140 COMMENTS S-3 COW 1/11/94 c 0.2 1360 <3 c3 ce S-3 COW 2/8/94 c 0.2 1460 c4 c4 c7 S-3 COW 3/8/94 c 0.2 1470 <5 c5 c6 S3 COW 4/12/94 c 0.2 1360 <4 c5 c4 S-3 COW 4/12/94 c 0.2 1330 <4 e5 c3 DUPLICATE ANALYSIS f S-3 COW 5/10/94 c 0.2 1370 e4 <4 c5 S-3 COW 5/24/94 < 0.2 1460 <4 <4 c5 S-3 COW 6/14/94 c 0.2 1470 <3 c3 c3 S3 COW 6/29/94 c 0.2 1340 c4 c4 c5 S-3 COW 7/12/94 c 0.1 1390 c3 c4 c4 S-3 COW 7/26/94 < 0.2 1360 c5 c5 c6 S-3 COW 8/9/94 c 0.2 1490 <4 c4 c4 S-3 COW 8/23/94 c 0.2 1450 <4 c4 c6 S-3 COW 9/13/94 c 0.1 1300 <4 c4 c5 S-3 COW 9/27/94 c 0.1 1400 <4 c4 c4 , S-3 COW 10/11/94 c0.2 1410 <3 <3 c4 , S-3 COW 10/25/94 <0.3 1530 <3 c4 c5 l S-3 COW 11/8/94 c 0.2 1370 <3 c3 c3 S-3 COW 11/22/94 c0.2 1490 c5 c5 c6 S-3 COW 12/13/94 c0.2 1490 <4 c4 c5 I l l l l l I s l l, l d 1994 Annual Radiological Environmental Operating Eeport Wolf Creek Generating Station Page 34 of 54
1 I i i: l t
?
1 TABLE 16 1994 Fish Radiological Analyses. j (pci/kg, wet, analysis error reported in Appendix B) SPECIES LOC DATE K-40 MN-54 FE-59 CO CO-60 ZN-65 CS-134 CS-137 H-3 WHITE CRAPPIE WCCL 4/22 3530 c 10 < 30 e 10 < 10 < 30 < 10 24 SM BUFFALO WCCL 4/22 3370 < 10 c 30 c 10 e 10 < 20 < 10 < 10 COMMON CARP WCCL 4/22 3790 < 10 < 30 c 10 c 10 < 30 < 20 < 20 BM BUFFALO JRR 6/7 3330 < 10 c 20 e 10 < 10 < 20 < 10 c 10 LM BASS JRR 6/7 3520 < 10 e 30 < 10 < 10 < 30 e 10 < 10 CHANNEL CATFISH JRR 6/7 3350 < 10 < 30 < 20 < 10 < 30 'c 20 < 20 BM BUFFALO .WCCL MAIN 10/11 2330 c 10 < 30 < 10 c 10 c 30 c 10 < 10 5500 DAM l WALLEYE WCCL MAIN 30/11 4680 < 20 < 30 c 20 < 20 < 3 'O c 20 < 20 7100 { DAM SM BUFFALO WCCL DC 10/11 3250 < 10 < 30 c 10 < 10 < 30 < 10 < 10 6600 WIPER WCCL DC 10/11 4050 < 10 < 30 c 10 < 10 < 30 < 10 < 10 7600 WHITE BASS WCCL 10/11 3490 < 10 < 30 < 10 < 20 < 30 < 20 c 20 6600 CAUSEWAY CHANNEL CATFISH WCCL 10/11 3000 < 10 c 30 < 10 c 10 < 30 < 10 < 10 7000 CAUSEWAY BM BUFFALO
- WCCL MAIN 10/11 2240 < 10 < 30 < 10 < 20 < 30 < 10 < 20 5700 ,
DAM 1 BM BUFFALO WCCL- 10/14 2190 c 20 < 40 < 20 <. 20 < 40 < .20 < 20 4700 l OUTLET " I POOL SM BUFFALO / RIVER WCCL- 10/14 3610 c 10 < 30 c l'e c 10 c 30 < 10 c 20 4300 l CARPSUCKER OUTLET l POOL WHITE CRAPPIE JRR 10/26 3850 < 20 < 30 < 10 < 20 < 30 < 20 < 20 c 300 i COMMON CARP JRR 10/26 4150 c 20 < 50 c 20 < 20 < 40 < 20 < 20 c 300
- Duplicate Analysis !
1 l l
)
I I l 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 35 of 54 l
h t TABLE 17 l 1994 Land Use Census Residence Data 1993 1994 TOTAL NO. OF DISTANCE (Mi) / . DISTANCE (Mi)/ POPULATION RESPONSES / CLOSEST . CLOSEST RESIDENCE- l SECTOR FOR SECTOR HOUSEHOLDS RESIDENCE , A 12 115. 1.4/A1.4 2. 6 /A2. 6 twr.11731 B 12 6/6 3.1/B3.1 3.1/B3.1-QURD1712- i C 21 9/9 1.9/C1.9 1.9/C1.9-16RD1655-D 2 1/,.5 2.1/D2.1 2.1/D2.1-QULA1571 E 11 5/_1 1.8/E1.8 1.8/E1.8-QULA1485 F 11 14/14 1.6/F1.6 1.6/F1.6-14RD1711 G 12 8/10 1.6/Gl.6 1.6/G1.6-QURD1384 , H 2.Q ffE 3.1/H3.1 3.1/H3.1-12RD1711. I J 2.Q flE 3.3/J3.3 3.3/J3.3-OXLA1141 K 11 1/.5 2.6/K2.6 2.6/K2.6-12LA1439 , L 52 22/22 2.1/L2.1 2.1/L2.1-NARD 1339 , M 2.E 13/14 1.6/M1.6 2.4/M2.4-14RD1321 l l N 22 E./.R 2.1/N2.1 2.6/N2.6-HW751465 P 11 27/28 2.8/P2.8 2.7/P2.7-16RD1255 Q 22 10/11 1.4/Q1.4 1.4/Q1.4-NALA1574 ; R S 21.1 2.1/R2.1 2.1/R2.1-NALA1650 , NOTE: Entries underlined indicate changes from the 1993 Land Use Census. { l P r I 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 36 of 54
I t TABLE 18 1994 Land Use Census Milk and Garden Data { 1993 1994 1993 1994 D/Q l DISTANCE DISTANCE DISTANCE DISTANCE (DEPOSITION (MI) / MILK (MI) / MILK (MI)/ CLOSEST (MI) / CLOSEST CONSTANT) / t SECTOR ANIMAL ANIMAL GARDEN GARDEN RANKING i A none none 1.4/A1.4 2.9/A2.9-17LA151B 1.56E-09/3 , B 4.9/B4.9 none 4.2/B4.2 4.2/B4.2-18RD1758 6.13E-10/s C none none 2.6/C2.6 2.2/C2.2-16RD1670 B.63E-10/4 D none none 2.1/D2.1 2.1/D2.1-QULA1571 4.97E-10/13 i E none none 1.8/E1.8 1.8/E1.8-QULA1485 5.80E-10/10 i F 4.9/F4.9 none 1.8/F1.8 1.8/F1.8-14RD1730 7.07E-10/6 , G 3.6/G3.6 none 1.6/G1.6 1.6/G1.6-QURD1384 1.93E-09/2 , H 4.9/H4.9 none 4.9/H4.9 3 .1/H3 .1-12 RD1711 6.97E-10/7 ; J none none 4.0/J4.0 3.B/J3.8-11RD1535 3.92E-10/14 l K none none 4.1/K4.1 4.1/K4.1-NARD 1120 3.62E-10/15 j L none none 2.6/L2.6 2.6/L2.6-NARD 1308 5.55E-10/12 I M none none 2.4/M2.4 2.4/M2.4-14RD1321 5.61E-10/11 l N none none 2.6/N2.6 2.6/N2.6-HW751455 5.86E-10/9 i P none none 4.3/P4.3 4.3/P4.3-16RD1112 2.31E-10/16 ; Q none none 3.9/Q3.9 2.3/02.3-MTLA1619 7.22r-10/5 R none none 2.1/R2.1 2.1/R2.1-NALA1650 2.11E-09/1 I NOTE: Underlined entries indicate changes fr:m the 1993 Land Use census. ; i 1 l i l 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 37 of 54 l 1
TABLE 19' . 1994 US IPA Interlaboratory Comparison Program EPA INTERLABORATORY COMFARISON FROGRAM 1994 Enviremmasatal r Co11ection Teledyne Brown i Date Media Nuclide EPA Resultta) L t-ad Renult(b) Deviation (c) 01/28/94 Water Gr-Beta 62.0 1 10.0 72.33 i 3.79 1.79 02/04/94 Water 1-131 119.0i 12.0 110.33 1 0.00 -1.30 03/04/94 Water H3 4936.0 1 494.0 4833.33 i 152.75 , -0.36 04/19/94 Water Gr-Beta 117.0 1 18.0 102.67 i 6.43 -1.38 Co-60 20.0 1 5.0 23.67 i 3.21 1.27 Cs-134 34.0 1 5.0 34.00 i 1.73 0.00 i Cs 137 29.0 1 5.0 34.00
- 2.65 1.73 06/10/94 Water Co-60 50.0 1 5.0 43.00 1 2.00 -2.42 Id)
Zn-65 134.0 i 13.0 13.33 1 0.58 -16.08 ld Ru-106 252.0 1 25.0 201.33 i 9.29 -3.51 (f) Cs-134 40.0 1 5.0 29.33 i 3.79 -3.70 W Cs-137 49.0 i 5.0 49.67 i 1.53 0.23 Ba-133 98.0 i 10.0 85.00 i 3.00 -2.25 lb) 07/12/94 Water Gr-Beta 10.0 1 5.0 16.00 i 0.00 2.08 5 08/d,94 Water H-3 9951.0 i 995.0 9700.00 1 100.04 -0.44 i 08/26/M ,CrFilter Cs-137 15.0 1 5.0 17.00 i 1.73 0.69 l 10/07/94 Water I-131 79.0 1 8.0 71.00 1 3.00 1.73 rootnotes: (a) EPA Results-Expected laboratory precision (1 sigma). Units are pCi/ liter for water and milk except K is in mg/ liter. Units are total pC1 for air particulate filters. Ib) Teledyne Results - Average i one sigma. Units are pCi/ liter for water and milk except K is in mg/ liter. Units are total pCl for air particulate Alters. (c) Normattud deviation from the known. (d A second aliquot was analyzed paying particular attention to volume aliquoted. The result. 52 pCi/1. was in good agreement with the EPA. The three original results. l each counted on a different detector, showed good precision. The measurement of l Co-60 has not been a problem. Future EPA cross-checks will be weighed and results ! followed to check for a possible trend 'out of contro1*. l 1 (c) The averaje value of three analyses on the " Report of Analysis' was 133 pCi/ liter ! which is in good agreement with the EPA. Apparently. Incorrect results (by a factor ! of ten) were entered into the EPA computer. Future data will be printed from the ; computer screen to check entries. , I 1 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 3B of 54
1 l 1 TABLE 19 (Cont) . 1994 US EPA Interlaboratory Comparison Program I l l
)
i i g2 1 EPA DETsntma rORT COMPARISOlt PROGRAM 1994 l ht : Fasemates: i (0 he EPA has indicated that the Radiation Quality Assurance Program has been ; expertencing i-vli with the ruthentinm.106 analysis. See attmehad letter frosn ! I!PA. (g he Arzt aliquot. prepared a Jag to EPA dilution instructions was counted on i four detectors in the 111ter Marinelli geometry with Cs-134 results (based on the 'P96 ' kev peak) in pC1/1 of 32.0,25.1. 31.7. and 30.8. De 31.7 result was not reported. I Had that been reported instead of 25.1. the average would have beer 31.5 and the , normatired deviation would have been -2.94 instand of 3.70. A secord aliquot was , prepared and a single measurunent was made with the result of 31.1 pC1/1. An ; undiltted ahquot was rnessured in a 150 ml with the result of 33.5 pCi/1. ; nat result is c rable with the results. Dus none of : sample l preparation (dilution. volume determination maintaining correct pH. etc.). sample j geometry, or detector emetenry seem to be the cause of the loir results. l (b) "Ihere is no apparent reason for the lour result, however the average value. 85 pC1/1 is ' in good agr**mant to the grand average (86.46). No corrective action pinnned l
- (0 EPA results for gross beta in water were corrected for 20% crosstalk into the beta l channel from the Th-230 alpha spike. Recent measuremenen show that the crosstalk '
can be much higher (37% for Tennelec counter #3 and 54% for gamma products j counter #1). 'Ibe normatired deviation from the grand average was only 0.38. j Future results will be corrected with speciSc crosstalk values determined by I counting Tb-230 standards. j l l P i 4 1 i t 1 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 39 of 54 ) I
TABLE 19 (Cont) . 1994 US EPA Interlaboratory Comparison Progrant uesg
. .fg.
Ig/
* e -
UNmED STATES ENylRONMENTAl. PROYECMON AGENCY oPFICE or HEstanCu aseo oEvtkosess9fr c twvenomenstwrac isourroness systems a ama=a ronv4.as vesas ao aos ouve LAs vcsas wavaan sele >wve (702/7e52300 FTs sa&23 col Dear Participant The Radiation Quality Assurance Program has been experiencing problems with the Ruthenius-106 currently used in the Performance Evaluation (PE) Studies and in the Standards Distribution Program. If these problems can be satisfactorily resolved, this analyte vill ance again > be placed into this PE Study. If the problems cannot be resolved, the , Ruthenium-106 vill be replaced. Formal written notice vill be given to all participants that are i enrolled in the Gamma in Vater PE Study before the Ruthemius-106 is
- reintroduced or replaced. At that time, new calibration standards will be available to all participants in the Gamma in Vater PE Study.
Sincerely, George D11 beck Chemist Periormance Evaluation Program Radioanalysis Branch (RSA-RADQA) h 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 40 of 54
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DIRECT RADIATION PATHWAY SAMPLING LOCATIONS e = TLD LOCATIONS 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 42 of 54
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~S= DRINKING WAllER A= SURFACE WATER E= GROUND WATER 4= SHORELINE SEDIMENT AND BOTTOM SEDIMENT
@ = SPECIAL SAMPLE LOCATIONS 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 43 of 54
i FIGURE 4 i
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DISTANT SAMPLING LOCATIONS e = TLD m= DRINKING WATER A= MILK . = BROADLEAF VEGETATIOW j IRRIGATED CROPS 1 1994 Annual Radiological Environmental Operating Report Wolf Creek Generating Station Page 45 of 54
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1994 Annual Radiological Environmental Operating Report ! Wolf Creek Generating Station Page 54 of 54 i
l Appendix A Summary Tables in the format of NRC Radiological ' Assessment Branch Technical Position ' Revision 1, Novetnber 1979 I i 1 Page A-1
.w. ... - -
, f ENVIRONMENTAL RADIOL 9GICAL MONTIURING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 Location of Facility Coffev County. Kansas Reporung Period Annual 1994 ICounty, State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator Imcations location with Highest Annual Mean ControlImmtions Nonroutine Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measurements" - station No. 4e Air Particulate Gross (265) 3 28(212/212) 32 3.2 miles WNW 28(53/53) 27(53/53) 0 (X10-3 pCI/Cu.M.) Beta (10-48) (10-44) (13-45) 1-131 (265) 7 -(0/212) N/A N/A -(0/53) - y Gamma (20) to
- Be-7 I 0 93(16/16) 32 3.2 miles WNW 101(4/4) 91(4/4)
}" (71-117) (93-117) (65-125) ru K-40 24 27(2/16) 3 3.0 miles NNE 48(1/4) 20(1/4) 0 (7.1-48) -- - stations se ana ao External TLD (348) 0.05 .171(322/332) 11 1.6 miles E .199(8/8) .167(16/16) Radiation Quarterly (.098 .223) (.170 .223) (.141 .188) (mR/ day)
~
Nominal Lower Umit of Detection (LLDI
*
- Mean and range based upon detectable measurements only. Fraction of detectable measurements at spectned locations is Indicated in parentheses If)
_ _ _ _ _ _ _ _ _ _ _ _ . _ . _ _ _ _ _ _ . _ . _ ~ . . _ _ _ . . . .. _ , . _ . . _ _ . _ _ _ _ . _ . - . . . _ _ _ , . _ . _
ENVIRONMENTAL RADIOLOGICAL MONilDRING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.S'IN 50-482 Incation of Facility Cosev County. Kansas Reporting Period Annual 1994 (County State) Analysis and lower Limit Number of - Medium of Pathway Total Number of All Indicator locations Imcation with Highest Annual Mean Control Imcations Nonroutine Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) "Ra nge Distance and Directions " Range " Range Measurements" J. T "z --2 "_ __. i Fish Gamma (16) (pC1/kg wet) K-40 500 339C(11/11) JRR 4 miles W 3640(5/5) 3640(5/5) 0 (2190-4680) (3330-4150) (3330-4150 Cs-137 6 24(1/11) WDCL 24(1/11) -(0/5) 0 Trtitum (10) 300 6175(8/8) WCCL 6175(8/8) -(0/2) 0 2 (4300-7600) (4300-7600) -- E y S-4 4, Food and Gamma (15) Garden Crops (pCl/kg wet Be-7 90 349(8/9) S-4 <l5 miles WNW 543(5/6) 543(5/6) 0 weight) (146-589) (197 787) (197-787) K-40 500 3977(9/9) R-12.1 miles NNW 4883(3/3) 3443(6/6) 0 (2470-5670) (4030-5670) (2260-4400) Cs-137 10 17(1/9) R-12.1 miles NNW 17(1/3) -(0/6) 0 Ra-226 200 -(0/9) NA NA -(0/6) 0 Th-228 20 -(0/9) N/A --
-(0/6) 0 Ti...:. l Imwer umit of Detection (ILDI .
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses ($
, . , - - --..---e- - r~+ .- . - .v,4 -- ~ - - =e..m
* -- - ~ - , . - . . - - - - - , ,...e- - - - - . . . - - . - , . - - - - - -
- ENVIRONME2frAL RADIOIDGICAL MONITORING PROGRAM
SUMMARY
Name of Facthty wok Creek Nuclear Docket No.STN 50-482 location of Facibly Co8cr CountiLEsnama . Reporting Period Annual 1994 (County. State) Analysis and lower Umst Number of Medium of Pathway Total Number of All Indicator Imcations Incation with Haqthest Annual Mean CentralImations Nonroutine- l Sam ed ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (O Reported (Unit of surement) Perforened (LLD) " Range Dis' nce and Directions " Range " Range Measurements" - NRU1 Irrigated Crop Gamma (5) (pCl/kg wet weight) Be-7 20 800(l/3) NR-D2 800(I/2) -(0/2) 0
>10 miles S -- --
K-40 500 7523(3/3) NR-D2 9870(2/2) 9475(2/2) 0 (2830-16500) >10 miles S (3240-16500) (2550J16400) I W P l l l
= nomin=1 umer umit or octecuan sua
*
- mean and rense based upon detectable meneumnents only. 1%etson of detectable menemamente at specined lacetions is indienced in perenthe.e. to
s-ENVIRONMENTAL RADIOLOGICAL MG . mfg _PROGRAK.
SUMMARY
s Name of Facility Wolf Creek Nuclear Docket No.S1N 50-482 Incation of Facility CoRev County. Kansas Reporting Period Annual 1994 (County, State) i Analysis and lower Limit Number of 1 Medium of Pathway Total Number of All Indicator Imcations Incation with Highest Annual Mean contralImcallons Nonroutine Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (0 Reported
- (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measurements" Station M Milk 1-131 (19) 3 -- --
-(0/19) 0 "
(pCl/I) Gamma (19) K-40 100 -- -- 1419(19/19) 0 (1300-1530) I W b f
^i n
4
- Nominal IAwer Limit of Detecuan (LLDI
" Mean and range based upon detectable measurements only. 1%ction of detectable meneurements at spectned locations is indicated in parentheses (0
__ . _ . _ . _ . _ _ _ _ . . _ _ . . _ _ _ _ _ . . - . . . _ . _ _ _ . _ _ . - _ . . _ a _. . .._..___..-,.__..._.__.;_._._.__.._._...______._._..._. _ . . . _ .
ENVIRONMENTAL RADIOLOGICAL MONffDRING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 Incation of Facility Coffev County. Kansas Reporting Period Annual 1994 (County State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator Imcations Incation with Highest Annumt han Control Locations Nonroutine Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range "Ranste Measurements" Station No.JRR Sediment / Silt Gamma (11) (pCl/kg . dry weight) BE-7 300 632(l/9) WC & 11th Road 'i32(l/1) -(0/2) 0 3.8 miles S -- -- K:40 500 9969(9/9) JRR 4 miles W 16700(2/2) 16700(2/2) 0 (4820-14900) (16400-17000) (16400-17000) 2 Co-58 20 -(0/9) NA NA -(0/2) 0 g -- -. 7 m Mn-54 30 -(0/9) NA NA -(0/2) O Co-60 20 374(7/9) DC 0.6 miles WNW 999(2/2) -(0/2) 0 (74-1100) (897-1100) -- Cs-134 60 189(2/9) . DC 0.6 miles WNW 189(2/2) -(0/2) 0 (168-210) (168-210) -- Cs-137 60 314(8/9) DC 0.6 miles WNW 632(2/2) 271(2/2) 0 (78-723) (540-723) (241-301) Ra-226 500 1926(9/9) MUDS 2520(1/1) 2195(2/2) 0 (1350-2600) 1.5 miles WNW -- (2160-2230) Th-228 40 1059(9/9) JRR 4 miles W 1390(2/2) 1390(2/2) 0 (707-1460) (1290-1490) (1290-1490)
- Nominal Lower Limit of Detection (ILD)
" Mean and range based upon detectable meneusements only. Fraction of detectable measurements at spectned locatione is indicated in parentheses (Q
ENVIRONMFXTAL RADIOLOGICAL MONTIURING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.S'IN 50-482 Incation of Facility Cafev County. Kansas Reporting Period Annual 1994 (County, State) Analysis and I.mwer Limit Number of Medium of Pathway Total Number of All Indicator Imcations Incation with Highest Annual Mean Contrgl larations Nonroutine ' Sampled ofAnalysis Detection " Mean (0 Name- "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measuremente" 9tauen No.JRR Shoreline Soll Gamma (11) (pCI/kg dry weight) K-40 500 10148(9/9) MUDS 12200(1/1) '7865(2/2) 0 (7820-12200) 1.5 miles WNW -- (6550-9180) ' Co-58 20 41(1/9) DC 0.6 miles WNW 41(l/2) -(0/2) O m CD y Co-60 30 140(2/9) DC 0.6 miles WNW 1s O(2/2) -(0/2) 0
, (71-209) (71-209) --
Cs-134 60 89(1/9) DC 0.6 miles WNW 89(I/2) -(0/2) ; O Cs-137 60 77(4/9) EEA 3 miles NNW 93(1/1) -(0/2) 0 (44-122) -- -- Ra-226 500 2800(9/9) H 1.5 miles SSE 9280(1/1) 2030(2/2) 0 (l130-9280) -- (l510-2550) Th-228 40 1219(9/9) H 1.5 miles SSE 1460(1/1) 1034(2/2) 0 (708-1460) -- (877-I190) i Mominal Imwer umit of Detection ILLDI
" Mean and range based upon detectable measwements only. Fractirm of detectable measumnente at specWhed locations to indicated in parentheses 18 1
_-m ,4.- ,..-.-,-..~~-...---,-----w ----.---w. - _ _ ..o-v. emw.w.e-.-,4 - - . ....-..-me.- < . = - , . . - . . , . s.-w.s.e-- ~~.-w -. , . . - - - . .--.,..c - - _ . . . .
. _ _4--
e_ ENVIRONMENTAL RADIOIDGICAL MONTIORING PROGRAM
SUMMARY
1 Name of Facility Wolf Catek Nuclear Dodset No.STN 50-482 Incation of Factisty Coffev County. Kanese Reporting Period Annual 1994 (County, State) Analysis and lower Limit Number of Medium of Pathway Total Number of All Indicator imcations Imcation with Highest Annual Mean ControlImcations Monroutine Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directione " Range " Range Measuremente" No Centret Soll Gamma (3) (PC1/kg dry weight) Be-7 300 2500(2/3) Al 1.4 miles N 2650(1/1) -- 0 (2350-2650) -- K-40 500 10483(3/3) MUDS 12400(1/1) -- 0 u (6950-12400) 1.5 miles WNW --
<E Cs-137 60 202(3/3) Al 1.4 miles N 293(1/1) --
0 Y m (99-293) -- Ra-226 500 1787(3/3) MUDS- 2630(1/1) -- 0 (1170-2630) 1.5 miles WNW .. Th-228 40 1006(3/3) MUDS 1220(1/1) - - - 0 (718 1220) 1.5 miles WNW ..
- Nominal Imwer umit of C,.6,.L (ILD)
" Mean and range beoed upon detectable meneuremente only. Fraction of detectable measuresnente at spectned locettono le ineheated in parentheses (Q
R ENVIRONMENTAL RADIOIDGICAL MONHURING PROGRAM
SUMMARY
Name of Facility wok.CreclLNuclear Docket No.STN 50-482 location of Facility Coffev County. Kansas Reporting Period Annual 1994 (County, State) Analysts and lower Limit - Number of. Medium of Pathway Total Number of All Indicator locations location with Highest Annual Mean ContralImcations Nonroutine Sampled ofAnalysis Detection " Mean (f) Name "Mean (f) "Mean 10 Reported (Unit of Mer .,orement) Performed (LLD) " Range Distance and Directions ** Range " Range Measurements" NoContal Vegetation Aquatic Gamma (6) (pCl/kg wet weight) Be-7 100 601(6/6) WCCL Outlet Pool 859(1/1) -- 0 (255-859) 3.3 miles S -- K-40 500 2537(6/6) DC ALT 3585(2/2) -- 0
,o (1560-4170) 1.5 miles NW --
Mn-54 40 7.5(1/6) DC 0.6 rntles WNW 7.5(1/2) -- 0 m
? .. ..
Co-58 10 9.8(2/6) DC 0.6 miles WNW . 9.8(2/2) -- 0 (9.1 - 11) (9.1 - 11) , i Co-60 10 98(2/6) DC 0.6 mdes WNW 98(2/2) -- 0 (95-100) (95-100) Ce-134 20 21(1/6) DC 0.6 miles WNW 21(1/2) -- 0 Cs-137 10 48(2/6) DC 0.6 miles WNW 48(2/2) -- 0 (46-50) (46-50) Ra-226 200 414(2/6) DC 0.6 talles WNW 414(2/2) -- 0 (411-417) (411-417) Th-228 20 155(3/6) DC 0.6 miles WNW 203(2/2) -- 0 (59-221) (185-221) Nominal Imwer Limit of Detection (LLDl -
" Mean and range based upon detectable measurements only. Fraction of detectable ..-_w.e..-..ts at specifled locatione to indicated in parentheses (t)
_ _ _ _ _ _ _ _ _ _ . _ _ _ . _ _ _ _ _ . _ . . . _ _ _ . _ _ . _ _ _ _ _ . _ _ . . _ . _ _ _ _ _ _ _ _ _ _ _ . _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ , . . . , _ _ , . , . - , , _ ,r _ . _ . . . _ . . . . . , . _ _m.,_..._,.r.,..--m ..._,,_m.,m,, .-..m.._ o
ENVIRONMENTAL RADIOIDGICAL MONr1DRING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.STN 50-482 Location of Facility Coffev County. Kan=== Reporting Period Annual 1994
. (County, State)
Analysis and Lower Limit Number of . Medium of Pathway Total Number of All Indicator IAcations location with Hishest Ann ===l Mean Control Locatlana Nonrouune Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (O Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range
' ~ ~
" Range Measurementa" No controt Vegetation Terrestrial Gamma (2)
(pCI/kg wet weight) Be-7 100 7580(2/2) EEA 3 miles NNW 8470(1/1) -- 0 (6690-8470) -- K-40 500 4115(2/2) EEA 3 miles NNW 5680(l/1) -- 0 y (2550-5680) -- E P 8 l t
- Nominal Imwer Limit of Detection (LLD) l
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at spectfled locations is Indicated in parentheses (Q l
i
-N ENVIRONMENTAL RADIOLOGICAL MONfIDRING PROGRAM
SUMMARY
Name of Facibty wok Creek Nuclear Docket No.S'IN 50-482 Imcation of Facility Cafew County. Kansas Reporting I%rlod Annual 1994 (County, State) ' Analysts and Imrer IJmit Number of Medium of Pathway Total Number of All Indicatar Locations imcation with Highest Annual Mean CantalImemunns Nonroutine Sampled ofAnalysis Detection " Mean (0 Name "Mean (0 "Mean (0 Reported (Unit of Measurement) Performed (LLD) **Ra nge Distance and Directione " Range " Range ' Measurements" WW-15 , Water 1-131 (26) 0.5 -(0/14) NA NA -(0/12) 0 Drinking (pCl/l) Gross (26) 2 6.7(14/14) LW40-11.3 miles SSE 6.7(14/14) 6.4(12/12) O Beta (3.3- 13) (3.3- 13) (4.6-8.2) Gamma (26) --
-(0/14) NA NA -(0/12) . O m TriUum (8) 1000 -(0/4} NA NA -(0/4) 0 g .. .. ..
to
? ,
2 s-1s Water. 1-131 (17) 0.5 -(0/13) NA NA -(0/4) 0 Ground -- -- (pCi/l) . Gamma (17) K-40 100 60(1/13) B-12-2.2 miles NNE 65(1/4) 65(1/4) 0 Tritium (17) 1000 -(0/13) NA NA -(0/4) 0 i l
- Nominal Imurer unit of Detection (LLDI .
-1 !
" Mean and range beoed upon detectable measurements only. Fraction of detectable measurements at spectned locations to Indicated in parentheses (4 i
__ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ . _ . _ _ _ _ _ , . _. . . _ _ - _ - . , _ , . . _ ~ . . , _ _ - . . _ _ . . - . _ , - _ _ , - - - . _ - . ~ . - . , . . _ - . . . . . . . . , . . . . . , . . . _ _ . - . _ _ _
M ENVIRONMENTAL RADIOIDGICAL MONITORING PROGRAM
SUMMARY
Name of Facility Wolf Creek Nuclear Docket No.S~IN 50-482 location of Facility Coffev County. Kansas Reporting Period Annual 1994 (County State) Analyses and lower Limit Number of Medium of Pathway Total Number of All Indicator locations location with Highest Annual Mean Cantml Immtions Nonroutine - Sampled ofAnalysis Detection ** Mean (0 Name "Mean (0 "Mean (O . Reported (Unit of Measurement) Performed (LLD) " Range Distance and Directions " Range " Range Measurements" Mush Water Surface Gamma (41) (pCI/D K-40 60 51(1/29) DC 0.6 miles WNW 51(1/12) -(0/12) 0 Tritium (41) 1000 9579(29/29) DC 0.6 miles WNW 10000(12/12) -(0/12) 0 o (2700-14000) (7500-14000) -- i$ en Y 4 i
- Nominal inwer Limit of Detection (LLD)
" Mean and range based upon detectable measurements only. Fraction of detectable measurements at spectiled locations is indicated in parentheses (4
5 Appendix B 1994 Individual Sample Results t r t t I F F L t b l l l Page B-1 ) l
)
WOtX CREEK NUCLEAR OPERATING CORPORATION AIR PARI 1CUIATE AND CilARCOAL FIL'IERS STATION NUMBER 02 COLLECIlON DATE MID COUffr A P FILTER MID COUlTF CHARCOAL F1LTER START STOP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS DATE (pCI/Cu.M.) DATE (pCI/Cu.M.) 12/28 01/04 3.40E 08 OC 01/14 3.110.3 E-02 01/07 LT. 1. E-02 01/04 01/11 3.30E 08 OC 01/21 3.9 i 0.4 E-02 01/15 LT. 1. E-02 . 01,11 0I/I8 3.30E 08 OC 01/25 3.5 i 0.4 E-02 01/22 LT. 1. E-02 01/18 01/25 3.40E 08 OC 02/02 3.010.3 E-02 01/28 LT. 2. E-02 01/25 02/01 3.30E 08 CC 02/10 3.310.3 E-02 02/05 LT. 2. E-02 j 02/01 02/08 3.00E 08 OC 02/17 2.8 i 0.3 E-02 02/12 LT. 2. E-02 [ 02/08 02/15 3.10E 08 OC 02/24 3.0 i 0.4 E-02 02/19 LT. 1. E-02 b 02/15 02/22 3.20E 08 OC 03/04 2.5 i 0.3 E-02 02/25 LT. 1. E-02 02/22 03/01 2.90E 08 OC 03/09 2.310.3 E-02 03/09 LT. 4. E-02 N 03/01 03/08 3.20E 08 OC 03/19 2.5 i 0.3 E-02 03/15 LT. 3. E-02 03/08 03/15 3.20E 08 OC 03/23 2.010.3 E-02 03/19 LT. 9. E-03 03/15 03/22 2.80E 08 OC 03/30 1.6 i O.3 E-02 03/26 LT. 1. E-02 03/15' 03/22 2.80E 08 OC 03/30 1.7 i 0.3 E-02 03/29 LT. 2. E-02 03/22 03/29 2.90E 08 OC 04/06 1.9 i 0.3 E-02 04/02 LT. 2. E-02 03/29 04/05 2.80E 08 OC 04/16 2.210.3 E-02 04/06 LT. 2. E-02 04/05 04/12 2.60E 08 - OC 04/20 2.0 i 0.3 E-02 04/15 LT. 2. E-02 04/12 04/19 2.80E 08 OC 04/27 2.7 i 0.4 E-02 04/23 LT. 1. E-02 04/19 04/26 2.70E 08 OC 05/05 2.5 i 0.3 E-02 04/30 LT. 2. E-02 04/28 05/03 2.70E 08 OC 05/12 1.4 i 0.3 E-02 05/07 LT. 2. E-02
- Duplicate Analysis
i , i ,r L R - E T ) . L I 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 - F 1 M. 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 L u E E E E E E E E E E E E E E E E E E E E A13C O/ ClC t 3 3 3 . . . 1 2 1 2 2 1 1 3 2 2 2 3 1 3 2 1 1 p R ( T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. - A T. T. T. T. T. H C L L L L L L L L L L L L L L L L L L L L . U l U 4 1 7 8 5 1 6 5 2 8 5 2 5 2 19 61 OEE 1 2 2 2 0 2 0 0 1 1 9 81 . 1 1 1 2 3 0 2 0 0 CMT A / / / / / / / / / / / / / / / / / / / / DTD I 5 5 5 5 6 6 6 6 7 7 7 7 7 8 8 S 8 9 9 9 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 - I M N 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 O A 0 0 0 -0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 - I T S RT) E. E E E E E E E E E E E E E E E E E E E E A R EB.M t E O T E T LSu 3 4 3 3 3 3 3 3 4 3 3 4 3 3 3 3 4 3 3 4 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 O 0 0 0 0 P LI FSC I O/ i 1 1 i i i i 1 i i i i i i 1 i i i i i R F PRC l 0 5 5 6 5 5 1 4 5 3 8 7 7 0 0 8 2 9 9 0 O L A G (p - C 2 2 2 2 2 2 2 2 3 2 2 2 2 3 3 2 3 2 2 4 o OA 0 2 mRC T R - A R A E E CH MB - P D U O N N U R A N l U A 2 E 1 OI OEE 8 62 30 3 1 0 0 3 01 9 1 3 4 0 7 1 2 2 I 2 2 3 1 1 1 5 2 9 4 5 9 1 2 2 0 1 1 C A AT E I CMT DTD I A / / / / / / / / / / / / / / / / / / / / 5 5 6 6 6 6 6 6 7 7 7 7 7 8 8 8 8 9 9 9 - U U T 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N C S I M K I 1 . E R . E A R P _ C R sIA e o w .S T - I N C O OC0 C CC C OCO C C OC OCO C O C E C ( O I ( C O OC OC E C C
- O I
( U . E 8 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 0 U E E 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 0 0 O V 7 7 8 8 8 8 6 8 7 8 7 7 8 8 7 8 7 9 0 9 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 3 2 O 7 4 4 7 4 8 5 2 91 6 21 9 8 3 0 8 3 _ EPE I 1 2 2 3 0 1 1 1 2 2 0 2 0 0 1 2 3 0 TOT / / / / / / / / / / / / / / / / / / / / 1 ATA 5 5 5 5 5 6 6 6 6 7 7 7 7 8 8 8 8 8 9 9 s
- DSD 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 t
s y l a N n O A I T C ET ' h k LRE 3 0 7 7 4 1 7 4 1 8 5 2 9 16 2 1 9 8 3 0 8 i 0 1 1 1 2 3 0 1 2 2 0 2 0 0 1 2 3 0 p LAT / / / / / / / ///////////// u OTA 5 CSD 0 05 050 50 5 0 05 060 60 6 0 06 070 70 7 0 07 080 80 8
- 8 8 9 D 2E b 1
WOtX CREEK NUCLEAR OPERATING CORPORATION AIR PARUCULATE AND CHARCOAL FIL*lERS STATION NUMBER 02 COLLECT 10N DATE MID COUNT A P FILTER MID COUNT CHARCOAL FlLTER START STOP TIME GROSS BETA TIME I-131 . DATE DATE VOLUME UNITS DATE (pCl/Cu.M.) DATE (pCl/Cu.M.) 09/13 09/20 2.90E 08 OC 09/26 2.010.3 E-02 09/23 LT. 3. E-02 09/20 09/27 2.90E 08 OC 10/03 2.4 i 0.3 E-02 09/30 LT. 1. E-02 09/27 10/04 2.90E 08 OC 10/09 4.8 i 0.4 E-02 10/07 LT. 2. E-02 10/04 10/11 2.90E 08 OC 10/18 3.510.4 E-02 10/16 LT. 2. E-02 10/11 10/18 3.00E 08 OC 10/25 2.3 i 0.3 E-02 10/22 LT. 2. E-02 y 10/18 10/25 2.90E 08 OC 10/31 2.510.3 E-02 10/28 LT. 3. E-02 10/25 11/01 3.00E 08 OC 1I/07 2.7 i 0.3 E-02 11/03 LT. 2. E-02
- 1. 11/01 11/08 2.90E 08 OC 11/14 3.510.4 E-02 11/12 LT. 2. E 11/08 1I/15 2.90E 08 CC 11/21 2.610.3 E-02 11/19 LT. 3. E-02 11/15 II/22 3.00E 08 CC 12/02 2.4 i 0.3 E-02 11/29 LT. 2. E-02 11/22 11/29 2.90E 08 T 12/05 3.0 i 0.3 E-02 12/01 LT. 3. E-02 1I/29 12/06 2.90E 08 E 12/12 2. 8 i 0.3 E-02 12/09 LT. 1. E-02 12/06 12/13 2.90E 08 OC 12/20 3.5 i 0.4 E-02 12/20 LT. 3. E-02 12/13 12/20 2.90E 08 OC 12/29 4.0 i 0.4 E-02 12/23 LT. 2. E-02 12/20 12/27 3.00E 08 OC 01/06 3.0 i 0.3 E-02 12/31 LT. 2. E-02 12/27 01/03 3.00E 08 OC 01/10 4.010.4 E-02 01/06 LT. 2. E-02
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;p n Tj WORF CREEK NUCEEAR OPERATB90 CORPORATION -
AIR PAR 11CUIA1E AND CHARCOAL FIL*IERS STATION NUMBER 03 COLLECIlON . DATE MID COUNT A P FILTER MID COUNT CHARCOAL F1 Lama START STOP TIME GROSS BETA TIME I-131 DATE DA'IE VOLUME UNITS DATE (pct /Cu.M.) DATE bCt/Cu.M.) 05/17 05/24 3.00E 08 CC .06/03 2.4 i 0.3 E-02 05/27 LT. 2. E-02 05/24 05/31 2.90E 08 OC -06/10 2.1 i 0.3 E-02 06/05' LT. 2. E-02 05/31 06/07 - 3.00E 08 OC 06/13 2.3 i 0.3 E-02 06/11c LT. 1. E-02 ': 06/07 06/14 2.80E 08 OC 08/20 2.1 i 0.3 E-02 06/16 LT. 2.' E 06/14 06/21 2.90E 08 OC 06/29 2.7 i 0.3 E-02 06/25- LT. ' 2. E-02 06/21 06/28 3.00E 08 OC 07/13 3.6 i 0.4 E-02 07/02- LT. 1. E-02 06/28 07/05 3.00E 08 OC 07/I4 2.5 i 0.3 E-02 07/06 LT. 1. E-02 = 07/05 07/12 3.10E 08 CC 07/20 2.710.3 E-02 07/15 LT. 2. E-02 07/12 07/19 3.00E 08 OC 07/27 2.3 i 0.3 E-02 07/22 LT. 2. E-02 07/19 07/26 3.10E 08 OC 07/31 3.8 i 0.4 E-02 07/31 LT. 2. E-02 07/26 - 08/02 3.00E 08 OC -08/11 2.9 i 0.3 E-02 . 08/06 - LT. 2. E-02 08/02 08/09 3.10E 08 OC' 08/15 3.110.3 E-02 08/12' LT. 2. E-02 08/09 08/16 3.10E 08 OC 08/22 2.9 i 0.3 E-02 08/19 LT. 1. E-02 08/16 08/23 3.10E 08 OC 08/29 3.6 i 0.4 E-02 08/26- LT. 2. E-02 08/23 08/30 2.90E 08 OC 09/04 2.8 i 0.3 E-02 09/01 LT. 2. E-02 08/30 09/06 3.10E 08 OC 09/15 2.7 i 0.3 E-02 09/09 LT. 1. E-02 09/06 09/13 2.90E 08 ^OC 09/19 4.1 i 0.4 E-02 - 09/16 LT. 1. E 09/13 09/20 2.80E 08 OC 09/26 2.6 i 0.3 E-02 09/23 LT. 3.- E-02 09/20 09/27 2.80E 08 OC 10/03 2.4 i 0.3 E-02 09/30 LT. 1. E-02 09/27 10/04 2.90E 08 . OC 10/09 4.2 i 0.4 E-02 '- 10/07 LT. 2. EiO2. L--.__ -_-__vw-_A-m.ava2*-mamv-m-u-__a _mw-w,rw,w-%,ww+- war wsmmw- L,- ---a ew -w e ww w, m_e6-- - m,dww.w: . -w e.%-ewwgeg-.e wiser- hvw-+'weeawrT+-4Wwi1r-imeh-e F en-ww- et-Hwm w wewwmeup-wwww d% w a g - w-wa-.mm vay,-wwegis Am, .m.m-w M
5 1 & b WOtX CREEK NUCLEAR OPERATING CORPORATION AIR PART1CUIATE AND CHARCOAL FIL1ERS STA110N NUMBER 03 COL 1EC110N DATE MID COUNT A P FILTER MID COUNT CHARCOAL FlLTER START STOP TIME GROSS BETA TIME l-131 DATE DATE VOLUME UNITS DATE (pC1/Cu.M.) DATE (pCl/Cu.M.) 10/04 10/11 2.80E 08 m 10/18 3.7 i 0.4 E-02 10/16 LT. 2. E-02 10/11 10/18 2.80E 08 OC 10/25 2.4 i 0.3 E-02 10/22 LT. 2. E-02 10/18 10/25 2.80E 08 CC 10/31 3.3 i 0.4 E-02 10/28 LT. 3. E-02 10/18* 10/25 2.80E 08 OC 11/02 3.410.4 E-02 10/29 LT. 2. E-02 10/25 11/01 2.90E 08 OC 11/07 2.8 i 0.3 E-02 11/03 LT. 2. E-02 11/01 11/08 2.80E 08 OC 11/14 3.9 i 0.4 E-02 11/12 LT. 2. E-02 11/08 11/15 2.80E 08 OC I1/21 2.6 i 0.3 E-02 11/19 LT. 3. E-02 ' = 11/15 11/22 2.90E 08 OC 12/02 2.7 i 0.3 E-02 11/29 LT. 2. E-02 11/22 11/29 2.90E 08 OC 12/05 2.810.3 E-02 12/01 LT. 3. E-02 1I/29 12/06 2.90E 08 OC 12/12 2. 5 i 0.3 E-02 12/09 LT. 1. E-02 12/06 12/13 2.90E 08 OC 12/20 3.0 i 0.3 E-02 12/20 LT. 3. E-02 12/13 12/20 2.90E 08 OC 12/29 4.2 i 0.4 E-02 12/23 LT. 2. E-02 12/20 12/27 3.00E 08 OC 01/06 3.2 i O.3 E-02 12/31 LT. 2. E-02 . 12/27 01/03 3.00E 08 - OC 01/10 4.010.4 E-02 01/06 LT. 2. E-02
*Dupilmte Analysis
. 4 _
WotF CREEK NUCLEAR OPERATING CONFOttATION AIR PARTICULATE AND CHARCOAL FILTERS STATION NUMBER 32 COLLEC110N DATE MID COUlTF A P FILTER MID COUNT CHAiK CAL MLa r,n START STOP TIME GROSS BETA TIME I-131 DATE DA'IE VOLUME UNITS DATE (pCl/Cu.M.) DA'TE (pCl/Cu.M.) - 12/28 01/04 3.30E 08 OC 01/14 3.010.3 E-02 01/07 LT. 1. E-02 ' O1/04 01/11 3.10E 08 OC 01/21 4.3 i 0.4 E-02 'O1/15' - LT. 1. E-02 0I/11 01/18 3.00E 08 OC 01/25 4.4 i 0.4 E-02 0I/22 LT. 1. E , OI/18 01/25 2.90E 08 OC 02/02 2.2 i 0.3 E-02 01/28 LT. 2. E-02 l 01/25 02/01 3.00E 08 T 02/10 3.5 i 0.4 E-02 02/05 LT. ' 2. E-02 02/01 02/08 2.90E 08 OC 02/17 2.710.3 E-02 02/12 . LT. 2. E-02
- 02/08 02/15 2.80E 08 OC 02/24 - 2.710.4 E-02 02/19 LT. 1. E-02
- m 02/15 02/22 2.80E 08 OC 03/04 2.7 i 0.3 E-02 02/25 . LT. 1. E-02 ,
- 02/22 - 03/01 2.80E 08 OC 03/09 3.1 i 0.4 E-02 ' 03/09 LT. 4. E-02 03/01 03/08 2.90E 08 OC 03/19 2.6 i 0.3 E-02 03/15 LT. 4. E-02 03/08 - 03/15 2.80E 08 E 03/23 2.3 i 0.4 E-02 03/19 LT. 1. E-02 03/15 03/22 2.90E 08 OC 03/30' 2.1 i 0.3 E-02 03/26 LT. 1. E 03/22 03/29 3.00E 08 OC 04/06 2.2 i 0.3 E-02 04/02 LT. 2. E-02 03/29 04/05 2.90E 08 OC 04/16 2.310.3 E-02 04/08 LT. 2. E-02 04/05 04/12 2.70E 08 CC 04/20 2.0 i 0.3 E-02 04/15 . LT. 2. E-02 '
04/12 04/19 2.90E 08 OC 04/27 2.5 i 0.4 E-02 04/23- LT. 1. E-02 04/19 04/26 ~ 2.80E 08 OC 05/05 2.2 i 0.3 E-02 04/30 LT. 2. E-02 04/26 05/03 3.00E 08 OC 05/12 1.0 i 0.2 E-02 05/07 LT. 2. E-02 t 05/03 05/10 2.90E 08 OC 05/18 2.2 i 0.3 E-02 05/14 LT. 2. E-02 05/10 05/17 2.80E 08 OC -05/26 2.1 i 0.3 E-02 05/21 LT. 2. E-02 i m-- . _ -mm. . . , - . _ . - . _ - , . ..--..,2 . , - + . . . . - . m. m.....-.v .---~..-,...-.-.--...-~.i...---,.._.,-...---.me ..~...m..-c..-_~.__m em.--- ~,._-.o_-,
& I
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WOLF CREEK NUCIEAR OPERATING CORPottA1 Mitt AIR PAR 11CULATE AND CHARCOAL FIL'IERS STA110N NUMBER 32 COLLECI1ON DATE MID COUNT A P FILTER MID COUlff C&h0AL FIL1ER - m. START STOP TIME GROSS BETA TlME l-131 -; DA'IE DA'IE VOLUME UNITS -DATE loci /Cu.M.) DATE (pCI/Cu.M.) 05/17 05/24 2.80E 08 OC 06/03 2.8 i 0.3 E-02 05/27 LT. 3. E } 2.90E 08 05/24 05/31 OC 06/10 2.310.3 E-02 06/05 LT. 2. E-02
- 05/31 06/07 2.90E 08 OC 06/13 2.2 i 0.3 E-02 06/11 LT. ~ 1. E-02 06/07 06/14 2.70E 08 OC 06/20 1.9 i 0.3 E-02 06/16 LT. 2. E +
06/14 06/21 2.90E 08 CC 06/29 2.5 i 0.3 E-02 06/25 LT. 2. E , 06/21 06/28 2.80E 08 OC 07/13 3.6 i 0.4 E-02 07/02 LT. 1. E-02 , W 06/28 07/05 2.80E 08 OC 07/14 2.7 i 0.3 E-02 07/08 LT 1. E-02 ^ 07/05 07/12 2.80E 08 OC 07/20 2.710.3 E-02 07/15 LT. 3. E-02 07/05* 07/12 2.80E 08 OC 07/21 2.410.3 E-02 ** 07/12 07/19 2.80E 08 OC 07/27 2.7 i 0.3 E-02 07/22 LT. 2. E-02 07/19 - 07/26 2.60E 08 OC 07/31 3.1 i 0.4 E-02 ,07/31 LT. 2. E-02 07/26 08/02 2.70E 08 OC 08/11 2.8 i O.3 E-02 08/05- ~ LT. 3. E-02 08/02 08/09 2.80E 08 OC 08/15 2.7 i 0.3 E-02 08/12 LT. 3.~ E-02 08/09 08/16 2.70E 08 CC 08/22 3.1 i 0.3 E-02 08/19 ~ LT. 1. E-02 08/16 08/23 2.70E 08 OC 08/29 3.3 i 0.4 E-02 08/26 LT. 3. E-02 -- 08/23 08/30 2.90E 08 OC 09/04 3.110.3 E-02 09/01 LT. 2. E-02 08/30 09/06 2.90E 08 OC 09/15 3.0 t 0.3 E-02 09/09 LT. 1. E-02 08/30* 09/06 2.90E 08 OC 09/15 2.7 i 0.3 E-02 09/10 LT. 7. E-03 09/06 09/13 2.90E 08 OC 09/19 4.3 i 0.4 E-02 09/16 LT. 1. E-02 09/13 09/20 2.90E 08 OC 09/26 2.0 i 0.3 E-02 09/23 LT. 3. E-02
*Duptkate Analyses
**Dupikste analyste not performed. -
WOlE CREEK NUCLEAR OPERATING CORPORATION AIR PARI 1CULATE AND CHARCOAL FILTERS STAT 10N NUMBER 32 COLLEC110N DA'IE MID COUNT A P FILTER MID COUlTT CHARCOAL FILTER START STOP TIME GROSS BETA TIME 1-131 DATE DATE VOLUME UNITS DATE (pC1/Cu.M.) DATE (pC1/Cu.M.) 09/20 09/27 2.90E 08 OC 10/03 2.4 i 0.3 E-02 09/30 LT. 1. E-02 09/27 10/04 2.90E 08 CC 10/09 4.4 i 0.4 E-02 10/07 LT. 2. E-02 10/04 10/11 2.80E 08 OC 10/20 3.5 i 0.4 E-02 10/16 LT. 2. E-02 10/11 10/18 2.90E 08 OC 10/25 2.2 i 0.3 E-02 10/22 LT. 2. E-02 10/18 10/25 2.80E 08 OC 10/31 2.8 i 0.3 E-02 10/28 LT. 3. E-02 10/2a 1I/01 2.90E 08 T 11/07 3.I i 0.3 E-02 11/03 LT. 2. E-02 ua 11/01 11/08 2.80E 08 OC 11/14 3.1 i 0.4 E-02 11/12 LT. 2. E-02 m 11/08 11/15 2.80E 08 OC 11/21 2.4 i 0.3 E-02 11/19 LT. 3. E-02 o 11/15 11/22 2.90E 08 OC 12/02 2.8 i 0.3 E-02 11/29 LT. 2. E-02 11/22 11/29 2.90E 08 OC 12/05 2.6 i 0.3 E-02 12/01 LT. 3. E-02 11/29 12/06 2.80E 08 OC 12/12 2. 6 i 0.3 E-02 12/09 LT. 1. E-02 12/06 12/13 2.90E 08 OC 12/20 3.3 i 0.4 E-02 12/20 LT. 3. E-02 12/13 12/20 3.00E 08 OC 12/29 4.3 i 0.4 E-02 12/23 LT. 2. E-02 12/13* 12/20 3.00E 08 CC 12/29 4.2 i 0.4 E-02 12/24 LT. 8. E-03 12/20 12/27 3.00E 08 OC 01/06 3.3 i 0.3 E-02 12/31 LT. 2. E-02 12/27 01/03 3.00E 08 OC 01/10 4.3 i 0.4 E-02 01/06 LT. 2. E-02
- Duplicate Analysis
m W* J N N N N N N N N N N N n N N N N N N N N c2 9 o 9 9 9 9 o 9 9 9 o o 9 o 9 9 9 9 o o jgg m w w w w w mw w w w w w w w w w w w w o2= a a a aa a a aa 6 6 sa aaaa a aa MS 9 9 9 9 9 9 9 9 9 9 9 9 9 9 99 9 9 9 9
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i , WOEF N NUCLEAR OPERA 11IEO CORFORATION . AIR PARI 1CUTA'IE AND CHARCOAL FILTERS a STATION NUMBER 37 l > COLLECllON DA1E MID COUlU A P FILTER MID COUlU CHARCOAL filar a , START S'lVP TIME GROSS BETA TIME - I-131 DA'IE DA"IE VOLUME UNITS DA'IE (pCl/Cu.M.) DATE (pCI/Cu.M.j ' C5/03 05/10 2.90E 08 CC 05/18 2.0 i 0.3 E-02 05/14 LT. 2. E ' CS/10 05/17 2.90E 08 OC 05/26 2.2 i 0.3 E-02 05/21 LT. 2. E-02 C5/17 05/24 2.90E 08 OC 06/03 2.3 i 0.3 E-02 05/27 LT. 3. E-02 s C5/24 05/31 2.90E 08 OC 06/10 2.1 i 0.3 E-02 06/05 LT. 2. . E C5/31 06/07 2.90E 08 OC 06/13 2.2 i 0.3 E-02 06/11 LT. 1. E-02 06/07 06/14 2.80E 08 OC 06/20 2.010.3 E-02 06/16 LT. - 2. E-02 , y 06/14 06/21 2.90E 08 CE 06/29 2.5 i 0.3 E-02 06/25 LT. 2. E-02 06/21 06/28 2.90E 08 OC 07/13 3.210.4 E-02 07/02 LT. 1. E-02
'. 06/28 07/05 2.80E 08 OC 07/14 2.610.3 E-02 07/08 LT. 1. E-02 07/05 07/12 2.90E 08 OC 07/20 2.5 i 0.3 E-02 07/15 LT. 2. ' E-02 07/12 07/10 2.80E 08 OC- 07/27 2.7 i 0.3 E-02 07/22 LT. 2. E-02 07/19 07/26 2.70E 08 OC 07/31 1.8 i 0.3 E-02 07/31 LT. 2. E-02 07/26 .08/02 2.80E 08 OC 08/11 3.0 i 0.3 E-02 08/05 LT. 2. E-02 08/02 08/09 2.60E 08 OC 08/15 2.6 i 0.3 E-02 08/12 - LT. 3. E-02 08/09 08/16 2.60E 08 OC 08/22 3.210.4 E-02 08/19 LT. 1. E-02 08/16 08/23 3.30E 08 OC '08/29 3.4 i 0.3 E-02 08/26 LT. 2. E-02 .
C8/16' 08/23 3.30E 08 CC 08/29 3.4 i 0.3 E-02 08/27 LT. 2. , E-02 08/23 08/30 3.10E 08 OC 09/04 3.010.3 E-02 09/01 LT. 2.1 E-02 ' 08/30 09/06 3.20E 08 OC 09/15 2.8 i 0.3 E-02 09/09 LT. 1. E-02 ' 09/06 09/13 3.20E 08 OC 09/19 4.3 i 0.4 E 09/16.. . LT. 1. E-02 . Dupiscate An.iy.s.
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woss cassa secamam oranATmo comPonATION AIR PAlmCULATE AND CEe.RCOAL FILTERS , ' STA"I1ON NUMBER 37 t COLLECTION DATE MID COUPrF ~ A P FIL'IER MID COUlTT CHARCOAL F1Lar M START STOP TIME GROSS BETA TIME - I-131 DATE DATE VOLUME UNITS DATE (pC1/Cu.M.) DATE (pC1/Cu.M.) 09/13 09/20 3.00E 08 OC 09/26 2.4 i 0.3 E-02 09/23 LT. 3. E-02 ; 09/20 09/27 3.30E 08 OC 10/03 2.5 i 0.3 E-02 09/30 . LT. 1. E-02 -; 09/20* 09/27 3.30E 08 OC 10/03 2.3 i 0.3 E-02 10/04 LT. 2. - E-02 09/27 10/04 3.10E 08 OC 10/09 4.5 i 0.4 E-02 -10/07 L.T. 2. E-02 . 10/04 10/11 3.20E 08 OC 10/18 3.4 i 0.3 E-02 10/16 LT. 2. E-02 . 10/11 10/18 3.20E 08 OC 10/25 2.3 i 0.3 E-02 10/22 LT. 2. E-02
-1 2 10/10 10/25 ' 3.10E 08 OC 10/31 2.9 i 0.3 E-02 10/28 LT. 3. E-02 '
e 10/25 11/01 3.20E 08 OC 11/07 3.410.3 E-02 11/03 LT. 1. E-02 ' 11/08 3.00E 08 OC 11/14 4.010.4 E-02 11/12 ~- LT. 2.' E-02 h11/01 11/08 11/15 3.00E 08 OC 11/21 2.710.3 E-02 11/19 LT. 3. E-02 , 1I/15 11/22 3.50E 08 OC -12/02 2.2 i 0.3 E-02 11/29 LT. 1. - E-02 11/22 11/29 2.80E 08 OC 12/05 3.010.3 E-02 12/01 LT. 3. E-02 I 1I/29 12/06 2.80E 08 OC 12/12 3.0 i 0.3 E-02 12/09- LT. 1. E-02 , 12/06 12/13 3.20E 08 OC 12/20 3.2
- 0.3 E-02 12/20- LT. 3. E-02 12/13 12/20 2.90E 08 OC - 12/29 4.7 i 0.4 E-02 12/23 LT. 2. E-02 '
12/20 12/27 3.00E 08 OC 01/06 3.310.3 E-02 12/31-- LT. - 2. E-02 12/27 01/03 3.00E 08 OC 01/10 3.7 i 0.3 E-02 01/06 LT. 2. E-02 Dupbcate Analysis 1
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R E T ) L . 2 2 2 2 3 2 2 2 3 3 2 2 2 3 2 2 2 2 2 2 . I F M. 0- 0 0- 0 -0 0 - 0 0- 0 0- 0 -0 0 - 0 0- 0 0- 0 -0 0 - - - - - - - - - L 1 u E E E E E E E E E E E E E E E E E E E E 3C A1/ . . . . . . . . . . . . . . . . . . . . OC CI p R l 2 1 2 1 9 2 1 1 8 8 2 1 1 9 2 1 1 2 1 1 A ( T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. T. _ H L L L L L L L L L L L L L L L L L L L L . C - U l U 7 1 7 5 1 4 6 5 2 8 0 5 2 1 5 2 19 6 1 1 9 OEE CMTA 1 2 2 0 1 1 1
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2 0 0 1 1 2 3 0 2 0 0 I 5 5 5 6 6 L 6 6 7 7 7 7 7 7 8 8 8 8 9 9 - DTD I 0 0 0 0 0 C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 M . N 0 A 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0- 0 0- 0 0 0 -0 0 - 0 0 - 0 0- 0 0- 0 0 0 -0 0 - 0 1 T - - - - - - - - 1 S A R RE ). E E E E E E E E E E E E E E E E E E E E EBM. T 3 3 3 3 3 3 3 3 4 3 3 3 3 4 3 3 3 3 3 3 . R O 1 E LSu 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 , P t L I FSC I Ol/ 1 i i 1 i 1 1 1 1 i i i i 1 i i 1 i 1 1 5 F PRC 9 4 3 4 9 1 2 7 5 6 8 6 8 4 9 8 2 1 7 6 - O L AG(p 1 2 2 2 1 2 2 2 3 2 2 2 2 3 2 2 3 3 2 2 _ C G OA 40 N C - 1 R R 1 A A E t 5 H B E C M -
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ATA 9 9 9 0 0 0 0 1 1 1 1 1 1 2 2 2 2 1 s _ DSD i a 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 s - l y - a N n O A l I t e C a ET 6 3 10 7 4 8 5 8 51 5 21 9 6 3 0 7 i c LRE LA* I 0 2 2 0 1 1 1 2 0 0 1 2 2 0 1 2 2 l p
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c _ 1 J. s WOEF CREEK NUCEEAR OPERATING CORFORA110N
' AIR PAR 11CULATE FIL'IERS -
EXPOSURE PA'nfWAY - AIRBORNE IS0110PIC ANALYSIS ON QUARTERLY COMPOSTIE (pCl/Cu.M.) STA'I1ON NUMBER 02 DATE COLLECIED: 12/28-03/29 03/29-06/28 06/28-09/27 09/27-01/03 GAMMA SPECTRUM ANALYSIS: BE-7 7.8110.78 E-02 9.0410.90 E-02 8.8710.89 E-02 1.0210.13 - E-01 1 K-40 LT.8. E-03 LT.8. E-03 LT. 1. - E-02 LT.2. E-02 MN-54 LT.3. E-04 LT.5. E-04 LT.6. - E-04 LT.7. E-04 CO-58 LT. 3. E-04 LT 6. E-04 LT.4. E-04 LT. - 1. E-03 o FE-59 LT.9. E-04 LT.1. E-03 LT. 1. E-03 . LT. 3. E f CO-60 LT. 5. E-04 LT. 5. E-04 LT.5. E-04 LT. 7. E-04
, ZN-65 LT. 1. E-03 LT. 1. E.03 LT. 1. E-03 LT.2. E-03 NB-95/ZR-95 LT.4. E-04 LT.6. E-04 LT.4. E-04 L T. 1. - E-03 RU-103 LT.4. S-04 LT.7. - E-04 LT. 5. ' E-04' LT.2. E RU- 106 LT.3. E-03 LT.4. E-03 LT. 4. E-03 - LT.6. E-03 I-131
~
LT. 1. E-03 LT.2. E-03 LT. ' l. E-03 LT. ' 2. E-01 CS-134 LT.4. E 04 LT.5. E-04 LT.6. - E-04 LT. 7. - E-04 CS-137 LT.3. E-04 LT.5. E-04 LT.6. E-04 LT.6. E-04 LA-140/BA-140 LT.5. E-04 LT.2. E-03 LT. 1. E-03 LT. 2. . E-02 CE-141 LT.7. E-04 LT. 1. E-03 LT. 8. E-04 - LT.3. E-03 CE-144 LT.2. E-03 LT.3. E-03 LT. 3. E LT.4. E-03 RA-226 LT.7. E-03 LT. 1. E-02 LT. 1. E-02 LT. 1. E-02 TH-228 LT.7. E LT.9. E-04 LT. 1. E-03 LT. 1.' E-03 W-erhd W- %- eeed 4 -Wee-W* e4**wk,W1..*-+4dw esisewed e e m nw r4*e- %wed-we--ene*M-b"eadddeMW- em<W+ ~9-e ' + eew%M-V4 Aet'--sei 4 m +-4-e%* -MeM'M'8eame# 4+--+-W M4 - "- ---------t-a- '
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k WUEX CREEK NUCERAR OPERATEUG CORPORATION AIR PARITCUIEIE FIL"IERS - EXPOSURE PA'IHWAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARIERLY COMPOSTIE (pCI/Cu.M.) STATION NUMBER 03 DATE COLLECIED: 12/28-03/29 03/29-06/28 06/28-09/27 09/27-0I/03 GAMMA SPECTRUM ANALYSIS: BE-7 7.0810.71 E-02 8.63io.86 E-02 9.0610.91 E-02 ' 1.0110.12 E-01 ' K-40 4.7810.61 E-02 LT.2. E-02 LT. 1. E LT.9. E-03 . MN 54 LT. 5. E-04 LT.5. E-04 LT. 4. E-04 LT.6. E CO-58 LT.5. E-04 LT.5. E-04 LT.5. E-04 LT.9. E-04 y FE-59 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT.3. E 03
% CO-60 LT.5 E-04 LT. 6. E-04 LT. 5. E-04 LT.7. E-04 to ZN-65 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT. 5. E-04 LT.6. E-04 LT,5. E-04 LT.9. _E-04 h NB-95/ZR-95 E-04' LT. 1.
E-03 i RU-103 LT.5. E-04 LT.6. E-04 LT.5. RU-106 LT.4. E-03 LT.4. E-03 LT.4. E-03 LT. 4.' E-03 1-131 , LT. 1. E-03 LT.2. E-03 LT. 9. E-04 LT. ' 2. E-01 CS-134 LT, 5. E-04 LT.5. E-04 LT.5. E-04 LT.6. E-04 CS-137 LT.5. E-04 LT.6. E-04 LT. 5. E-04 LT.5. E-04 LA-140/BA-140 LT. 1. E-03 LT.2. E-03 LT. 1. E-03 LT.2. E-02 CE-141 LT.6. E-04 LT.7. E-04 LT. 5. E-04 LT. 3. E-03 CE-144 LT.2. E-03 LT.2. E-03 LT.2. -E-03 LT. 3. E-03 RA-226 LT. 7. E-03 LT.6. E-03 LT.6. E-03 - LT. 9. E-03 TH-228 1.0910.50 E-03 LT.6. E-04 LT.6. E-04 LT.9. E-04-- i
WOIX NE NUCIEAR OPERATING CORPORATION AIR PARTICULATE FIL'IERS EXPOSURE PKI11WAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARIERLY COMPOSITE (pCl/Cu.M.) STA110N NUMBER 32 DATE COLLECTED: 12/28-03/29 03/29-06/28 06/28-09/27 09/27-01/03 GAMMA SPECIRUM ANALYSIS: BE-7 9.2510.92 E-02 9.8610.99 E-02 9.6610.97 E-02 ~ 1.1713.12 E-01 K-40 LT. 1. E-02 LT.2. E-02 LT.2. E-02 LT. 1. E-02 MN-54 LT. 5. E-04 LT.5. E-04 LT.6. E-04 LT.6. E-04 CO-58 LT.5. E-04 LT.6. E-04 LT.6. E-04 LT.8. E-04 o FE-59 LT. 1. E-03 LT.2. E-03 LT. I. E-03 LT. 3. E-03 f CO-60 LT.6. E-04 LT.7. E-04 LT.7. E-04 L T. 5. E-04 m ZN-65 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 NB-95/ZR-95 LT.5. E-04 LT.6. E-04 LT. 6. E-04 LT. 1. E-03 RU- 103 LT.6. E-04 LT.7. E-04 LT.6. E-04 LT. 1. E-03 RU-106 LT.5. E-03 LT. 5. E-03 LT.5. E-03 LT. 5. E-03 1-131 LT.2. E-03 LT.3. E-03 LT. 1. E-03 LT. 1. E-01 CS-134 LT.4. E-04 LT.6. E-04 LT.7. E-04 LT.5. E-04 CS-137 LT.5. E-04 LT.6. E-04 LT. 6. E-04 LT. 5. E-04 LA-140/BA-140 LT.2. E-03 LT.2. E-03 LT. 1. E-03 LT.3. E-02 CE-141 LT.9. E-04 LT. 1. E-03 LT. 8. -E-04 LT.2. E-03 CE-144 LT.3. E-03 LT.3. E-03 LT. 3. E-03 LT.2. E-03 RA-226 LT.9. E-03 LT.9. E-03 LT. 9. E-03 LT.7. E-03 Til-228 LT.9. E-04 LT.8. E-04 LT. 8. E-04 LT.6. E-04 l l l l
WOtX CREEK NUCLEAR OPERA 11NG CORPORATION AIR PAR 11CULATE FIL1ERS EXPOSURE PATIIWAY - AIRBORNE ISOTOPIC ANALYSIS ON QUARIERLY COMPOSITE (pC1/Cu.M.) } STATION NUMBER 37 l DATE COLLEC'IED: 12/28-03/29 03/29-06/28 06/28-09/27 09/27-01/03 GAMMA SPEC'IRUM ANALYSIS: BE-7 8.0810.81 E-02 9.9310.99 E-02 9.4510.94 E-02 1.0510.11 E-01 l K-40 LT.2. E-02 7.0514.12 E-03 LT. 9. E-03 LT.2. E-02 l MN-54 LT. 5. E-04 LT.5. E-04 LT.4. E-04 LT. 6. E-04 ) CO-58 LT.6. E-04 LT. 5. E-04 LT.4. E-04 LT.9. E-04 i u FE-59 LT. 1. E-03 LT.9. E-04 LT. 9. E-04 LT.3. E-03 ! E) CO-60 LT. 6. E-04 LT.4. E-04 LT.5. E-04 LT. 5. E-04 h ZN-65 LT. 1. E-03 LT.9. E-04 LT. 9. E-04 LT. 1. E-03 E3 NB 95/ZR-95 LT.6. E-04 LT.5. E-04 LT. 5. E-04 LT. 1. E-03 RU-103 LT. 6. E-04 LT. 5. E-04 LT. 5. E-04 LT. 2. E-03 140-106 LT.5. E-03 LT. 3. E-03 LT.3. E-03 LT. 5. E-03 1-131 LT.2. E-03 LT.2. E-03 LT. 9. E-04 LT.2. E-01 CS-134 LT. 6. E-04 LT.4. E-04 LT.4. E-04 LT.6. E-04 CS-137 LT.6. E-04 LT. 5. E-04 LT.4. E-04 LT.5. E-04 LA-140/BA-140 LT. 1. E-03 LT. 1. E-03 LT. 6. E-04 LT.2. E-02 CE-141 LT.8. E-04 LT.8. E-04 LT.7. E-04 LT. 2. E-03 CE-144 LT.3. E-03 LT.3. E-03 LT.2. E-03 LT.3 T 03 RA-226 LT.8. E-03 LT.8. E-03 LT.8. E-03 LT.7. e-03 TH-228 LT.8. E-04 LT.7. E-04 LT. 7. E-04 LT.7 E-04
WOLF CREEK NUCEEAR OPERATUtG CORPORATION AIR PAR 11CULATE FILTERS EXPOSURE PATHWAY - AIRBORNE ISO 1DPIC ANALYSIS ON QUARTERLY COMPOS 11E (pC1/Cu.M.) STATION NUMBER 40 DATE COLLECTED: 12/28-03/29 03/29-06/28 06/28-09/27 09/27-01/03 GAMMA SPECTRUM ANALYSIS: l
.J BE-7 6.5010.65 E-02 8.6110.86 E-02 8.7610.88 E-02 1.2510.12 E-01 K-40 LT. 7. E-03 LT. 1. E-02 1.9610.46 E-02 LT. 8. E-03 MN-54 LT.3. E-04 LT.4. E-04 LT.4. E-04 LT.4. E-04 CO-58 LT.4. E-04 LT. 5. E-04 LT.4. E.04 LT.6. E-04 y FE-59 LT. 1. E-03 LT. 1. E-03 LT. 1. E-03 LT.2. E-03 'g CO-60 LT.4. E-04 LT.4. E-04 LT.4 E-04 LT.4. E-04 m ZN-65 LT.8. E-04 LT.9. E-04 LT. 1. E-03 LT. 1. E-03 LT.4. E-04 LT. 5. E.04 LT.4. E-04 LT.7. E-04 h NB-95/ZR-95 RU-103 LT.4. E-04 LT.5. E-04 LT.4. E-04 LT. 1. E-03 RU-106 LT.3. E-03 LT.4. E-03 LT.4. E-03 LT.3. E-03 1-131 LT. 1. E-03 LT.2. E-03 LT. 8. E-04 LT. 1. E-01 CS-134 LT.4. E-04 LT.5. E-04 LT.4. E-04 LT.4. E-04 CS-137 LT.3. E-04 LT.4. E-04 LT.4. E-04 LT. 5. E-04 LA-140/BA-140 LT. 1. E-03 LT. 1. E-03 LT.8. E-04 LT.2. E-02 CE-141 LT.6. E-04 LT.6. E-04 LT. 5. E-04 LT.2. E-03 CE-144 LT.2. E-03 LT.2. E-03 LT.2. E-03 LT. 3. E-03 RA-226 LT.7. E-03 LT. 6. E-03 LT.6. E-03 LT.8. E-03 TH-228 LT 6. E-04 LT.5. E-04 LT.6. E-04 LT.7. E-04 o - - - - - - .. __ _ - _ - _ _ _ _;
WDEX t'WN NUCIEAR OFMtATMG COItFOIIATWit EXPOSURE PATHWAY - INGES110N ANIMAIS/ GAME (pCl/KG WET) STA110N NUMBER SCTA DATE COLLECTED: 11/22 QUAIL GAMMA SPECIRUM ANALYSIS: BE-7 LT. 1. E 02 K-40 5.1110.51 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 FE-59 LT.3. E 01 LT. 1. E 01 [ CO.60 m ZN-65 LT.3. E 01
? NB-95/ZR-95 LT. 1. E 01 N RU-103 LT. 1. E 01 RU- 106 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.8. E 01 j RA-226 LT.2. E 02 -
l TH-228 LT.2. E 01 l \ l l- _ ___ . ~ . . . ~ . - _ _ _ - . _ . . . . . . _ . _ _ _ _ . . . ~ _ _ . _ . . _ . - . _ - - - . . . _ . . _ . . - . . - _ . . _ - . . - . ~ . _ - . _ -
. _ _ _ - _ . - - - - _ - . _ . _ . . ~ _ _ - - - _ _ - - - - . _ _ _ _ . -
WOEX CREEK NUCIEAR OPERATN40 CORFOttATION EXPOSURE PA~D1WAY - INGESTION - ANIMALS / GAME , (PCl/KG WE11 STATION NUMBER SCTG DATE COLLECTED: 11/22 12/31 cAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT. 1. E 02 K-40 5.5010.55 E 03 3.3610.34 E 03 MN-54 LT. 1. E 01 LT. 1. E 01 CO-58 LT. 1. E 01 LT. 1. E 01 FE-59 LT.3. E 01 LT.3. E 01 CO-60 LT. 1. E 01 LT. 1. E 01 2 ZN-65 LT.3. E 01 LT.3. E 01 N NB-95/ZR-95 LT. 1. E 01 LT. 1. E 01 i
- RU-103 LT. 1. E 01 LT. 1. E 01 E$ RU-106 LT.9. E 01 LT.9. E 01 1-131 LT. 2. E 01 LT.3. E 01 CS.134 LT. 1. E 01 LT. 1. E 01 CS-137 LT. 1. E 01 LT. 2. E 01 LA-140/BA-140 LT. 1. E 01 LT.2. E 01 CE-141 LT.2. E 01 LT.2. E 01 CE-144 LT.7. E 01 LT.8. E 01 RA-226 LT.2. E 02 LT.2. E 02 TH-228 LT.2. E 01 LT.2. E 01
+
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--, -. _ _ _ _ _j 1 WOtE CREEK NUCIEAR OPERN11NG CORPORATION EXPOSURE PA'llfWAY - AIRBORNE
'INERMOLUMINESCENT DOSIMETERS (net mR/ day)
STATION FIRST QUARTER NUMBER 01/04/94-04/09/94 STA-01 0.15510.004 . STA-02 0.14210.017 STA-03 0.14910.009 STA-04 0.15710.014 . STA-05 0.14610.014 STA-06 0.14710.010 STA-07 0.14410.005 STA-08 0.15910.010 y STA-09 0.14310.007
$ STA-10 0.16310.013 STA-11 0.17210.005 4 STA-12 0.15610.018
- STA-13 0.16110.016 STA- 14 0.15910.008 STA-15 O.14910.009 -
STA-16 0.14910.009 STA-17 0.15910.014 STA-18 0.16710.020 STA-19 0.16110.011 STA-20 0.15910.020 STA-21 0.14910.032 STA-22 0.17810.019 STA-23 0.15110.029 STA-24 0.15510.012 D =_-m_ _ _ _ _ _ - .s*_- _ m__ _. rw-- * -,-r- -.w-, v -- - ~e . ---w m e*-, , , , - - , , - +-=--<r--w-----wnw n~ - = , > --v- w - w. <e,-= v --~.v- w.- -e
WOLF CREEK NUCIE.AR OPERATING CORPORATION EXPOSURE PATHWAY - AIRBORNE THERMOLUMINESCEffr DOSIMETIERS (net mR/ day) t STATION FIRST QUARTER ! NUnmru 01/04/94-04/09/94 l '- STA-25 0.12710.002 STA-26 0.14410.012 STA 27 0.15410.000 STA-28 0.136i0.014 .
. STA-29 0.12810.008 STA-30 0.17410.013 STA-31 0.14610.007 u STA-32 0.148tO.005 E STA-33 0.15910.008 '
h STA-34 0.163i0.007 k STA-35 0.16310.010 STA-36 0.I5510.011 STA-37 0.15210.015 STA-38 0.17310.013
- STA-39 0.17010.009 STA-40 0.14810.014 STA-41 0.16810.009 STA-42 0.I1010.010 STA-43 0.108*0.007 I
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WOLF CREEK NUCIEAR OPERK11NG CORPORA 110N EXPOSURE PA1HWAY - AIRBORNE
'IMERMOLUMINESCENT DOSIMETERS (net mR/ day)
STATION FIRST QUARTER NUuMR 01/04/94-04/09/94 CTA-01 0.15810.013 STA-02 0.14610.005 STA-03 0.15210.008 STA-04 0.15210.018 STA-05 0.14310.004 CTA-06 0.15010.008 STA-07 0.13910.008 o STA-08 0.15610.007 0.14410.009 f STA-09 m CTA-10 0.15710.004 k* STA-II 0.16610.012 STA-12 0.15810.015 STA-13 0.14910.016 STA- 14 0.16610.007 STA- 15 0.16210.019 STA-16 0.15010.005 STA-17 0.15210.011 STA-18 0.16110.007 STA-19 0.16410.004-l STA-20 0.16110.000 STA-21 0.13910.000 STA-22 0.15610.002' STA-23 0.16410.012 STA-24 0.16210.013 i . _._._________._._m_____. . _ _ _ _ . . - .~ , . . _ . . . . _ . , _ _ . _ . . . - _ . - . - . - - , - - ..-_. --__.._. _ _ ,;.._,. , - . . . ~ . _ _ . , - . _ _ . _ _ __ , ._
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z WOEX CN NUCIZAR OPERATING CORPORATION EXPOSURE PA'IEWAY - INGESVON FEED & FORAGE (pCl/KG WEll STA' HON NUMBER NR-D1 DKIE COLLECIED: 09/27 CORN GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 K-40 2.8310.28 E 03 MN-54 LT.4. E 00 CO-58 LT.4. E 00 FE-59 LT.9. E 00 CO-60 LT. 5. E 00 2 ZN-65 LT. 1. E 01 55 NB-95/ZR-95 LT. 4. E 00 tjo RU-103 LT.4. E 00
$ RU-106 LT.4. E 01 1-131 LT.5. E 00 ,
CS-134 LT.4. E 00 CS-137 LT.4. E 00 LA-140/BA-140 LT.5. E 00 CE-141 LT.6. E 00 CE-144 LT.3. E 01 RA-226 LT.8. E 01 TH-228 LT.7. E 00 i l 4
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WOIX CREEE NUCIEAR OPERATEOG CORPORATION EXPOSURE PKIEWAY - INGESTION PEED & FORAGE (pCl/KG WE11 STATION NUMBER NR-D2 DATE COLLECIED: 10/17 10/17 CORN AIEALFA GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 8.0413.65 E 02 K-40 3.2410.32 E 03 1.6510.16 E 04 MN-54 LT.4. E 00 LT. 5. E 01 CO-58 LT.4. E 00 LT.5. E 01 FE-59 LT. 1. E 01 LT. 1. E 02 CO-60 LT.4. E 00 LT. 5. E 01 g ZN-65 LT. 1. E 01 LT. 1. E 02
- NB-95/ZR-95 LT.5. E 00 LT. 5. E 01
? RU-103 LT. 5. E 00 LT.6. E 01 3 RU-106 LT 4. E 01 LT.4. E 02 I-131 LT, 1. E 01 L T. 1. E 02 CS-134 LT.4. E 00 LT. 5. E 01 CS-137 LT.4. E 00 LT. 5. E 01 LA-140/BA-140 LT.7. E 00 LT. 3 E 01 CE-141 LT.7. E 00 LT. 1. E 02 CE-144 LT.3. E 01 LT.4. E 02 RA-226 LT.8. E 01 L T. 1. E 03 TH-228 LT.7. E 00 LT. 1. E 02 RADIOCHEMICAL ANALYSIS: ,
1-131 LT.6.E01 . . _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ . _ _ . _ _ . _ . _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ . _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ - . _ _ _ - _ _ _ - _ _ _ _ _ _ . .m. . . ,_. --.. . .~. ,,. . _ , ,._ .-m _ . . - ___.m . . _ . ,., ~, - _ .z.
WOLF CREEK NUCIEAR OPERATING COEtPOItATION EXPOSURE PKDIWAY - INGES110N FEED & PURAGE (pCl/KG WE11 STKI1ON NUMBER NR-U1 DATE COLLECTED: 10/17 10/17 10/17* SOYBEANS CORN SOYBEANS GAMMA SPECIRUM ANALYSIS: BE-7 LT. 5. E 01 LT.4. E 01 LT. 6. E 01 K-40 1.6410.16 E 04 2.5510.25 E 03 1.6310.16 E 04 MN-54 LT.6. E 00 LT.4. E 00 LT.6. E 00 CO-58 LT.6. E 00 LT. 5. E 00 LT.6. E 00 FE-59 LT. 2. E 01 LT. 1. E 01 LT.2. E 01 y CO-60 LT.7. _ E 00 LT.4. E 00 LT.7. E 00 ,% ZN-65 LT.2. E 01 LT. 1. E 01 LT.2. E 01
- E 00 NB-95/ZR-95 LT.6. LT.5. E 00 LT. 7. E 00 RU-103 LT.6. E 00 LT.5. E 00 LT. 7. E 00 N RU-106 LT.5. E 01 LT.4. E 01 LT. 5. E 01 1-131 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CS-134 LT.6. E 00 LT. 5. E 00 LT.7. E 00 CS-137 LT.6. E 00 LT. 5. E 00 LT.6. E 00 LA-140/BA-140 LT.7. E 00 LT.7. E 00 LT. 9. . E 00 CE-141 LT.9. E 00 LT.8. E 00 LT. 1. E 01 CE-144 LT.3. E 01 LT.3. E 01 LT.3. E 01 RA-226 LT.9. E 01 LT.9. E 01 LT. 1. E 02 TH-228 LT.9. E 00 LT.8. E 00 LT. 1. E 01
'Duplimte Analysis
WOW CREEE NUCLEAR OPERATMG CORPORATION EXPOSURE PATHWAY - INGEST 10N FISH (pCI/KG WET) STAT 10N NUMBER WCCL DATE COLLECIED: 04/22 04/22 04/22 10/11 10/11 W. CRAPPIE SM MO BUFFALO CARP BM BUFFAID WALLEYE GAMMA SPECFRUM ANALYSIS: BE-7 L T. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT 1. E 02 LT. 1. E 02 K-40 3.5310.35 E 03 3.3710.34 E 03 3.7910.38 E 03 2.3310.23 E 03 4.6810.47 E 03 MN-54 LT. 1. E 01 L T. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 CO-58 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 L T. 1. E 01 LT.2. E 01 m FE-59 LT.3. E 01 LT. 3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 h CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 m ZN.65 LT.3. E 01 LT. 2. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 d, NB-95/ZR-95 LT. 1. E 01 L T. 1. E 01 LT. 1. E 01 L T. 1. E 01 LT.2. E 01 RU- 103 LT. 1. E 01 LT. 1. E 01 LT. 2. E 01 LT.2. E 01 LT.2. E 01 RU- 106 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 1131 LT. 2. E 01 LT.2. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 CS-137 2.4211.04 E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LA-140/BA-140 LT. 2. E 01 LT. 2. E 01 LT.2. E 01 LT.2. E 01 LT. 2. E 01 CE-141 LT. 2. E 01 LT. 2. E 01 LT.2. E 01 LT.3. E 01 LT.3. E 01 CE-144 LT.7. E 01 LT.6. E 01 LT.9. E 01 LT. 1. E 02 LT. 1. E 02 - RA-226 LT. 2. E 02 LT.2. E 02 LT.3. E 02 LT.3. E 02 LT.3. E O2 TH.228 LT.2. E 01 LT. 2. E 01 LT.2. E 01 LT.3. E 01 LT.3. E 01 TRI'11UM ANALYSIS: H-3 5.5 1 0.3 E 03 7.1 i 0.4 E 03 _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ . _ _ - - - _ _ . ._ _ . - . - . . _ _.~. , . - _ _ _ , - . ._ _ . _ _ _ _ . . _ . ,__ _
wou cassa mucsaan orsmATueG CORPORATION EXPOSURE PA1HWAY - INGESTION FISH (pCl/KG WE11 STA110N NUMBER WCCL DATE COLLECIED: 10/11 10/11 10/11 10/11 10/11 SM MO BUFFAID WIPER WHITE BASS CHANNEL CAT - BM BUFFALO
- GAMMA SPECIRUM ANALYSIS:
BE-7 LT.9. E 01 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 - K-40 3.25i0.32 E 03 4.05t0.41 E 03 3.4910.35 E 03 3.0010.30 E 03 2.24ic.22 E 03 MN-54 LT. 1. E 01 LT. 1. E 01 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 LT. 1. E 01 LT. 1.' E 01
,o FE-59 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 g CO-60 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT. 2. E 01 m ZN-65 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT.3. E 01- LT. 3. E 01 E3 NB-95/ZR-95 LT. 1. E 01 LT. 1. E 01 LT. 2. E 01 LT. 1. E' 01 LT. 1. E 01 RU-103 LT. 1. E 01 LT. 1. E 01 LT. 2. E 01 LT. 1. E 01 LT 2. E 01 , RU-106 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 '
l I-131 LT.2. E 01 LT. 2. E 01 LT.2. E 01 LT. : 2. E 01 LT.2. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. - E 01 - LT. 1. E 01 CS-137 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LA-140/DA-140 LT. 1. E 01 L T. 1. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01 i CE-141 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT.2. ' E 01 LT.3. E 01 CE-144 LT.6. E 01 LT.9. E 01 LT.8. E 01 LT.7. E 01 LT. 1. E 02 I RA-226 LT.2. E 02 LT.3. E 02 LT.3. E 02 LT.2. E 02 LT.3. E 02 TH-228 LT. 2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 . LT. 3. E 01 1 i 'IRI11UM ANALYSIS: H-3 6.610.4 ' E 03 7.6 i 0.4 E 03 6.6 i 0.4 E 03 7.0 i 0.4 ' E 03 5.7 i 0.3 E 03
- l. 'Duplimte Analysis l
i i __ _ _ . . _ . _ _ _ _ _ _ . _ . _ _ . _ _ . . _ _ _ . _ _ _ . - . . _ . . . _ _ _ _ _ . . .. _. .. _ ._. _ .-..._., _ _ _ _ _ . m _ . __ _ ._ ._ _ _ _ ... _ _ _ ____
WOLF CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA~IHWAY - INGEST 10N FISH (pCl/KG WE'Il STA'110N NUMBER WCCL - OLTILET POOL DATE COLLECIED: 10/14 10/14 BM BUFFAID SM BUFFALO / RIVER CARPSUCKER GAMMA SPECIRUM ANALYSIS: T BE-7 LT.2. E 02 LT. 1. E 02 K-40 2.1910.22 E 03 3.6110.36 E 03 MN-54 LT.2. E 01 LT. 1. E 01 CO-58 LT.2. E 01 LT. 1. E 01 o FE-59 LT.4. E 01 LT.3. E 01 h CO-60 LT.2. E 01 LT. 1. E 01 m ZN-65 LT.4. E 01 LT. 3. E 01 E, NB-95/ZR-95 LT.2. E 01 LT. 1. E 01 RU-103 LT. 2. E 01 LT. 1. E 01 RU-106 LT.2. E 02 LT. 1. E 02 , I-131 LT.4. E 01 LT.2. E 01 CS-134 LT.2. E 01 LT. 1. E 01 CS-137 LT. 2. E 01 LT.2. E 01 LA-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.4. E 02 LT. 2. E 02 TH-228 LT.3. E 01 LT.2. E 01 TRFI1UM ANALYSIS: H-3 4.7 1 0.4 E 03 4.3 1 0.4 E 03
WotX cweer NUCIEAR OPERATEG CORPORA 110N EXPOSURE PATHWAY - INGESTION FISH (pC1/KG WET) STATION NUMBER JRR DATE COllECIED: 06/07 06/07 06/07 RGH FISH BM BUITALO GM FISH LG MO BASS GM FISH CHANNEL CAT GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT. 1. E 02 LT. 1. E 02 K-40 3.3310.33 E 03 3.5210.35 E 03 3.3510.33 E 03 MN-54 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CO-58 L T. 1. E O1 LT. 1. E O1 LT.2. E O1 FE-59 LT.2. E 01 LT.3. E 01 LT.3. E 01 y CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 % ZN-65 LT.2. E 01 LT.3. E 01 LT.3. E 01 to NB-95/ZR-95 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 RU-103 E 01 E 01 LT.2. E 01 h RU-106 LT. 1. LT. 1. E 02 LT. 1. LT. 1. E 02 ' LT. 1. E 02 1-131 LT.2. E 01 LT.3. E 01 LT.3. E 01 CS-134 L T. 1. E 01 LT. 1. E 01 LT.2. E 01 CS-137 LT. 1. E 01 LT. 1. E 01 LT.2. E 01-LA-140/BA-140 LT.2. E 01 LT. 2. E 01 LT.2. E 01 CE-141 LT. 1. E 01 LT.2. E 01 LT. 2. E 01 CE-144 LT.6. E 01 LT.6. E 01 LT. 8. E 01 RA-226 LT.2. E 02 LT.2. E 02 - LT.3. E 02 TH-228 LT.2. E 01 LT.2. E 01 LT.3. E 01
WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PKIEWAY - INGES110N FISH (pC1/KG WET) STATION NUMBER JRR DA1E COLLECIED: 10/26 10/26 - W CRAPPIE COMMN CARP GAMMA SPECTRUM ANALYSIS: BE-7 LT. 1. E 02 LT. 2. E 02 K-40 3.8510.38 E 03 4.1510.42 E 03 MN-54 LT.2. E 01 LT.2. E 01 CO-58 LT. 1. E 01 LT.2. E 01 FE-59 LT.3. E 01 LT.5. E 01 2 CO-60 - LT. 2. E 01 LT.2. E 01
$ ZN-65 LT. 3. . E 01 LT.4. E 01 y NB-95/ZR-95 LT. 1. E 01 LT.2. E 01 y RU- 103 LT.2. E 01 LT.2. E 01 RU- 106 LT. 1. E 02 LT.2. E 02 I-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.2. E 01 CE-141 LT.2. E 01 LT.3. E 01 CE-144 - LT.8. E 01 LT. 1. E 02 RA-226 LT.2. E 02 LT.4. E 02 TH-228 ' LT. 2. E 01 LT. 3. E 01 -
TR;T10M ANALYSIS: H-3 LT.3. E 02 LT.3. E 02
WOIX CREEK NUCIRAR OPERA 11NG CORPORATION EXPOSURE PATHWAY - INGES110N FOOD / GARDEN CROPS (PCI/KG WET) STA110N NUMBER G-1 DATE COLLECTED: 05/31 06/28 07/26 08/23 09/27 CABBAGE CABBAGE CABBAGE CABBAGE CABBAGE GAMMA SPECIRUM /EALYSIS: BE-7 LT. 1. E 02 1.4610.73 E 02 3.9710.74 E 02 4.1710.81 E 02 5.8910.79 E 02 K-40 5.0310.50 E 03 3.7010.37 E 03 2.6910.27 E 03 4.0310.40 E 03 2.4710.25 E 03 MN-54 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CO-58 LT. 1. E 01 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 ,o FE-59 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 $ CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 m ZN.65 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT.2. E 01 LT. 2. E 01 /a ND-95/ZR-95 LT. 1. E 01 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 RU.103 LT. 1. E 01 LT.9. E 00 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 RU-106 LT. 1. E 02 LT. 9. E 01 LT.9. E 01 LT. 1. E O2 LT. 9. E 01 1131 . LT. 2. E 01 LT. 1. E 01 LT.2. E 01 LT.2. 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. 1. E 01 CS-137 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 L T. 1. E 01 LA-140/BA-140 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 CE-141 LT.2. E 01 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 - CE-144 LT.9. E Os LT.5. E 01 LT.6. E 01 LT.6. E 01 LT.6. E 01 RA-226 LT.3. E 02 LT,2. E 02 LT.2 E 02 LT.2. E 02 LT.2. E 02 TH-228 LT.3. E 01 LT.2. E 01 LT.2. E 01 LT. 1. E 01 LT.2. E 01
WOtX CREEK NUCI2AR OPERATEUG CORPORATIOff EXPOSURE PKIEWAY - INGESTION FOOD / GARDEN CROPS (PCI/KG WET) STATION NUMBER G-l' DATE COLLEC'IED: 10/25 CABBAGE GAMMA SPECIRUM ANALYSIS: BE-7 2.2310.67 E 02 K-40 3.2210.32 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 g FE-59 LT.2. E 01
- CO-60 LT. 1. E 01 7 ZN-65 LT. 2. E 01
$ NB-95/ZR-95 LT. 1. E 01 RU-103 LT. 1. E 01 RU-106 LT. 9. E 01 I-131 LT. 1. E 01 CS-134 LT. 1. E 01 CS-137 LT. 1. E 01 IA-140/BA-140 LT. 1. E 01 CE-141 LT. 1. E 01 CE-144 LT.6. E 01 RA-226 LT.2. E 02 Til-228 LT.2. E 01 I
l t
~
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i%; 4 WOLF rums NUCLEAR OPERA 1NEG CORPORATION EXPOSURE PATHWAY - INGES'110N FOOD / GARDEN CROPS (PCI/KG WET) ,
- STA110N NUMBER S-4 DA'IE COLLECTED: 05/31 06/28 07/26 ~08/23 09/27 CABBAGE CABBAGE CABBAGE CABBAGE CABBAGE GAMMA SPECIRUM ANALYSIS:
BE-7 LT. 8. E 01 - 1.9710.53 E 02 6.38i1.12 E 02 5.65i1.15 E 02 7.8711.10 E 02 K-40 4.4010.44 E 03 4.33i0.43 E 03 3.1710.32 E 03 4.1010.41 E 03 2.2610.23 E 03 MN-54 LT.9. E 00 LT.8. E 00 LT. 1. E 01 LT. 2. E 01 LT. 1. E 01. CO-58 LT.9. E 00 LT. 7.' E 00 LT. 1. E 01 LT. 2. ~ E 01 LT. 1. E 01 y FE-59 LT.2. E 01 LT.2. E 01 LT.3. E 01 - LT.3. E 01 LT.3. E 01 g CO-60 LT. 1. E 01 LT. 1. E 01 LT. 1. E 01 ' LT. 1. E 01 LT. 1. E 01 c) ZN-65 LT. 2. E 01 LT. 2. E 01 LT. 3. E 01 LT.4. E 01 LT.3. E 01 E NB-95/ZR-95 LT. 1. E 01 LT. 8. E 00 LT.2. E 01 LT. 2. E 01 LT. 1. . E 01 RU-103 LT. 1. E 01 LT.8. E 00 LT. 2. ' E 01 LT. 2.' E 01 LT.1. E 01 RU- 106 LT.8. E 01 LT.7. E 01 LT. 1. E O2 LT. 1. E 02 - LT.~1. E 02 I-131 LT. 1. E 01 L T. 1. E 01 LT.3. E 01 LT. 3. E 01 LT.2. E 01 CS-134 LT. 1. E 01 LT.9. E 00 LT. 2. E 01 LT.2. E 01 LT.2. E 01 i CS-137 LT. 1. E 01 LT.8. E 00 LT.2. E 01 LT.2. E 01 LT. 2. E 01 - LA-140/BA-140 LT. 1. E 01 LT. 7. E 00 L T. 2.' E 01 LT.2. E 01 LT.2. E 01 CE-141 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 LT.2. E 01 LT.2. ..E 01 CE-144 LT.5. E 01 LT. 6. E 01 LT.9. E 01 LT. 1. E 02 LT.9. E 01 RA-226 LT.2. E 02 LT. 2. E 02 LT.3. E 02 LT.3. E 02 LT.3. E 02 TH-228 LT. 2. E 01 LT. 2. E 01 LT. 2. E 01 LT.2. E 01 LT.2. E 01 Y l l l l
, . TB ll WOIX CREEK NUCLEAR OPERATING CORPORATION ~ 4 EXPOSURE PAR 1WAY - INGES110N -
FOOD / GARDEN CROPS (PCI/KG WET) .; STA110N NUMBER S-4 DATE COLLECIED: 20/25 CABBAGE GAMMA SPECI' RUM ANALYSIS: BE-7 5.3010.89 3 02 K-40 2.4010.24 E 03 MN-54 LT. 1. E 01 CO-58 LT. 1. E 01 u FE-59 LT.3. E 01 CO-60 L T. 1. E 01
, ZN-65 LT.3. E 01 k" NB-95/ZR-95 LT. 1. E 01 RU-103 LT. 1. E 01 RU- 106 L T. 1. E 02 1-131 ,
LT.2. E 01 - CS-134 L T. 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
V WOLF CREEK NUCIEAR OPEItATING ColtPOltATION EXPOSURE PKIIIWAY - INGESTION FOOD / GARDEN CROPS (PCI/KG WET) STATION NUMBER R-1 DATE COLLECIED: 05/31 06/28 07/26 08/23 09/27 10/25 LETTUCE CABBAGE LETTUCE * *
- GAMMA SPECTRUM ANALYSIS:
BE-7 2.3210.76 E 02 3.2010.63 E 02 4.64i1.11 E 02 K.40 4.9510.50 E 03 4.0310.40 E 03 5.6710.57 E 03 MN.54 LT. 1. E G1 LT.9. E 00 LT.2. E 01 CO-58 LT.9. E 00 LT.8. E 00 LT. 2. E 01 FE-59 LT.2. E 01 LT.2. E 01 LT. 3. E 01 - u CO-60 LT. 1. E 01 LT. 1. E 01 LT. 2. E 01
'{ ZN-65 LT.2. E 01 LT.2. E 01 LT.3. E 01 m NB-95/ZR-95 LT. 1. E 01 LT.9. E 00 LT.2. E 01 k RU-103 LT. 1. E 01 LT.9. E 00 LT.2. E 01 RU-106 LT.9. E 01 LT.8. E 01 LT. 1. E 02 1-131 LT. 1. E 01 LT. 1. E 01 LT.3. E 01 CS-134 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 CS-137 LT. 1. S 01 1.7110.76 E 01 LT.2. E 01 LA-140/BA-140 LT. 1. E 01 LT. 1. E 01 LT.2. E 01 CE-141 LT.2. E 01 LT. 1. E 01 LT.2. E 01 CE-144 LT.8. E 01 LT.5. E 01 LT. 1. E 02 RA-226 LT.2. E 02 LT.2. E 02 LT.3. E 02 Til-228 LT.2. E 01 LT.2. E 01 LT. 3. E 01
- Sample unavailable.
e WOIX CEtEEK NUCLEAR OPERA'I1NG CORPORA'110N EXPOSURE PKIEWAY - INGESTION iIILK (PCI/ LITER) STA" HON NUMBER S-3 DATE COLLECIED: 01/11 02/08 03/08 04/12 04/12' RADIOCHEMICAL ANALYSIS: 1131 LT.2 E-01 LT.2 E-01 LT. 2. E-01 LT.2. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT. 3. E 01 LT.4. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 K-40 1.3610.14 E 03 1.4610.15 E 03 1.4710.15 E 03 1.3610.14 E 03 1.3310.13 E 03 J MN-54 LT. 3. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00
$ CO-58 LT.3. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 y FE-59 , LT. 7. E 00 LT. 1. E 01 LT. 1. E 01 LT.8. E 00 LT. 8. E 00 g CO-60 LT. 3. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 ZN.65 LT. 7. E 00 LT. 1. E 01 LT. 1. E 01 LT.9. E 00 LT. 8. E 00 NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT. 5. E 00 LT.4. E 00 LT.4. ' E 00 RU-103 . LT 4. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 -
RU- 106 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.4. E 01 LT. 3. E 01 1-131 LT.6. E 00 LT.8. E 00 LT.8. E 00 LT.5. E 00 LT.5. E 03 CS-134 LT.3. E 00 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.4. E 00 CS-137 LT.3. E 00 LT. 4- E 00 LT. 5. E 00 LT. 5. E 00 LT. 5. E 00 IA-140/BA-140 LT.4. E 00 LT.7. E 00 LT.6. E 00 LT.4. E 00 LT.3. E 00 CE- 141 LT. 5. E 00 LT.8. E 00 LT. 8. E 00 LT. 6. E 00 LT. 6. E 00 CE-144 LT.2. E 01 LT.3. E 01 LT. 3. E 01 LT. 2. E 01 LT.3. E 01 RA-226 LT.6. E 01 LT.9. E 01 LT. 8. E 01 - LT. 8. E 01 LT.8. E 01 ' TH-228 LT. 5. E 00 LT. 8. E 00 L T. 8.- E 00 LT.7. E 00 LT.7. E 00
- Duplicate Analysis
- _ _ - _ _ - ---__ _ __-___--_-_ ____ _-__--- _____-_ __-_--. __. .-_ _ _ _ . _ _ - _ . _ _ - - . - . ~ ~ - _ . - - . . . , . . - - , . . . - . _ - . - . - . _ _ -
- c WOur CREEK NUGEAR OPERATING CONFOgtATION .
EXPOSURE PATHWAY - INGESTION MILK (PCI/ LITER) STAllON NUMBER S-3 DATE COllECIED: 05/10 05/24 06/14 06/29 07/12 RADIOCHEMICAL ANALYSIS: I.131 LT.2 E-01 LT.2 E-01 LT.2. E-01 LT.2. E-01 LT. 1. E-01 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E 01 LT. 3. E O1 LT.3. E 01 LT.3. E O1 LT.3. E 01 K-40 1.3710.14 E 03 1.4610.15 E 03 1.4710.I5 E 03 1.3410.13 E 03 1.3910.14 E 03 o MN-54 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 ' f CO-58 LT.3. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT. 3. E 00 m FE-59 LT.9. E 00 LT.9. E 00 LT.7. E 00 LT.8. E 00 LT. 7. E 00 E CO-60 LT.4. E 00 LT.4. E 00 LT. 3. E 00 LT. 4. E 00 LT.3. E 00
- ZN.65 LT. 1. E 01 LT.9. E 00 LT.7. E 00 LT.9. E 00 LT.7. E 00 NB-95/ZR-95 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU-103 ,
LT. 4. E 00 LT. 4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 RU.106 LT.3. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 I-131 LT.6. E 00 LT. 5. E 00 LT.4. E 00 LT.7. E 00 LT.4. E 00 , CS-134 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT. 5. E 00 LT. 5. E 00 LT.3. E 00 LT.5. E 00 LT.4. E 00 CE-141 LT. 7. E 00 LT. 6. E 00 LT.5. E 00 LT.6. E 00 LT. 5. E 00 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.6. E 01 LT.7. E 01 LT. 7. E 01 TH-228 LT. 6. E 00 LT. 6. E 00 LT.5. E 00 LT. 7. E 00 LT. 6. E 00
WOEX CREEK NUCE2AR OPERATING CORPORATION EXPOSURE PATHWAY - INGES110N MILK (PCI/ LITER) STATION NUMBER S-3 DATE COLLECIED: 07/26 08/09 08/23 09/13 09/27 RADIOCIIEMICAL ANALYSIS: I-131 LT. 2. E-01 LT. 2. E-01 LT.2. E-01 LT. 1. E-01 LT. 1. E-01 GAMMA SPECIRUM ANALYSIS: BE-7 LT.4. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 LT. 3. E 01 K-40 1.3610.14 E 03 1.4910.15 E 03 1.4510.15 E 03 1.3010.13 E 03 1.4010.14 E 03 MN-54 LT. 5. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 g CO-58 LT.5. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00
- FE-59 LT. 1. E 01 LT.9. E 00 LT.9. E 00 LT.8. E 00 LT.8. 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.9. E 00 LT.9. E 00 LT.9. E 00 LT.9. E 00 -
NB-95/ZR-95 LT. 5. E 00 LT.4. E 00 LT.4. E 00 ' LT. 3. E 00 LT.4. E 00 RU-103 . LT. 5. E 00 LT.4. E 00 LT.4. E 00 LT.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 I-131 LT.8. E 00 LT.5. E 00 LT.7. E 00 LT.6. 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 f T. 6. E 00 LT.4. E 00 LT.6. E 00 LT.5. E 00 LT. 4. E 00 CE-141 LT. ti. E 00 LT.6. E 00 LT.8. E 00 LT.7. E 00 LT. 6. E 00 CE-144 LT.3. E Oi LT.2. E 01 LT. 3. E 01 LT.3. E 01 LT. 3. E 01 RA.226 LT.9. E 01 LT.7. E 01 LT.9. E 01 LT. 8. E 01 LT.8. E 01 TII-228 LT.8. E 00 LT.6. E 00 - L T. 7.. E 00 LT. 7. E 00 LT.7. E 00 .__.__m- _ --___m* - - - - - _ +-.-+ , , - - - - + <- a - - - - um v -- - -- -- w- - - - - . . y .%-- - ,- --p-i. ,
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WUEX CREEE NUCIEAR OPERATEIG COEFORATION EXPOSURE PATHWAY _- AQUATIC SEDIMEPrr/ SILT t QC1/KG DRY) . STATION NUMBER DC DATE COllECIED: 05/31 10/26 10/26* GAMMA SPECTRUM ANALYSIS: , CE-7 LT.3. E 02 LT.4. E 02 LT. 3. E 02 K-40 1.2910.13 E 04 1.1410.11 E 04 1.4010.14 E 04 MN-54 E 01 LT.4. LT.4. E 01 LT.4. E 01 CO-58 LT.4. E 01 LT.5. E 01 LT.4. E 01 : FE-59 LT.9. E 01 LT. 1. E 02 LT. 8. E 01 , CO-60 1.1010.11 E 03 8.9710.90 E 02 9.4210.94 E 02 i [ ZN-65 LT. 1. E O2 LT. 1. E 02 LT.8. E 01
- NB-95/ZR-95 LT.4. E 01 LT. 5. E 01 LT.4. E 01
?' RU-103 LT.4. E 01 LT. 5. E 01 LT.4. E 01 O RU-106 LT.3. E 02 LT. 3. E 02 LT.3. E 02 i 1-131 LT.6. E 01 LT. 1. E 02 LT 1. E 02 '
CS-134 2.1010.42 E 02 1.6810.41 E 02 1.8710.32 E 02 CS-137 7.23i0.72 E 02 5.4010.54 E 02 6.7810.68 E 02 LA-140/BA-140 ~ LT. 5. E 01 LT.7. E 01 LT. 6. E 01 - CE-141 LT. 5. E 01 LT. 8. E 01 LT. 6. E 01 l CE-144 LT.2. E 02 LT.3. E 02 LT.2. E 02 - RA-226 1.4710.51 E 03 2.6010.70 E 03 1.8710.56 E 03 TH.228 1.4610.15 E 03 1.1210.11 E 03 1.1710.12 E 03
'Dupilmte Analysis t
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m WOEX - NUCLEAR OPERATEUG CORPORA'I10N EXPOSURE PATHWAY- AQUA 11C SEDIMENT / SILT (pCi/KG DRY) STATION NUMBER WC & 1Ith ROAD DATE COLLECTED: 1I/30 GAMMA SPECTRUM ANALYSIS: BE.7 6.3212.46 E 02 K-40 8.9210.89 E 03 MN-54 LT.3. E 01 CO-58 LT.3. E 01 FE-59 LT.8. E 01 y CO-60 LT.4. E O1 g ZN-65 LT. 1. E 02
- E 01 NB-95/ZR-95 LT.4.
LT.4. E 01 [ RU-103 CD RU-106 LT.3. E 02 1-131 LT.9. E 01 CS-134 LT.4. E 01 CS-137 LT.4. E 01 LA-140/BA-140 LT.6. E 01 CE-141 LT. 6. E 01 CE-144 LT. 2. - E 02 RA-226 1.9810.56 E 03 TH-228 9.2810.93 E 02
. . _ . . - . . _ . . - . _ _ . _ _ _ . _ . . . . _ , . . _ _ . _ _ _ . _ - _ - - . - _ . _ . _ _ _ _ . _ . . - _ _ , _ - ~ - - - . , . . . . . - _ . . . ..
WOIX CREEK NUCIAAR OPERATING CORFORA110N EXPOSURE PATHWAY - AQUA 11C SEDIMENT SILT (pCl/KG DRY) STATION NUMBER BEMIS COVE SECTOR H DATE COLIECTED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 K-40 1.0910.I1 E 04 MN-54 LT.4. E 01 CO-58 L F. 4. E OI u FE-59 LT.9. E 01 8.7512.99 E O1 { CO-60 , ZN-65 LT. 1. E O2 L NB-95/ZR-95 LT.5. E 01 -
- RU-103 LT.4. E 01 RU- 106 LT.4. E 02 I-131 LT. 1. E 02 CS-134 LT.5. E 01 CS-137 3.7PJto.48 E 02 LA-140/BA-140 LT 6: E 01 CE-141 LT.8. E 01 CE-144 LT.3. E 02 RA-226 1.8210.66 E 03 TH-228 1.1110.11 E 03
WOIX CREBE NUC12 AR OPEstATMG COgtPORATION EXPOSU.2 FXnIWAY - AQUA'11C SEDIMEPrr SILT (pCl/KG DRY) STATION NUMBER UHS INTAKE AREA SEC*DR G DATE COLLECIED: 10/26 GAMMA SPECIRUM ANALYSIS: CE-7 LT.4. E 02 K-40 1.2010.12 E 04 MN-54 LT.4. E 01 CO-58 LT.4. E 01 FE-59 LT.9. E 01 , g CO-60 1.2710.37 E 02 ,
- ZN-65 LT. 1. E 02 NS-95/ZR-95 LT.6. E 01 E RU-103 LT.5. E 01 RU-106 LT.3. E 02 1-131 LT. 1. E 02 CS-134 LT.4. E 01 CS-137 2.6010.42 E O2 LA-140/BA-140 LT.7. E 01 CE-141 LT. 7. E 01 CE-144 LT.3. E 02 RA-226 1.8810.62 E 03 TH-228 1.1110.11 E 03 t
WOEX N NUCIEAR OPEIRATING CONFOItATION EXPOSURE PATHWAY - AQUATIC SEDIMENT SILT (pCl/KG DRY) STATION NUMBER SADDLE DAM 4 SECTOR K DATE COLLECTED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 K-40 7.1810.72 E 03 , MN-54 LT.4. E 01 CO-58 LT.3. E 01 . FE-59 LT.7. E 01 2 CO-60 LT.4. E 01
% ZN-65 LT.7. E 01 y NB-95/ZR-95 LT.4. E 01 9 RU-103 LT.4. E 01 RU- 106 LT.3. E 02
. 1-131 LT.9. E 01 , CS-134 LT.4. E 01 CS-137 7.7713.39 E 01 EA.140/BA-140 LT.8. E 01 CE-141 LT.6. E 01 CE-144 LT.2. E 02 RA-226 1.3510.55 E 03 TH-228 8.6310.86 E 02
WOLF CREEE NUCEEAR OPERATEUG CORPORATICII EXPOSURE PAINWAY - AQUATIC SEDIMENT SILT (pCI/KG DRY) STA110N NUMBER S. REINKER ROAD SECTOR L DATE COMECTED: 10/26 GAMMA SPECIRUM ANALYSIS: BE-7 LT.2. E 02 K-40 4.8210.48 E 03 MN-54 LT.2. E 01 CO-58 LT.3. E 01 o FE-59 LT.6. E 01 y CO-60 7.3812.49 E 01
, ZN-65 LT.6. E 01 & NB-95/ZR-95 LT.3. E 01 N
RU-103 LT.3. E 01 RU-106 LT.2. E 02 I-131 LT.7. E 01 ,
^
CS-134 LT.3. E 01 CS-137 1.3010.29 E 02 LA-140/BA-140 L?. 5. E 01 CE-141 LT.4. E 01 CE-144 LT. 1. E 02 RA-226 1.4510.39 E 03 l TH-228 7.0710.71 E 02 i l l l i. i
WOEF CREEK NUCIEAR OPERATDOG CORPORATION EXPOSURE PA111WAY- AQUA 11C SEDIMENT SILT (pC1/KG DRY) STA110N NUMBER MUDS DATE COLLECIED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 K-40 1.0410.10 E 04 MN-54 LT.4. E 01 CO-58 LT.4. E 01 FE-59 LT.8. E 01 CO-60 1.2910.35 E 02 2 ZN-65 LT. 9. E 01 $ NB-95/ZR-95 LT.5. E 01 cn RU-103 LT.4. E 01 g RU-106 LT.3. E 02 1-131 LT. 1. E 02 CS-134 LT.4. E 01 CS-137 1.3210.37 E 02 LA-140/BA-140 LT.8. E 01 CE-141 LT.7. E 01 CE-144 LT.3. E 02 RA-226 2.5210.57 E 03 TH-228 1.0510.11 E 03
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WOLF CHERE 140CIEAR OPEIRATEUG CORFOEtATION EXPOSURE PATHWAY - AQUA 11C , SEDIMENT SILT (pCl/KG DRY) STKIlON NUMBER N. HOUSERS SECTOR R DATE COUECTED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 K-40 1.1210.1I E 04 MN-54 LT.3. E 01 CO-58 LT.3. E 01 u FE-59 LT.7. E 01 S CO-60 2.0310.30 E 02 h ZN-65 LT.7. E 01
& NB-95/ZR-95 LT.4. E 01
- RU-103 LT.4. E 01 RU- 106 LT.2. E 02 I-131 LT.8. E 01 CS-134 LT.4. ~ E 01 CS-137 2.7010.35 E 02 IA-140/BA-140 LT. 5. E 01 CE-141 LT. 6. E 01 l CE-144 LT.2. E 02 RA-226 2.2610.52 E 03 TH-228 1.1810.12 E 03 i
I _ - . _ . - - - - _ _ _ _ . - - - . - - _ . _ - .~ - - . . . . . - . - - . - . . . ~,- ~ . , . .-,.. .. - -- - . - ..- .-~ _ , . , - - - _ - _ . . . _ , _ - . _ . - _ _ - - - _ _ - - _ _
W WDEX - NUCLEAR OPEEATHUG COUtPOItAT10N EXPOSURE PA'IlfWAY - AQUA'I1C - SEDIMENT SILT (pC1/KG DRY) STA*I1ON NUMBER JRR DATE COLLECIED.- 05/31 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 LT.3. E 02 K.40 1.7010.17 E 04 1.64i0.16 E 04 MN-54 LT.5. E 01 LT.3. E 01 CO-58 LT.4. E 01 LT.3. E 01 FE-59 LT. 1. E 02 LT.7. E 01 CO-60 LT.4. E 01 . LT. 3. E 01 [ ZN-65 LT. 1. E 02 LT.6. E 01 S NB-95/ZR-95 LT.6. E 01 LT.4. E 01 7 RU-103 LT.5. E 01 LT. 3. E 01 l $ RU-106 . LT.4. E 02 LT.3. E 02 I-131 LT.8. E 01 LT. 8. E 01 CS-134 LT.6. E 01 LT.4. E 01 CS-137 3.0110.50 E 02 l 2.4110.34 E 02 LA-140/BA-140 LT.7. E 01 LT.5. E 01 CE-141 LT.7. E 01 LT.6. E 01 CE-144 LT.3. E 02 LT.2. E 02 RA-226 2.1610.69 E 03 2.2310.52 E 03 TH-228 1.4910.15 E 03 1.2910.13 E 03
WOtX reser NUCIEAR OPERATING CORPORATION EXPOSURE PA11tWAY- AQUATIC SHORELINE SOIL (pC1/KG DRY) STA110N NUMBER EEA DA~IE COLLECIED: 10/14 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 K-40 1.2110.12 E 04 MN-54 LT.4. E 01 CO-58 LT.4. E 01 FE-59 LT.9. E 01 CO-60 LT.3. E 01 o', ZN-65 LT.9. E 01 E NB-95/ZR-95 LT.4. E 01 (" RU-103 LT.4. E 01
$ RU-106 LT.3. E 02 I-131 LT.9. E 01 CS-134 LT.5. E 01 CS-137 9.2712.93 E 01 LA-140/BA-140 LT.6. E 01 CE-141 LT.6. E 01 CE-144 LT.2. E 02 RA-226 2.0510.54 E 03 TH-228 1.2410.12 E 03
.. _ _ _ _ . _ . . _ _ _ _ . _ _ . . ~ . - . . _ . . . - . - . . . _ . . . __ _- _ _ _ . . - . . . . _ . _ . _ _ _ - - . . . . . . , _ _ . _ _ . - . . . __ __
WOIX CREEE NUCI. EAR OPERATING CORPORA 110N EXPOSURE PA111WAY- AQUATIC SHORELINE SOIL (pCI/KG DRY) STATION NUMBER DC DATE COLLECTED: 05/31 10/26 GAMMA SPECIRUM ANALYSIS: BE-7 LT.4. E 02 LT.3. E 02 K-40 1.1110.I1 E 04 8.4010.84 E 03 MN-54 LT.4. E 01 LT.4. E 01 CO-58 LT.4. E 01 4.0712.25 E 01 FE-59 LT. 1. E 02 LT.7. E 01 CO-60 7.0712.78 E 01 2.0910.33 E 02 [ZN-65 LT.9. E 01 LT. 7. E 01
- NB 95/ZR-95 LT. 5. E 01 LT.4. E 01 1 T' RU-103 LT.4. E 01 LT.3. E 01
$ RU-106 . LT.3. E 02 LT.3. E 02 I-13i LT.7. E 01 LT.8. E 01 CS- 134 8.8913.26 E 01 LT. 4. E 01 CS-137 1.2210.37 E 02 4.4412.56 E O1 LA-140/BA-140 LT.7. E 01 LT.7. E 01 CE-141 LT.7. E 01 LT. 5. E 01 CE-144 LT.3. E 02 LT. 2. E 02 RA-226 2.4310.68 E 03 1.1310.48 E 03 Til-228 1.4310.14 E 03 7.0810.71 E 02
WOEX N NUCI2AR OPERATING COItPOItATION EXPOSURE PA'HIWAY - AQUATIC SHORELINE SOIL (pCI/KG DRY) STATION NUMBER JRR DATE COLLECIED: 05/31 10/26 10/26' GAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 02 LT.3. E 02 LT.3. E 02 K-40 9.1810.92 E 03 6.5510.66 E 03 7.0510.70 E 03 MN-54 LT.3. E 01 LT. 3. E 01 LT.3. E 01 CO-58 LT.2. E 01 LT. 3. E 01 LT.3. E 01 FE-59 LT.6. E 01 LT. 7. E 01 LT.8. E 01 CO-60 LT.2. E 01 LT. 3. E 01 LT. 3. E 01 c", ZN-65 LT.6. E 01 LT.9. E 01 LT.9. E 01
$ NB 95/ZR-95 LT.3. E 01 LT.4. E 01 LT. 5. E 01 1:n RU-103 LT.3. E 01 LT.4. E 01 LT.4. E 01 $ RU-106 LT.2. E 02 LT.3. E 02 LT.3. E 02 I-131 LT. 5. E 01 LT. 1. E 02 LT. 1. E 02 CS-134 LT.3. E 01 LT.4. E 01 LT.4. E 01 CS-137 LT.3. E 01 LT.4. E 01 LT.4. E 01 LA-140/BA- 140 LT.4. E 01 LT. 6. E 01 LT.7. E 01 CE-141 LT.5. E 01 LT. 6. E 01 LT. 7. E 01 CE-144 LT.2. E 02 LT.2. E 02 LT. 2. E 02 RA-226 2.5510.48 E 03 1.5110.57 E 03 1.3010.57 E 03 Til-228 1.1910.12 E 03 8.7710.88 E 02 9.1710.92 E 02
- Duplicate Analysis l
WOfX CitEEE NUCI2AR OPEIRATING COptPORA110N EXPOSURE PA11tWAY- AQUA 11C SHORELINE SOIL (pCl/KG DRY) STA110N NUMBER UHS INTAKE AREA SECTOR G DATE COLLECIED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 K-40 8.5310.85 E 03 MN.54 LT.3. E 01 CO-58 LT.3. E 01 y FE-59 LT.7. E 01 y CO-60 LT.3. E 01 en ZN-65 LT.9. E 01 E NB-95/ZR-95 LT.4. E 01 RU.103 LT.4. E 01 RU 106 LT.3. E 02 1-131 LT.9. E 01 CS-134 LT.4. E 01 CS-137 LT.4. E 01 1A-140/BA-140 LT.6. E 01 CE-141 LT.7. E 01 CE-144 LT. 3. E 02 RA 226 1.8210.55 E 03 TH-228 1.1710.12 E 03
WOLF CREEK NUCIEAR OPEIRATING CORPORA 110N EXPOSURE PKIHWAY - AQUA'I1C SHORELINE SOIL (pCl/KG DRY) STATION NUMBER BEMIS COVE SECTOR H DA'IE COLLECIED: 10/26 GAMMA SPECTRUM ANALYSIS: CE-7 LT. 5. E 02 K-40 1.2010.12 E 04 MN-54 LT.5. E 01 CO-58 L T. 5. E 01 ' y FE-59 LT. 1. E 02 y CO-60 LT.5. E 01 cu ZN-65 LT. 1. E 02 LT.8. E 01 h NB-95/ZR-95 RU-103 LT. 6. E 01 RU-106 LT.4. E 02 I-131 ^ LT. 1. E 02 CS-134 LT.6. E 01 .. CS-137 LT.6. E O1 IA-140/BA-140 LT. 1. E 02 CE- 141 LT. 1. E 02 CE-144 LT.3. E 02 RA-226 9.2810.95 E 03 TH-228 1.4610.15 E 03 _ _ _ _ _ _ _ . . . - . _ _ _ . - . . - - - . . . . . - - _ _ . _ - . ~ . - -.. - - . . - - -. . . . . . . - . . . . ... .. -. , . - -
WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PKINWAY - AQUATIC SHORELINE SOIL (pCI/KG DRY) STATION NUMBER SADDLE DAM 4 SECIOR K DATE COLLECIED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 K-40 7.8610.79 E 03 MN 54 LT.3. E 01 CO-58 LT.3. E 01 g FE-59 LT. 6. E 01
- CO-60 LT.3. E 01
? ZN-65 LT.7. E 01 S NB 95/ZR-95 LT.3. E 01 RU-103 LT.3. E 01 RU-lO6 LT.3. E 02 1-131 LT.8. E 01 CS-134 LT.3. E 01 CS-137 LT.3. E 01 LA-140/BA-140 LT.6. E 01 CE-141 LT. 5. E 01 CE-144 LT.2. E 02 RA-226 1.8110.47 E 03 TH-228 1.1510.12 E 03
WOIX CREEK NUCIEAR OPERATING CORPOptATION EXPOSURE PATHWAY - AQUA *HC SHORELINE SOIL (pCl/KG DRY) STATION NUMBER S. REINKER ROAD SECTOR L DATE COLLECIED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 02 K-40 7.8210.78 E 03 MN-54 LT.3. E 01 CO-58 LT.3. E 01 g FE-59 LT.6. E 01 S CO-60 LT. 3. E 01 ? ZN.65 LT. 6. E 01 O 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 LT.3. E 01 IA-140/BA-140 LT.5. E 01 CE-141 LT.5. E 01 CE-144 LT.2. E 02 RA-226 1.5710.46 E 03 TH-228 9.7410.97 E 02
. - . . _ _ . .. ._ _ _ . . _ - - _ _ _ . _ _ - - ._ __ . _ . . . . _ _ _ ~ . _ - _ _ . . - - _ . . _ _ _ _ _, - . _ - , .
WOEX Cmen NUCl2AR OPERATRIG CDEtFORATION EXPOSURE PATHWAY- AQUATIC SHORELINE SOIL (pCi/KG DRY) STA110N NUMBER MUDS DATE COLLECTED: 10/26 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E O2 K-40 1.2210.12 E 04 MN-54 LT.4. E 01 CO-58 LT.3. E 01 FE-59 LT.9. E 01 g CO-60 LT.4. E 01 g ZN-65 LT.9. E 01 m NB-95/ZR-95 LT. 5. E 01 M RU-103 LT.4. E 01 RU 106 LT.3. E 02 I-131 LT. 1. E 02 CS-134 LT.5. E 01 CS-137 LT.4. E 01 LA-140/BA-140 LT.7. E 01 CE-141 LT.6. E 01 CE-144 LT.2. E 02 RA-226 2.4710.52 E 03 TH-228 1.4310.14 E 03
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WOEX CREEE NUCIEAR OPERATING CORPORA 110N EXPOSURE PATHWAY- AQUATIC SHORELINE SOIL (pCl/KG DRY) STATION NUMBER N. HOUSERS SECTOR R DATE COLLECTED: 10/26 GAMMA SPECTRUM ANALYSIS: EE-7 LT.3. E 02 K-40 1.1310.11 E 04 MN-54 LT.3. E 01 CO-58 LT.3. E 01 LT.7. E 01 [ FE-59
- CO-60 LT.4. E 01
? ZN-65 LT.7. E 01
$ NB-95/ZR-95 LT.4. E 01 RU-103 LT.4. E 01 RU- 106 LT.3. E 02 1-131 ,
LT. 1. E 02 CS- 134 LT.4. E 01 CS-137 4.9912.50 E 01 1A-140/BA-140 LT.7. E 01 CE-141 LT.6. E 01 CE-144 LT.2. E 02 RA-226 2.6410.47 E 03 TH-228 1.4110.14 E 03
WOEF - NUCIEAR OPERATHUG COEtPOIRA110N EXPOSURE PA"IHWAY 'IERRESTRIAL SOIL (pCl/KG DRY) STA110N NUMBER A-1 DATE COLLECIED: 06/21 GAMMA SPECI' RUM ANALYSIS: BE-7 2.65i0.37 E 03 K-40 6.9510.69 E 03 MN-54 LT.3. E 01 CO-58 LT.3. E 01 FE-59 LT.8. E 01 o CO-60 - LT.4. E 01 LT. 8. E 01 { ZN-65 , NB-95/ZR-95 LT.4. E 01 & RU-103 LT.4. E 01
- RU-106 LT.3. E 02 I-131 LT.6. E 01 CS-134 LT.4. E 01 CS-137 2.9310.45 E 02 IA-140/BA-140 LT.5. E 01 CE-141 LT.7. E 01 CE-144 LT.3. E 02 RA-226 1.1710.59 E 03 TH-228 7.1810.72 E 02
WOLF CBEM NUCI2AR OPERATING CORPOItATION EXPOSURE PA111WAY - TERRESTRIAL SOIL (pC1/KG DRY) STA'I1ON NUMBER EEA DATE COLLECIED: 10/14 4 GAMMA SPECTRUM ANALYSIS: BE-7 2.3510.44 E 03 K-40 1.2110.12 E 04 MN-54 LT. 5. E 01 CO-58 LT.3. E 01 y FE-59 LT. 1. E 02 $ CO-60 LT.4. E O1 LT.9. E 01 [ ZN-65 4 NB-95/ZR-95 LT.6. E 01
- RU-103 LT. 5. E 01 RU-106 LT.4. E 02 I 131 LT. 1. E O2 CS-134 LT.6. E 01 2.1410.52 E 02 CS-137 IA-140/BA-140 LT.9. E 01 CE-141 LT. 1. E 02 CE-144 LT.4. E 02 RA-226 1.5610.91 E 03 TH-228 1.0810.11 E 03
s
.s WDEX CREEE N*JCI2AR OPEIRATING CORPORA 110N EXPOSURE PATHWAY 'IERRESTRIAL SOIL (pCI/KG DRY)
STATION NUMBER MUDS DATE COLLECTED: 11/01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 02 K-40 1.2410.12 E 04 MN-54 LT.4. E 01 CO-58 LT.4. E 01 y FE-59 LT.9. E 01 E CO-60 LT.4. E 01 [ ZN-65 LT. 1. E 02 & NB-95/ZR-95 LT. 5. E 01 " RU-103 LT.4. E 01 RU- 106 LT.3. E 02 I-131 LT. 1. E 02 ' CS-134 LT.5. E O1 CS-137 9.8713.62 E 01 LA-140/BA-140 LT. 8. E 01 CE-141 LT.7. E 01 CE-144 LT. 2. E 02 RA-226 2.6310.69 E 03 TH-228 1.2210.12 E 03
%5-WOLF CREEK NUCIEAR OPERATING CORPORAT1ON EXPOSURE PA'IHWAY - AQUA'I1C VEGETA'I1ON - AQUA 11C (pCI/KG WET)
STA110N NUMBER DC DATE COLLECTED: 04/22 04/22 AIDAE ALGAE GAMMA SPECTRUM ANALYSIS:
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CE-7 7.2110.72 E 02 7.1910.72 E 02 K-40 1.6810.17 E 03 1.7310.17 E 03 MN-54 7.5013.49 E 00 LT.5. E 00 CO-58 1.0510.40 E 01 9.0613.64 E 00 a". FE-59 LT. 1. E 01 LT. 1. E 01 N CO-60 9.9911.00 E O1 9.5310.95 E O1
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LT.6. E 00 LT. 5. E 00 RU- 106 LT. 5. E 01 LT.4. E 01 1-131 LT. 1. E 01 LT. 1. E 01 CS-134 2.0710.48 E 01 LT.5. E 00 CS-137 4.9810.58 E 01 4.6410.46 E 01 LA-140/BA-140 LT.9. E 00 LT.8. E 00 CE-141 LT. 1. E 01 LT.9. E 00 CE-144 LT.3. E 01 LT. 3. E 01 RA-226 4.1710.85 E 02 4.1110.71 E 02 Til-228 2.2110.22 E 02 1.8510.18 E 02
( WOIX CREEE NUCI2AR OPERATING CORPORATION
- EXPOSURE PATHWAY- AQUA 11C t
VEGETA110N - AQUKI1C (pCl/KG WET) STATION NUMBER DC ALT DATE COLLECTED: 05/31 07/19 LOTUS AMERICAN LOTUS GAMMA SPECTRUM ANALYSIS: BE-7 2.55tl.16 E 02 7.55tl.34 E 02 K-40 3.0010.30 E 03 4.1710.42 E 03 MN 54 LT. 2. E 01 LT. 2. E 01 CO-58 LT. 2. E 01 LT. 2. E 01 LT.4. E 01 E 01 [ FE-59 LT. 3. , o CO-60 LT.2. E 01 LT.2. E 01
? ZN-65 LT.4. E 01 LT.4. E 01
$ 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 1-131 LT. 3. 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. 2. E 01 CE.141 LT.2. E 01 LT. 2. E 01 CE-144 LT. 1. E O2 LT.9. E 01 RA-226 LT. 3. E 02 LT. 3. E 02 TH-228 LT.3. E 01 LT. 3. E 01 l
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1-. , : WOLF CEtEEE NUCIEAR OPERATING CORPORATION EXPOSURE PA*11tWAY - AQUA 11C VEGETATION - AQUA 11C (pCl/KG WET) STA110N NUMDER WCCL - OITILET POOL DATE COLLECTED: 10/14 AIEAE GAMMA SPECTRUM ANALYSIS: EE-7 8.5910.86 E 02 K-40 3.0810.31 E 03 MN 54 LT.6. E 00 CO-58 LT. 6. E 00 g' FE-59 LT. 1. E 01 (D CO-60 LT. 8. E 00 m ZN-65 LT.2. E 01 5 NB-95/ZR 95 LT.7. E 00 RU- 103 , LT.7. E 00 RU- 106 LT.6. E 01 I.131 LT. 1. E 01 CS-134 LT.7. E 00 CS-137 LT.7. E 00 LA.140/BA-140 LT.9. E 00 CE-141 LT. 1. E 01 CE-144 LT.4. E 01 RA-226 LT. 1. E 02 TH-228 5.9110.64 E 01 _ _ - - _ _ -._ - . _ - - .__ _._ _, _ _ _ _,_ _- . . _ _ _ . _ _ - . _ . ~ . . . _ _ _ _ - _ - . . . . _ . _ _ - _ - - , _ _
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. WOEX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA'lHWAY - AQUATIC VEGETATION - AQUATIC (pCl/KG WET) STATION NUMBER EEA DATE COLLECIED: 10/14 POND WEED r GAMMA SPECTRUM ANALYSIS: BE-7 2.9410.66 E 02 K-40 1.5610.16 E 03 MN-54 LT.8. E 00 CO-58 LT. 8. E 00 g FE-59 LT.2. E 01
- CO-60 LT.9. E 00
? ZN-65 LT.2. E 01 U NB-95/ZR-95 LT.9. E 00 RU-103 LT. 1. E 01 RU-106 LT.8. E 01 l'131 LT.2. E 01 CS-134 LT. 1. E 01 CS-137 LT. 1. E 01 IA-140/BA-140 LT. 1. E 01 .
CE-141 LT. 1. E 01 CE-144 LT.6. E 01 RA-226 LT.2. E 02 TH-228 LT.2. E 01 __.-.___.._..-__m____.___.___--m- - _ _ _ _ _ _ _ --_,..,u__ _m m _m-_,_m e-- mm+_______ _ e w- s- -m-- .e,. _q__.,,s - c..,,w-, ..v.r.y.,,5 . 4 ,g -y .- e ay ,,ymn,o-_ , , ,, , ,%,,,,,, . - D~'t2 a =PFw*
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WOLF N NUCI2AR OPERATING COItPORATION EXPOSURE PADiWAY AQUATIC VEGETATION - TERRESTRIAL (pCl/KG WET) STKHON NUMBER EEA DA~IE COLLECTED: 10/14 VEGETATION / TERR GAMMA SPECTRUM ANALYSIS: BE-7 8.4710.85 E 03 K-40 5.6810.57 E 03 MN-54 LT. 3. E 01 y CO-58 LT.3. E 01 E FE-59 LT. 7. E 01 CO-60 LT.4. E 01 4 ZN-65 LT.8. E 01 N NB-95/ZR-95 LT.4. E 01 RU-103 LT.4. E 01 RU-106 LT. 3. E 02 1-131 LT.6. E 01 CS-134 LT.4. E 01 CS-137 LT.4. E 01 LA-140/BA-140 LT.5. E 01 CE-141 LT. 6. E 01 CE-144 LT.2. E 02 RA-226 LT.7. E 02 TH-228 LT.7. E 01
WOIX CREEE NUCI2AR OPERATING COItPORA110N EXPOSURE PATHWAY - AQUA'I1C VEGETATION 'IERRESTRIAL (pCl/KG WET) STATION NUMBER MUDS DA1E COLLECIED: 11/01 TERRESTRIAL GAMMA SPECTRUM ANALYSIS: BE-7 6.6910.67 E 03 K-40 2.5510.28 E 03 MN-54 LT.3. E 01 - CO-58 LT.2. E 01 2 FE-59 LT.5. E 01 % CO-60 LT.3. E 01 cn ZN-65 LT.6. E 01 h NB-95/ZR-95 LT.3. E 01 RU- 103 , LT. 3. E 01 RU-106 LT.2. 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.3. E 01 CE-141 LT.4. E 01 CE-144 LT. 1. E 02 RA-226 LT. 5. E 02 TH-228 LT.4. E 01
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WOIX CREEE NUCLEAR OPERA 11NG CORPORATION EXPOSURE PATHWAY - WATERBORNE DRINKING WATER (PC1/ LITER) STA110N NUMBER LW40 DATE COLLECTED: 09/06-10/04 10/04-11/02 11/02-12/06 12/06-01/03 RADIOCilEMICAL ANALYSIS: GR-B 6.5 i 1.4 E 00 6.4 i 1.9 E 00 7.1 i 1.4 E 00 4.5 i 1.4 E 00 1-131 LT. 5. E-01 LT. 5. E-01 LT. 6. E-01 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.9. E 01 LT.3. E 01 LT.3. E 01 o K-40 LT. 5. E 01 LT.2. E 02 LT. 1. E 02 LT.6. E 01 y MN-54 LT.3. E 00 LT.9. E 00 LT.3. E 00 LT.4. E 00 m CO-58 LT.3. E 00 LT.9. E 00 LT.4. E 00 LT.3. E 00 L FE.59 LT. 6. E 00 LT.2. E 01 LT. 7. E 00 LT. 7. E 00 CO-60 LT.3. E 00 LT.9. E 00 LT.4. E 00 LT.4. E 00 ZN.65 LT.5. E 00 LT.2. E 01 LT.8. E 00 LT. 8. E 00 NB-95/ZR-95 LT. 3. E 00 LT.9. E 00 LT.3. E 00 LT.4. E 00 RU.103 LT.3. E 00 LT. 1. E 01 LT.4. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT. 8. E 01 LT.3. E 01 LT.4. E 01 1-131 LT.6. E 00 LT.2. E 01 LT. 6. E 00 LT.5. E 00 CS-134 LT.3. E 00 LT. 1. E 01 LT.4. E 00 LT.4. E 00 CS-137 LT.4. E 00 LT. 1. E 01 LT.4. E 00 LT.4. E 00 LA-140/BA-140 LT. 5. E 00 LT. 1. E 01 LT.5. E 00 LT.4. E 00 - CE-141 LT.6. E 00 LT. 2. E 01 LT. 5. E 00 LT.6. E 00 CE-144 LT.2. E 01 LT.7. E 01 LT.2. E 01 LT.3. E 01 RA-226 LT.7. E 01 LT.2. E 02 LT.7. E 01 LT.8. E 01 TH-228 LT.6. E 00 LT.2. E 01 LT.6. E 00 LT. 7. E 00 TRITIUM ANALYSIS: 07/06-10/04 10/04-01/03 H-3 LT. 5. E 02 LT.2. E 02
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wou CREEE NUCutAR OPERAMNG CORPORAMON EXPOSURE PA'lHWAY - WKIERBORNE DRINKING WATER (PCI/ LITER) STKITON NUMBER BW15 DATE COLLECTED: 11/02-12/06 12/06-01/03 RADIOCHEMICAL ANALYSIS: CR-B 7.0 i 1.3 E 00 5.6 i 1.3 E 00 I-131 LT. 7. E-01 LT.2. E.01 GAMMA SPECIRUM ANALYSIS: BE-7 LT.3. E 01 LT.2. E 01 u K.40 LT.6. E 01 LT.4. E 01 LT.3. E 00 LT. 3. E 00 ( MN-54 m CO-58 LT.3. E 00 LT. 3. E 00 h FE-59 LT.8. E 00 LT. 6. E 00
- E 00 CO-60 LT. 3. E 00 LT. 3.
ZN-65 LT.6. E 00 LT. 6. E 00 NB-95/ZR-95 LT.3. E 00 LT. 3. E 00 RU-103 LT.4. E 00 LT.3. E 00 RU-106 LT.3. E 01 LT.3. E 01 I-131 LT.6. E 00 LT.4. E 00 CS-134 LT.3. E 00 LT.3. E 00 CS-137 LT.3. E 00 LT.3. E 00 LA-140/BA-140 LT. 5. E 00 LT.4. E 00 CE-141 LT. 7. E 00 LT. 5. E 00 CE-144 LT. 3. E 01 LT. 2. E 01 RA-226 LT.9. E 01 LT. 6. E 01 TH-228 LT.7. E 00 LT. 5. E 00 TRrI1UM ANALYSIS: 10/04-01/03 H-3 LT.2. E 02
WOIX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PA'IHWAY - WA~IERBORNE GROUND WATER (PCI/IIIER) STKI1ON NUMBER B-12 DATE COLLECIED: 02/15 05/17 08/16 08/16' RADIOCHEMICAL ANALYSIS: I-131 LT. 1. E-01 LT.2. E-01 LT.3. E-01 LT. 2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 2. E 01 K-40 LT.5. E 01 6.4512.90 E 01 LT.5. E 01 LT. 5. E 01 o MN-54 LT.3. E 00 LT.4. E 00 LT.3. E 00 ' LT. 3. E 00 y 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 5. E 00 & CO-60 LT.3. E 00 LT.4. E 00 LT.3. E 00 L T. 3.. E 00 ZN-65 LT.7. E 00 LT.8. E 00 LT.6. E 00 LT. 5. ' E 00 NB-95/ZR-95 LT.4. 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.3. E 01 LT.3. E 01 LT. 2. E 01 1-131 LT.7. E 00 LT.7. E 00 LT. 4.- E 00 LT.4. E 00 CS-134 LT. 3- E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT 3. E 00 - LT.4. E 00 IA-140/BA-140 LT. 5. E 00 LT.6. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT. 7. ' E 00 LT.6. E 00 LT. 5. E 00 L T. 5.' ' E 00 CE-144 LT.3. E 01 LT.3. E 01 LT.2. E 01 - LT.2. E 01 RA-226 LT.8. E 01 LT.7. E 01 LT.7. E 01 LT.6. E 01 TH-228 LT. 7. E 00 LT.6. E 00 LT.6. E 00 LT.6. . E 00 TRIT 1UM ANALYSIS:
H-3 LT. 1. E 02 LT.4. E 02 . LT. 5. E 02 LT.5. E 02 cNplie h%
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WOEX CREEK NUCLEAR OPERATING CORPOptA110N EXPOSURE PATHWAY - WATERBORNE GROUND WKIER (PCI/ LITER) STATION NUMBER B-12 DATE COLLECTED: 11/15 RADIOCHEMICAL ANALYSIS: I-131 LT.2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 01 K-40 LT.4. E 01 MN-54 LT.3. E 00 2 CO-58 LT.3. E 00
$ FE-59 LT.5. E 00 p CO-60 LT.3. E 00
$ ZN-65 LT.6. E 00 NB-95/ZR-95 LT. 3. E 00 RU-103 LT.3. E 00 RU- 106 LT. 2. E 01 1-131 LT.4. E 00 CS-134 LT. 3. E 00 CS-137 LT.3. E 00 LA-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 TRIT 1UM ANALYSIS:
H-3 LT. 2. ~ E 02
wors cRazz nucur.AR OPERATEG CORPORATION EXPOSURE PATHWAY - WKIERBORNE GROUND WATER (PCl/ LITER) STA"ITON NUMBER C-10 DATE COLLECTED: 02/15 05/17 08/16 11/22/94 RADIOCHEMICAL ANALYSIS: I-131 LT. 1. E-01 LT. 2. E-01 LT.2. E-01 LT. 2. . E-01 GAMMA SPECTRUM ANALYSIS: 1 BE-7 LT.4. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 K-40 LT. 6. E 01 LT. 1. E 02 LT. 5. E 01 5.9512.38 E 01 MN-54 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 o CO-58 LT.4. E 00 LT.4. E 00 LT. 3. E 00 LT.3. E 00 LT. 7. E 00 LT. 1. E 01 LT.6. E 00 LT.7. E 00 f FE-59 m CO-60 LT.4. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00
& ZN.65 L T. 8. E 00 LT. 1. E 01 LT.6. E 00 LT.7. E 00 N
NB-95/ZR-95 LT.4. E 00 LT. 5. E 00 LT.3. E 00 LT.4. E 00 RU-103 LT. 5. E 00 LT. 5. E 00 LT.3. E 00 LT.4. E 00 RU- 106 LT.3. E 01 LT.4. E 01 LT.3. E 01 LT.3. E 01 1-131 LT.8. E 00 LT.8. E 00 LT.4. E 00 LT.6. E 00 CS-134 LT. 4. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.5. E 00 LT. 3. E 00 LT.4. E 00 LA-140/BA-140 LT.7. E 00 LT.8. E 00 LT.4. E 00 LT. 5. E 00 CE-141 LT. 9. E 00 LT.8. E 00 LT.6. E 00 LT. 5. E 00 CE-144 LT.4. E 01 LT.3. E 01 LT.2. E 01 LT.2. E 01 RA-226 LT. 1. E 02 LT.9. E 01 LT.6. E 01 LT.6. E 01 Til-228 L T. 1. E 01 LT.8. E 00 LT.6. E 00 LT.6. E 00 TRrI1UM ANALYSIS: 11-3 LT. 1. E 02 LT.4. E 02 LT.5. E 02 L T. 2.- E 02
WOtX CREEK NUCLEAR OPERATING COEtPORATION EXPOSURE PKnIWAY - WATERBORNE CROUND WATER (PCI/ LITER) STKHON NUMBER F-20 DATE COLIECTED: 11/15 RADIOCHEMICAL ANALYSIS: 1-131 LT.2. E-Ol CAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 K.40 LT. 6. E 01 MN-54 LT.3. E 00 y CO-58 LT.2. E 00 $* FE-59 LT.6. E 00 CO-60 LT.3. E 00 E ZN.65 LT.6. E 00 0 NB-95/ZR-95 LT. 3. E 00 RU-103 LT.3. E 00 RU-106 LT.2. E 01 1-131 LT.5. E 00 CS-134 LT. 3. E 00 CS-137 LT.3. E 00 1A-140/BA-140 LT.4. E 00 CE-141 LT.7. E 00 CE-144 LT. 3. E 01 RA-226 LT.8. E 01 TH-228 LT.7. E 00 TRIT 1UM ANALYSIS: H-3 LT.2. E 02
. . . . . ~
wogy rman NUCutAR OPERATUSG CORPORADON EXPOSURE PA'IHWAY - WA1ERBORNE . , GROUND WA"IER (PCI/ LITER) STA~I10N NUMBER C-49 4 DATE COLLECTED: 02/15 05/17 08/16 11/15 RADIOCHEMICAL ANALYSIS: , I-131 LT. 1. E.01 LT.2. E-01 LT. 1. E.01 LT,2. E-01 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 K.40 LT.6. E 01 LT.5. E 01 LT.6. E 01 LT.9. E 01 MN-54 LT. 3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 o CO-58 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 g FE-59 LT.6. E 00 LT 6. E 00 LT.8. E 00 LT.7. E 00 m CO-60 LT.4. E 00 LT.4. E 00 LT. 5. E 00 LT.3. K 00 do ZN-65 LT.7. E 00 LT.7. E 00 LT. 1. E 01 LT.7. E 00 i NB-95/ZR-95
- LT.3. E 00 LT. 3. E 00 LT.5. E 00 L.T. 3. ' E 00 RU-lO3 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT. 3.' E 00 RU-106 LT.3. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 l-131
~
LT.7. E 00 LT.6. E 00 LT.6. E 00. LT.5. E 00 CS-134 LT.3. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 CS-137 LT.4. E 00 LT.4. E 00 LT. 5. . E 00 LT.4. E 00 IA-140/BA-140 LT. 6. E 00 LT.5. E 00 LT.6. E 00 LT.4. E 00 CE-141 LT. 7. E 00 LT.7. E 00 LT.7. E 00 LT.5. E 00 CE-144 LT.3. E 01 LT.3. E 01. LT.3. ' E 01 LT.2. E 01 RA-226 LT. 8. E 01 LT.7. E 01 LT.9. E 01 LT. 6. E 01 TH-228 LT. 7. . E 00 LT. 6. E 00 ' LT. 1. E 01 LT.6. E 00 , TRTI1UM ANALYSIS: H-3 LT. 1. E 02 LT.4. E 02 LT.5. ~ E 02 LT.2. E 02 t-
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A R R . R-EY W E T BE - PA OW EC L/ U I M 1 1 00000001 0 000 01 1 0 00000000000000000 0 2 0 RH AF I N EEEEEEEEEEEEEEEEEE E AT tA R PC N ( uP U O I cE S T 5 353374. 734. 36335 6266 . . . . . . . . . . . . uR A 1 4 nU T S
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000 00 000 0000 0 0 00 00 0 .- EEEEEEEEEEEEEEEEEE E 0 2 393374 734. 34 4 44 5276 5 i
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WOIF CREEK NUCl2AR OFEMATING CORPORATION EXPOSURE PATHWAY - WATERBORNE SURFACE WATER (PCI/ LITER) STATION NUMBER MUSH DATE COLLECIED: 11/15 12/22 GAMMA SPECTRUM ANALYSIS: BE-7 LT.2. E 01 LT. 3. E 01 K-40 LT.4. E 01 LT. 5. E 01 MN-54 LT.2. E 00 LT.3. E 00 CO-58 LT.2. E 00 LT.3. E 00 FE-59 LT.4. E 00 LT.7. E 00 2 CO-60 LT.2. E 00 LT.4. E 00
$ ZN-65 LT.4. E 00 LT.7. E 00 p NB-95/ZR-95 LT.2. E 00 LT. 3. E 00 g RU-103 LT.3. E 00 LT.4. E 00 RU- 106 LT.2. E 01 LT. 3. E 01 1-131 LT.3. E 00 LT.5. E 00 CS-134 LT.2. E 00 LT.4. 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.4. E 00 LT. 6. E 00 CE-144 LT.2. E 01 LT.2. E 01 RA-226 LT.5. E 01 LT.7. E 01 TH-228 LT.4. E 00 LT.6. E 00 TRI~DUM ANALYSIS:
H-3 LT.2. E 02 LT. 2. E 02
WOIX CREEK NUCLEAR OPERATING CORPORATION EXPOSURE PATHWAY - WATERBORNE SURFACE WATER (PCI/ LITER) STATION NUMBER DC DATE COILECIED: 01/18 02/15 03/15 04/19 04/19' GAMMA SPECTRUM ANALYSIS: BE-7 LT.4. E 01 LT.3. E 01 LT.4. E 01 LT.3. E 01 LT.2. E 01 K.40 LT 1. E 02 LT.5. E 01 LT. 1. E 02 LT.4. E 01 LT. 5. E 01 UN-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. 5. E 00 LT.3. . E 00 LT.3. E 00 FE-59 LT.9. E 00 LT. 5. E 00 LT. 1. E 01 LT.6. E 00 L T. 5. E 00 o CO-60 LT.4. E 00 LT.3. E 00 LT.5. E 00 LT. 4. E 00 LT.3. E 00
$ ZN.65 LT. 1. E 01 LT.5. E 00 LT. 1. E 01 LT.8. E 00 LT.5. S 00 m NB-95/ZR-95 LT. 5. E 00 LT.3. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 E RU.103 LT. 5. E 00 LT. 3. E 00 LT. 5. E 00 LT.3. E 00 LT.3. E 00 RU-106 LT.4. E 01 LT. 2. E 01 LT.4. E 01 LT.3. E 01 LT.2. E 01 I-131 LT.8. E 00 LT.6. E 00 LT.8. E 00 LT.4. E 00 LT.4. E 00 CS-134 LT. 5. E 00 LT.3. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 CS-137 LT. 5. E 00 LT. 3. E 00 LT.5. E 00 LT.3. E 00 LT.3. E 00 LA.140/BA-140 LT.6. E 00 LT.4. E 00 LT.7. E 00 LT.4. E 00 LT.3. E 00 CE-141 LT.7. E 00 LT. 6. E 00 LT.8. E 00 LT. 5. E 00 LT.5. E 00 -
CE-144 LT.3. E 01 LT.2. E 01 LT. 3. E 01 LT. 2. E OI LT.2. E 01 RA-226 LT.8. E 01 LT.6. E 01 LT.9. E 01 LT. 6. E 01 LT. 6. E 01 TH-228 LT.8. E 00 LT.6. E 00 LT. 7. E 00 LT.6. E 00 LT.5. E 00 TRI11UM ANALYSIS: H-3 7.5 i 0.5 E 03 9.6 i 0.5 E 03 1.0 1 0.1 E 04 1.1 1 0.1 E 04 1.0 1 0.1 E 04
' Duplicate Analysis
WORF ruter NUCERAR OPERATEUG CORFORA110N EXPOSURE PATHWAY - WATERBORNE SURFACE WATER (PCI/L11ER) STA*110N NUMBER DC DATE COLLECIED: 05/17 06/21 07/19 08/16 09/20 GAMMA SPEC 1 RUM ANALYSIS: BE-7 LT.4. E 01 LT. 2. E 01 LT.3. E 01 LT. 3. E 01 LT. 3. E 01 K.40 5.1312.93 E 01 LT.4. E 01 LT.7. E 01 LT. ' 8. E 01 LT.5. E 01 MN-54 LT.4. E 00 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 CO-58 LT.4. E 00 LT.2. E 00 LT.3. E 00 LT.3. E 00 ' LT. 3. E 00 FE-59 LT.9. E 00 L T. 5. E 00 LT. 7. E 00 LT. 6. E 00 LT.5. E 00 CO-80 LT.4. E 00 LT.2. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 y g EN-65 LT.9. E 00 LT. 5. E 00 LT. 7. E 00 LT.6. E 00 LT.6. E 00
- LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 NB-95/ZR-95 RU-103 LT.4. E 00 LT. 3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 o RU-106 LT.4. E 01 LT. 2. E 01 '. LT.3. E 01 LT. ' 3. E 01 LT.3. E 01 -
1-131 LT.7. E 00 LT.4. E 00 ' LT.6. E 00 LT.4. E 00 LT.4. 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.3. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 IA-140/BA-140 LT. 6. E 00 LT.3. E 00 LT.6. E 00 - LT.4. E 00 LT.4. E 00 CE-14 I LT.6. E 00 LT. 5. E 00 LT. 9. E 00 LT. G. E 00 LT. 6. E 00 CE-144 LT.2. E 01 LT. 2. E 01' LT. 4.- E 01 LT. 2. - E 01 ' LT.3. E 01 RA-226 LT.7. E 01 LT. 6. E 01 . LT. 1. E 02 - LT. 6.' E 01 LT.8. E 01 TH-228 LT.7. E 00 LT.5. E 00 LT.8. E 00 LT.6. ~ E 00 LT.6. E 00 TRI110M ANALYSIS: H-3 9.6 i 0.5 E 03 9.5 i 0.5 E 03 1.4 i 0.I E 04 8.8 i 0.5 E03. 1.1 2 0.1 E 04
wow c===r wuctaAR OPERATMG CORPORATION EXPOSURE PATHWAY - WATERBORNE SURFACE WA'IER (PCl/ LITER) STA110N NUMBER DC DATE COLLEC1ED: 10/18 10/18* 11/15 12/22 GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 LT.3. E O1 LT.3. E O1 LT.3. E O1 K.40 LT.7. E 01 LT. 8. E 01 LT.8. E 01 LT. 6. E 01 MN-54 LT.3. E 00 LT. 3. E 00 LT.3. E 00 LT. 3. E 00 CO-58 LT,3. E 00 LT. 3. E 00 LT.3. E 00 LT.4. E 00 y FE-50 LT. 6. E 00 LT.7. E 00 LT.6. E 00 LT.6. E 00
$* CO 60 LT. 3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 ZN-65 LT.6. E 00 LT.7. E 00 LT.6. E 00 LT.8. E 00 NB-95/ZR-95 LT.3. E 00 LT. 3. E 00 LT.3. E 00 LT.4. E 00 RU-103 LT. 3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 RU-106 LT.3. E 01 LT.3. E 01 LT. 3. E 01 LT. 3. E 01 1-131 LT.4. E 00 LT.5. E 00 LT.4. E 00 LT.6. E 00 CS-134 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.4. E 00 CS-137 LT.3. E 00 LT.3. E 00 LT.3. E 00 LT.4. E 00 IA-140/BA-140 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.6. E 00 CE-141 LT.5. E 00 LT.6. E 00 LT.4. E 00 LT.7. E 00 CE-144 LT 2. E 01 LT. 2. E 01 LT.2. E 01 LT. 3. E 01 RA-226 LT.6. E 01 LT.6. E 01 LT. 6. E 01 LT. 9. E 01 TH-228 LT.6. E 00 LT.6. E 00 LT. 5. E 00 LT. 8. E 00 i
j TRI110M ANALYSIS: I H-3 1.0 i 0.1 E 04 1.1 1 0.1 E 04 9.6 i O.3 E 03 9.4 1 0.3 E 03 i CDuplicate Analysis l l l
i WOLF CREEK NUCI2AR OPERATING CORPORATION EXPOSURE PATHWAY - WATERBORNE SURFACE WA'IER (PCI/ LITER) STAT 10N NUMBER SP DATE COLLECIED: 01/18 02/15 03/15 04/19 05/17 GAMMA SPECTRUM ANALYSIS: BE-7
- LT. 3. E 01 LT.3. E 01 LT. 3. E 01 LT. 3. E 01 K-40 LT. 1. E 02 LT.8. E 01 L T. 1. E 02 LT. 5. E 01 MN-54 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 CO-58 LT.3. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00 FE-59 LT.8. E 00 LT.6. E 00 LT. 7. E 00 LT.6. E 00 y CO-60 LT.4. E 00 LT.3. E 00 LT. 3. E 00 LT.3. E 00
$ ZN-65 LT.8. E 00 LT. 6. E 00 LT. 8. E 00 LT.6. E 00 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 [ NB-95/ZR-95 g RU-103 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 N RU-106 LT.4. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 1-131 LT.7. E 00 LT.5. E 00 LT.4. E 00 LT.5. E 00 CS-134 LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.3. E 00 CS-137 - LT.4. E 00 LT.3. E 00 LT.4. E 00 LT.4. E 00 1A-140/BA-140 LT.6. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 CE-141 LT.6. E 00 LT.5. E 00 LT. 5. E 00 LT. 5. E 00 CE-144 LT.2. E 01 LT.2. E 01 LT. 2. E 01 LT.2. E 01 RA-226 LT.7. E 01 LT. 6. E 01 LT. 7. E 01 LT. 6. E 01 Tll-228 LT.7. E 00 LT.6. E 00 LT.6. E 00 LT. 5. E 00 TRIT 1UM ANALYSIS: H-3 9.8 i 0.5 E 03 1.1 1 0.1 E 04 1.010.1 E 04 9.4 i 0.5 E 03
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._7 WOEF CEREEE NUCEEAR OPERA 11NG COEtPOItA110Et EXPOSURE PKIHWAY - WKIERBORNE SURFACE WKIER (PCl/ LITER)
STATION NUMBER SP DA'IE COLLECIED: 11/15 12/22 GAMMA SPEC'IRUM ANALYSIS: BE-7 LT.2. E 01 LT.3. Ei3 K-40 LT.9. E 01 LT.5. E 01 i MN-54 LT. 3. E 00 LT.3. E 00 CO-58 LT. 3. E 00 LT.3. E 00 FE-59 LT.6. E 00 LT.7. E 00 2 CO-60 LT.3. E 00 LT.3. E 00
- $ ZN-65 LT.G. E 00 LT.8. E 00 to NB-95/ZR-95 LT.3. E 00 LT. 3. E 00 y RP-103 LT.3. E 00 LT.4. E 00 RU- 106 LT.3. E 01 LTs 3. E 01 I-131 LT.4. E 00 LT.6. E 00 CS-134 LT. 3. E 00 LT.4. E 00 CS-137 LT.3. E 00 LT.4. E 00 LA-140/BA-140 LT.3. E 00 LT.5. E 00 CE-141 LT.5. E 00 LT. 6. E 00 CE-144 LT.2. E 01 LT.2. E 01 RA-226 LT.6. E 01 LT.7. E 01 TH-228 LT. 5. E 00 LT.6. E 00 TRTI1UM ANALYSIS
H-3 9.4 i 0.3 E 03 9.5 i 0.3 E 03
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WOEF CREEE NUCLEAR OPERATEUG CORFORATION EXPOSURE PA1HWAY - WATERBORNE SURFACE WATER ' (PCI/ LITER) STA110N NUMBER WCCL DATE COLLECIED: 10/26 10/26 10/26 10/26 10/28 IUHS/ INTAKE 2BEMIS COVE- 3 SADDLE DAM 4S-REINKER RD . MUDSWCCL AREA SCCG TCTOR H 4.SCCK SEC L SECTOR P GAMMA SPECTRUM ANALYSIS: BE-7 LT.3. E 01 ' LT. 4. E 01 LT. 3. E 01 LT.3. E 01 LT. 3. E 01 K-40 LT. 5. E 01 LT.6. E 01 LT. 5. E 01 LT.5. E 01 LT. 5. E 01 MN.54 LT.3. E 00 LT.4. E 00 LT.3. E 00 LT.3. E 00 . LT. 3. E 00 CO-58 LT.3. E 00 LT. 3. E 00 LT.3. . E 00 LT. 3. E 00 LT.3. E 00 2 FE-59 LT. 6. E 00 ' LT. 7. E 00 LT.6. E 00 LT. 7. E 00 LT. 7. E 00 E CO-60 LT.3. E 00 - LT.4. E 00 L.T. 3. E 00 LT.4. E 00 L T. 3.~ E 00 ' y ZN.65 LT.6. E 00 LT.8. E 00 LT.6. E 00 LT.7. 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 - LT. 3. E 00 RU-103 LT.4. E 00 ~ LT. 4. E 00 LT.3. E 00 LT.4. E 00 LT.4. : E 00 RU.106 LT.3. E 01 LT.3. E 01 LT.3. E 01 LT. 3. E 01 LT.3. E 01 I-131 LT.5. E 00 LT.6. E 00 LT.4. E 00 LT.5. E 00 LT. 6. E 00 CS-134 LT.3. E 00 LT.4. E 00 - LT.3. E 00 LT.4. E 00 . L T. 3.- E 00 CS-137 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.4. E 00 LT.3. E 00 - LA-140/BA-140 LT.4. E 00 LT. 5. E 00 LT.4. E 00 LT.4. E 00 - LT. 6. . E 00 CE-141 LT.6. E 00 LT.7. E 00 LT. 5. E 00 LT.6. E 00 LT. 6. E 00 CE-144 LT. 3. 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. 8. E 01 LT.6. E 01 LT.8. E 01 LT. 7. E 01 TH-228 LT.7. E 00 LT.7. E 00 - LT. 5. E 00. LT.7. E 00 - LT. 7. E 00 TRI11UM ANALYSIS: H-3 9.7 i 0.5 E 03 9.2 1 0.5 E 03 9.6 i 0.5 E 03 9.2 i 0.5 E 03 2.7 i 0.3 E 03
WORF CREEE NUCLEAR OPERATEUG CORFORATION - ' EXPOSURE PATHWAY - WKIERBORNE SURFACE WKIER (PCI/ LITER) STA110N NUMBER WCCL DATE COLLECTED: 10/26 SN HOUSERS SECTOR R 4 GAMMA SPECIRUM ANALYSIS: s BE-7 LT.3. E 01 K-40 LT.7. E 01 MN-54 LT.4. E 00 CO-58 LT.4. E 00 FE-59 LT.8. E 00
- 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 1-131 LT.7. E 00 CS-134 LT.4. E 00 CS-137 LT.4. E 00 LA-140/BA-140 LT. 6. E 00 CE-141 LT.7. E 00 CE-144 LT.3. E 01 , RA-226 LT. 8- E 01 TH-228 LT.7. E 00 TRrilUM ANALYSIS: - H-3 9.3 1 0.5 E 03 9 *
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