ML20155G339
| ML20155G339 | |
| Person / Time | |
|---|---|
| Site: | Wolf Creek  |
| Issue date: | 12/31/1985 |
| From: | Koester G KANSAS GAS & ELECTRIC CO. |
| To: | Martin R NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION IV) |
| References | |
| KMLNRC-86-077, KMLNRC-86-77, NUDOCS 8605050372 | |
| Download: ML20155G339 (120) | |
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.e Wolf Creek Generating Station Dockrb No: STN 50-482 Facility Operating License No: NPF-42 ANNUAL RADIOLOGICAL ENVIROISIENTAL OPERATING REPORT Report No: 1 Reporting Period: March 11, 1985 through December 31, 1985 Submitted by:
Kansas Gas and Electric Company 860505037203j$$482 PDR ADOCK PDR R
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TABLE OF CONTENTS P_ag List of Tables....................................................
11 List of Figures...................................................
iii Introduction......................................................
1 I.
Program Description.........................................
2 II.
Discussion of Results.......................................
5 III. Annual Land Use Survey Results and Program Revis. ions........
10 IV.
Monitoring Program Deviations...............................
12 V.
EPA Interlaboratory Comparison Program Res'ults..............
14 TABLES......................................................
15 FIGURES.....................................................
26 Appendix A:
Summary tables in format of NRC Radiological Assessment Branch Technical Position, Revision 1, November 1979...........................
A-1 Appendix B:
Individual sample results...........................
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LIST OF TABLES E *$ *.
Table 1:
Sampling Location Numbers, Distances, and Directions............................................
15 Table 2:
Gross Beta Analysis Results of Air Particulate Samples...............................................
16 Table 3:
Gamma Analysis Results of Air Particulate Composite Samples...............................................
17 Table 4:
19 8 5 KG& E TLD Re s ul t s.................................
18 Table 5:
Gross Beta Analysis Results of Drinking Water Samples...............................................
19 Table 6:
Gamma Analysis Results of Broadleaf Vegetation Samples...............................................
20 Table 7:
Gamma Analysis Results of Shoreline Sediment Samples...............................................
21 Table 8:
Gamma Analysis Results of Aquatic Vegetation Samples...............................................
22 Table 9:
Results of 1985 Annual Land Use Survey................
23 Table 10:
Results of EPA Interlaboratory Comparison Tests.......
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LIST OF FIGURES Lan Figure 1:
Airborne Particulate and Radioiodine Sampling Locations............................................
26 Figure 2:
TLD Locations........................................
27 Figure 3:
Water Sampling Locations.............................
28 Figure 4:
Milk Sampling Locations..............................
29 Figure 5:
Broadleaf Vegetation Sampling Locations..............
30 Figure 6:
Fish, Shoreline Sedia'ents, and Aquatic Vegetation Sampling Locations...................................
31 Figure 7:
Distant Sampling Locations...........................
32 Figure 8:
1985 Gross Beta Air Concentrations...................
33 Figure 9:
Nearsite Average vs. Control TLDs....................
34 Figure 10: Variation of Nearsite TLD Results....................
35 Figure 11:
1985 Operational TLD Results.........................
36 Figure 12: Drinking Water Gross Beta Analysis Results...........
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4 F-Introduction 4
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This represents the first Annual Radiological Environmental Operating Report for Kansas Gas and Electric Company's Wolf Creek Generating Station (WCGS),
located in Coffey County, Kansas, approximately five miles northeast of Burlington, Kansas.
This report covers the period from January 1 to December 31, 1985.
Fuel loading began at WCGS on March 12, 1985. The operational phase of the 1-Radiological Environmental Monitoring Program began with initial criticality on May 22, 1985, with the first detectable quantities of radioactivity l
reported in plant effluents in June, 1985.
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This report contains a description of the Radiological Environmental j.
Monitoring Program conducted by Kansas Gas & Electric (KG&E), results of sample analyses performed by Teledyne Isotopes, a discussion of monitoring i
program results, a discussion of program deviations and revisions, and a discussion of the results of the EPA Interlaboratory Comparison Program.
Individual sample results and a summary of results in the NRC Branch l
Technical Position specified format are included as appendices to the q
report.
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The impact of the operation of WCGS on the surrounding environment uss limited to the detection of small amounts of tritium in surface water and i
Co-58 in rooted aquatic plant samples in the.immediate vicinity of the discharge cove of Wolf Creek Cooling Lake.
Both nuclides were reported in liquid effluents during the second, third, and fourth quarters of 1985. No plant related radioactivity was detected at the nearest offsite sampling i
locations downstream of effluent release points in unrestricted access areas (drinking water location LW-40 at LeRoy, shoreline sediment location NR on the Neosho River, and irrigated crop location N1-D1 near the Neosho River).
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No measurable impact on human exposure was seen lor the liquid pathway i
during 1985.
l No conceptrations of radioactivity over Technical Specification reporting l
levels 'gere seen from either plant related or other sources for any pathway.
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I.
PROGRAM DESCRIPTION Radiological environmental samples were collectd according to the schedule in Table 3.12-1 of the Wolf Creek Technical Specifications and Section 4.0 of the Offsite Dose Calculation Manual.
All samples were collected by 4
KG&E's Environmental Management Group and sent to Teledyne Isotopes for analysis.
The following is a description of the sampling and analysis program by individual pathways.
Airborne Particulates and Iodine:
Low volume air sampling pumps continuously collected particulate samples on 47mm glass fiber filters; samples were then drawn through charcoal cannisters to collect I-131.
Filters and charcoal cannisters were changed out weekly, labeled, and shipped to Teledyne Isotopes for analysis. Total sample volume used to calculate air concentrations was determined from the average of the initial and final sampling flowrate and the total time of collection.
Gross beta analysis of the air particulac'e samples was performed approximately 72 hours8.333333e-4 days <br />0.02 hours <br />1.190476e-4 weeks <br />2.7396e-5 months <br /> following filter collection to allow decay of radon and thoron daughter products. 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.
l Charcoal cannisters were counted in groups of f'ive for qualitative and quantitative determination of the presence er absence of I-131; positive indication of I-131 (which was not detected in 1985) would have been followed by quantitative analysis of individual cannisters.
Air samples were collected from the three sectors with the highest ground level D/Q, the nearby community of New Strawn, and a control location.
Distances and directions to sampling locations from the plant site are listed in Table 1; locations are shown in Figure 1 (nearby locations) and Figure 7 (distant locations).
TLD:
9 The thermoluminescent dosimeters (TLDs) used during 1985 were provided by Teledyne Isotopes. The TLDs consisted of rectangular teflon wafers impregnated with CaSO :Dy.
Prior to placement in the field, the dosimeters 4
were annealed for at least one hour at between 250 and 260 degrees centigrade then placed in polyethylene pouches and holders containing 0.093 inches of copper shielding to filter out low energy radiation. New field dosimeters were exchanged with exposed dosimeters and the exposed dosimeters
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were returned to Teledyne Isotopes for analysis. Freshly annealed control dosimeters were sent with the exposed TLDs to record transit exposures received during shipment to Teledyne as well as system background of the TLD reader. 4
1 Gamma exposures were: measured onia Teledyne Model 8300 TLD reader; j
individual dosimeters were then re-irradiated with a known exposure from a Cs-137 source and read again to determine individual dosimeter calibration factors.
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In general, TLDs were located 3-41 feet above the. ground on utility poles; they were placed inside either plastic thermostat 2 boxes or fiberglass air particulate sampler housings to protect them fron'aoisture and tampering.
Two TLDs were placed at each location to provide duplicate measurements.
TLD locations are shown on Figure 2 (nearsite) and Figure '7 (distant).
Table 1 provides distances and directions of each location from the WCGS site.
Water Monthly composite samples of drinking water were collected by continuously drawing aliquots at two hour intervals. Grab samples of surface: water and ground water were collected on a monthly and. quarterly basis, respectively.
All samples were sent to Teledyne Isotopes for analysis.
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All water samples were analyzed on a Ge(Li) detector to determine if gamma emitters were present.
In addition to gamma analysis, a radiochemical analysis for I-131 was performed on drinking water and ground water samples. Gross beta analysis was also performed on drinking water samples.
All water samples were analyzed for tritium on a quarterly basis by liquid scintillation counting (monthly drinking water and surface water samples were combined into quarterly composites for tritium counting).
Drinking wat'er sampling locations are at the water treatment stations' for the towns of Burlington (upstream control location) and Leroy (downstream indicator location).
Surf ace water sampling locations are at the John Redmond Reservoir outfall (control) and the Wolf Creek Cooling Lake discharge cove (indicator). Ground water is sampled from three wells located hydrologically downgradient from Wolf Creek Cooling Lake and from an upgradient control well. All water sampling locations are listed in Table 1 and shewn in Figures 3 and 7.
Ingesticn:
Milk samples were collected on a semi-monthly basis from April through November (while milk animals were on pasture grass) and on a monthly' basis the remainder of the year (when animals were on sected feed). Samples were sent to Teledyne Isotoies where radiochemical analyses for I-131 and ganas analyses were performe6 on each sample.
Locations.are shown in Figure 4.
Broadleaf vegetation samples were collected monthly during the growing season. Occasionally alternate sampling locations were used when quantities of vegetation were limited, such as early or late in the growing season or during dry periods.
Additionally, a sample of crops irrigated with water
,j from the Neosho River downstream of Wolf Creek Cooling Lake was collected during harvest. The crop was intended for animal consumption only. All vegetation samples were sent to Teledyne Isotopes and analyzed by gamma spectroscopy.
Locations are shown in Figure 5.
Fish samples were collected semiannually with several recreationally important species being sampled.
Samples of boneless meat portions were sent to Teledyne Isotopes and analyzed by gamma spectroscopy. Locations are shown in Figure 6.
All sampling locations above are listed i'n Table 1: distant locations are shown in Figure 7.
(Fish sampling locations may vary somewhat from Figure 6 according to sample availability.)
J Shoreline Sediment & Aquatic Vegetation:
Semiannual shoreline sediment samples were collected from the Neosho river below the Wolf Creek-Neosho confluence and from a more conservative location on Wolf Creek Cooling Lake. Gamma analysis was performed by Teledyne Isotopes on each sample.
Sampling Locations are listed in Table 1 and shown on Figures 6 and 7.
Although not required by the routine monitoring program, aquatic vegetation samples composed of rooted aquatic plants and algae were collected from the discharge cove area (location DC on Figure 6) of Wolf Creek Cooling Lake.
Gamma isotopic analysis was performed on each sample.
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II.
DISCUSSION OF RESULTS Analysis results for all pathways are summarized in Appendix A using the format described in NRC Radiological Assessment Branch Technical Position, j
Revision 1, November 1979; results for individual samples are listed in Appendix B.
In this section, results are discussed by pathway and analysis type.
Operational results are related to control location results, preoperational values, sources of radioactivity, and effluent releases when applicable.
Trends or seasonal effects seen in the data are also discussed.
Airborne Particulates and Iodine:
Results of weekly gross beta analyses of air particulate filters are listed for each location in Table 2.
The averages of the four indicator locations near the site are also compared to control location values in Figure 8.
The graph shows no identifiable variation from the preoperational range of 0.0064 to 0.084 pCi/m3 (excluding high results obtained following an atmospheric nuclear weapon test by China in 1980) and,no significant increase in the indicator location results following plant operation.
Two obvious peaks, one in February before fuel loading and the other in late November are evident in Figure 8.
'Such peaks appear seasonally during winter and early spring months.
Preoperational gamma analysis of individual air filters have demonstrated that elevated levels of cosmically produced Be-7 are primarily responsible for these peaks.
Gross beta analysis of air particulate samples is known to be a sensitive indicator of airborne radioactivity levels.
(Concentrations increased to a maximum of 0.43 pCi/m3, over ten times higher than normal background levels, following the Chinese atmospheric nuclear weapon test in October of 1980.)
No increase or effect due to plant operation is indicated by operational results.
This conclusion is further confirmed from gamma analysis results of quarterly air particulate filter composites. The only radionuclides detected were Be-7 (cosmically produced) and, occasionally, K-40 (a naturally occuring terrestrial radionuclide).. both at concentrations comparable to preoperational levels (see Table 3).
Gamma analysis of charcoal cannisters for I-131 revealed no detectable concentrations at either indicator or control locations.
In summary, no contribution of airborne radioactivity due to plant operation was identified for 1985. All radioactivity detected was attributable to terrestrial nuclides, cosmically produced nuclides, or fallout from previous weapons tests.
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i TLDs:
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j Quarterly gamma exposures measured at each location for 1985 are shown in j
Table 4.
Values are the average of results for two dosimeters at each i
4 location, normalized to a 90-day standard quarter. TLD results are i
considered operational beginning began with second quarter data for 1985 since effluent releases did not begin until June.
4 Results from TLDs located near the plant site (less than approximately three miles distant), which would be most sensitive to changes due to plant 1
operation, were combined into quarterly averages. These nearsite averages, l
using locations 1, 2, 7, 8, 9, 10, 11, 12, 13, 14, 18, 26, 27, 28, 29, 30, 37, and 38, are compared to control TLD results in Figure 9.
In addition, variation of the nearsite avetages from the control location results are 3
plotted graphically in Figure 10.
(Figures 9 and 10 also include preoperational data for comparison.) No increase is seen in nearsite gamma exposures over control location values.
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The operatioaal gamma exposure rate at each'iocation was plotted along with 7
the preoperational average and range in Figure 11.
It can be seen that operational exposure rates are well within the preoperational range, 'with no significant variation from the preoperational average.
J No changes to area gamma exposure rates as a result of plant operation were identified. Measured gamma exposures were attributable to a combination of terrestrial and fallout gamma emitters and cosmic radiation.
Drinking Water:
Results of gross beta analysis of drinking water samples are listed in Table j
5; Figure 12 depicts these results graphically along with pesoperational values for comparison.
No significant difference between the indicator and control locetions was found. Additionally, no increase over preoperational. concentrations was evident, as is seen in Figure 12. No effect due to plant operation is 4
identified in drinking water samples by gross beta analysis.
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This conclusion is confirmed by the results ' of I-131, ' tritium, and gamma isotopic analyses; no other radionuelides sure 'seen. at detectable levels.
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,o Surface Water:
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j No gamma emitters were detected [in surface water samples for 1985; however, j
tritium tes detected in the fourth / quarter sampinifrom Wolf CreekiCooling Lake near the circulating water discharge point '(location DC;on Figure 3) at j
a concentration of 1600 + 500 pCi/ liter. - The sample. wes:reanalysed for
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confirmation with a more sensitive analysis technique giving a result of 2000'+ 130 pCi/ liter.
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Although some tritium occurs naturally in water, it is assumed that much of 6
the measured concentration was attributable to plant operation, since no tritium was detected ir. the fourth quarter control sample (detection limit =
700 pCi/ liter) and no tritium was found in any preoperational surface water sample. This also correlates well to plant liquid effluent releases, reported as 0.137, 48.3, and 103.1 Ci of tritium for the second, third, and fourt,h quarter of 1985, respectively.
Although Wolf Creek Cooling Lake is not used as a source of drinking water, a hypothetical dose calculation assuming ingestion of water with an average tritium concentration of 2000 pCi/ liter gives a maximum dose of 0.052 arem (whole body dose to a child) for one quarter. The composite drinking water j
samples from the Neosho River at LW-40, downstream from the outfall of Wolf Creek' Cooling Lake, contained no detectable tritium during this time, as has i
already been noted above in the discussion on drinking water results.
Therefore, no public exposure to detectable tritium occurred for the year.
Although a single indication of tritium is not sufficient for projecting trends, this pathway will be monitored closely in the future to identify jl potential problems.
Ground Water:
j The oaly radionuclides detected in ground water samples was K-40 during the fourtt quarter at the control location.
K-40 is a naturally occurring terres trial radionuclide and has occasionally been detected in preopetstional samples (as have Ra-226 and tritium).
No I-131, tritium, or other gamma emitters were detected during the year.
No effect on ground water due to plant operation was identified.
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Milk:
All milk samples analysed for 1985 contained naturally occurring K-40 at concentrations consistent with preoperational levels. Yearly average concentrations ranged from 1140 to 1312 pCi/ liter for co(s milk; goat's milk from location P-2 generally contained 20-40% higher concentrations, averaging 1614 pCi/ liter.
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Two of the 68 milk samples collected also contained detectable Cs-137 from fallout. Concentrations of 7.26 and 7.1.9 pCi/ liter at location F-1 and P-2, respectively, were measured in the samples collected on 2/12/85, prior to fuel load. This is consistent with preoperational experience in which Cs-137, Th-228, and I-131 have been detected in milk.
Radiochemical analysis for I-131 revealed no detectable concentrations in any sample.
No effects on area milk production due to plant operation were seen for the year.
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o Food & Garden Crops:
Gamma analysis of broadleaf vegetation samples revealed naturally occurring gamma emitters K-40 and Be-7 at concentrations comparable to preoperational background levels (see Table 6).
Cs-137 was also detected in samples from locations A-1 and Q-2 during May.
Concentrations were 0.0270 pCi/ gram (wet weight) at location A-1 and 0.0128 pCi/ gram at location Q-2.
As is the case for other pathways, these concentrations of Cs-137 are attributed to fallout. The range of fallout Cs-137 seen in preoperational samples was 0.0131 to 0.0478 pCi/ gram.
Also, Cs-137 was not released in airborne plant effluents during the second quarter.
Finally, Cs-134 was not detected, although it would be expected in comparable quantities if the occurrance of Cs-137 was related to plant operation (Cs-134 decays with a shorter halflife than Cs-137; detection of Cs-137 alone indicates older fallout as opposed to newly produced fission products).
Although broadleaf vegetation is a fairly sensitive indicator of airborne radioactivity (with Nb/Zr-95, Ce-141, Ce-144, and Th-328 having been seen in preoperational samples), results show no contribution due to plant i
operation.
In addition to broadleaf vegetation, a sample of corn was collected which was irrigated with water from the Neosho River below the Wolf Creek Cooling Lake outfall. The crop was intended for animal consumption only. Gamma analysis revealed naturally occurring K-40 to be present in the sample, with no nuclides detected due to plant operation.
a Fish:
K-40 was found in all fish samples collected with an average concentration of 3.2 pCi/ gram (wet weight) for Wolf Creek Cooling Lake and 3.6 pCi/ gram at the control location. These concentrations were within the range seen during the preoperational period.
No other gamma emitters were detected and no ef fects related to plant operation were identified.
Shoreline Sediments:
Gamma analysis of shoreline sediment samples detected naturally occurring terrestrial radionuclides K-40, Ra-226, and.Th-228,' cosmically produced Be-7, and Cs-137, attributable to fallout for the same reasons as were discussed in the section on food and garden crops.
Concentrations in both indicator and control location sacples were consistent with levels seen during the preoperational period (see Table 7).
l Although location DC should be an especially conservative indicator location, no radionuclides released in effluents were seen in any samples, and no effects of plant operation were identified. -
Aquatic vegatation:
1 Although net required by the specified routine monitoring program, algae and rooted aquatic plant samples were collected from Wolf Creek Cooling Lake during 1985.
Results of gamma isotopic analysis are shown in Table 8.
In addition to Be-7, K-40, Cs-137, and Th-228, httributable to natural sources or fallout as described in previous sections, Co-58, an activation product, was also detected in the rooted aquatic plant sample from October.
Releases of 0.0134, 13.2, and 63.2 mci of Co-58, reported in liquid effluents for the second, third, and fourth quarters of 1985, respectively, were probably responsible for its presence in this sample.
Co-58 was not detected in preoperational samples from either indicator or control locations.
It should be noted that the measurel concentration was near the detection limit for this nuclide and that rooted aquatic plants are not a direct pathway to human exposure. However, since this sampling patiway appears to be a sensitive indicator of plant related effluents, it has oeen added to the routine operational monitoring p.ogram.
Although the single result does not rake trend projection possible, analysis results will be followed closely in the future to identify potential problems.
III. Annual Land Ise Survey Essalts and Program Revisions The 1985 Annual Laid Use Survey was completed in November.
Information was collected using a edabination of mailed survey forms, telephone contacts,
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and door to door c ontacts.
Results of the survey, showing the distances to the nearest residences, milk producing animals, and vegetable gardens within five miles of the plant site, are given in Table 9.
Milk animals were located in four sectors, listed in the table. Three changes from the previous survey were identified. Milk producers in sectors C and E (northeast and east of the plant) had sold animals, leaving no milk producing locations out to five miles in those sectors.
Additionally, a new location was identified 2.3 miles ENE of the plant (sector D), although only young animals were at this location which were not producing milk at the time of the survey.
The annual average D/Q st this location was lower than at current sampling locations, so that no revisions to the monitoring program would be required even if milk should become available at this location.
Gardens growing broadleaf vegerables were located within five miles of the plant in all sectors.
Six changes were identified frpa the previous survey, as noted in Table 9.
One change involved the identification in sector D (ENE of the plant site) of a new garden at a distance of 2.3 miles, slightly nearer than the previous location at 2.4 miles. The other five changes were to adjust the nearest garden locations in sectors H K, M, P, and Q to greater distances than identified by the previous survey, due to either deletion of the previous garden or a more accurats distance sessurement. ' No changes to broadleaf vegetation sampling locations were necessary as a result of these adjustments.
Program revisions were made during 1985 involving changes to milk and broadleaf vegetation sampling locations and addition of the aquatic vegetation pathway to the routine monitoring program.
Milk sampling location C-11 was deleted from the program in January because milk animals were sold at this location. No other milk producing locations were available within five miles of the plant and the remaining sampling locations satisfied Technical Specification requirements; therefore, no replacement locations were added.
Broadleaf vegetation sampling location Q-1 was deleted from the program because -the resident moved; location Q-2 was deleted because the resident did not plant a fall garden and had no plans for planting a garden in 1986.
Location G-1 was added as a replacement, providing a third sampling location to the routine program.
Finally, due to detection of Co-58 in a sample of rooted aquatic vegetation in 1985, this pathway was added to the routine monitoring program in December. Semiannual samples of ' aquatic vegetation ~or algae will be collected from the discharge cove area, since this pathway appears to be a potentially sensitive indicator of radioactivity in liquid effluents..
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It should be noted that dose calculations are perform d for airborne and liquid pathways for a hypothetical individual at the exclusion area boundary in the highest X/Q and D/Q sector (for airborne pathways) and at the circulating water discharge point (for liquid pathsays).
Calculated doses
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are therefore conservative, and not affected by changes in residence, milk animal, and broadleaf vegetation locations identified by the Annual Land Use Survey.
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IV. MONITORING PROGRAM DEVIATIONS Deviations from the 1985 sampling schedule are described below by pathway.
j along with causes for the deviations and necessary corrective actions.
Airborne Particulates and Iodine Location 37, (6/7/85 - 6/11/85): A partiel sample was collected because the sampler air pump was not started for the f irst three days of the sampling period. The resulting small ssmple volume also reduced the detection sensitivity for radioiodine, yielding a de tection limit of 70 pCi/m3, 3
slightly above the desired value of 60 pCi/m.
This was due to an operator oversight and is not expected to recur. to corrective action is planned.
TLD Location 14, (first quarter):
The TLDs at this location were placed in the field eight days later than the other TLDs (1/10/85 instead of 1/2/85) because the utility pole on which they had be'n located was removed and a new location had to be found.
Drinking Water Location LW-40, (January):
A grab sample was taken on 2/5/85 in lieu of the specified composite sarple for January because of a compositor malfunction leading to inadequate sample volume.
Readjusting the volume control on the compositor corrected the problem.
Location BW-15 and LW-40, (April): The specified detection limit for I-131 was not, achieved because an incorrectly filled out shipment form led to a delay in the I-131 radiochemical analysis.
From gamma isotopic analysis, LLDs of 20 pCi/ liter and 10 pCi/ liter for locations BW-15 and LW-40, respectively, were achieved rather than the 1.0 pCi/ liter specified.
Corrective action was taken to insure that personnel were f amiliar with the correct procedure for filling out shipment forms; in addition, the analysis laboratory will notify KG&E in the future if requested analyses appear to deviate from the routine program.
Location LW-40, (July):
A partial composite was collacted for approximately the first half of the month rather than the' entire month because the sampling line became clogged and backpressure dislodged the line from the sampling pump. Corrective action was taken to replace the sampling line with new Tygon tubing and clean the sample intake fixture. Personnel were also cautioned to visually inspect the sampling assembly when collecting samples to prevent a recurrence of this type of malfunction.,
Location LW-40, (September):
Although I-131, tritium, and gamma isotopic analyses were performed, insufficient sample remained for a gross beta analysis to be performed because a second I-131 analysis depleted the sample volume. Since no systematic problem was identified with either sample i
collection or sample analysis procedures, and because consistent, adequate results are obtained on a routine basis, no corrective action is planned.
Further action will be considered if a recurring problem is identified.
Milk i
Location F-1, (second half of April thrsugh first half of June) and Location Q-5, (August through the end of 1985):
Samples were unavailable because cows were dry at these locations.
Unavailability of these sample was temporary and there sere no a.iternate milk sampling locations within five miles of the plant site, therefore no corrective actions were taken.
Such unavailability is expacted to recur since milk production at most locations is marginal and locations ar.? rel atively few in number.
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V.
EPA Interlaboratory Comparison Program Results Teledyne Isotopes, contracted to perform analysis of radiological environmental samples for KG&E, participated in the EPA Interlaboratory j
Comparison Program during 1985.
Table -10 shows intercomparison test results for the year. The table lists the sample number and date, the sampic media, the nuclide or analysis type, the known value reported by the EPA, the measured value reported by Teledyne Isotopes (based on triplicate analysis), and the normalized deviation from the known.
(The normalized des iation is determined by the dif ference in the measured result from the-EPA reported known, divided by the standard error of the mean as a measure of the degree of precision. A normalized deviation larger than + 3.0 prompts followup action to identify the cause of the discrepancy.)
Results are listed in the table only for sample media and analyses types performed for KG&E.
Of the 42 sample analyses listed, only one, a gross beta analysis of a mixed alpha / beta liquid sample for 4/19/85, exceeded a normalized deviation of
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3.0.
Followup investigation determined that a conversion factor developed to correct for nuclides with low beta energies had not been applied to a mixed beta sample containing low energy beta emitters.
No major problem was identified for any sample medium or specific analysis.
Past experience shows that corrective actions have been initiated promptly when necessary. Overall performance of the analysis laboratory, as seen in the intercomparison results, indicates good control of quality of analyses.
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TABIAS I
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TABIE 1: SAMPLING IACATION NUNBERS, DISTANCES (cileo) AND CIRECTIONS TLD and Air Particulate Location Distance /
Location Distance /
Location Distance /
Location Distance /
Number Direction Number Direction Number Direction Number Direction 1
1.4/N 11 1.6/E 21 3.8/S 31 3.0/WNW 2
2.7/N 12 1.8/ESE 22 4.1/SSW 32 3.2/WNW 3
3.0/NNE 13 1.5/SE 23 4.5/SW 33 3.7/WNW 4
4.0/NNE 14 2.6/SE 24 4.1/WSW 34 4.0/NW 5
4.0/NE 15 4.5/ESE 25 3.6/W 35 4.6/NNW 6
4.4/ENE 16 4.2/E 26 2.6/WSW 36 4.2/N 7
1.9/NE 17 3.6/SE 27 2.1/SW 37 2.1/NNW 8
1.6/NNE 18 3.2/SSE 28 2.8/SW 38 1.2/NW 9
2.0/ENE 19 4.0/SSE 29 2.6/SSW 39 13.0/N 10 2.4/ENE 20 3.3/S 30 2.2/W 40 15.0/WNW Ground water Drinking Water Surface Water 4
1 B-12 2.2/NNE BW-15 3.9/SW MUSil 3.6/W T
-C-10 2.8/W LW-40 10/SSE DC 0.6 WNW C-49 2.9/SW D-65 3.9/S Milk and Food Products A-1 1.3/N Q-1 1.2/NW C-Il 4.5/NE Q-2 1.4/NW F-1 1.3/ESE Q-5 3.4/NW G-1 1.4/SE R-1 2.2/NNW P-2 2.9/WNW S -3
>l5.0/WNW S-4 15.0/WNW Fish Shoreline Sedments Aquatic Vegetation Irrigated Crops DC 0.6/WNW DC 0.6/WNW DC 0.6/WNW NR-D1 9.2/S JRR 4/W JRR 4/W NR 6.5/S
T;b1'a 2: 1985 GROSS BETA ANALYSIS RESULTS FOR AIR PARTICULATE SAMPLES (pCi/CU. METER)
INDICATOR CONTROL S
Month LOC 2 LOC 3 LOC 32 LOC 37 AVERAGE STD DEV LOC 40 JAN 0.029 0.032 0.030 0.035 0.032 0.003 0.032 0.025 0.030 0.028 0.030 0.028 0.002 0.033 0.026 0.025 0.027 0.029 0.027 0.002 0.027 0.017 0.022 0.019 0.022 0.020 0.002 0.025 FEB 0.026 0.032 0.021 0.027 0.027 0.005 0.028 0.065 0.070 0.048 0.071 0.064 0.011 0.065 0.034 0.032 0.029 0.031 0.032 0.002 0.030 0.022 0.020 0.021 0.022 0.021 0.001 0.024 MAR 0.024 0.025 0.022 0.026 0.024 0.002 0.021 0.020 0.017 0.027 0.025 0.022 0.005 0.023 0.020 0.017 0.019 0.021 0.019 0.002 0.019 0.022 0.023 0.023 0.026 0.024 0.002 0.024 0.015 0.019 0.020 0.021 0.019 0.003 0.020 APR 0.018 0.017 0.022 0.020 0.019 0.002 0.018 0.028 0.023 0.022 0.025 0.025 0.003 0.025 0.021 0.017 0.023 0.025 0.022 0.003 0.022 0.023 0.017 0.023 0.024 0.022 0.003 0.023 HAY 0.026 0.022 0.027 0.025 0.025 0.002 0.022 0.025 0.024 0.027 0.025 0.025 0.001 0.026 0.019 0.019 0.020 0.022 0.020 0.001 0.020 0.031 0.022 0.028 0.030 0.028 0.004 0.027 0.025 0.018 0.020 0.021 0.021 0.003 0.024 JUN 0.025 0.019 0.018 0.029 0.023 0.005 0.019 0.021 0.018 0.019 0.020 0.020 0.001 0.020 0.019 0.018 0.023 0.020 0.020 0.002 0.022 0.021 0.018 0.027 0.024 0.023 0.004 0.024 JUL 0.02:
0.029 0.034 0.033 0.029 0.006 0.031 0.026 0.026 0.032 0.032 0.029 0.003 0.032 0.033 0.019 0.033 0.036 0.030 0.008 0.032 0.027 0.020 0.023 0.024 0.024 0.003 0.025 AUG 0.018 0.015 0.022 0.027 0.021 0.005 0.025 0.036 0.022 0.027 0.029 0.029 0.006' O.027 0.023 0.021 0.024 0.019 0.022 0.002 0.030 0.027 0.019 0.021 0.025 0.023 0.004 0.022 0.036 0.018 0.032 0.035 0.030 0.008 0.035 SEPT 0.026 0.013 0.023 0.025 0.022 0.006 0.025 0.031 0.026 0.029 0.030 0.029 0.002 0.031 0.029 0.017 0.018 0.020 0.021 0.005 0.016 0.022 0.016 0.020 0.020 0.020 0.003 0.020 OCT 0.022 0.015 0.020 0.023 0.020 0.004 0.023 0.019 0.020 0.017 0.020 0.019 0.001 0.016 0.023 0.021 0.022 0.025 0.023 0.002 0.029 0.024 0.029 0.024 0.024 0.025 0.003 0.023 NOV 0.031 0.030 0.030 0.039 0.033 0.004 0.032 0.018 0.014 0.009 0.021 0.015 0.005 0.017 0.025 0.014 0.022 0.026 0.022 0.005 0.024 0.047 0.036 0.041 0.045 0.042 0.005 0.042 0.059 0.054 0.046 0.056 0.054 0.006 0.061 DEC 0.060 0.058 0.058 0.064 0.060 0.003 0.062 0.045 0.045 0.037 0.039 0.042 0.004 0.043 0.044 0.045 0.042 0.0;9 0.043 0.003 0.043 0.018 0.020 0.017 0.016 0.018 0.002 0.018 TABLE 3: GAltfA ANALYSIS RESULTS OF AIR PARTICULATE COMPOSITE SAMPLES 3
(pCi/m )
Location:
2 3
32 37 40(control)
Be-7 1 QTR 0.0777 0.0756 0.0885 0.0839 0.0693 2 QTR 0.0872 0.0733 0.106 0.0985 0.0934 3 QTR 0.100 0.0400 0.0801 0.0795 0.0926 4 QTR 0.0686 0.0629 0.0684 0.0709 0.0788
)
Preoperational range (0.0388 - 0.1170)
K-40 1 QTR 0.00557 2 QTR 0.0197 3 QTR 0.00635 4 QTR 0.00827 a.-
4 Table 4:
1985 KG&E TLD RESULTS (mR/90 DAYS)
LOCATION QTR 1 QTR 2 QTR 3 QTR 4 1
14.7 17.1 18.1 17.6 2
14.4 15.8 16.2 16.6 3
14.3 16.2 16.3 18.7 4
16.6 17.3 17.7 17.5 5
15.0 15.8 17.8 16.7 6
14.2 16.1 14.7 17.5 7
12.8 15.2 15.8 14.4 8
14.1 16.5 16.2 16.7 9
14.7 15.9 15.7 16.5 10 17.0 17.4 17.1 17.7 11 15.8 18.9 18.2 18.7 12 14.7 17.4 18.8 17.6 13 14.8 17.6 17.0 17.6 14 15.5 17.8 18.0 17.5 15 15.0 16.9 17.6 17.4 16 15.3 17.6 17.6 20.5 17 14.8 17.6 18.0 17.6 18 16.5 17.7 17.9 19.1 19 16.1 17.2 18.2 18.9 20 15.2 17.8 18.3 18.4 21 12.8 14.7 13.8 16.3 22 14.7 16.4 16.6 17.6 23 14.1 16.7 16.2 18.2 24 15.3 17.0 16.5 17.0 25 11.9 13.4 13.4 14.0 26 14.7 15.6 15.7 16.1 27 15.2 17.0 17.4 17.5 28 12.7 14.3 13.9 15.3 29 12.5 14.8 14.4 15.7 30 14.3 16.1 15.3 16.1 31 15.7 16.8 16.6 17.1 32 15.1 16.8 16.5 16.5 33 14.8 17.9 17.8 17.4 34 15.7 17.4 17.5 18.0 35 13.8 16.2 16.6 16.7 36 15.0 16.6 18.2 16.9 37 15.1 16.6 15.5 16.9 38 15.7 18.5 17.5 18.9 39 16.7 16.9 17.8 17.3 40 13.7 15.0 15.1 16.0
) '
e
~1 TABLE 5: GItOSS BETA ANALYSIS RESULTS OF DRINKING WATER SAMPLES (pCi/ liter)
Location LW-40 Location BW-15 Month (Indicator)
(Control)
JAN 5.6 5.1 FEB 4.8 5.2 MAR 6.4 6.0 APR 3.7 3.5 MAY*
5.9 6.1 JUN 5.3 4.8 JUL 5.3 5.5 AUG 4.6 4.5 SEP 7.4 OCT 4.6 5.4 NOV 3.7 4.5 DLC 5.5 4.6 Range of Preoperational Values:
4.1 - 10.0 pCi/ liter Operational Results began with initial criticality on 5/22/85 Results not available, see Section IV, " Monitoring Program Deviations"
l TABLE 6: GAMMA ANALYSIS RESULTS OF BROADLEAF 4
VEGETATION SAMPLES (pC1/gm - w t weight)
Location:
A-1 Q-2 R-1 S - 4(Control)
Nuclide Month Be-7 MAY 0.511 0.377 0.466 0.325 JUN 0.641 0.970 1.64 JUL 0.319 0.355 0.351 AUG 0.434 0.195 0.416 SEP 0.522 1.07 OCT 0.488 0.491 NOV 0.439 K-40 MAY 4.35 1.75 4.96 5.94 JUN 4.60 4.40 5.64 JUL 3.63 2.42 2.19 3.79 AUG 2.69 2.34 5.55 SEP 3.69 4.84 OCT 3.28 3.91 NOV 3.01 Cn-137 MAY 0.0270 0.0128 JUN JUL AUG SEP OCT NOV 9
a I
TABLE 7: CAMMA ANALYSIS RESULTS OF SHORELINE SEDIMENT SAMPLES (pCi/ gram-dry weight)
Indicator Location (Date)
Be-7 K-40 Cs-137 Ra-226 Th-228 DC (5/21)
<0.4 11.9 0.222 1.97 1.36 NR (6/28)
<0.4 15.6 0.711 3.34 1.37 DC (10/15) 0.541 12.0 0.0504 3.14 1.70 NR (11/18)
<0.6 14.4 0.264 2.07 1.37 Indicator Location 0.541 13.5 0.31 2.6 1.5 Average Control Location
<0.3 10.4 0.171 2.65 1.65 JRR (6/28)
Preoperational 0.511 11.2 0.42 2.2 1.3 Average 9
TABIE 8: GAMla ANALYSIS RESULTS OF AQUATIC VEGETATION SAMPLES (pCi/ gram - wet weight)
Sample Type (Date)
Be-7 K-40 Co Cs-137 Th-228 Algae (5/21/85)*
1.68 3.56 0.0133 0.0587
.f Rooted Aquatic Plants (5/21/85)* 0.234 3.29 0.0495 0.154 Rooted Aquatic Plants (10/15/85) 0.541 2.36 0.047 0.0144 0.0536 Since initial criticality was on 5/22/85 and detectable effluents were not released until June, these samples are considered preoperational.
j _
r 3
TABLE 9 RESULTS OF 1985 LAND USE SURVEY DIRECTION DISTANCE (MILES) TO NEAREST SECTOR FROM PLANT RESIDENCE MILK ANIMAL GARDEN A
N 1.3
, None 1.3 B
NNE 3.0*
None 3.0 C
NE 1.7 None*
1.7 D
ENE 1.9 2.3*'
^
2.3*
E E
1.7 None*
1.7 F
ESE 1.5 1.3 1.5 G
SE 1.4 None 1.4 H
SSE 2.9 None 3.0*
J S
- 3. 3.
None 3.3 K
SSW 3.9*
None 4.0*
L SW 2.1 None 2.5 M
WSW 1.8 None 3.1*
N W
2.1*
None 2.7 P
WNW 2.9*
2.9 3.0*
Q NW l.4*
3.4 1.4*
R NNW 2.0**
None 2.2 3
Indicates Change from 1984 Data.
- Part-time residence. -.
TABLE 10 RESULTS OF EPA INTERLABORATORY COMPARISON TESTS 3
SAMPLE SAMPLE EPA TELEDYNE NORMALIZED NUMBER DATE TYPE NUCLIDE RESULTS (ilo)
RESULTS (ilo)
DEVIATION 363 01/18/85 Water Gr. Beta 15 1 5 15 1 1 0.10 365 01/25/85 Food I-131 35 + 6 26 + 2
-2.50 Cs-137 29 I 5 31 7 3 0.69 K
1382 1 120 1393 1 32 0.16 366 02/08/85 Water Co-60 20 + 5 19 + 2
-0.50 Zn-65 55 I 5 57 7 2 0.70 Cs-134 35 I 5 37 7 4 0.80
~
Cs-137 25 + 5 31[2 2.00 367 02/02/85 Water H-3 3796 + 366 3933 1 58 0.60 368 03/01/85 Milk I-131 9.0 1 0.9 8+1
-1.90 370 04/05/85 Water I-131 7.510.8 6.7 + 0.6
-1.80 372 04/12/85 Water H-3 3559 1 364 3367 + 321
-0.90 374 03/29/85 Air Gr. Beta 36 + 5 37 + 3 0.23
~
Filter Cs-137 6t5 6+0 0.00 375 05/24/85 Water Gr. Beta 11 + 5 12.7 1 0.6 0.58 376 04/19/85 Water Gr. Beta 72 + 5 92 + 3 7.04 Co-60 15 I 5 20 7 2 1.73 Cs-134 15 7 5 15 7 1
-0.11 Cs-137.
12[5 16[3 1.50 378 06/14/85 Water H-3 2416 + 351 2367 + 115
-0.24 379 06/07/85 Water Co-60 14 + 5 16 + 1 0.58 Zn-65 47 I 5 48 I 3 0.46 Ru-106 62 7 5 54 I 3
-2.88 Cs-134 35 I 5 33 7 4
-0.69 Cs-137 20[5 23[2 1.15 381 07/19/85 Water Gr. Seta 8+5 4.3 + 0.6
-1.27 383 06/28/85 Milk I-131 11 + 6 9+1
-0.58 Cs-137 11 I 5 11 + 3 0.00 K
1525 + 76 1540 1 35 0.34 385 08/16/85 Water H-3 4480 + 448 4433 1 153
-0.18 386 08/09/85 Water I-131 33 1 6 37 1 2 1.05.
,e w
e TABTE 10 RESULTS OF EPA INTERLABORATORY COMPARISON TESTS (Con't)
SAMPLE SAMPLE EPA TELEDYNE NORMALIZED i
NUMBER DATE TYPE NUCLIDE RESULTS (+1o)
RESULTS (+1 a)
DEVIATION 388 07/26/85 Food I-131 35 + 6
~31 I 1 0.69 37 + 2 0.67 Cs-137 29 I 5
~
K 1514 + 76 1633 + 51 2.72 390 09/20/85 Water Gr. Beta 8+5 4+0
-1.38 391 08/30/85 Air Gr. Beta 44 + 5 43 + 3
-0.34 Filter - Cs-137 8+5 10[1 0.69
~
392 10/11/85 Water H-3 1974 + 345 2133 + 208 0.80 394 10/04/85 Water Co-60 20 + 5
- 18 + 3
-0.81 Zn-65 19 I 5 25 I 3 2.19 Cs-134 20 I 5 18 I 3
-0.58 Cs-137 20[5 22[1 0.81 l
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Figure 7:
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1985 GROSS BETA AIR CONCENTRATIONS (OPERATIONAL) 0.07
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-- 1
Figure 9 I
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ug E
x C
l N
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8 g
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- a 8
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- e 9
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A l
N lo O
8 r l
I t
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o 1
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8
=
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R 1
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TA I
I RA V
I 0891 M
g 0
5 0
5 0
2 1
1 a
0 1
1 1
2 1
^6 a4 j o 20ND ghbd e
,ge l
.se I
Figure 11 I
l 1985 OPERATIONAL TLD RESULTS COMPARISON TO PREOPERATIONAL 0.3 0.28 Preoperational Upper Range 0.26
/\\
O.24 I
/
0.22 01 1
g 0.16 T
\\
N 0.14 i
O
^
0.12 Preoperational Lower j
0.1 Range 0.08 0.06 O.04 0.02 0
..i..i..i..i..i..i..i..i..i..i..i..
1 4
7 10 13 18 19 22 25 28 31 34 37 40 P
LOCATION I
O OPER.(2, 3, 4 QTRs)
+
PREOP AVERAGE
Figure 12 j
DRINKING WATER Gh. BETA ANALYSIS RESULTS 15 14 13 12 1
11 10
~
g 9
g mb 8
N I
{
p<
3 7
0 A
8 I
l 3
W l
i 1
5
-E
~
J 1
4 Y
g 3
g N
b 2
e la K
8 b
1 h.
l i
O iiisiiiisiiiiisi : :iiiiiiiiiiiiiiiiiiiiiiiiissiiiiiiii,iiiii 1980 1981 1982 l
1983 l
1984 l
1985 l
O INDICATOR
+
CONTROL 1
\\
I
?
l l
APPENDICES 1985 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT WOLP CREEK GENERATING STATION Prepared by TELEDYNE ISOTOPES 50 Van Buren Avenue Westwood, New Jersey 1
Prepared for Kansas Gas and Electric Company I
l i
l
.. - i
T_ABLE OF CONTENTS: APPENDICES 9
Page Appendix A:
Summary tables in format of NRC Radiological Assessment Branch Technical Position, Revision 1, November 1979........................................
A-1 Appendix B:
Individual sample results Air Particulate and Charcoal Filters............
A-7 Composite Air Particulate Filters...............
A-17 Thermoluminescent Dosimeters....................
A-22 Drinking Water.................................. A-26 Ground Water.......................*.............
A-32 Surface Water................................... A-37 Fish............................................
A-45 Food and Garden Crops...........................
A-48 Irrigated Crops.................................
A-54 Milk............................................ A-55 Shoreline Sediments.............................
A-69 Aquatic Vegetation.............................. A-72 A-ii l
1
o
>0 APPENDIX A:
SUMMARY
TABLES
~
e
?
d i
/
/ s*
Y
(NVIRONM[NIAt RADIOLOGl CAL MONITORING PROGRAM
SUMMARY
Name of Facility __ Kansas Gas and Electric Docket No.
SIN 50-482 Location of Facility Cof fey County, Kansas Reporting Period Annual 1985 (Count y,5t ate)
An alys i5 and Lower Ltait Number of Medium or Pathway Total Number of All Indicator locations Location with Highest Annual Mean Control Locations Nonroutine Sampled of Analysis Detection
- Mean ( f )
Name
- *Me an ( f ) * *Me an ( f )
R.epor t ed (Unit of Measurement) Performed (LLD)
- *R ange Distance and Directions ** Range
- *R ange Measurements **
Station No. 40 Air Gross (260) 3 27(208/208) 37 2.1 miles NNW 29(52/52) 28/(52/52)
O Partiquiate Bet a (8.5-71)
(16-71)
(16-65)
(X10-J pCl/
3, e,
Cu M.)
Gamma (20)
Be-7 1
79(16/16) 32 2.8 miles WNW 86(4/4) 84(4/4) 0 (40-106)
(68-106)
(69-93)
K-40 24 11(3/16) 32 2.8 miles WNW 20(1/4) 6.4(1/4) 0 (5.6-20)
Stations 39 and 40 External TLD Radiation Quarterly (320) 0.05 0.18(304/304) 11 1.6 miles E 4.20(8/8) 0.18(16/16) 0 (mR/ day)
(0.13-0.23)
(0.17-0.21) (0.15-0.20)
Nominal Lower Limit of Detection (LLD)
Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
Y
ENVIRONMENTAL RADIOLOGICAL MONiiURiNG P'usn.vt SwtMARY
.5,.
Kansas Gas and Electric Docket No.
SIN'su-482 Name of facility Location of f sdlity Cof fey County, Kansas 4 Heporting feriod Annual 1985 i
(County,5 tate) 1 o
4 Analysis and Lower Limit Number of g -
'Medits or Pathway Total Number of All I Adicator locations location with_ Highest Annual Mean Control Locations Nonroutine Sampled of Analysis Detection
- Me 3n ( f)
Name
- Mean (f) *%an (f)
Reported (Unit of Measurement) Performed (LLD)
- Range Distance and Directions ** Range
- *R ange Measurements **
' Water 1-131 (24) 0.5
-(0/12)
N/A N/A
-(0/12)
-0 Drinking
' - )
(pCi/fl
- p i
~<
Gross (23) 2 5.0(11/11)
BW-15 3.9 miles SW 5.2(12/12) 5.2(12/12) 0 m
Beta (3.7-6.4)
(3.5-7.4)
(3.5-7.4) c Gamma (24) 1-
-(0/12)
N/A N/A
-(0/12) 0 t
o Y'
, ' Ititlum (8) 1000
-(0/4)
N/A N/A
-(0/4) 0 s
$2 Water.
B-12 Grmed (pCi/A) 1-131 (16) 0.5
-(0/12)
N/A N/A
-(()/4 )
0 60.
-(0/12)
B-12 2.2 miles NE 12(1/4) 72(1/4) 0 Tritita (16) 1000
-(0/12)
N/A N/A
-(0/4) 0 Mush Water. Surf ace Gamma (24)
-(0/12)
N/A N/A
-(0/12) 0 (pCi/t)
Tritita (8) 1000 1600(1/4)
DC 0.6 miles WNW 1600(1/4)
-(0/4) 0 3
Nominal Lower Limit of Detection (LLD)
Mean and range based upon detectable measurements only. fraction of detectable measurements at specified locat 6ns is indicated in parentheses (f)
W SS*
vs.
ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM $lMMARY Name of Facility kansas Gas and Electric Docket No.
STN 50-482 Location of facility Cof fey County, Kansas Reporting Period Annual 1985 (County,5 tate)
Analysis and Lower Limit Number of Medium or Pathway Total Number of All Indicator locations Location with Highest Annual Mean Control Locations Nonroutine Sampled of Analysis Detection
- Me an ( f)
Name
- *Me an ( f) * *Me an ( f )
keported (Unit of Measurement) Performed (LLO)
- *R ange Olstance' and Directions ** Range
- *R ange Meas ur ement s*
- J. Henmond keservoir Fish Gamma (10)
(pC1/g)
K-40 0.5 3.2(8/8)
JRR 4 miles W 3.6(2/2) 3.6(2/2) 0 (wet weight)
(2.7-3.5)
(3.5-3.1)
(3.5-3.1)
Food and Garden Crops.
Gamma (19) 5-4 Be-7 0.1 0.48(11/12) 5-4 15 miles WNW 0.68(7/7) 0.68(7/1)
O to (ptt/g wet (0.20-0.97)
(0. 3 3-1. 6 )
(0.33-1.6) weight)
K-40 0.5 3.4(12/12) 5-4 15 miles WNW 4.7(7/1) 4.7(7/7) 0 (1.8-5.0)
(3.0-5.9)
(3.0-5.9)
Cs-137 0.02 0.020(2/12)
A-1 1.3 miles N 0.027(1/6)
-(0/7) 0 (0.013-0.027)
Nominal Lower Limit of Detection (LLO)
- . Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
. tv.
[NVIPONMENTAL RADIOLOGICAL MON 110 RING PROGRAM
SUMMARY
Name of facility Kansas Gas and Electric Dockyt No.
STN 50-482 Location of facility Cof fey County, Kansas Reporting Period Annual 1985 (County. State)
Analysis and Lower Limit Nisaber of Medium or Pathway Total Number of All Indicator Locations Location with Highest Annual Mean Control Locations honroutine Sampled of Analysis Detection
- Me an ( f )
Name
- Me an ( f) **Me an ( f)
Reported
'(Unit of Measurement) _ Performed (LLD)
- Range Distance and Directions ** Range
- *R ange Measurements **
Irrigated Crops Gamma (1)
NONE (pCi/g K-40 0.5 2.6(1/l)
NR-01 9.2 miles S 2.6(1/l)
O wet weight)
?e Nominal Lower Limit of Detection (LLD)
- Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)
O e
W-
ENVIR0000 ENTAL RADIOLOGICAL MONITORING PROGRAM
SUMMARY
Name of Facility Kansas Gas and Electric Docket No.
SIN 50-482 Location of Facility Cof fey County, Kansas Reporting Period Annual 1985 (County,5t ate)
P Analysis and Lower Limit Number of Medium or Pathway Total Ntaber of All Indicator locations Location with Highest Annual Mean Control Locations honroutine Sampled of Analysis Detect ion
" Mean (f)
Name
- *Me an ( f) * *Me an ( f)
Reported (Unit of Measurement) Performed (LLD)
- *R ange Distance and Direct tons ** Range
- *R ange Measurements **
St at ton S-3 Milk I-131(68) 0.2
-(0/48)
N/A N/A
-(0/20) 0 (pCl/ liter)
Ganna (68) 7 K-40 100 1345(48/48)
P-2 2.9 miles WNW 1614(20/20) 1312(20/20) 0 vi (779-1930)
(I320-1930)
(1140-1760)
Cs-137 5
7.2(2/48 F-1 1.3 miles ESE 7.3(1/20)
-(0/20) 0 (7.2-7.3 Shoreline Sediment (PCl/9 (dry weight)
Ganna(7)
J. Redmond Neservoir Se-7 0.4 0.54(1/4)
DC 0.6 miles WNt 0.54(1/2)
-(0/1) 0 K-40 0.5 13.5(4/4)
NR 6.5 miles S 15.0(2/2) 10.4(1/1) 0 (11.9-15.6)
(14.4-15.6)
Cs-137 0.06 0.31(4/4)
NR 6.5 miles 5 0.49(2/2) 0.17(1/l) 0 i
(0.050-0.71)
(0.26-0.71)
Ra-226 0.5 2.6(4/4)
NR 6.5 miles 5 2.7(2/2) 2.7(1/1) 0 (2.0-3.3)
(2.1-3.3)
Th-228 0.04 1.5(4/4)
JHR 4 MILES W l.7(1/1) 1.7(1/1) 0 (1.4-1.1)
Nominal Lower Limit of Detection (LLD)
- -Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (t)
ENVIRONMENTAL RAD 10 LOGICAL MUNI10R!NG PROGRAM
SUMMARY
Name of facility Kansas Gas and Electric Docket No.
STN 50-482 Location of Facility Cof fey County, Kansas Reporting Period Annual 1985 (County,St ate)
Analysis and Lower Limit Number of Medium or Pathway Total Number of All Indicator Locations Location with Highest Annual Mean Control Locations Nonroutine Sampled of Analysis Detectton
- Mean (f)
Name
- Me an ( f) **Me an ( f)
Psepdrted junitofMeasurement) Performed (LLD)
- R ange Distance and Directions ** Range
- *R ange Measurements **
Vegetatton, Gamma (3)
NONE Aquatic Be-7 0.1 0.82(3/3)
DC 0.6' miles WNW 0.82(3/3) 0 (pCl/g wet (0.23-1,1)
(0.23-1.7) g weight)
K-40 0.5 3.1(3/3)
DC 0.6 alles WNW 3.l(3/3) 0 (2.4-3.6)
(2.4-3.6)
Co-58 0.02 0.047(1/3)
DC 0.6 miles WNW 0.047(1/3) 0 Cs-137 0.02 0.025(3/3)
DC 0.6 miles WNW 0.025(3/3) 0 (0.013-0.049)
(0.013-0.049)
Th-228 0.04 0.089(3/3)
DC 0.6 miles WNW 0.089(3/3) 0 (0.054-0.15)
(0.054-0.15)
Nominal Lower Limit of Detection (LLD)
Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is ird!:sted in parentheses (f) 4
APPENDIX B: DATA TABLES
{
l
~ - -. -
~
,g.
1 KAN545 GAS AND ELECTFIC CG P O 8 11)( 208 E X PH50Rr P AT HW A v - i f r t>Lp Nt Alh P AR T ILUL Al f L CH ARL( A L F ILIE RS Si & II Cf 4 NUMnip J2 COLL. TIME AP F ILieu M 10-CCUf 4 T CH E CO AL F IL T ER 51ARi 5IOP GRf)SS RETA TIPE I -1 31 UATE DATE VEL LME UhllS IPCl/Cb. 4 8
.CAff 11ME IPCl/CU. M i 01/02 01/08 2.34E 08 00 29 + -0. 5 E -0 2 01/11 L. T.
4.
E-0?
01/08 01/15 2.84E 08 CC 2 5 + -0. 4 E-02 01 /19 L.T.
2.
E-02 01/15 01/22 2.82E 08 CC 2.6 +-0.4 E-02 01/24 L.T.
4.
E-05 01/22 01/29 2.85E CE CC 1 7
+-0. 3 E-02 ts 2 /0 9 L.T.
3.
E-07 01/22 01/29 3.0CE 08 CC (a) 02/01 L.T.
3.
E-02 01/29 02/05 2.85E 08 CL 2.6
+-0.4 E -0 2 02/08 L. T.
4 E-0?
02/05 02/12 2.82E 08 CC 6.5 +-0. 5 E-02 ( b )
02/16 L.T.
2.
E-02 02/12 02/19 2.87E 08 CL
- 3. 4 +- 0. 4 r.0 2 02/21 L.T.
4 E-02 02/19 02/26 2.93E OF CC 2.2
+-0.3 E-02 02/2R I.T.
2.
E-02 02/26 03/05 2.910 C8 CC 2.4
+-0. 4 E-02 03/08 L.T.
3.
?-0?
03/05 03/12 2.87E 08 CC 2.0 +HD.J E-02 03/16 L. T.
3.
E-02 03/12 03/19 2.88E 08 CC 2.0 +-0.3 E-02 03/21 L.T.
4.
E- 02 03/19 03/26 2.8%E 08 00
- 2. 2 + -0. 3 E -0 2 03/28 L. T.
4
[-02 03/Ze 04/02 2.87E C8 CC 1.5
+-0.J E-02 04/05 L.T.
4.
E-02 7
04/02 04/Di 2.96E C8 CC 1.8
+-0. 3 E-0 2 04/13 L.T.
,3.
E-0)
-4 04/09 04/16 2.82E 08 EC 2.8 +-0.4 E-02 C 4 /18 L.T.
3.
E- 0 2 04/16 04/24 3.14E 08 CC 2.1
+-0. 3 E-C2 04/26 L.T.
2.
E- 0 2 04/24 04/33 2.360 08 CC
- 2. 3
+-0. 4 E -02 05/02 L.T.
3.
- 2. 6
+-0. 3 F-02 05/09 L.T.
4.
E-02 04/30 05/07 2.77E C8 CC (a) 05/13 L.T.
3.
T-02 05/07 05/14 2.86E 08 CC 2.5 +-0.3 E-02 05/te L.T.
4.
E-02 05/14 05/21 2.75E 08 CC 1.9 + -0. 5 E- 02 05/23 L.T.
4.
E- 02 05/21 05/28 2.7 7E 08 CC 3.1
+-n.4 E-02 05/31 L.T.
3.
E-02 05/28 06/04 2.73E CE CC 2.5
+-0.4 E-02 06/0e L.T.
4.
E-07 06/04 06/11
- 2. 5 +-0. 3 E-0 2 06/13 L.f.
4
?-02 06/11 06/18 2.70E 08 CC 2.1 + -0. 3 E -02 C6/2C L.T.
4.
E- 0 2 06/18 06/25 2.F3E 08 CC 1.9 + -0. 3 E-02 06/28 L.I.
3.
E-0 2 06/25 07/02 2.83E 08 CC 2.1
+-0. 3 5 0 2 OT/05 L. T.
4 E-02 07/02 07/C9 2.80E 08 CC 2.1
+-0. 3 E-0 2 07/f3 L.T.
3.
E-02 07/09 07/16 2.6PE 08 CC 2.6 +-0.4 E-02 07/20 L.T.
3 F- 0 2 07/le 07/23 2.85E 08 CC 3.3
+-0.4 E-02 07/2e L.T.
3.
E- 0 2 07/23 0 7/30. 2.94E 08 CC
- 2. F. +- 0. 3 E -02 08/01 L.T.
3.
E-0 2 07/ 3C 08 /06 2.82F 08 CC 1.8 + - 0. 3 E -0 2 08 /0 P L. T.
3.
E-02 08/06 08/13 2.59E CR CC 3.6 +-0. 4 E-0 2 08/15 L.T.
5.
E-02 08/13 08/20 2.63E DE CC 2.3 +- 0. 4 E-02 08/22
L. T.
3.
E-0?
- 2. 7 e-6. 3 E-01 08/29 l'. T. 4 E- 0 2 08/2 7 C9/03
- 2. 7 8E C8 CC 3.6 +-0.4 E-02 09/0e L.f.
2.
E-02 (c)
(b) a) Duplicate analysis Counted twice to confirm the hi her than usual activity.
i t
(c) TI 36852 was light in color and showed very little deposition of particulate matter.
n ANSAS C AS AP40 E LEC Tkic C C P G tlux 203 I UO5URL Pales. Av - AIR ELEM Alk P4Hi t CUL 4T L L CHak(L4L llLitFS S T A i lt,14 PeUMHfA C2 COLL. T IME SP F IL I Lk M10-COHf.i (H ANC0 AL FILIFE STANT STOP Gk025 eE T A TIPE l-131 DATE DATE VOLUMf ukITS (PCl/CU. M i CATE T IME 19C 1/00. M i 08/21 CS/03 2.Far 08 CL (a) 05/0e L.T.
2.
E-02 09/03 09/10 2.5 7t Od CC 2.6 +-0. 3 E-0 2 05/13 L.T.
3.
E-02 09/10 09/17 2.62E C8 CC 3.1
+-0.', E-02 CS /15 L.T.
5.
E- 0 7 09/17 09/24 2.FCE 08 CC
- 2. 5 * -0. 4 E-02 09/26 L.I.
3.
E-02 05/24 IJ/01 2.bOE 08 CC 2.2 e-0. 3 E-02 10/03 L.T.
3.
E-02 10/01 10/08 2.7tt CH CC 2.2
- -0. 3 E-0 2 10/10 L.T.
4.
E-0?
10/06 10/15 2.sOf 06 CC 1.9 + d). 3 E-0 2 10/18 L.I.
3.
E-0?
10/15 10/22 3.0 7E 08 CC 2.3 * -0. 3 E-02 10/24 L.I.
2.
E- 0 2 10/22 10/29 3.0*E Os CC 2.4
+-0. 3 E -02 11/02 L.I.
3.
E- 0 2 10/25 11/05. 3.0dF 06 CC 3.1 e -0. 3 E -0 2 11/0S L.T.
2.
E-02 11/05 11/12 3.ItE 08 CC 1.8 +-0. 3 E-0 2 11/17 L.I.
3.
E-02 11/12 11/19 3.OsE 08 CC
- 2. 5 +-0. 3 E-0 2 11/21 L.I.
4.
E-02 11/19 11/26 3.12f Od LC
- 4. 7
+-0. 4 E-02 12/02 L.T.
4.
E-0?
E II/2e 12/03 3.let Cb CC 5.9 +-0.5 E-02 12/05 L.T.
4.
E- 0 2 12/03 12/10 3.29E 0a CC 6.0 * -0. 4 E -0 2 12/13 L. I.
2.
E-02.
12/10 12/17 3.uSE 08 CL
.5
+-0.4 E-02 12/19 L.T.
3.
E-02 12/17 12/24 3.09E 08 (C w.4 e-0.4 E-02 12/2F L.T.
3.
E-02 12/24 12/31 3.13 L Of LC 1.d
- -0.J E-02 01/03 L.T.
3.
E- 02 I
(
(
ed.c i. ?,
(a) Duplicate analysis 9
(>Q *
+
K n545 G45 4NO ELF (TFit. CL P 0 HCX 201 f 4P050kr P&iete Av - 4 th 0(k A0 Alk P Ak i lt,OL 41 F 6 Cet AF Cb4L F IL IFhs SiallGN AUMBFF 03 LilL L. TIHF AP tIties MIC-Couti ot aP CU AL FILIEP STApi SidP oHOSS 8t ia TIPL I-1 31 DAIE Dal E VCLOMF tskII5 1908/C0. M i CATE il%r (PCl/CU. H I 01/02 01/03 '2.51E CH FC 3.2 +-0.S E-02 01/11 1.1.
4 E-32 01/06 01/45 3.032 08 CC 3.0 + -0. 4 F-32 01/19 L.I.
2.
E-02 01/15 01/22 3.02E 08 Lc 2.5
+-0. 4 E-02 08/24 L.T.
4 E-05 01/22 01/29 3.00E 08 CC
- 2. 2 +-0. 3 E-0 2 02/01 L.T.
3.
E-02 01/25 02/05 3.05t C8 CC 3.2 + -0. 4 F -0 2 02/0E L.T.
3.
E- 0 2 02/05 02/12 3.01E.Cu CC F.C e-0. 5 E-02 ( b) 02/16 L.I.
2.
E- 0 2 02/12 02/19 3.125 08 CC 3.2
+-0.4 5-02 02/21 L.T.
4.
E-02 02/19 02/26 3.08E Ob (C 2.0
+-0. 3 E-02 02/28 L.T.
2.
E-0?
02/2e 03/J5 3.0!F 08 CC
- 2. 5 +- 0. 3 E-02 03/04 L.T.
3.
F-02 03/05 03/12 2.92E C8 CC
- 1. 7 +-0. 3 E -02 O!/I6 L.I.
3.
E- 0 ?
03/12 03/19 3.03E Cb CC
- 1. 7
+-0. 3 E -02 0?/21 L.I.
4.
E-02 03/15 03/26 2.99F 03 CC
- 2. 3 + -0. 3 E -0 2
( ?/28 L.I.
4.
E-0?
03/26 04/u2 2.92E 08 CC 1.9
+-0. 3 E-02 04/05 L.I.
4.
E-02 04/02 04/09 3.0 7i Od CC
- 1. 7 +-0. 3 F -0 2 04/13 t.1.
3.
F-o2 Y
04/02 04/39 3.01E G8 CC 04/15 L.T.
5.
E-02 04/09 04/16 3.0dE C8 CC 2.3
.3 E-02 04/18 L.T.
3.
E-02 04/1e 04 /24 3.5 3E 08, 00
- 1. 7. + -0. 3, E -0 2 04/26 L.T.
2.
E-O?
04/24 04/30 2.78E 08_,0C
- 1. F +-0. 3 L -0 2 0S/02 L.T.
3.
E-02 04/30 05/0F 3.17F Os CC
- 2. 2 + -0. 3 E -0 2 05/09 L.T.
4.
E-02 05/07 05/14 3.27E CH CC 2.4
+-0. 3 E-02 05/16 L.T.
3.
E-02 05/14 05/21 3.25E DE CC 1.9
+-0 3 F-02 05/23 L.T.
4 E-02 l05/21 05/28 3.1 EL C8 CC
- 2. 2
+-0. 3 E-02 05/31 L.T.
3.
E- 02 05/28 06/04 3.18E Ce CC 1.8 + -0. 3 E-02 06/De L.T.
4 E-02 06/04 06/11 3.32F Os CC 1.9 + -0. 3 E -0 2 06/13 L.I.
4.,
E-02 06/11 06/18 3.46E 08 -CC 1.6
+-0. 3 E-02 06/10 L.T.
- 3. ' E-02 06/16 06/25 3.17E 08 CC
- 1. 8
+-1. 3 E-0 2 06/2R L.T.
3.
F n2 06/25 07/02 3.33E C8 CC 1.8
+-0. 3 E-02 07/05 L '. T.
3.
E- 0 7 07/02 GT/09 3.26E C8 (C 2.9 +-0. 3 E-02 07/13 L.T.
1.
F-02 07/05 0T/16 2.9 8r 0h CC
- 2. 6 + *D. 3 E -0 2 07/20 L.T.
3.
E-02 0{/96 07/23 3.05E 08 CC 1.9
+-0. 3 E-02 07/26 L.T.
2.
E-0?
07/23 07/30 3.34F 08 CC 2.0 +-0. 3 F -0 2 08/01 L.T.
3.
F-0?
07/30 08/06 3.11E C8 CC 1.5
+-0. 3 E-0 2 08/08 t.T.
3.
E- 0 2 08/06 08/13 2.84E C8 CC 2.2
+-0. 3 0-02 08/15 L.f.
4.
E-02 08/13 08/20 2.93F 08 CC 2.1 + -0. 3 E -0 2 08/22 L.T.
3.
E-02 08/20 08/2F 2.92F 08 (C 1.9
+-0. 3 E-02 08/29 L.T.
4.
E-0?
08/27 05/03 2.deE 08 CC 1.8 +-0. 3 E -02 09/06 L.T.
2.
F- 0 2 09/02 09/10 2.87L C8 CC
- 1. 3
+-0 3 E-02 09/1?
L.T.
2.
E- 0 2 (a) Duplicate analysis (b) Counted twice to confirm the higher than usual activity.
t-A Ah545 Ga5 AND [L ECIF IC L6 P u 604 20,4 EAPOSURE PATHmAV - A l6 80H hi Alb PapistutAIE & Cua6CCAL fititus hiAllO4 NUMBFW 03 Cott. TI1E AP FitiEH MIC-COUNT CH A900 AL F ILI ER
$IART SIOP GEus$ o814 il4F I -1 31 0 ATE diTE vcLuPE Uk815 GPLl/CU. M 1 CATE TIME IPCI/LU. M i JS/10 09/17 2.8 FE 08 (C 2.6 e-0.* E-02 09/19 L.I.
4.
E-02 09/l1 09/24 3.01E 06 CC
- 1. 7 e-0. 3 E-02 09/26 L '. i.
3.
E-02 OS/24 IC/01 3.05E 08 (C 1.6 e-0. 3 E -0 2 1u/03 L.I.
3.
F-02 10/01 10/06 2.9 7E C8 CC 1.3
+-0.3 E-G2 IC/1C L.T.
4.
E- 0 ?
IG/0m 10/15 2.SSE C8 LC 2.3 +-0. 3 E-02 10/18 L.T.
2.
E- 0 2 10/15 10/22 3.25E 08 CC-2.1 * -0. 3 F -0 2 10/24 L. T.
2.-
F-02 10/22 10/29 3.llE 06 CC 2.S +-0. 3 E-0 2 31/02 L.T.
3.
E-02 1u/ 25 11/05 3.tet 06 CC 3.0 + 3. 3 E-02 11/09 L.I.
2.
E-02 11/05 11/12
- 3. lee Ce CC 1.4 +-0. 2 E-02 11/1F, L T 3.
E- 0 ?
11/12 11/19 3.0*E C8 CC 1.4 +-0.2 E-02 11/21 L.7T 4.
f-02 11/12 11/19 3.04E 08 CC (a) 11/72' L
- i.'
2.
L-02 p
11/19 11/26 2.92E 08 LC 3.6 +-0.4 E-02 17/Of L '. I. 4 F-0?
!!/2e 12/03 2.8tE 05 CC 5.4. e- 0. 5 E-02 12/05 t.T.
4.
E-02 1
+-0. 5 E-02 12/12 L.T.
2.
~ E- 0 2 C3 '
12/10 12/1/
- 2. doe Cb (C 4.5 e-C.4 E-02 12/19 L.T.
3.
E-02 12/17 12/24 2.79E 08 CC 4.5 +-0.' E-02 12/27 L.T.
3.
t-02 12/24 12/3!
2.93E 06 CL 2.0 e-0. 3 E-62 01/03 L.T.
3.
E-02 (a) Duplicate asialysis w
t
(> Q *
-+w e
KAN545 GAS %NO CLrggplC LG i
P C HCM 204 l
EAPOSURF P4THh4Y - AlketHht l
Alp PARIICULAIE & CHANCt4At FILIERS SinflEN huMoF k 32 LOLL. TIME AP tit 1EE MIC-CLUNT CH/PCOAL FILTEP START S IU P GdC55 bE I4 ilmL I-131 l
04TF 04TE VOL UM E ukIIS IPCE/Co. 1 1 C41c ilME (PCl/CU. M i 01/02 01/08 2.4eE C8 LC 3.0
+-J.4 E-02 01/11 L.I.
4 F-02 01/08 01/15 2.93L 08 CC 2.H
+-1.4 E-02 01/15 L.T.
2.
F- 0 2 01/15 Pl/22 2.90E 08 CC
- 2. 7 + -0. 4 E-02 01/24 1.1.
4.
F-0 2 01/22 d1/29 2.90E 08 CL 1.9
+-0. 3 E-0 2 02/01 L.I.
3.
E-0?
01/25 02/05 3.Olf Od CC 2.1
+-0. 3 E-0 2 02/0E L.I.
3.
E-0?
C2/05 02/12 2.52E Oe CC 4.8
+-0.4 E-02 ( b)
J2/16 L.T.
2.
2-02 02/12 02/19 2.87E C8 (C 2.9 +-0.4 E-02 02/21 L.I.
4.
E-02 02/1% 02/2 6 2.9FE 08 (C 2.1 + - 0. 3 E - 02 02/28 L.T.
2.
E-0 2 02/2e 03/05 3.0 5F 08 CC
- 2. 2 + d). 3 F -0 2 O !/0 P L.T.
3.
E-02 03/05 03/12 2.95E 08 CL
- 2. 7
+-0. 4 E-02 03/16 L.T.
3.
E-02 03/05 03/12 2.95E 08 CC (a)
.83/18 L.T.
4.
E-02 03/12 03/19 2.96E Cd LC 1.9 +-0. 3 E-0 2 03/2I L.T.
4.
E- 02 03/19 03/26 2.93E 08 CC
- 2. 3 + -0. 3 E-02 03/2d L.T.
4.
E- 0 2 03/26 04/02 2.99E OR LC 2.0 + wn. 3 E -0 2 04/01 L. I.
4.
L-02 p
1 04/02 04/09 3.02E 08 CC 2.2 +-0. 3 E-0 2 04/13 L.I.
3.
E-02 04/09 04/16 3.01E 08 CC 2.2
+-0. 3 E-d 2 34/18 L.T.
3.
r-05 04/16'04/24 3.250 C8 CC
- 2. ? +- C. 3 E-02 04/2e L.T.
2.
E- 0 7 04/24 04/30 2.64C 08 (C
- 2. 3 +- 0. 4 E-02 05/02 L.T.
3.
E- 0 2 04/30 05/0F 3.00E 08 CC
- 2. T + -0. 3 E -0 2 J5/09 L. T.
4.
E-02 05/07 05/14 3.0 3E 08 CC
- 2. 7 +-0. 3 E-0 2 05/16 L.T.
4.
E-02 05/14 05/21 2.95E or CC 2.0
+-3. 3 E-0 2 05/23 L.T.
4.
E-02 05/21 05/28 3.02E G8 CL 2.8 +-0. 3 E-0 2 05/31 L.T.
3.
E- 0 2 05/2E 06/04 3.04E 08 LC 2.0 + -0. 3 E-02 06/0e L.T.
4.
E- 0 2 06/04 06/11 3.01F 08 CC 1.8 + 41. 3 E -0 2 ue /13 L.T.
4.
E-02 06/11 06/18 3.20E G8 CC 1.9 +-0. 3 E -0 2 06/40 L.T.
3.
E-02 06/16 06/25 2.eEE Oe CC 2.3 +- 0. 3 E-0 2 06/28 L.T.
3.
- 2. T
+-0. 3 E-02 07/05 L.T.
4.
E- 0 ?
07/02 OT/09 2.93E C8 CC 3.4 + -0. 4 E -02 07/13 L.T.
3.
E-0?
f 0 7/09 O T/16 2.90! 08 CC 3.2 e-0.4 E -0 2 07/2C L.I.
3.
E-02 07/16 07/23 3.00E 08 CC 3.3
+-0. 4 E-02 07/26 L.T.
2.
E-02 07/23 01/30 3.0 7L Ge CC
- 2. 3 +-0. 3 E -0 2 08/01 L.T.
3.
F-02 07/23 07/30 - 3.0 7E C8 CC (a) 08/C3 L.T.
3.
E- 0 2 07/3C 08/06
- 3. doe 08 iL
- 2. 2 + -0. 3 E-02 38/08 L.T.
3.
E- 0 2 08/06 08/13 2.9tE 08 00
- 2. T + d). 4 E -0 2 08/15 L. T.
4.
E-02 08/13 08/20 2.99E 08 CC 2.4
+-0.3 E-02 08/22 L.I.
2.
E-02 08/20 08/2T 2.SSE 08 CC 2.1
+-0.3 E-02 08/29 t.T.
4.
F-02 08/21 0G/03 3.llE Ce.CC 3.2
+-0.9 E-02 C9/C6 L.T.
2.
E- 0 2 l
i f
(b)a) Duplicate analysis
(
Counted twice to confirm higher than usual activity.
1 l
~m
--._._m m.
. _ _s
,--m b
A AA5A5 GAS Afeu EL ECib lC CC 9 0 80s 2CA F E PU 5 ub r.
p A les. Ay - A I R dth M Alb P AbilLOL Af t & CH Ab CCAL Fl&IENS hi A11Le AUM6re 32
,dlY-COUhi ChabCOALFILTEP' COLL. IIMC AP FILTEM 5149T SILP GAOSS niiA
' TIME
~ l -131 Cait bate VCL UPt ukIIS lPCl/CL. M l Call TIME IPC l/CO. M l 05/0! 05/10 2.9ef Os CC 4.3 e-n.) 9-02 ov /13 L.T.
2.
E-02 04/10 09/17 2.9hE C8 CC 2.9 e-4.4 E-02 09/15 L.I.
4.
E-02 1
09/17 09/24 2.9th 06 LC 1.8 e-0. 3 E-02 09/24 L.T.-
3.
E-02 05/24 10/01 3.GSE Ce CC 2.0 e-0. 3 E -02 13/C?
t.I.
3.
E- 02 10/01 10/Ce 2.95C Co CC 2.0 +-C. 3 E-02 10/11 L.T.
4.
E-02 10/06 10/15 3.13E 08 CC I.7 + -0. 3 E -0 2 10/I6 L. T.
2.
E-02 16/15 10/22 3.22E Ce LC 2.2 e-0.3 E-02 10/24 L.I.
2.
E-02 10/22 10/29 3.22E 08 CL 24 e-0. 3 E-0 2 11/02 L.T.
2.
E-OS 10/25 11/05 3.116 Ce CC 3.0 e-0. 3 E-02 11/05 L.T.
2.
E- 0 2 11/05 11/12 3.2*E C8 CL d.5 +-2.0 E-03
!!/lF L.I.
3.
E-0 2 11/12 11/19 3.11F C8 CC
- 2. 2 e -c. 3 E -0 2 11/21 L. I.
4.
E-02 p
s 11/15 11/26. 3.12E 08 CC 4.1 e-0.4 E-02 12/02 L.T.
4.
E-02
-y 11/24 12/03-3.tSE 06 (C 4.6 +-0.4 E-0 2 12/05 L.T.
4 E-02 9
12/03 12/10 3.2et ce CC S.e +-0.4 E-02 12/11 L.T.
2.
E-C2 12/10 12/11 3.1CE Co CC 3.1
+-0. 4 E-02
-12/19 L.T.
3.
E- 0 2 12/17 12/24 3.13F 08" CC 4.2 +-0.4 E-02 12/21 L. I.
3.
E-0?
12/24 12/31 3.22E Ge CC
- 1. 7 e-0. 3 E-0 2 01/03 L.T.
3.
E-07 1
s 9!
a 4
D g
O n ANSAS GA5 Aho rt FCikiC Lei P C HCR 2 0 tl E uGSud f P)IHn4V - Sik elk hi Alk P AHil LUL AI E C C HAF LUAL & ILif HS ST All(N NJMtiFP 37 LOLL. IINE AP FITTER MIC-CCUNT CH ARCle AL FItTEP START S illP barss Bria IlpE I-131 OATE DATE VOLUMF dhlis IPCI/CU. 1 3 CATE TIME IPCI/CU. 84 I I
01/02 01/C8 2.4eE Cd LL 3.5
+-0.5 F-02 01/11 L.T.
4.
F-02 01/06 01/15 2.99E Ge CC 3.0
+-0.4 L-02 01/1S E.T.
2.
E- 0 ?
01/15 01/22 2.17E C8 CC 2.v
- -0. 4 E-02 01/2*
L.T.
4.
F- 0 2 l
01/22 91/29 3.00E 08 CC 2.2 +-0.5 F-02 02/01 L.T.
3.
E-02 01/25 02/05 3.06F 06 CC 2.7
+-0.* E-02 C2/CE L.T.
3.
E-02 02/05 C2/12 3 006 08 Lt.
F.1
+-3.5 E-02 (b) 02/tt L.I.
2.
F-02 02/05 02/12 3.CCE CA LL (a) 02/15 t.l.
5.
E- 02 1
02/12 02/19 3.02F C8 CC 3.1
+-0.4 E-02 02/21 L.I.
4 E-0?
02/15 02/26 3.03F 08 CC
- 2. 2 + -0. 3 E -0 2 02/26 L. T.
2.
E-0?
02/26 03/05 3.02E 08 CC 2.6 + -0. 3 E-02 03/08 L.T.
3.
F-02 03/05 03/12 3.0 7E 08 CL 2.5 +- 0. 3 F -0 2 03/16 L.I.
3.
F-1?
+-0.3 5-02 03/21 L.T.
4.
E- 0 ?
03/14 03/26 2.95E Ct CC 2.t
- -0.4 t-02 03/28 L.T.
4.
E-02 a
03/2e 04 /02 2.955 0H CC 2.1 + -0. 3 E -0 2 04/C5 L.T.
4 E-02 C
04/02 04/09 3.20E 06 CC 2.0
+-0. 3 E-0 2 04/13 L.T.
2.
E-0?
04/05 04/16 2.9tt 08 CC 2.5
+-0. 3 E-02 04/18 L.I.
3.
E-02 04/It 04/24 3.3tt CP CC 2.5
+-3. 3 E-02 04/26 L.T.
2.
E- 0 2 09/24 04/30 2.64E Ca CL
- 2. 4
+-0. 4 E-02 05/02 L.T.
3.
E-02 04/30 05/07 2.9 7E 08 CC
- 2. 5 + -0. 3 E -0 2 05/0S L.T.
4.
E-02 l
05/07 05/14 3.07E OP CC
- 2. 5
+-0. 3 E-02 05/16 L.T.
4 E-02 1
05/14 05/21 2.85F 0e LC 2.2 +-0. 3 E-0 2 05/23 L.T.
4.
E-02 05/21 05/28 2.82L CF (L 3.0 +-0. 4 E-0 2 05/31 L.T.
3.
E- 0 2 C5/2e Ot/C4 2.93E Ce LC 2.1
+-0.3 E-02 06/06 L.I.
4.
E-02 l
05/26 06/o, ' 2.93E 08 CC (a)
Ct/Cf L.T.
1.
L-02 06/07 06/11 1.7df 08 CC 2.9
- -0.5 E-02 06/f3 L.T.
7.
E-02 06/11 De/18 3.05E CP CC 2.0
+-0 3 E-0 2 06/2C l.T.
4.
E- 0 ?
06/16 0e/25 2.51C C8 CC
- 2. 0 + -0. 3 E-02 06/28 L.T.
3.
E- 0 2 l
06/25 07/02 2.93F 08 CC 2.4 +-0.3 F-02 0 7 /C5 L.T.
4.
E-02 07/02 0F/09 3.12E 08 LC 3.3 +-0. 4 E-0 2 07/13 L.T.
3.
F-02 1
07/09 0F/16 2.9EE 08 LC 3.2 +- 0. 4 E-0 2 07/20 L.T.
3 E-02 j
07/le 07/23 3.CtE CA CC 3.6
+-0. 4 E-02 07/7e t.I.
2.
E-O F i
- 2. * +- C. 3 E-0 2 08/01 L.I.
3.
E-02 07/10 08/06 3.01E 08 (C 2.7 +-0.4 E -0 2 C E /C f L.T.
3.
E-02 08/06 08/13 2.92E 06 (C 2.9 +-0. 4 E -02 08/15 L.I.
4 E-02 08/13 08/20 2.9eE Oe LL 1.s e-0. 3 E -0 2 08/22 L.T.
2.
E-02 08/2C OE/27 3.0CE C8 CC 2.5
+-0.3 E-02 08/29 L.I.
4.
E- 02 l
(a) Duplicate analysis l
(b) Counted twice to confirm higher than usual activity.
l l
m
- __. _ _. ~. - _. -.
.~ __
. _ - - _ _ -....~
~_n.-
l h AA5A5 G A5 ANO EL ECIF IL Cl -
P O 810x 20o F1teuSU6F P4TH6eAY AREstphF Alp PAWilLOLAIE & CHAECCAL F4 LIENS 51 All tid NUMecR 37 CCLL. TIME Av iILTEk PIC-ECUNI CH AF CO AL F ILI F R START SiuP GRuS5 o it ilMF 1-1 31 r
CATE 0 ATE WCLuPt ukIT5 RPLl/LL. M I CAIE IIPE BPCl/CO. M i 0b/21 09/J3 2.9dF Oh LC 3.5
+-0.4 F-02 09/06 L.T.
2.
E-02 09/03 09/10 2.41f Oh *(C 2.5 6-0. 3 E-te2 09/11 L.I.
2.
E-02 C9/tt CS/lF 2.97E Od' CL 3.0 e-n.4 E-02 05/15 L.I.
4 E-32 05/17 09/24
- 2. Set Ce (C 2.0 +-Os3 t-02 09/2e L.T.
3.
E- 0 2 09/I T 09/24 2.96E Ch CC (a) ov/2T L.T.
2.
t-02 05/24 10/01 2.968 08 CC 2.0 e-n. 3 E-02 10/0?
L.T.
3.
E-02 IC/01 10 /G d.2.99E 08 CC
- 2. 3 e-G. 3 E -02 1 C /10 L.T.
4.
E-02 BC/06 50/15
- 2. 7 5E Ct CC 2.0 e-J.3 E-02 10/14 t.T.
3.
F- 0 2 10/15 10/42 2.81E CE LC 2.S e-0.3 E-02 IG/24 t.T.
2.
E- 0 2 10/22 10/2S 2.dt[ Ca CC 2.4 +- C. 3 E-02 11/02 L.T.
3.
E-02 10/25 11/05 2.Fef 08 CC 3.9 + -0. 4 E -02 11/05 L. I.
2.
E-02 11/05 11/12
- 2. F 7E Ce LC 2.1 e-0.3 E-02 11/IT L.T.
4.
E-02 l
s 11/12 11/ts 2.62E Ob LC 2.e
+-0.? F-02 11/21 L.T.
4.
F-02 l
4:
11/15 11/26 3.0tE Ce CL 4.S e-D. 4 E-02 12/02 L.f.
4.
E- 0 2 11/24 12/03 3.C3E Ce CC
- 5. 6 *-0. 5 E-02 12/OS L.I. 4 E- 02 12/03 12/10 3.Dof Os CC 6.4 e-0.5 E-02 12/13 L.T.
2.
E-02 12/10 12/1T 3.0CE 08 (C 3.S
+-0.4 E-02 12/1s L.T.
3.
E-02 12/11 12/24 3.04E Os CC
- 3. 9 +- 0. 4 E -0 2 12/27 t.T.
3.
E-02 12/11 12/24 3.04E C8 CL (a) 12/27 L.I.
1.
E- 0 2 12/24 12/31 3.03E CH CC 1.c
+-0. 3 E-02 01/03 L.T.
3.
E-02 i
l (a) Dupilcate analysis e
m__
_-1
._m
,.,7
.m t
i n AN54 5 G AS V40 "t f( I6 8 0 CL i
e C d6E 261 I
EaPuSUAF PAihWAY - A IF uCR Af AlH P AsilLUL AIE L (HA6(CAL f lLif H5 ST ATION MsMhER 40 I
CfLL. TIME SP FILICh MIC-COUNT CHAPCOAL FILT[R 51191 SibP GbCSS Elia TIAF I -1 31 UAlf paTE WCLuPI 05I15 IPCl/CL. 9 )
[AIE TIMF IPC I/ CU. M i 01/02.11/36 2.5IE 06 CC 1.2 e-1.S E-02 01/11 L.T.
2.
t-O' 01/06 01/15 2.8fE C8 CC 3.3 0-0.4 E-0 2 nl/IS L.I.
I.
E-0?
01/21 L.T.
4.
E-0) 01/15 n1/22 2.SHE 08 (C 2.T e en. 4 E -( 2 0l#24 L.T.
2.
E-O?
01/22 01/29 2.90[ 06 CC 2.5
+-n.
- E-02 02/01 L.T.
2.
E- 0 2 01/25 02/05 3.00E 06 (C 2.8 e-0. 4 E-02 32/04 L.T.
2.
E-02 d2/05 02/12 2.dfE CP CC 6.5 e-0.5 E-02 ( b) 02/It L.T.
1.
E-02 n2/12 02/15 2.5 3E C6 00 2.0 e-n.4 E-n2 02/21 L.T.
2.
F-02 02/15 n2/26 - 2.95E 08 LC 2.4 e-C. 3 E -02 L2/2F L.I.
1.
E-0?
02/26 n3/05 3.03E 08 CC 2.1 e-0. 3 E-02 03/06 t.1.
2.
E- 0 2 03/05 03/12 3.02E Ge (C
- 2. 3
+-n. 3 F-02 03/16 t. T.
1.
E-02 03/12 03/19 2.SSE C6 (C 1.9
+-n.3 E-02 03/21 L.I.
2.
F-02 03/15 03/26 2.deE CP (C 2.4 +-0.4 E-02 03/28 L.T.
2.
F-n2
>=
n3/26 04/02 2.87[ CP CL 2.0 +-0. 3 E -02 C4/C5 L.I.
2.
E- 0 2 1,
04/02 04/n9 3.02E C8 CC 1.d e-0. 3 E-02 04/13 L.I.
1.
E- 0 2 (n
04/05 04/16 3.04E n8.CC 2.5 +-n. 3 E-0 2 04/18 L. T.
2.
E-02 d4/le 04/24 3.38E C8 CL 2.2 e-n.3 E-02 04/2e L.I.
2.
E-C7 04/24 04/30 2.60E Oe CC 2.3 e-0.4 E -0 2 05/02 L. T.
2.
E-n2 04/30 05/07 2.99E Ce (C
- 2. 2 + -0. 3 E-D2 05/05 L.I.
2.
E-n?.
05/0 7 C5/14 3.0SE os CC 2.t e-0. 3 E-02 05/tt L. f.
2.
E- 0 2 05/14 05/21 2.96F nn CC 2.0 e n). 3 E -02 n5/23 L. T.
2.
E-02 05/21 65/2a 3.0tL 08 CC
- 2. 7
+-0. 3 E-0 2 05/31 L. T.'
2.
E-02 05/28 06/04 3.0 4t OE CC 2.4 e-0. 3 E-02 06/06
-L.T.
2.
E-02 06/04 06/11 3.0CE Ce CC 1.5
+-0. 3 E-02 De /13 t.T.
2.
E- 02 06/11 06/18 3.12[ Ce CC 2.0 e-0. 3 E-62 06/21 L.T.
2.
E-02 04/1E 06/25 2.9 7F 08 CC 2.2.e+m.3 L.32 ut/?F L. T.
2.
E-02 i
06/25 07/02 3.ItE 08 (C 2.4
+-c.3 E-n?
0F/05 L.T.
2.
E-0?
06/25 07/02 3.1tE DE CC (a) 07 /n 8 L.T.
3.
E-02 67/02 07/09. 2.91E C8 CC J.1
+-0. 4 E -G 2 07/13 L.T.
2.
E- 02 07/09 07/16 3.03E Cd CC 3.2 e-C.4 E-02 n7/20 L.T.
2.
E-n 2 0 7/16 G 7 /2 3 2.94F 08 CC
- 3. 2 + -o. 4 E -0 2 07/24 L. I.
1.
E-02 0F/23 07/30 3.000 08 LC 2.5 e-0.3 E-02 08/01 L.T.
- 2..'[-02 bl/30 08/d6 2.97E Ge CL 2.5 +-0.3 E-02 08/08 L.I.
2.
F-02 CS/06 08/13 2.9eE Ce CL -
- 2. 7
+-0. 4 E-0 2 08/15 L.T.
2.
E-n*
08/13 0s/20 2.54E Cs CC 3.0. e-0. 4 E-02 08/22 L.T.
2.
E- 0 2 08/26 Os/27 2.93F 08 CC
- 2. 2 e -3. 3 E -0 2 C8/25 L. T.
2.
E-02 08/27 09/03 3.13E Ce LC 3.5 e-0.4 C-02 09/06 L.I.
1.
E-02
'(a) Duplicate analysis (b) Counted twice to confirm higher than usual activity.
s-w w
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THE ELECTAC COMPANY i
GLENN L KOESTER vsca peasseget hwCLaan Mr. R. D. 'ia tin, Regional Acininistrator U.S. NucieTr Regulatory Ccxrmission Region IV 611 Ryan P,.aza Drive, Suite 1000 Arlington, Texas 76011
%WC 86-077 Fe.
Docket No. STN 50-482
?".j :
Annual Radiological Envirornental Operating Report
Dear Mr. Mar' in:
Enclosed ie the Annual Radiological Environmental Operating Report which is being subnitted pursuant to Wolf Creek Generating Station Technical Specificat.on 6.9.1.6.
This report covers the operation of Wolf Creek i
Generating Station for the period of March 11, 1985, to December 31, 1985.
Yours very truly, Glenn L. Koester Vice President - Nuclear GLK:see cc: PO'Connor (2)
JCu:rmins Document Control Desk (18)
)
I i
l l
201 N. Market - nictuta, Kansas - mar Address: P0. !ox 206 I Nchita, Kansas 67201 - Telephone: Area Code (316) 2616451