ML20151Z988

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1987 Annual Radiological Environ Operating Rept
ML20151Z988
Person / Time
Site: Wolf Creek Wolf Creek Nuclear Operating Corporation icon.png
Issue date: 12/31/1987
From: Velma King, Withers B
WOLF CREEK NUCLEAR OPERATING CORP.
To:
NRC OFFICE OF ADMINISTRATION & RESOURCES MANAGEMENT (ARM)
References
NUDOCS 8805060029
Download: ML20151Z988 (134)


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WOLF CREEK NUCLEAR OPERATING CORPORATION WOLF CREEK GEKERATING STATION 1987 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT Prepared by Vincent A. King April 29. 1988 88050$0029 871231 PDR ADOCK 03000482 l R DCD

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'INEE OF CGCBtIB 2099 ,

List of Tables .................................................... 2  :

Ids t of Figures . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 Introduction ...................................................... 4 I. Prw i-n Descriotion ......................................... 5 II. Discussion of Results ....................................... 8 III. Annual I.and Use Survey Results and Prwi-Ti Revisions . . . . . . . . 13 IV. M:mitorira Frwi-n Deviations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14 V. EPA Interlaboratory Carcaris<m Fiwi-n Results . . . . . . . . . . . . . . 16 Tables ............................................................ 18 i

Figures ........................................................... 33 Appendix A Statuary tables in fonnat of NRC Radiological Assesanent Branch 'mchnical Posi",lon, Revision 1, Novernber 1979 . . . . . . . . . . . . . . . . . . . . . . . . . . A-1 ,

Appendix B: Individual sanple results . . . . . . . . . . . . . . . . . . . . . . . . . . . A-9 4

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i 1987 ANNUAL RADIOWGICAL ENVIRCNENTAL OPERATING REFOR"!

Page 1 of 46 NOLF CREEK GENERATDG STATICE L

l LIBF T ' MIDIS fa9ft Table la 1987 Radiological Environmental itnitoring Prc.gnun 9apling Schedule .................................... 18 Table 2: Sanpling location Nurters, Distances, and Directicms ........................................... 21 Table 3: Gross Beta Analysis Results of Air Particulate Sanples .............................................. 22 Table 4: Gamte Analysis Results of Air Particulate Caposite Sanples . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 24 Table 5: 1987 TID Results ..................................... 25 Table 6: Gross Beta Analysis Results of Drinking Water Sanples . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 26 Table 7: Tritium Analysis Results of Surface Water ............ 27 Table 8: Gamma Analysis Results of Shoreline Aariimant Sanples . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 28 Table 9: Ganma Analysis Results of Aquatic Vegetation Sanples . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 29 Table 10: Results of 1987 Iand Use Survey . . . . . . . . . . . . . . . . . . . . . . 30 Table 11: Results of EPA Interlaboratory Cmparison 'Msts . . . . . . 31 1

1987 ANNUAL RADIGILGICAL DWIR0tMNIAL OPERATDG REKRT NOLF CREEK GDEFATDG STATION Page 2 of 46

LISP W FIGLRES

.EA99 Figure 1: Airborne Pathway Sanpling Iocations . . . . . . . . . . . . . . . . . . 33 Figure 2: Direct Radiation Pathway Sanpling Iocaticos . . . . . . . . . . 34 Figure 3: Naterborne Pathway Sanpling Incations . . . . . . . . . . . . . . . . 35 Figure 4: Ingestion Pathway Sanpling Iocations . . . . . . . . . . . . . . . . . 36 l Figure 5: Distant Sanpling Iocations . . . . . . . . . . . . . . . . . . . . . . . . . . . 37 Figure 6: 1987 Grosa Beta Air Concentrations ................... 38 Figure 7: Indicator / Control Ccuparison . . . . . . . . . . . . . . . . . . . . . . . . . 39 Figure 8: Operational H D Results by Quarter ................... 40 Figure 9: Nearuite HD Variation by Quarter . . . . . . . . . . . . . . . . . . . . 41 Figure 10: Drinking Nater Gross Beta Activity ................... 42 Figure 11: Tritiun Releases / Concentrations in N0CL. . . . . . . . . . . . . . . 43 Figure 12: Liquid Effluents Released to NOCL .................... 44 Figure 13: Cs-137 in Shoreline Sediment ......................... 45 Figure 14: Cs-137 in Aquatic Vegetaticn . . . . . . . . . . . . . . . . . . . . . . . . . 46 i

1987 ANNUAL RADIOLOGICAL DNIRCtMNIAL OPEPATDG REPCRT NOLF CREEK GENERATDG STATICN Page 3 of 46 l

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Introhetim

'Ihis represents the 1987 Annual Radiological Envirmmental Operating Report for Wif Creek Generating Station (NCGS), located in Coffey County, Fansas, approximately five miles northeast of Burlington, Fansas. 'Ihis report covers the period fr m January 1 to Deceber 31, 1987.

Ebel loading began at NCGS cn March 12, 1985. 'Ihe operational phase of the Radiological Enviromental 2nitoring Frgeom began with initial criticality on May 22, 1985, with the first detectable quantities of radioactivity reported in plant effluents in June, 1985.

'Ihis report ccntains a description of the Radiological Envizmmental Monitoring Prw tam conducted by Wolf Creek Nuclear Operating Corporation (WC20C), results of sanple analyses perfonned by Teledyne Isotopes, a discussion of nonitoring g.% tare results, a discussion of program deviations and revisions, and a discussion of the results of the Environmental Protection Agency (EPA) Interlaboratory Ccmparison Fr%tain. Individual sanple results and a sumary of results in the Nuclear Regulatory Ccmnission (lac) Branch Technical Position specified fonnat are included as appendices to the report.

Tritium frm routine plant releases was detected in Wolf Creek Cooling Iake (WCCL) throughout the year. Activaticn products (Mn-54, Co-58, Co-60, and Sb-125) were detected in lake sediment and aquatic vegetation in the imediate vicinity of the NCCL discharge cove. Finally, two fish sanples

, frm NCCL contained Cs-137 which is assmed to be due to NOGS operation, although fallout Cs-137 (which is regularly detected in other sanpling media) is probably also partially reflected in the measured cmcentrations.

All nuclide concentrations were below applicable Technical Specification reporting levels.

No tritium or other plant related nuclides were detected at the nearest downstream w pling point with unrestricted access (drinking water sanpling location IN-40 at IaRoy).

No measurable inpact cn human exposure due to plant operation was seen for the year.

1987 ANNUAL RADIOWGICAL DWIRCNdENTAL OPERATDG REPCRT WOLF CREEK GDDATDG STATICH Page 4 of 46

I. IHO@AM DFSCRIPTIN Radiological envimamental samples wre collected acconiing to the schedule in Table 3.12-1 of the Wolf Creek Technical Specifications and Section 4.0 of the Offsite Dose Calculation Panual. All samples wre collected by WCtOC's Environmental Panagemnt Group and sent to 'Ibledyne Isotopes for analysis. Table 1 lists sag ling pathways and frequencies of sampling and analysis.

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

Airborne Particulates and Iodine:

Ioa volum air sampling pumps continuously collected particulate samples on 47mn glass fiber filters; samples wre then drawn through charcoal canisters to collect I-131. Filters and charcoal canisters wre changed out wekly, labeled, and shipped to 'Ibledyne Isotopes for analysis. 'Ittal sample volu:re used to calculate air concentrations was detennined frm the average of the initial and final sa:rpling flowrate and the total time of collection.

Gross beta analysis of the air particulate samples was perfonrad approximately 72 hours8.333333e-4 days <br />0.02 hours <br />1.190476e-4 weeks <br />2.7396e-5 months <br /> following filter collectico to allow decay of radon and thoron daughter products. Each filter was nounted on a stainless steel planchette and counted on an autamtic alpha-beta counter.

Weekly air particulate filters wre ccrnbined into quarterly cmposites for each location and analyzed for gamm anitting isotopes on a Ge(Li) detector.

Charcoal canisters wre routinely counted in groups of five to detennine the presence or absence of I-131. Positive indication of airtorne I-131 would have been supplomnted by separate analysis of individual canisters for each location.

Air samples wre collected fran the three sectors with the highest ground level D/Q, the nearby comunity of !W Straw, and a control location.

Distances and directicns to sampling locaticats frun the plant site are listed in Table 2; locaticns are shcm in Figure 1 (nearby locations) and Figure 5 (distant locations).

TLD:

'Ihe thernoluminescent dosineters (TLDs) used during 1987 mre provided by

'Ibledyne Isotopes. 'Ihe TIDs consisted of rectangular teflon wafers inpregnated with CaSO :Dy. Rior to placarmt in the field, the dosineters wre annealed for at 4least 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. !W field 1987 A!NUAL RADIOLOGICAL EtWIROtMEtTTAL OPERATIlG REPORT WOLF CREEK GEtERATIIG STATIOti Page 5 of 46

r dosimeters were exchanged with exposed dosimeters and the exposed dosimeters ware returned to %1edyne Isotopes for analysis. Freshly annealed control dosimeters were sent with the exposed TIDs co record transit exposures received during shipment as well as eysten background of the TLD reader.

Ganma exposures were measured on a h ladyne Model 8300 TLD reader; individual dosimeters were then re-irradiated with a known exposure frm a Cs-137 source snd read again to detemine iMividual dosimeter calibration factors.

In general, TIDs were located 3-4 feet above the grouM cn utility poles; they wre placed inside either plastic thentostat 1: oxes or fiberglass air particulate sanpler housings to protect than frm noisture aM ta.pering.

Two TIIe were placed at each location to provide duplicate measuratents.

TLD locations are shown cn Figure 2 'nearsite) and Figure 5 (distant). ,

Table 2 provides distances and directions of each location frm the NCGS site.

Water Monthly conposite sanples of drinking water were collected by continuously i drawing aliquots at two hour intervals. Grab sanples of surface water and ground water were collected on a nenthly and quarterly basis, respectively.

All sanples were sent to Teledyne Isotopes for analysis.

All water sanples were analyzed cn a Ge(Li) detector to detemine if ganma anitters were present. In ackiitico to gama analysis, a radiochanical analysis for I-131 was perfomed cn drinking water and ground water sanples. Gross beta analysis was also performed cn drinking water sanples.

Tritium analysis was perfomed by liquid scintillation counting cn a quarterly basis for drinking water aM ground water, and on a nonthly basis for surface water.

Drinking water sanpling locations are at the e ter treatment stations for the towns of Burlingtrn (upstream centrol location) and Ieroy (downstream indica *or locaticn). Scrface weiter sanpling locaticns are at the John Redmcnu Reservoir outfall (ccntrol) and the Wolf Creek Cooling Iake discharge cove (iniicator). Ground water is sanpled frem three wells +

located hyirologically downgradient frm Wolf Creek Cooling Lake and frm an upgradient ccntrol m il. All water sanpling locaticns are listal in Table 2 and shcwn in Figures 3 aM 5.

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r 1987 AN!UAL BADIGOGICAL DWIROM2H'AL OPEATUG REPORT NOLF CREEK GENEATDG STATICN Page 6 of 46

1 Incestion:

Milk sa."ples were collected on a smi-monthly basis frun April through Ncmrter (while milk animls were en pasture grass) and on a monthly basis the reminder of the year (when animals were on stored feed). Sanples were sent to Teledyne Isotopes where radioch mical analyses for I-131 and gan n analyses were periomed on each sanple. Locations are shown in Figures 4 and 5.

Broadleaf vegetation sanples were mllected monthly during the growing season. Occasionally alternate sanpling locations were used when quantities of vegetation were limited, such as early or late in the growing season or during dry periods. Akiitionally, a sanple of crops irrigated with water fran the Neosho River downstream of Wolf Creek Cooling Iake was collected during harvest. All vegetation sanples were sent to 'Ibledyne Isotopes and analyzed by gann spectrosecpy. Incations are shown in Figures 4 and 5.

Fish samples were collected semiannually with several recreationally inpartant species being sanpled. Sanples of boneless meat portions were sent to 'Ieledyne Isotopes and analyzed by gann spectroscopy. Iocations are shown in Figure 4.

All sanpling locations above are listed in Table 2.

Shoreline sedinent & Acuatic Veaetationt eeniannual sanples of shoreline sediment and aquatic vegetation ware collected fran the discharge cove area (location "DC" on Figure 3) of Malf Creek Cooling Iake. Gama analysis was perfomed on each sanple.

1987 ANNUAL BADIOwGICAL DWIRCNG2TI' A L OPERATDG REPCRT WOLF CREEK GDERATUG STATICN Page 7 of 46

1 II. DISCESIW T RIEHKS I

Analysis results for all pathways are sinmarized in Appendix A using the l fomat described in NRC Radiological Assessnunt Branch ibchnical Iosition, '

I Revisim 1, evmber 1979; results for individual samples are listed in Appendix B.

In this sectico, 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.

Airbome Particulates and Iodine Fesults of gross beta analysis of weekly air particulate filters are shown in Table 3. In addition, the four indicator locations are averaged and plotted graphically with the control location in Figure 6. Finally, Figure 7 shows the relative variation of the irdicator average as a percentage of the control location results.

It can be seen in Figure 6 that indicator and ccntrol locations tracked together closely for the year with no significant peaks or other distinctive features. Figure 7 shows a slight deviation between the irdicator average and the control location results during Septaber and October. This was caused by concentrations for indicator locaticus 2 and 3 being smewhat lower than the control locatico concentrations. The cause of this decrease is nest likely increased deposition of particulate matter during a relatively dry pericd resulting in increased self-absorption during counting of the filters frtzu locations 2 arxi 3. Reoccurrences would not be readily predictable and the effect was not prcnounced enough to warrant nodifying the routine sanpling frequency, although follow-up sttriies are undexway to confim whether increased depositica ard self-absorption or sme other factor is respcosible (see the discussion in Section IV of this report, "Monitoring Program Deviations").

Results of weekly analysis of charcoal filters for I-131 showed no concentrations above the detection limit during the year.

Results of quarterly gama analysis of air particulate filters ccriposites are sunnarized in Table 4, which shows that naturally occurring Be-7 ard K-40 were detected regularly, as was the case during pracperational nonitoring.

m effect:s of plant operation were seen via the airtorne pathway for the year.

TIDs:

Quartcly ganna exposures naasured at each location for 1987 are shown in

. Table S. Values are the average of results for two dosineters at each

location, nornalized to a 90-day standard quarter.

1987 NNJAL RADIOWGICAL DWIRCtMDU'AL OPEATUG REPCRT WOLF GEEK GDIERATDG STATICN Page 8 of 46 r vn-v -

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Results frem TIDs located near the plant site (less than approxistely three miles distant), which would be m st sensitive to changes due to plant operation, were cmbined into quarterly averages. 'Ibese nearsite averages, using locations 1, 2, 7, 8, 9, 10, 11, 12, 13, 14, 18, 26, 27, 28, 29, 30, l 37, and 38, are cmpared to centrol TID results in Figure 8. In addition, variation of the nearsite averages frm the control location results are plotted graphically in Figure 9. Figure 9 also includes preoperational data for emparison.

Ib changes to area gama exposure rates as a result of plant operation were identified.

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Drinkino Water:

Results of gross beta analysis of drinking water sanples are listed in Table 6; Figure 10 depicts these results graphically along with preoperational valuas for empariscn.

!b significant difference between the indicator and control locations was fourx1 except that the results at the control location appeared to be scrnewhat erratic during the lar.: nwo nonths of the year. (tb cause was readily apparent for this efiect.) Additionally, nc increase over preoperational ccmcentratiens das evident, as is seen in Figure 10. tb effect due to plant operation was identified in drinking water sanples by gross beta analysis.

'Ihis conclusico is confimad by the results of I-131, tritium, and gann isotopic analyses; no other radienuclides were seen at detectable levels.

Surface Water:

Tritium resulting frm WCI3S operation was detected in all surface water sanples collected frm WCCL in 1987, corresponding to a total of 316.6 Curies released during the year. Measured ccncentreticns are shown in Table

7. In Figure 11, NCCL tritium ccncentrations are plotted alcag with nonthly liquid tritium releases since WOGS began operaticn.

It car. be seen in Figure 11 that nonthly tritium releases have been fairly constant, with decreases in late 1986 and again in late 1987 during the refueling outages. Surface water concentrations appear to be steady or passibly slightly increasing during 1987 with an average concentratien of 4800 pCi/litar for the year. 'Ihe peak ccncentratico seen in April (11,000 pCi/ liter en 4/21/87) is irm a sanple collected at the saw tim a batch release was in progress, so that the collected volme was not yet thoroughly mixed in the total lake volume.

1987 ANNUAL RADICEDGICAL DWIRCNGNTAL OPDATItG REPCRT NOLF CREEK GDimATI!G STATION Page 9 of 46

A second surface water sanpling location was aMM in February away frm the discharge cove so that m:>re thorough mixing would occur prior to sanple i collection and a nore representative indication of WCCL outflw could be '

obtained. Iocatim WC, which is inuxiiately below the WCCL spillway on Wolf Creek, was a&ied in February for this purpose. Location WC was replaced with location SP, imnediately above the WCCL spillway, due to low and intemittent flow frm the spillway. Water frm location SP is considered to be representative of outflow frm WCCL. Table 7 shows that tritium ccncentrations measured at locations NC and SP were in the same range as ,

those frm the discharge cove, with the exception of the peak measured in April.

All tritium concentraticns measured were below applicable 'IWhnical Specification reporting levels.

'Ihere were no other radionuclides detected in surface water for the year.

Ground Water:

Naturally occurring K-40 was measured in two ground water sanples during 1987. Ib other gama enitters or tritium were detected.

1 No effect on ground water due to plant operation was identified.

l i

M1Ikl All milk sanples analyzed for 1987 contained naturally occurring K-40 at concentrations consistent with preoperational levels. Yearly average concentrations were 1180 sci / liter for cow's milk and 1580 pCi/ liter for goat's milk.

Cs-137 was detected in two milk sanples frm bc+;h indicator and control
locations. Measural ccncentraticas were 6.9414.02 pCi/ liter at control location S-3 on 2/10/87 and 6.65t3.35 FCi/ liter at indicator locatico P-2 on '

6/9/87. Both values are consistent with preoperational levels and are attributed to fallout.

No other gann anitters were detected and no plant related effects were identified during the year.

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4 Food & Garden Croce:

Gane analysis of broadleaf vegetaticn sanples revealed naturally occurring ,

gama enitters K-40 and Be-7 at ccncentrations ecmpareble to preoperational l bacaJround levels.

No other gama snitters were detected for the renainder of the year, and no .

effects of plant operation were identified.

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I 1987 ANNUAL RADIOLOGICAL DWIROMNTAL OPERA'!IIG REKRT j WOLF CREEK GDIERATING STATIOi Page 10 of 46 r

In addition to broadleaf vegetation, a sanple of soybeans was collected which was irrigated with water frm the Neosho River below the Wolf Creek Cooling Iake outfall. Gama analysis revealed naturally occurring K-40 to be present in the sanple, with no nuclides detected due to plant operation.

fifhi Naturally occurring K-40 was fourri in all fish sanples collected with average concentrations of 3.3 pCi/ gram (wet weight) for WCCL sanples and 3.6 pC1/ gram at the control location. 'Ibese concentrations were within the range seen during the preoperational period.

In addition, two sanples frm WCCL, collected on 10/6/87, contained detectable levels of Cs-137 at concentrations of 0.13410.017 and 0.15210.017 pC1/ gram (wet weight). Although fallout Cs-137 is regularly measured in other environmental nedia and is probably reflected in these values, it .4.s assumed that these concentrations are attributable to NOGS operational releases (see Figure 12). (Note: Preliminary analysis results for 1988 indicate that no Cs-137 was detected in fish sanples collected on 4/5/88).

A dose calculation for a hypothetical individual, assundng a maxinum ingestion rate (16 kg per year frm Reg. Guide 1.109) at the maxinum neasured Cs-137 ccncentration results in an annual dose of 0.36 mrm (critical age group = teen, critical organ = liver).

tb othcr radionuclides were detected in fish during the year.

Shoreline Sediments:

Table 8 shows gama mitters detexed in shoreline s,xiiment sanples during 1987. In additicn to naturally occurring nuclides, Co-58 and Cs-137 were also detected.

Co-58 was measured as a result of NOGS operation in the 10/27/87 sanple frm the discharge cove at a ecocentratico of 0.048810.0224 pC1/ gram (dry weight). 'Ihis concentration is scuewhat lower than was neasured in 1986.

'Ihe Cs-137 crmeentrations measured are c:nsidered to be due primarily to fallout rather than plant operation since they are at or below concentraticos neasured preoperaticnally. 'Ihis can be seen in Figure .13 which plots both preoperaticnal and operaticnal cancentrations of Cs-137 in shoreline sediment sanples frm the discharge cove location.

1987 ANNUAL RADIOELGICAL DNIROtNDUAL OPEATDG REPORT WOLF CREEK GDERATDG STATICN Page 11 of. 46

Acuatic Veoetatim:

A ca binaticn of naturally occurring nuclides, fission products, and activation products were detected in algae and rooted aquatic plant sanples fran the NCCL discharge cove during the year. A sumary of the concentrations measured is shown in Table 9.

Naturally occurring nuclides measured were Be-7, K-40, Ra-226, and 'th-228.

Activation products seen in the samles were Mn-54, Co-58, 00-60, and Sb-125, all of which were attributable to operational releases (see Figure 12). Concentrations measured were generally less than those seen in 1986 for Mn-54, Co-58, and Co-60. Sb-125 had not been detected previously and correlated to operational liquid releases of 0.0264 Curies reported during the fourth quarter of 1987.

Fission product Cs-137 was detected in the algae and rooted aquatic vegetation sanples fran 6/23/87. While it is possible that operational releases may have ccntributed to these conce trations (as discussed in the section on fish sanpling results), these levels are at or below concentrations measured preoperationally, as can be seen in Figure 14. 'Ihe detection of Cs-137 in these sanples is therefore considered to be due to fallout to a greater extent than to NOGS operational releases.

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i 1987 ANtEAL RADICI4GICAL DWIRCNENIE OP3&TDG REPORT WOLF CREEK GDEATDU STATION Page 12 of 46  ;

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III. Arnal Iand U00 Survey Rmults arri Pruumu Havisions to 1987 Annual Land Use Survey ms cmpleted in October. Iniornation ms collected using a combination of milcxi survey fonns, telephone contacts, and dcor to door contacts. Results of the survey, showing the distances to the nearest residences, milk producing aninals, and vegetable gardens within five miles of the plant site, are su:marizcxi in Table 10.

'Ihe only change in the narest residences was in sector M, where the distance decreased frun 2.4 to 1.6 miles.

Distances to the nearest garden increased in sectors L, N, arri P, arxi decreased fran 4.1 to 3.8 miles in section K. Ib revisions to vegetation sagling locations were necessary as a result of these changes.

Milk sagling locations P-2 (goat's milk) and Q-5 mre deleted in July and August, respectively, due to a lack of future availability of milk. A potential new sampling location ms identified in sector F at a greater, and therefore less conservative, location than the current location F-1. 'Ihe new location es designated F-8 an:1 my be used as an alternate sa@ ling location if milk is unavailable at F-1. Finally, location E-1 ms identified as having milk animls, but the resident at that location has indicated that the milk is not used for humn consumption. ('Ihe sam situation currently exists at location D-2.)

It should be noted that dose calculations are perfonned for airborne and liquid patheys for a hypothetical individual at the exclusion area boundary in the highest X/Q and D/Q sector (for airborne patheys) and at the circulating mter discharge point (for liquid patheys). Calculated doses are therefore not affected by changes in residence, milk aninal, and broadleaf vegetation locations identified by the Annual land Use Survey.

Finally, sagles flun a second surface ster location wre collected beginning in February to provide results more representative of the average Wolf Creek Cooling Lake ccocentration. Initially, Iccation NC on Wolf Creek inmodiately belcw the WCCL min dam spillm y m s used (February through April). Mowever, due to intennittent ficw over the spillmy, this location m s replaced in June by location SP, which is on WCCL in the inmediate vicinity of the nain dam spillmy, hhile this as not a fornal revision to the Badiological Environmental Monitoring Program during 1987, results are include-1 in this repart.

1987 A?NUAL PADICILGICAL DWIROME!7fAL OPERATI!G REPCRT NOLF CREEK GDIERATIIG STATION Page 13 of 46

IV. M3tI'KRDG.PEXMM DEVIMIG6 Airborne Particulates and Iodine:

3/10/87 - 3/24/87 (All locations): Following a calibratica of the mass flometer used to calibrate air sanpling punps, it was uncertain whether the cormet taperature correctico factor had been used by the verdor performing the calibration. (%e vendor had recently changed its procedure to use a different calibration taperature for new mass floweters.) If an error was mde, the actual air concentrations during this tw week period should have been 7% lower than the values reported. Future performnce of the vendor will be nonitored to ensure such calibraticns are correct.

4/14/87 -

4/21/87 (I.ocation 32): Reported results were erroneously low because foreign material blocking the exhaust nozzle of the air sanpling punp caused an incorrect measurment of flowrate at the intake orifice. Se punp was reoved from service to perfom corrective maintenance.

4/21/87 - 4/28/87 (Iocation 32): ne sanpling punp notor turned out mking it inpossible to calculate sanple volune and resulting air concentration.

We sanple filter was counted and results reported as total pC1. Se sanpling punp was rmoved frun service. (Notes his as not the sane sanoling pmp that malfunctioned at the same location on the previous week.)

9/15/87 - 9/22/87 (Locaticos 2 and 3): Although the sanpling punp appearai to be operating properly at locaticn 2, deposition cn the filter was light and the calculated concentration was low. No cause was i& atified, ard the problen did not recur. Additionally, the filter holder at locatica 3 was loose and there was scrne damage to the edge of the filter, although resulting concentration does not appear to have been significantly affected.

9/22/87 - 10/20/87 (Incations 2 and 3): Analysis results for these two locations were somewhat lower than those for the reaining locations during this pericd. It is felt that since this was a relatively dry period, additional particulate deposition may have lowered counting results at these locations due to self-absorption in the sanple filters. A study is currently urderway to see if a correlation exists between deposited ssple weight and resulting ecocentraticos. Ib correlation was established between low activity and particular sanpling punps, so that punp malfunction was ruled out as a factor.

We above were ecmsidered isolated occurrences which did not indicate p % wnatic probl es.

Drinkina Water 3/4/87 - 4/7/87 (Iocaticn BR-15): Se cmposite drinking water sanple for March at the control locatico contained an insufficient volune to cmplete the required analyses. A grab sanple collected on 4/7/87 was substitutal for the cmposite sanple. Corrective nodifications were made to the cmposite sanpler.

1987 ANNUAL RADIOWGICAL DWIRCtEDTIAL OPERATDG REJ1T NOLF CREEK GDDATDG STATICN Page 14 of 46

10/7/87 -

1/5/88 (Iocaticos BW-15 and IM-40): Triti m analysis of the Fourth Quarter 1987 drinking water ccuposites for both locaticns were not perfomed in a timely manner. (Analyses were empleted cn 2/22/88 rather than within the 30 day turnaround time requested.) No data was lost and required detectico limits were achieved. While this appears to be an isolated incident, the perfomance of the analysis laboratory will be nonitored to ensure that a recurring adverse trend does not develop, liGh 8/12/87 - 10/13/87 (Iccatica F-1): Milk was tertporarily unavailable frm this locatico during the period indicated. Such unavailability occurs frequently since there is marginal milk production at this location. No corrective actions were taken because at the time there were no other identified locations producing milk for human consunption within five miles of the plant site.

Food and Garden Croos Sanples were unavailable during April at all locations and during Novmber at locaticn S-4. In additica, no sanples were available frm location G-1 during the entire year due to insect damage. Alternate location R-1 was substituted for locatico G-1 during June and July.

Ib oorrective acticms were necessary since these sanples are to be collected "when available" during the growing season.

'Ihe irrigated crop sanple frm locaticn NR-D1 cn 10/9/87 was inadvertently returned frm the analysis laboratory without being analyzed. 'Ihe sanple had not been ruoved frcra the packaging material and was returned with the shipping container. 'Ibe sanple was subsequently re-shipped and analyzed cn 10/31/87. No data was lost, and all required detection limits were achied for applicable nuclides. 'Ibe sanple receipt procedure was reviewed during the next Oaality Assurance audit of the analysis laboratory, arri no A similar event has occurred pwgagiratic problem was identified.

previously, however, and the performance of the ar.alysis laboratory will continue to be nonitored to ensure a recurring trend does not develop.

1 I

f 1987 AtHIAL RADIMOGICAL DWIRCtMENIAL OPEATUG REPORT NOLF CREEK GmERATDG STATION Page 15 of 46 J

V. WA InterM--kuy n==Mam F1- Results hledyne Isotopes, contracted to perfom analysis of radiological environmental sanples for NCNJC, participated in the EPA Interlateratory Cm parison Prog &n during 1987.

Table 11 shcus interemparison test results 2or the year, including 1986 results which were not available for the 1986 Annual Repart. We table lists the sanple nureber and date, the sanple nedia, the nuclide or analysis type, the known value reported by the EPA, the measured value reported by hledyne Isotopes (based on triplicate analysis), aM the nonnalized deviation fran the known. (We nonnalized deviation is determined by the difference in the measured result fran the EPA reported known, divided by the standard error of the mean as a measure of the degree of precision. A normslized deviation larger than + 3.0 prmpts followup action to identify the cause of the discrepancy.) Results are listed in the table only for sanple nedia and analyses types perfomed for NCt0C.

Five of the 54 interemparisen results exceeded a nonnalized deviation of 3.0.  % e discussion of corrective actions provided by Teledyne are shown below. Ib systanatic problan was identif ted for any sanpling media or specific analysis. Interemparison test results and followup acticos will continue to be evaluated to ensure that no ache.rse trends develop, wst #434, Cs-137 in Milk, tbunalizM Deviation = 3.12, (11/4/86):

2 o three results were 42, 50 and 52. W e efficiency for Cs-137 was checksd and no reason for the two high results could to ascertained. %e efficiency of the two detectors giving high results is being checked.

Test #441,Zn-65 in Water, Nonnalized Deviation = 6.00, (2/6/87):

lb reason could be ascertained for the high resd t for Zn-65. Previous results had a normalized deviation fran the known of -0.34 (10/10/86) and 0.58 (06/06/86). %erefore this does not appear to be a trend. Further cross-checks will be studied for any problans.

Test #451, Gross beta, tbrmalized Deviation = -3.24, (4/27/87):

his result and two previous EPA beta results were 6% low. Additionally, our (Teledyne) in-house beta spikes are low by the same percentage.

Analysts have been retrained in transferring all sanple residue into the planchets.

'Ibst #457, I-131 in Water, tbrmalized Deviation = 3.08, (8/7/87): ,

he high result is due to erroneously high electrode reading of stable iodine in the sanple leading to errtneously low chstical yields. After repeating the electrede reading, the calculated average of I-131 is 49.6 Ici/L. ( % 1edyne) technicians have been made aware to be suspicious of high electrode readings, in which case sanples will be dilutsi and/or oxidized and re-measured.

1987 AtC1UAL BADIGIIGICAL DWIRONDTIAL OPDATItG REPCRT NOLF CREEK GDIGATDG STATIQ1 Page 16 of 46

Test #465, Cr-51. Nomalized Deviation = 7.16, (10/9/87):

'Ihe efficiency calibration for Cr-51 for the ganma spectronster detectors was checked and appeared correct. 'Ihe other 5 isotopes measured in this sanple were within two standard deviations indicating there is no systematic error. At this activity level, Cr-51 is difficult to measure due to the low branching intensity of the ganma ray and being in the high background region of the spectrum.

1987 ANNUAL RADIGOGICAL DWDOMNIAL OPDATUG REPCIC WOLF CREEK GDEATDG STATICN Page 17 of 46


--_____ __ -~'- - _____.

t i

1 l

l J

o b5 4 *: '

h TagitK 1 vs 2 Mf naplotaGICAL userIguagenfrnL esmet10ItsesG Fes0 Gun

~'" - - '

h n

H Nisaber of Gigles b~ Exposure Pitimiy an] Swgiling an] Type an! Frepency g aral/or Sugile Sasq)le Locations Collection Frer]tency of An.nlysis d I3 1. AIIeneE 2b Cbntinuous operation Rwliololine an! Five locations, Rxliolodine cannister.

Particulates station nuensers 2, of sasupler with sasq)le i

Analyze wekly for 3, 32, arel 37 on collection es reepairet for I-131.

Figure 1 aral location by dust loaling but at K 40 (control) on laist wwkly. Analyze for gross beta g t"igure 5. radio.w-tivity approxi-autely 72 hours8.333333e-4 days <br />0.02 hours <br />1.190476e-4 weeks <br />2.7396e-5 months <br /> following filter charvje. Perfona g gansna isotopic arulysis y on each :asuple dum gross o beta activity is greater

o than 10 tiam the yearly j mean of cont ro' sarg>les.

f Perform 9.womi isotopic

analysis on conposite (by location) once per quarter.
2. DIfnCT HADIATI(W 3811D locations within (barterly at each Gwena dose gnrterly.

5-mile ralius of site location.

(station ntader 1-38 on Figure 2) arti two of fsite locations (station 39 an!

40 on Figure 5); two y TfD dosimeters at each d2 1ocation.

I U .

I on l o m

b m

yw% --e1p-4 e-= *w-P*- t-%yw ww'wp- - - - - - - , - v- yew r 9 , -

-g--7--- -

--w 9 v y-,-- -

e- w ,m- -,y .- ,yw y w - g ,- , -?- --- m --

m - - - --

be 45

{ Tast21 (Omt'd) en &

Mp MGdMDCRL MN DEBIITEMIE M SIWWLIIE; S3518E2 tamd>er of Samples O F2posure Pattway ars! Suplirwy ark! Type an! Fregency gh g _ art 1/or Sample Suple tocations Collection Frerpency of Analysis o-gh

3. WATENDORtE d 13 a. Surface One suple frces Wolf Pt>nthly grab sanple Pt>nthly gasms isotopic g3 Creek Cooliraj take arm! trititmo analysis.

m discharge cove, one k sample fran WTL anain g dam spillway (see q Figure 3).

b. Groural *Ihree locatiorus at 02arterly 02arterly ganumn isotopic O C-10, C-49, D-65, aral trititan analysis, one control location g at B-12 (see Figure 3).

di c. Drir*irmj temicipal water tt>nthly composite

  • tt>nthly gross tieta armt m supplles at Ibrlirmjton 9.usms isotopic <whilysis.

(upstrease) at:3 testoy Ourterly trititan analy-x (downstreann) . sis of composite sample.

  • -3 (See Figures 3 arm! 5) .
d. Sedinient fran One sanple fran Wolf Sinianrmily Stweiannual guemi isotopic Shoreline Crmk Coolir 3 take arulysis.

discharge cove (see Firjures 3 armi 5).

e. Arputic One suple frue Wolf Ssnianrmally Srsaiarwmul gswan isotopic

~8 vejetation Crm k Coolirej take arulysis.

$ discharge cove (see Figure 3).

y O

n - - -

$ *Cumposite s.wplirvj slull t*r p?rforan=1 by collectirny an alirpiot at interv. Is not excselirvj 2 hours2.314815e-5 days <br />5.555556e-4 hours <br />3.306878e-6 weeks <br />7.61e-7 months <br />.

4 N 1 (Ooset'd) mantOtA1Gacht. BeartsuossespraL Monst10stlesc Pseurauwe

.WfEPLIIE K355RRE t&miber of Samples

.-e Engesure Pathway arm! Srpliraj an! Type arn! Fre=rta'sicy aral/or Swnple Swiele ferations Collection Frequency of Analysis M 4. IIKISTION

a. Hilk Sanples f ran F-1, P-2 Feininionthly sdien Cinema isotopic anl (deletal in July), 0-5 animals are on gusture; I-131 analysis of each (deletal in August), monthly at other tinw s. sample.

an! a control swiple QI fran S-3 (see Figures 1 am! 5).

h. Fish Ore sunple from Wolf Serniarinual ly Guiana isotopic analysis O

Creek Cooliraj take, on ollble tortions.

sienitar sanple fran John Herknon! Heservoir spi 1Iway as control (see Figure 4).

c. Foal prulucts Bro.ml leaf voyetation tenthly durirvj lurvest. Gween isotopic arulysis sanples at locations A-1, on ojible portions.

G-1, ami R-1 (alterrute) on Figure 4; control at S-4 on Figute 5.

ce j One srple of crops At time of turvest. Cesma isotopic azulysis y irrigate 1 with Neosho on elible tertions.

O River taster fran locations O

" downstrewn of the Neordio-Wolf Creek conflueste

$ (location IR-ol on Figure 5).

I l

l Gi TAMEA 2: SRfGE.19E EADtTIGI MSWIFJtS, DISTNCES (smiles) Age) DE5WCTIGE Til) aunt Air Particulate tocation Distance / focation Distance / Incat ion Distance / focation Distance /

thenter Direction thmuder Direction t&msder Direction thauder Direction i IwH h

1 2

3 1.4/n 2.7/N 3.0/ tem:

11 12 13 1.6/E 1.8/ESE 1.5/SE 21 22 23 3.8/S 4.1/SN 4.5/m 31 32 33 3.0Aew 3.2A#M 3.7 Amu 4 4.0/ tee: 14 2.6/SE 24 4. INN 34 4.0/tm 5 4.0/NE 15 4.5/ESE 25 3.6/W 35 4.6/tsM 6 4.4/ENE 16 4.2/E 2(, 2.6/W W 36 4.2/N 7 1.9/NE 17 3.6/SE 27 2.1/N 37 2.1/ teed 8 1.6/tmE 18 3.2/SSE 28 QI 2.8/m 35' l.2/tw 9 2.0/ENE 19 4.0/SSE 29 2.6/S W 39 13.0/ta 10 2.4/DE 20 3.3/S 30 2.2Af 40 15.0Amed k Grourukater Drinkirej hater Surface Water 11 - 1 2 2.2/taE IW-15 3.9/ w t1tal 3.6/W C-10 2.8/W IM-40 10/SSE (C 0.6AeH C-49 2.9/W D-65 3.9/S H Milk arul Fool Proilucts A-1 1 . 4 /13 H-1 2.1/NtM

@ F-1 1.3/ESE S-3 >15.0Anu l

j G-1 1.6/SE S-4 15.0/WrW l

O

" Fish 12x>relire Salisments Aspit ic W*Jetat ion Irrigatol Crops IC 0.6/WrW IC O.6Anei IC 0.6 ARM HR-D1 9.2/S JRR 4A8 JRR 4)M tm 6.5/S

'nnble 3: 1987 Gluss Bitm msLYSIS pmmt GP AIR PNtrICMJttE SNETE (pci/CU. 3emm)

DOICAKR LOCATICNS CCNIBOL DOICA'KR STM OARD DATE. IE_2 IgL} IfC 32 IfC 37 g]lNfig DEVIATION ILC 40 12/30-01/06 0.019 0.017 0.021 0.021 0.020 0.002 0.020 01/06-01/13 0.028 0.030 0.029 0.032 0.030 0.001 0.030 01/13-01/20 0.028 0.029 0.029 0.016 0.026 0.006 0.030 01/20-01/27 0.020 0.020 0.020 0.021 0.020 0.000 0.020 01/27-02/03 0.021 0.019 0.019 0.018 0.019 0.001 0.018 02/03-02/10 0.017 0.016 0.022 0.017 0.018 0.002 0.017 02/10-02/17 0.036 0.024 0.036 0.033 0.032 0.005 0.033 02/17-02/24 0.026 0.023 0.020 0.021 0.023 0.002 0.020 02/24-03/03 0.023 0.019 0.025 0.026 0.023 0.003 0.023 03/03-03/10 0.034 0.027 0.027 0.031 0.030 0.003 0.024 03/10-03/17(1) 0.034 0.037 0.037 0.036 0.036 0.001 0.030 03/17-03/24(1) 0.023 0.021 0.020 0.071 0.021 0.001 0.020 03/24-03/31 0.016 0.019 0.018 0.018 0.018 0.001 0.019 03/31-04/07 0.024 0.010 0.022 0.022 0.020 0.006 0.023 04/07-04/14 0.023 0.020 0.022 0.023 0.022 0.001 0.020 04/14-04/21 0.027 0.027 0.007(2) 0.029 0.028(3) 0.001(3) 0.029 04/21-04/28 0.026 0.015 (2) 0.032 0.024 0.007 0.027 04/28-05/05 0.016 0.024 0.021 0.028 0.022 0.004 0.021 05/05-05/12 0.037 0.037 0.034 0.034 0.036 0.001 0.037 05/12-05/19 0.030 0.029 0.029 0.030 0.030 0.000 0.028 05/19-05/26 0.017 0.016 0.015 0.012 0.015 0.002 0.017 05/26-06/02 0.017 0.017 0.016 0.018 0.017 0.001 0.017 06/02-06/09 0.026 0.023 0.025 0.025 0.025 0.001 0.025 06/09-06/16 0.022 0.021 0.022 0.020 0.021 0.001 0.024 .

06/16-06/23 0.021 0.028 0.028 0.026 0.026 0.003 0.024 06/23-06/30 0.024 0.025 0.023 0.024 0.024 0.001 0.025 05/30-07/07 0.027 0.023 0.025 0.025 0.025 0.001 0.024 07/07-07/14 0.022 0.013 0.021 0.022 0.020 0.004 0.026 07/14-07/21 0.034 0.033 0.030 0.030 0.032 0.002 0.034 07/21-07/28 0.032 0.032 0.034 0.040 0.035 0.003 0.033 07/28-08/04 0.030 0.022 0.025 0.035 0.028 0.005 0.031 08/04-08/11 0.031 0.022 0.031 0.033 0.029 0.004 0.034 08/11-08/18 0.024 0.026 0.029 0.023 0.026 0.002 0.026 08/18-08/25 0.025 0.023 0.027 0.025 0.025 0.001 0.027 08/25-09/01 0.025 0.027 0.024 0.026 0.026 0.001 0.026 09/01-09/08 0.042 0.033 0.039 0.043 0.039 0.004 0.044 09/08-09/15 0.023 0.028 0.029 0.027 0.027 0.002 0.030 09/15-09/22 0.005 0.020 0.025 0.025 0.019 0.000 0.026 09/22-09/29 0.026 0.017 0.045 0.042 0.033 0.012 0.043 (1) Actual values may be 7% lower than shown (see Secticn IV, 'Mcnitoring Pm3mu Deviations")

(2) Sanpler malfuncticn at Iocation 32 (3) Iocaticn 32 not included in average, standard deviation 1987 ANNUAL RADIGIIX3ICAL DWIRCMBEAL OPEPATDG REPCRT NOLF CREEK GENEPATDG STATICH Page 22 of 46

'thble 3: 1987 GGS lush AlgETSIS Innsavan w  !

AIR PARrIGIJEIE SMEMS (Omt'd)

(sci /CU. letIR)

DOICA2tR IDCATIGG CQfIRCL DOICA20R STNOARD D8lE_ I4G_2 IgL3 J,gL}2 IDC 37 AVERAGE DLVIATICH IOC 40 09/29-10/07 0.014 0.011 0.021 0.022 0.017 0.005 0.025 10/07-10/13 0.020 0.014 0.026 0.029 0.022 0.006 0.028 10/13-10/20 0.026 0.026 0.038 0.041 0.033 0.007 0.038 10/20-10/27 0.035 0.026 0.033 0.036 0.033 0.004 0.036 10/27-11/03 0.035 0.031 0.030 0.026 0.031 0.003 0.037 11/03-11/10 0.023 0.024 0.033 0.032 0.028 0.005 0.031 11/10-11/17 0.024 0.020 0.028 0.033 0.026 0.005 0.029 11/17-11/24 0.036 0.026 0.032 0.036 0.033 0.004 0.032 11/24-12/01 0.031 0.032 0.028 0.029 0.030 0.002 0.032 12/01-12/08 0.038 0.034 0.042 0.039 0.038 0.003 0.042 12/08-12/15 0.024 0.015 0.017 0.018 0.019 0.003 0.017 12/15-12/22 0.043 0.046 0.047 0.043 0.045 0.002 0.042 12/22-12/29 0.030 0.033 0.031 0.032 0.032 0.001 0.032 1987 MCUAL RADIGOGICAL DNIROEENTAL OPERATDG REKRT WOLF CREEK GENERATDG STATICH Page 23 of 46

'INEE 4: GRIGOL ?M Insirum: T AIR PARTIQEJmt GEEGITE SAIEUS f 3

(pCL/m )

(corttrol) i toontion: 2 3 32 37 40 Be-7 1 QIR 0.0931 0.0672 0.0973 0.0999 0.0718 2 QIR 0.156 0.123 0.137 0.155 0.0847 i 3 QIR 0.0909 0.0712 0.104 0.125 0.108 4 QIR 0.0490 0.0517 0.0583 Q.0666 0.0596 K-40 1 QIR - -- 0.0128 -- --

2 QIR - - 0.00868 --- ---

3 QIR - -

0.00959 -- --

4 QIR - - - - -

1987 M& RIAL RADIGOGICAL DNIRCHENmL OPDATDG RDWT NULF CREEK GENEATDG STATICH Page 24 of 46

'm EE 5: 1987 HD puerunw (WStarded Ganzter*)

LCCATICH IST OIR .2tKLZB 3RD OIR 41H mR 1 17.1 15.7 17.2 16.4 2 15.6 14.5 15.2 15.3 3 17.1 16.0 16.7 13.8 4 16.8 15.6 17.7 16.7 5 15.9 14.6 15.2 15.2 6 15.8 14.5 16.4 15.2 7 14.5 13.7 15.4 14.3 8 15.7 14.9 16.2 15.5 9 17.1 14.7 15.8 15.1 10 16.9 15.7 17.9 16.6 11 18.2 17.2 , 18.5 18.0 12 17.2 15.8 17.0 17.6 13 17.5 15.5 16.2 17.1 14 17.5 16.3 17.7 17.1 15 17.4 15.9 17.5 17.0 16 17.2 15.9 17.4 17.3 17 19.1 15.9 16.9 17.0 18 17.8 16.8 16.4 17.8 19 17.5 15.9 17.5 17.3 20 17.0 15.9 17.4 17.5 21 14.6 13.4 13.9 14.4 22 15.4 14.7 17.4 17.8 23 16.2 14.6 16.0 16.6 24 16.8 15.8 18.0 17.7 25 12.9 12.2 13.5 14.1 26 16.0 14.5 15.7 15.6 27 17.2 15.9 17.0 17.0 28 14.0 13.6 14.6 14.4 29 14.1 12.9 14.5 14.3 30 16.1 14.4 15.7 15.4 31 15.8 14.8 15.8 16.0 32 15.8 14.4 15.7 16.2 33 17.7 16.4 17.8 17.0 34 17.1 16.0 18.2 17.2 35 16.5 14.8 15.8 15.9 36 16.8 15.2 17.1 16.6 37 15.4 14.4 15.9 15.8 38 18.6 17.1 18.0 18.1 39 16.3 16.4 17.6 16.5 40 15.0 13.1 14.6 14.6

  • Values are the average of two dosinatars at each location.

1987 AtNUAL RADIOLOGICAL DWIRCHGNTAL OPERATIN3 REPCRT WOIE CREEK GDEPATDG STATICN Page 25 of 46

(

'mIER 6: G40EE IER AIWLYSIS RERIAS & IRDGGM)

MmR SAMPIJE (pculitar) mamt rocarza Im-40 Incurra im-15 (Irxilantm) . f Omttoli January 7.3 1 1.6 7.8 1 1.6 February 5.1 1 1.2 6.5 1 1.4 March 5.7 3 1.2 6.6 1.4 Aptil 7.4 1 1.4 7.7 1 1.4 May 6.3 1 1.3 6.2 1 1.3 June 8.5 1 1.5 5.4 1 1.2 July 6.7 1 1.3 6.0 + 1.3 August 7.3 1 1.4 7.5 1 1.4 September 7.2 1 2.0 6.0 1 1.8 October 7.9 1 1.5 7.9 3 1.4 lb,wber 6.3 1 1.4 11 1 2 Decertter 6.2 1 1.5 3.8 2 1.4 Range of Preoperational Values: 4.1 - 10.0 pH/ liter 1987 ANtARL RADIOLOGICAL DWIRCit2NIAL OPDATUG FIKRT WOLF CREEK GDERATDG STATICN Page 26 of 46 i

B BLE 7: 'JRITIIM NRLYSIS RESERS CF S W FACE N M R (pCilliter)

IOCM'IN: EC SP NC MSH (Omm00) 01/20/87 3500 600 -- -

02/17/87 4100 1 600 -

3200 1 600 (WNE DEITfED 03/17/87 4800 600 -

2400 500- EUI YEAR; 04/21/87 11000 f 1000 -

4000 1 500 NCRMAL DEITTICH 05/19/87 4100 500 -- -

LIMIT = 800 pC1/

06/16/87 4400 1 500 4300 500 --

LITER) 07/21/87 3400 600 3100 600* -

08/18/87 4200 500 3700 500 -

09/15/87 5600 600 4200 600 -

10/20/87 5000 1 1200 4200 f 1200 -

11/17/87 3700 600 3700 I 600 -

12/22/87 4000 500 4500 500 -

  • Collection date for locaticn SP was 7/22/87 1987 MHJAL RADIGIIGICAL DNIRCtEDTTAL OPERATDC- REPTT NOLF CREEK GENERATDG STATICH Page 27 of 46

MB[E 8: GH9L ANPLYSIS RESEES T SEDELDE SEDDENT SAMPLES (pC1/ p - dry @ )

om Iocmm wrrn omcemwr1m 05/26/87 DC K-40 10.9 1 1.1 Cs-137 0.113 0.014 Ra-226 2.08 1 0.38 2-228 1.09 0.11 NR Be-7 0.280 1 0.145 K-40 13.0 1 1.3 Cs-137 0.0403 f 0.0097

<- Ra-226 1.17 1 0.31 2 -228 0.797 1 0.080 Ra-228 0.571 1 0.084 10/27/87 DC Be-7 0.535 f 0.172 K-40 9.11 1 0.91 Co-58 0.0488 0.0224 Cs-137 0.0875 1 0.0242 Ra-226 1.90 1 0.38 2-228 1.11 1 0.11 i

l 1

l l

l l 1987 MR1UAL RADIG4GICAL E2WIRCtM25'AL OPEATDG REPCRT l NOIE CREEK GWEATDG STATICN Page 28 of 46 w --

- w m-- -. y, y---y --- --,-,--w ---

gy,,-,-mm_- , , - -- -

'IPB2 9: GMem MmLYSIS RESEES T AQUPEIC vismeION SAMPUS - hxntics DC of NCCL (pci/ gram - wt weight) iwis vacerrm nocu1m omcemumIm TYPE 06/23/87 Rooted Aquatic Be-7 1.34 1 0.13 Plants K-40 1.83 1 0.18 Cs-137 0.0134 1 0.0046 Ra-226 0.298 0.105

'Ih-228 0.0706 1 0.0109 06/23/87 Algae Be-7 2.89 1 0.29 K-40 2.19 1 0.22 Mn-54 0.0209 1 0.0053 Co-58 0.0256 1 0.0051 Co-60 0.0389 1 0.0053 Cs-137 0.0769 0.0077 Ra-226 0.439 1 0.114

'Ih-228 0.221 f 0.022 10/27/87 Rootal Aquatic K-40 1,32 1 0.23 Plants Mn-54 0.0254 1 0.0140 Co-58 0.185 1 0.024 Sb-125 0.136 1 0.047 l

l l

l l

l l

l 1987 MMAL RADIGILGICAL EtNIRONDEAL OPERATDG REPCRT l NOLF CREEK GENERATUG STATIO1 Page 29 of 46 l

I 1

l l

l

'mB[E 10: RES0[DS T 1987 IJ20 USE SGNEY DIRECTICN DISTMCE (MILES) 'IO NEAREST i SirITE FROi PLANP RESIDE 2CE MILK ANIMAL GARDEN A N 1.4 None 1.4 B NNE 1.8 None 3.1 C NE 1.9 None 1.9 D ENE 2.1 2.3 2.1 E E 1.8 1.8* 1.8 F ESE 1.6 1.3 1.6 G SE 1.6 None 1.6 H SSE 3.1 None 3.1 J S 3.3 None 3.3 K SSW 2.6 None 3.8*

L SW 2.1 Ncne 2.8*

,M WSW l.6* None 2.4 N W 2.1 lbne 2.6*

P WiM 2.9 None* 3.5*

Q NW l.4 None* 1.4 R NNW l.9 tbne 2.1

  • Indicates Change fran 1986 Data.

1987 AtMIAL RADICILGICAL DWIRCtME2TIAL OPDATING REPCRT NOLF CREEK GENEATDG STATIOT Page 30 of 46

1 3

TMEE 11: RESOUIS T EPA INIEIRABCRMIGN CGIPARISCM TESTS SAMPLE SAMPLE EPA TELEDYNE IKRVALIZED NLEBER DATE TYPE / UNITS NUCL1DE RESULTS(11c) RESULTS (11c) DEVIATION (SEE NCTTES) 433 10/22/86 Water (1) Gr. Beta 51 5 48 1 1 -1.03 Co-60 24 5 29 1 4 1.84 Cs-134 12 5 12 1 0.00 Cs-137 815 7.7 1 0.6 -0.11 434 11/04/86 Milk (1) I-131 4016 54 f 3 1.54 Cs-137 39 1 5 4815 3.12 436 01/23/87 Water (1) Gr. Beta 10 5 11.7 1 0.6 0.58 438 02/27/87 Milk (1) I-131 9.0 1 0.9 8.7 0.6 -0.64 440 02/13/87 Water (1) H-3 4209 1 421 4100 1 200 -0.45 441 02/06/87 Water (1) Co-60 50 5 5012 0.11 zn-65 91 5 108 f 3 6.00 Ru-106 100 5 100 11 0.11 Cs-134 59 5 62 6 1.03 Cs-137 87 1 5 9214 1.73 443 01/30/87 Fced(2) I-131 78 8 74 1 1 -0.71 Cs-137 84 5 9116 1.98 444 03/20/87 Water (1) Gr. Beta 13 5 14 1 0.46 445 04/03/87 Water (1) I-131 7.0 1 0.7 6.7 0.6 -0.82 448 04/10/87 Air Gr. Beta 43 5 42 3 -0.34 Filter (3)Cs-137 815 811 0.00 450 05/22/87 Water (1) Gr. Beta 7 5 8.3 0.6 0.46 451 04/27/87 Water (1) Gr. Beta 66 I 5 56 f 2 -3.46 Co-60 8 5 8 1 0.00 Cs-134 20 5 15 2 -1.61 Cs-137 15 1 5 1211 -0.92 (1) pCi/ liter (2) pCi/kg (3) pCi/ filter 1987 ANNUAL RADICILGICAL DNIROtMEtTTAL OPERATDU REPORT NOLF CREEK GENERATHG STATIOi Page 31 of 46

TAB [E 11: RESERS T EPA INIERIABGUGUE COIPARISO4 'IEEr1S (Omt'd)

SAMPLE SAMPLE EPA TELEDYNE NORMALIZED NUMBER DATE TYPE / UNITS NUCLIDE RESULTS(ilo) RESULTS (11o) DEVIATION (SEE NOTES) 452 06/12/87 Water (1) H-3 2895 357 2800 1 100 -0.46 453 06/05/87 Water (1) Cr-51 41 5 <53 --

Co-60 64 1 5 63 4 -0.36 Zn-65 1015 <10 --

Ru-106 75 1 5 72 1 12 -1.03 Cs-134 4015 35 1 2 -1.84 Cs-137 80 5 79 1 4 -0.34 454 06/26/87 Milk (1) I-131 5916 49 f 3 -2.79 Cs-137 7415 77 1 5 1.03 456 07/24/87 Water (1) Gr. Beta 515 6.3 1 0.6 0.46 457 08/07/87 Water (1) I-131 48 i 6 59 i 1 3.08 459 07/31/87 Food (2) I-131 8018 88 1 11 1.73 Cs-137 5015 57 1 6 2.54 460 08/28/87 Air Gr. Beta 3015 26 1 3 -1.27 Filter (3)Cs-137 10 5 9 1 -0.35 462 09/18/87 Water (1) Gr. Beta 1215 13 1 1 0.35 464 10/16/87 Water (1) H-3 4492 1 449 4300 100 -0.74 465 10/09/87 Water (1) Cr-51 7015 91 1 12 7.16 Co-60 1515 16 1 1 0.46 Zn-65 4615 51 1 1 1.62 Ru-106 61 5 56 1 4 -1.85 Cs-134 2515 26 1 1 0.23 Cs-137 51 5 55 2 1.27 467 11/20/87 Water (1) Gr. Beta 19 1 5 <1.0 -

468 10/21/87 Water (1) Gr. Beta 72 I 5 73 f 2 -0.23 Co-60 16 5 19 1 3 1.15 Cs-134 16 5 14 ! 3 -0.58 Cs-137 24 5 25 4 0.25 469 12/04/87 Water (1) I-131 26 f 6 26 1 2 0.10 i

(1) ECi/ liter l (2) pC1/kg l (3) pC1/ filter 1987 ANNUAL RADIOLOGICAL DWIROtED7TAL OPERATIIG REPORT NOLF CREEK GENERATIlG STATION Page 32 of 46

FICURES I

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  • - AIRBORNE PARTICULATE AND RADIOIODINE 1987 A:21UAL RADIOLOGICAL E!NIROtNE21TAL OPERATIt1G REPORT WOIE CREEK GE!iERATI!1G STATIOt1 Page 33 of 46

FIGUEE 2

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l 1987 A!RIUAL RADIOLOGICAL E?NIR0!NDITAL OPERATI!1G REFORT l W'OLF CREEK GEtTERATI!1G STATIO!1 Page 34 of 46

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  • -DRINKING WATER A-SURFACE WATER m-GROUND WATER v-SHORELINE SEDIMENT /

ROOTED AQUATIC PLANTS l

l 1987 A:RIUAL RADIOLOGICAL EtNIRO!NDTTAL OPERATIt1G REPORT l il0IE CREEK GEtIERATItX3 STATIOt1 Page 35 of 46 l 1

FIGURE 4

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  • -MILK m-FOOD PRODUCTS 6-FISH (WCCL) A-FISH (JRR) 1987 AtR1UAL RADICIDGICAL DNIR0tNC1Tt.L OPERATI!1G REPORT WOLE CREEK GEt.'ERATIt1G STATIOtt Page 36 of 46

FIGURE 5 l

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  • -TLD s-DRINKING WATER 4- MILK *-BROADLEAF VEGETATION /

IRRIGATED CROPS l

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! 1987 A!RIUAL RADIOWGICAL ENVIR0!NDITAL OPERATIt1G REPORT WOT CREEK GENERATItJG STATION Page 37 of 46

g 0; nwan s .

R5 1987 AIRBORNE PARTICULATE ACTIVITY N9 WEEKLY GROSS BETA ANALYSIS RESULTS b"

Mo E 1.00E-01 58 ay yM 9.00E-02 d

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[ J F M A M J J A S O N D e

D INDICATOR AVERAGE + CONTROL LOCATION 40

FIGURE 7 8

95 INDICATOR / CONTROL COMPARISON o>

hh 1987 AIR PARTICULATE GROSS BETA RESULTS X$ 200 g 190 -

@8 180 eg y5 _

170 gh 160

$0 150 Oh g 140

$ 3 130 a < O q > 120 0 N 4 110 0 g _

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gg FIGURE 8 1

G" n

RE OPERATIONAL TLD RESULTS BY QUARTER gg (NEARSITE & CONTROL LOCATION AVERAGES) g" 24 -

E as 22 -

@ *m reak due to 5 20 - / Chernobyl gh" [ Accident

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8 1985 1986 1987 1988

$ 0 NEARSITE AVERAGE + CONTROL AVERAGE PREOP RANGE

FIGUIE 9 E 'S NEARSITE TLD VARIATION BY QUARTER ga2

( 5 OF CONTROL LOCATION VALUES )

nh

  • 140 130 -

es -

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a ych 110 u C1 o D o o o ooo o ooo oo o o oo oo o g ,,, a v v o 9 O 2 o 90 m .J o 80 o %

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FICURE 10 k! DRINKING WATER GROSS BETA ACTIVITY .

kh MONTHLY SAMPLE RESULTS (OPERATIONAL)

N si 1.2E+ 01 o"

OE R6 1.1E+ 01 -

i

$o Preoperational average 1.0E+01 - PI "" " " " d" " "' "

a c-0 h

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Preoperational average minus two stac<!ard deviations 2.0E+ 00 _

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$ 0.0E+00 i i ii,iii i i i i i i i iiiiiiiiiii i U 1985 1986 1987 1988 R

O LY-40 + PREOP AVERAGE A BW-15 (CONTROL)

@G FIGURE 11 95 TRITIUM RELEASES / CONCENTRATIONS OE ma IN WOLF CREEK COOLING LAKE

  • E 1.0E+05

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5

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, 1.0E+ 02 i i i i iiiiiiiiiiiii i iiiiiiiiiiiii -T i 1985 1986 1987 1988 El WCCL CONCENTRATION A LIQUID RELEASES

FIWRE 12 k5 LIQUID EFFLUENTS RELEASED TO WCCL o

Nh QUARTERIX OPERATIONAL RELEASES Eg 1.0E + 04 8

5 ^

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  • 1985 1986 1987 1988 2

O Cr-51 + M n--54 0 Co-58 A Co-60 X S b-125 V Cs-137

FIGURE 13 z-

$@ Cs-137 IN SIIORELINE SEDIMENT kb LOCATION DC, WOLF CREEK COOLING LAKE Q$ 1.0E+00 -

@ 7.9E-01 -

5 6.3E $o 5.0E @{

O"

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1981 1982 1983 1984 1985 1986 1987 1988 P.,

u

  • II PREOPERATIONAL o OPERATIONAL

h w

FIGUIE 14 a!

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Cs-137 IN AQUATIC VEGETATION N9 g" (PREOP & OP) AQUATIC PLANTS & ALGAE gy 0.20

$o 0.19 h, 0.18 9 0.17 0c ea 0.16

@$ 0.15

$ 0.14 Q 3 0.13 g

$ h 0.12

@ b 0.11 in F1 E

a F 0.10 i

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  • 0.06 S +

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0.02 4 dQ 0.01 + 0 0.00 .iiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiiii,giii o 1981 1982 1983 1984 1985 1986 1987 1988 f1 PREOP (ALGAE) + OPERATIONAL (ALGAE) 0 OPER (AQ. PLANTS)

APPIBOICES 1987 JNGL RADIfYmTr%L ENVIlOGIENEL TERA 5'DG REEUU MIF GEEK GEN 5UEDG SBTIOi ,

i WW TEL WINE ISOIOPES 50 Van Buren Avenue Westwood, New Jersey ,

Prepartd for Wolf Creek Nuclear Operating Corporation

- - - -----4 ,.- ,__.-. , . - . , _ . , - - . - , e-. - . - -..m -,,,=% ., r . --, ---y , , .-- - ,_m,.w,m ge.. -g-.----- r-, * , m---yg- g- --w-

TABLE OF CuisTanas: APPENDICES ESAE 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-8 Composite Air Particulate Filters ............... A-26 The nnolumine s cent Do s ime t er s . . . . . . . . . . . . . . . . . . . . A-31 Fish ............................................ A-35 Food and Garden Crops ........................... A-39 Milk ............................................ A-46 Shoreline Sediments .......,..................... A-57 Aquatic Vegetation .............................. A-59 Drinking Water .................................. A-60 Ground Water .................................... A-68 Surface Water ................................... A-72 A-il

APPENDIX A:

SUMMARY

TABLES 1

I

ENVIRONMENTAL RADIOLOGl*.AL MONITORING PROGRAM StMtARY Name of Facility Wolf Creek Nuclear Docket No. STN 50-482 Location of Factitty Coffey County, Kansas Reporting Period Annual 1987

. (County. State)

Analysts and Lowr Limit Number of Medtim or Pathway Total number of All Indicator tocations location with Highest Annual Mean Control tocations lionroutine Sampled of Analysts Detection ** Rean (r) name **Rean (I)

  • w an tr) Reported (Unit of Measurement) Performed (LLD) ** Range Distance and Directions ** Range * *R ange Measurements **

Station No. 40 Air Gross (258) 3 26(206/206) 37 2.1 miles N w 28(52/52) O Parttquiate 8 eta (5-47) (12-43)

(Il0-J PCl/

Ca.M.) 40 15 miles WW 28(52/52) 28(52/52) 0 (17-44) (17-44) 1-131 (258) 7 -(0/206) N/A N/A -(0/52) 0 Gamma (20) h Be-7 1 97(16/16) 37 2.1 miles N W 112(4/4) 81(4/4) 0 (49-156) (67-155) (60-108)

K-40 24 10(3/16) 32 3.2 miles WW 10(3/4) -(0/4) 0 (8.7-13) (8.7-13) --

Stations 39 and 40 External TLD (320)

Radiation Quarterly 0.05 0.18(304/304) 11 1.6 miles E 0.20(8/8) 0 (mR/ day) 0.17(16/16)

(0.13-0.24) (0.19-0.21) (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)

ENVIRosetENTAL RADIOLOGICAL MONITORING PROGRMt 5tsetARY Name of Factitty Idolf Creek nuclear Docket No. STN 50-482 Location of Facility Coffey County, Kansas Reporting Period Annual 1987 (County,5t ete)

Analysis and Lower Limit Number of Medlun or Pathway Total Number of All Indicator locations Location with Highest Annual Mean Control locations it.nroutine Sampled of Analysts Detection ** Mean (f) Name **Mean (f) **Mean (f) Reported (Unit of Measurement) Performed (LLD) * *R ange Distance and Directions ** Range ** Range Measurements **

J. Redmond Reservoir Fish Gamma (15)

(pC1/g) K-40 0.5 3.3(11/11) JRR 3.6(4/4) 3.6(4/4) o (met meteht) (2.2-4.1) (3.3-3.8) (3.3-3.8)

Cs-137 0.02 0.14(2/11) wCCL o.14(2/11) -(o/4) o (0.13-0.15) (0.13-0.15) --

T to 5-4 Food and Gamuna (16)

Garden Crops se-7 0.09 0.60(9/10) R-1 2.1 miles NNW o.63(2/2) 0.63(6/6) o (pct /g met (0.20-1.0) (0.62-o.63) (0.35-1.1) wefght)

K-40 0.5 5.2(10/10) NR01 15(1/1) 4.o(6/6) o (3.2-15) --

(1.5-9.5)

Cs-137 0.02 0.018(2/10) 5-4 15 miles ndNW o.022(1/6) 0.022(1/6) o (0.017-0.019) -- --

Th-228 0.04 -(0/10) 5-4 15 atles WNW o.046(1/6) 0.046(1/6) 0 hominal Lower Limit of Detection (LLD)

Mean and range based upon detectable measurements only. Fraction of detectable measurements at spectfled locations is indicated in paratheses (f)

ENVIROOMENTAL RADIOLOGICAL MONITORING PROGRAM SupMARY Name of Facility Wolf Creek Nuclear Docket No. STN 50-482 Location of Facility Coffey County, Kansas Reporting Period Annual 1987 ;i (County,5 tate) .

Analysis and Lower Limit Number of Meditse or Pathway Total Number of All Indicator Locations Location with Highest Annual Mean Control Locations Nonroutine Sampled of Analysis Detection ** Mean (f) Name **Mean (f) "Mean (f) . Reported (Unit of Measurement) Performed (LLD) ** Range Distance and Directions ** Range ** Range Measureement s**

Siation 5-3 Milk I-131 (44) 0.2 -(0/24) N/A N/A -(0/20) 0 (pCl/f) -- --

Gasuna (44)

K-40 100 1233(24/24) P-2 2.9 miles WNW 1584(9/9) 12 % (20/20) 0 (600-1780) (1170-1780) (1020-1630)

Cs-137 5 6.7(1/24) 5-3 15 miles WNW 6.9(1/20) 6.9(1/20) 0

=

a, -

Nominal Lower Limit of Detection (LLD)

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

1 ENVIRONNENIAL RADIOLOGICAL MONITORING PROGRAM St#9tARY Name of Facility Idolf Creek Nuclear Docket No. STN 50-482 Location of Facility Coffey County, Kansas Reporting Period Annual 1987 (County,5 tate) ,

Analysis and Lower Limit Number of feedle or Pathway Total Ihamber of All Indicator toCattons toCation with Highest Annual Mean Control Locations Nonroutine Sampled of Analysis Detection ** Rean (f) Name

  • W an (f)
  • W an (f) Reported (Unit of ferasurement) Performed (tLD) ** Range Distance and Directions ** Range **R ange Measurements **

Its Control 5s.oreline Soll (pCl/g (dry melght) Gamma (3)

Be-7 0.2 0.41(2/3) DC 0.6 mile WNW 0.54(1/2) -- 0

,. (0.28-0.54) --

e K-40 0.5 11(3/3) NR 6.5 miles 5 13(1/1) --

0 (9.1-13) --

Co-58 0.02 0.049(1/3) DC 0.6 mile idend 0.049(1/2) --

0 Cs-137 0.06 0.000(3/3) DC 0.6 mile idNW 0.10(2/2) -- 0 (0.040-0.11) (0.088-0.11)

Ra-226 0.5 1.7(3/3) DC 0.6 mile Wind 2.0(2/2) --

0 (1.2-2.1) (1.9-2.1)

Ra-228 --

0.57(1/3) NR 6.5 miles 5 0.57(1/3) --

0 Th-228 0.04 1.0(3/3) DC 0.6 mile idleW l.l(2/2) --

0 (0.000-1.1) (1.1-1.1)

  • paaminal Lower Limit of Detection (LtD) plean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (f)

ENVIR0lfl[NTAL RADIOLOGICAL MONITORING PROGRAM St#984RY Name of Facility Idolf Creek nuclear Docket No. STN 50-482 _

Location of Facility Cof fey County, Kansas Reporting Period Annual 1987 (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 honroutine Sampled of Analysis Detection ** Rean (f) Name "Mean (f) **Rean (f) Reported (Unit of Measurement) Performed (LLD) ** Range Distas.ce and Directions ** Range ** Range Measurements **

s ND 1 Uu 4RM.

Vegetation, h (3)

Aquatic Se-7 0.1 2.l(2/3) DC 0.6 mile lead 2.l(2/3) -- 0 (pC1/g met (1.3-2.9) (1.3-2.9) weig%t)

K-40 0.5 1.8(3/3) DC 0.6 atle hind 1.8(3/3) --

0 (1.3-2.2) (1.3-2.2) m -54 0.01 0.023(2/1) DC 0.6 mile Imad 0.023(2/3) -- 0 (0.021-0.025) (0.021-c.025) 7 U1 Co-58 0.01 0.11(2/3) DC 0.6 mile lead 0,11(2/3) --

0 (0.026-0.19) (0.026-0.19)

Co-60 0.01 0.039(1/3) DC 0.6 mile Nmd 0.039(1/3) --

0 Sb-125 0.05 0.14(1/3) DC 0.6 mile temi 0.14(1/3) --

0 Cs-137 0.01 0.045(2/3) DC 0.6 mile IdNW 0.045(2/3) --

0 (0.013-0.077) (0.013-0.077)

Ra-226 0.2 0.37(2/3) DC 0.6 mile Immi 0.37(2/3) ~ 0 (0.30-0.44) (0.30-0.4%)

Th-228 0.02 0.15(2/3) DC 0.6 mile land 0.lNE/3) --

0 (0.071-0.22) (0.071 '1 22) hominal 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)

9 ENvlR0leq[NTAL RADIOLOGICAL MONITORING PROGRAM Supn*8ty Name of Facility Wolf Creek Nuclear Docket sto. STN 50-482 Location of Facility Coffey County, Kansas Reporting Period Annual 1987 (County,51ste)

Analysts and Lower Limit Number of Medlw or Pathway Total Itamber of All Indicator tocations Location with Highest Annual Mean Control Locations Nonroutine Sampled af AnatysIs Detectton ** nean (r) Maae **nean (f} **nean (f) Reported (Unit of pleasurement) Performed (LLD) ** Range Distance and Directions **R uge **R ange Measurements **

BW-15 Cater I-131 (24) 0.5 -(0/12) N/A N/A -(0/12) 9 Drinking .- ..

(pCl/f)

Gross (24) 2 6.8(12/12) 8W-15 3.9 miles SW 6.9(12/12) 6.9(12/12) O Seta (5.1-8.5) (3.8-11) (3.8-11) r--=* (24) -(0/12)

N/A N/A -(0/12) 0 3 Tritium (8) 1000 -(0/4) N/A N/A -(0/4) 0 Cater. B-12 Ground (pC1/f) 1-131 (16) 0.5 -(0/12) NA -(0/4) 0 r- (16)

K-40 60 94(2/12) C-49 2.9 atles SW 122(1/4) -(0/4) 0 (66-122) -- -.

Tritium (16) 1000 -(0/12) N/A N/A -(0/4) 0

      • Nominal Lower Limit of Detection (LLD)

Mean and range based upon detectable measurements only. Traction of detectable ocasurements at specified locations is indicated in parenthest. (f)

ENVIR01stENTAL RADIOLOGICAL MONITORING PROGRAfl SismARY mame of factitty Wolf Creek muclear Docket no. STN 50-482 Location of Facility Coffey County, Kansas Reporting Period Annual 1987 (County.5t ate)

Analysis and Lower Limit Number of Medium or Pathwey Total member of All Indicator iocattons tocatlon with Highest Annual Mean Control toutlons NonroutIne Sampled of Analys1s Detection == nean (r) name ==Rean (f) ==mean (f) Reported (Unit of Measorement) Performed (LLD) **R ange Distance and Directions ** Range * *R ange Measurements **

Mush Water, Surface Gamma (34)

(pCf/f)

K-40 60 125(1/22) WC 125(1/3) -(0/12) 0 Tritium (34) 1000 4320(22/22) DC 0.6 mile IduW 4810(12/12) -(0/12) 0 (2400-11000) (3400-11000) --

k '

  • moninal 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)

l 1

APPENDII 8: DATA TABLES m ' = _ . _ _ _ _ _ - - - _ . . . - _ _ _ _

WOLF COEEK NUCLEA2 OPE 2nTING CORP EXPO 5URE PdTHWAY - DICBORNE AIR PARTICULATE & CHARCOAL FILTERS STATION NUM6ER 02 COLLECTION DATE MID-COUNT A P FILTER MID-COUNT CHARC0AL FILTER START STOP TIME GROSS SETA TIME I-131 OATE OATE VOLUME UNITS DATE (PCI/CU.M.) DATE (PCI/CU.M.3

_-- --- -___= _ _

__ _ _ _== _

12/30 01/06 3.07E 08 CC 01/26 1.9 +-0.3 E-02 01/11 L.T. 3. E-02 01/06 01/13 3.07E 08 CC 01/29 2.8 +-0.3 E-02 01/15 L.T. 3. E-02 C1/13 01/20 3 15E 08 CC 01/31 2.8 +-0.3 E-02 01/25 L.T. 3. E-02 01/20 01/27 3.01E 08 CC 02/05 2.0 +-0.3 E-02 01/28 L.T. 2. E-02 01/27 02/02 3.01E 08 CC 02/20 2.1 +-0.3 E-02 02/09 L.T. 4 E-02 02/03 02/10 3.02E OR CC 03/03 1.7 +-0.3 E-02 c2/15 L.T. 2. E-02 02/10 02/17 3.00E 08 CC 03/04 3.6 +-0.4 E-02 02/20 L.T. 2. E-02 2 C2/17 02/24 3.05E 08 CC 03/09 2.6 +-0.3 E-02 02/28 L.T. 3. E-02 02/24 03/03 2 91E 08 CC 03/24 2.3 +-0.3 E-02 03/05 L.T. 3. E-02 03/03 03/10 3.10E 08 CC 03/24 3.4 +-0.4 E-02 03/14 L.T. 3. E-02 03/10 03/17 3.04E 08 CC 03/26 3.4 +-0.4 E-02 03/21 L.T. 2. E-02 03/17 03/24 2.95E 08 CC 04/08 2.3 +-0.3 E-02 03/26 L.T. 3. E-02 03/24 03/31 2.89E 08 CC 04/15 1.6 +-0 3 E-02 04/02 L.T. 3. E-02 03/31 04/07 2.68E 08 CC 04/21 2.4 +- 0.3 E-0 2 04/12 L.T. 2. E-02 04/07 04/14 2.92E 08 CC 05/01 2.3 +-0.3 E-02 04/18 L.T. 2. E-02 64/14 04/21 2.82E 08 CC 05/04 2.7 +-0.4 E-02 04/23 L.T. 3. E-02 04/21 04/28 2.92E 08 CC 05/08 2.6 +-0.3 E-02 05/02 L.T. 2. E-02 04/28 05/05 2.87E 08 CC 05/26 1.6 +-0.3 E-02 05/12 L.T. 3. E-02 tol OUPLICATE ANALYSIS

WOLF CCFE2 NUCLES2 OPE 3ATING CORP EXPO 5URE DATHW V - atC80RNE AIR PARTICUL ATE & CHARCOAL FILTERS STATION NUM8ER 02 COLLECTION CATE MID-COUNT A P FILTER MID-COUNT CHARC0AL FILTER START STOP TIME GROSS BETA TIME I-131 0 ATE 0 ATE VOLUME UNITS OATE (PCI/CU.M.3 OATE (PCI/CU.M.3

. . . . . . . . = - . _ - - - - _=__

_ - _...... --- __ ==...= ---- _ = -

.. - _=.....

(A304/28 05/05 2.87E 08 CC 05/22 1.8 +-0.3 E-02 05/11 L.T. 4 E-02 05/05 05/12 2.89E 08 CC 05/26 3.7 +-0.4 E-02 05/15 L.T. 3. E-02 05/12 05/19 2.87E 08 CC 06/04 3.0 +-0.3 E-02 05/22 L.T. 2. E-02 05/19 05/26 2.83E 08 CC 06/05 1.7 +-0.3 E-02 05/28 L.T. 3. E-02 05/26 06/02 2.87E 08 CC 06/12 1.7 +-0.3 E-02 06/05 L.T. 3. E-02 06/02 06/09 2.90E 08 CC 06/19 2.6 +-0.3 E-02 06/12 L.T. 3. E-02 06/09 06/16 3.05E 08 CC 06/30 2 2 +-0.3 E-02 06/20 L.T. 3. E-02 06/16 06/23 2.96E 08 CC 07/08 2.1 +-0.3 E-02 06/28 L.T. 3. E-02

y. 06/23 06/30 3 03E 08 CC 07/13 2.4 +-0.3 E-02 07/03 L.T. 2. E-02 06/30 07/07 2.77E 08 CC 07/23 2.7 +-0.3 E-02 07/11 L.T. 2. E-02 07/07 07/14 3.02E 08 CC 07/31 2.2 +-0.3 E-02 07/21 L.T. 3. F-02 07/14 07/21 3.09E 08 CC 08/05 3.4 +-0.4 E-02 07/23 L.T. 3. E-02 07/21 07/28 2.97E 08 CC 08/07 3.2 +-0.3 E-02 08/01 L.T. 3. E-02

~

07/28 08/04 2.95E 08 CC 08/17 3.0 +-0.3 E-02 08/06 L.T. 3. E-02 08/04 08/11 2.83E 08 CC 08/21 3.1 +-0.4 E-02 08/16 L.T. 2. E-02 08/11 08/18 2.94E 08 CC 08/28 2.4 +-0.3 E-02 08/20 -L.T. 2. E-02 08/18 08/25 2.96E 08 CC 09/03 2.5 +-0.3 E-02 08/27 L.T. 2. E-02 tal08/18 08/25 2.96E 08 CC 09/03 2.7 +-0 3 E-02 08/29 L.T. 1. E-02 (Al OUPLICATE ANALYSIS

WOLF COEE2 NUCLEC3 OPE 2CTING COR? ,

EXPOSURE PSTHWAY - AIR 80RNE AIR PARTICULATE & CHARCOAL FILTERS STATION NUM8FR 02 COLLECTION DATE MIO-COUNT A P FILTER HID-COUNT CHARCOAL FILTER START STOP TIME GROS $ BETA TIME I-131 DATE DaTE VOLUME UNITS DATE (PCl/CU.M.) DATE (PCI/CU.M.1

- _.....=- --

...- ------ . .-=___-- --- .- - ----- --- .........--- _ =-- =

08/25 09/01 3.01E 08 CC 09/18 2.5 +-0.3 E-02 09/04 L.T. 2. E-02 09/01 09/08 3.00E 08 CC 09/22 4.2 +-0.4 E-02 09/11 L.T. 3. E-02 09/08 09/15 2.90E 08 CC 09/24 2.3 +-0 3 E-02 09/17 L.T. 3. E-02 09/15 09/22 3.02E 08 CC 10/02 5.4 *-1.9 E-03 09/24 L.T. 3. E-02 09/22 09/29 3.01E 08 CC 10/08 2.6 +-0.3 E-02 10/01 L.T. 2. E-02 09/29 10/07 3.4TE 08 CC 10/20 1.4 +-0.2 E-02 10/11 L.T. 2. E-02 10/07 10/13 2.49E 08 CC 10/23 2.0 +-0.3 E-02 10/17 L.T. 2. E-02 10/13 10/20 3.03E 08 CC 10/27 2.6 +-0.3 E-02 10/25 L.T. 2. E-02 10/20 10/27 3.03E 08 CC 11/04 3.5 +-0.4 E-02 10/30 L.T. 2. E-02 C) 11/03 10/27 3.02E 08 CC 11/12 3.5 +-0.3 E-02 11/06 L.T. 2. E-02 11/03 11/10 3.03E 08 CC 11/19 2.3 +-0.3 E-02 11/12 L.T. 2. E-02

~~

11/10 11/17 3.03E 08 CC 11/25 2.4 +-0.3 E-02 11/21 L.T. 3. E-02 11/17 11/24 2.91E 08 CC 12/02 3.6 +-0.4 E-02 12/01 L.T. 2. E-02 11/24 12/01 2.94E 08 CC 12/10 3 1 +-0.4 E-02 12/04 L.T. 2. E-02 12/01 12/08 3.01E 08 CC 12/17 3.8 *-0.4 E-02 12/12 t.T. 2. E-02 12/08 12/15 3.14E 08 CC 12/23 2.4 +-0.4 E-02 12/19 L.T. 2. E-02 12/15 12/22 3.10E 08 CC 01/05 4.3 +-0.4 E-02 12/25 L.T. 2. E-02 12/22 12/29 3.13E 08 CC 01/08 3.0 *-0.3 E-02 01/04 L.T. 2. E-02

COL F CCEE: muCLEC3 OPE 3 STING CORP E XPOSUR E PCTHWAY - Al".80RNE Att PA#TICULATE & CHARCOAL FILTERS STATION NUM8ER 03 COLLECTION OATE MI D-COUNT A P FILTER MIO-COUNT CHARCOAL FILTER STARY STOP TIME GROSS BETA TIME I-131 OATE DATE VOL UM E UNITS DATE (PCI/CU.M.) DATE (PCI/CU.M.8

. . - =--- - - -

_ . . . =_ _ - _ - ---

__=--- ..

12/30 01/06 2.97E 08 CC 01/26 1.7 +-0.3 E-02 01/11 L.T. 3. E-02 01/06 01/13 2.96E 08 C'C 01/29 3.0 *-0.3 E-02 01/15 L.T. 3. E-02 01/13 01/20 3.00E 08 CC 01/31 2.9 +-0.3 E-02 01/25 L.T. 3. E-02 01/20 01/27 2.81E 08 CC 02/05 2.0 +-0.3 E-02 01/28 L.T. 2. E-02 01/27 02/03 2 8&E 08 CC 02/20 1.9 *-0.3 E-02 02/09 L.T. 4. E-02 02/03 02/10 2.91E 08 CC 03/03 1.6 +-0.3 E-02 02/15 L.T. 3. E-02 02/10 02/1T 2.93E 08 CC 03/04 2.4 +-0.3 E-02 02/20 L.T. 2. E-02 02/17 02/24 3 00E 08 CC 03/09 2.3 +-0.3 E-02 02/28 L.T. 3. E-02 i

Fd 02/24 03/03 2.96E 08 CC 03/24 1.9 +-0.3 E-02 03/05 L.T. 3. E-02 H

03/03 03/10 3.01E 08 CC 03/24 2.T +-0.3 E-02 03/14 L.T. 3. E-02 03/10 03/17 2.99E 08 CC 03/26 3.7 +-0.4 E-02 03/21 L.T. 2. E-02 03/17 03/24 2 95E 08 CC 04/08 2.1 +-0.3 E-02 03/26 L.T. 3. E-02 03/24 03/31 2.89E 08 CC 04/15 1.9 +-0.3 E-02 04/02 L.T. 3. E-02 03/31 04/07 3.07E 08 CC 04/21 1.0 +-0.2 E-02 04/12 L.T. 2. E-02 (A103/31 04/07 3.07E 08 CC 04/21 1.2 +-0.2 E-02 04/13 L.T. 4 E-02 04/07 04/14 3.09E 08 CC 05/06 2.0 +-0.3 E-02 04/18 L.T. 2. E-02 04/14 04/21 3.06E 09 CC 05/04 2.7 +-0.3 E-02 04/23 L.T. 2. E-02 04/21 04/28 3 03E 08 CC 05/08 1.5 +-0.3 E-02 05/02 L.T. 2. E-02 (Al OUPLICATE ANALYSIS

woL F CCEE3 NUCLEAR OPE 0aTING CotP EXPOSURE pcTNw'Y - AIC80RNE AIR PARTICULATE 6 CHARCOAL FILTERS STATION NUM8ER 03 C OL L E CT ION DATE MI D-C OUNT A P FILTER MIO-COUNT CHARC0AL FILTER START STOP TIME GROSS BETA TIME I-131 DATE DATE VOLUME UNITS OATE IPCI/CU.M.5 DATE I*CI/CU.M.)

...... ___- =-__ --_ - - - - - - _

- - - . _ - _ - _ _ - - - - - _ = . = - - - - _

04/28 05/05 3.02E 08 CC 05/22 2.4 +-0.3 E-02 05/11 L.T. 4 E-02 05/05 05/12 2.85E On CC 05/26 3.7 +-0.4 E-02 05/15 L.T. 3 E-02 05/12 05/19 3.17E 08 CC 06/04 2.9 +-0.3 E-02 05/22 ..L.T. 2. E-02 05/19 05/26 3.08E 08 CC 06/05 1.6 +-0.3 E-02 05/28 L.T. 3. E-02 05/26 06/02 3.12E 08 CC 06/12 1.7 +-0.3 E-02 06/05 L.T. 2. E-02 06/02 06/09 3 10E 08 CC 06/19 2. 3 +-0. 3 E-02 06/12 L.T. 2. E-02 06/09 06/16 3.10E 08 CC 06/30 2.1 +-0.3 E-02 06/20 L.T. 3. E-02 06/16 06/23 2.96E 08 CC 07/08 2.8 +-0.4 E-02 06/28 L.T. 3. E-02

>I 06/23 06/30 3.03E 08 CC 07/13 2.5 +-0.3 E-02 07/03 L.T. 2. E-02 w

06/30 07/07 2.85E 08 CC 07/23 2.3 +-0.3 E-02 07/11 L.T. 2. E-02 07/07 07/I4 3.03E 08 CC 07/31 1.3 +-0.3 E-02 07/21 t.T. 3. E-02 07/14 07/21 3.04E 08 CC 08/05 3.3 +-0.4 E-02 07/23 L.T. 3. E-02 l 07/21 07/28 3.07E 09 CC 08/07 3.2 +-0.3 E-02 08/01 L.T. 3. E-02 07/28 08/04 3.06E 04 CC 08/17 2.2 +-0.3 E-02 08/06 L.T. 3. E-02 08/04 08/11 2.90E 08 CC 08/21 2.2 +-0 3 E-02 08/16 L.T. 2. E-02 Ost11 08/18 3.09E 08 CC Oe/28 2.6 +-0.3 E-02 08/20 L.T. 2. E-02 i

04/18 08/25 3.01E 08 CC 09/03 2 3 +-0.3 E-02 08/27 L.T. 2. E-02 on/25 09/01 3.06E 08 CC 09/18 2.7 +-0.3 E-02 09/04 L.T. 2. E-02

WOLF CGEE2 NUCLESQ OFF0ATING CORP EXPOSURE patNw2V - ela90RNE AIR PARTICULATE A CMaRCOAL FILTERS STaft0M NUM8ER 03 COLLECTION DATE MI D-C OUNT A P FILTER MID-COUNT CHARCOAL FILTER START STOP TIME CROSS SETA TIME  !-131 DATE DaTE VOLUME UNITS DATE (PCI/CU.M.9 DATE (*CI/CU.M.)

-............ ._ _- ==-- _ _- -_ ==- -

=_ . =- _--. ........ --

09/01 09/08 3.20E 08 CC 01/23 3.3 +-0.3 E-02 09/11 L.T. 3. E-02 09/08 09/15 3.00E 38 CC 09/24 2.8 +-0.3 E-02 09/17 L.T. 3. E-02 09/15 09/22 3.06E 08 CC 10/02 2.0 +-0.3 E-02 09/24 L.T. 3. E-02 09/22 09/29 3.06E 08 CC 10/08 1.7 +-0.3 E-02 10/01 L.T. 2. E-02 09/29 10/07 3.64E 08 CC 10/20 1.1 +-0.2 E-02 10/11 L.T. 1. E-02 10/07 10/13 2.49E 08 CC 10/23 1.4 +-0. 3 E-02 10/17 L.T. 2. E-02 10/13 10/20 3.00E 08 CC 10/27 2.6 +-0.3 E-02 10/25 L.T. 2. E-02 (A310/13 10/20 3.08E 08 CC 10/27 2.7 +-0.3 E-02 10/25 L.T. 2. E-02

[s 10/20 10/27 3.08E 08 CC 11/04 2.6 +-0.3 E-02 10/30 t.T. 2. E-02 w

10/27 11/03 3.02E 08 CC 11/12 3.1 +-0.3 E-02 11/06 L.T. 2. E-02 11/03 11/10 3.08E 08 CC 11/19 2.4 +-0.3 E-02 11/12 L.T. 2. E-02 11/10 11/17 3.13E 08 CC 11/25 2.0 +-0.3 E-02 11/21 L.T. 2. E-02 11/17 11/24 3.06E 08 CC 12/02 2.6 +-0.3 E-02 12/01 L.T. 2. E-02 11/24 12/01 3.04E 08 CC 12/10 3.2 +-0.4 E-02 12/04 L.T. 2. E-02 12/01 12/08 3.01E 08 CC 12/17 3.4 +-0.3 E-02 12/12 L.T. 2. E-02 12/08 12/15 3.04E 08 CC 12/23 1.5 +-0.3 E-02 12/19 L.T. 2. E-02 12/15 12/22 2.90E 08 CC 01/05 4.6 +-0.4 E-02 12/25 L.T. 2. E-02 12/22 12/29 2.83E OS CC 01/08 3 3 +-0.4 E-02 01/04 L.T. 2. E-OZ EA) DUPLICATE ANALYSIS

q WOLF CCEEE NUCLEAR OPE 2aTING CDR) ,

EXPO 5URE PCTHWAY - CI;80RNE AIR PARTICULATE & CHARCOAL FILTERS STATION NUM8ER 32 COLLECTION DATE M I D-COUNT A P FILTER MID-COUNT CHARCOAL FILTER START STOP TIME GROSS SETA TIME I-131 DATE DATE VOLUME UNITS DATE (PCI/CU.M.) DATE (PCI/CU.M.)

_- ....-- ____- .......... = .... - ----

,e 12/30 01/06 3 14E 08 CC 01/26 2.1 +-0.3 E-02 01/11 L.T. '3. E-02

~

01/06 01/13 3.10E 08 CC 01/29 2.9 +-0.3 E-02 01/15 L". T . 3. E-02 01/13 01/20 3.21E 08 CC 01/31 29 +-0.3 E-02 01/25 L.T. 3. E-02 01/20 01/27 3.04E 08 CC 02/05 2.0 +-0.3 E-02 01/28 L.T. 2. E-02 01/27 02/03 3.06E 08 CC 02/20 1.9 +-0.3 E-02 02/09 L.T. 4. E-02 02/03 02/10 3.04E 08 CC 03/03 2.2 +-0.3 E-02 02/15 L.T. 2. E-02 02/10 02/17 3.12E 08 CC 03/04 3.6 +-0.4 E-02 02/20 L.T. 2. E-02 02/17 02/24 3.16E 08 CC 03/09 2.0 +-0.3 E-02 02/28 L.T. 3. E-02 8

02/24 03/03 3.06E 08 CC 03/24 2.5 +-0.3 E-02 03/05 L.T. 3. E-02 03/03 03/10 3.16E 08 CC 03/24 2.7 +-0.3 E-02 03/14 L.T. 3. E-02 (A303/03 03/10 3.16E 08 CC 03/24 2.P +-0.3 E-02 03/16 L.T. 4. E-02 03/10 03/17 3.00E 08 CC 03/26 3 7 +-0.4 E-02 03/21 L.T. 2. E-02 03/17 03/24 3.06E 08 CC 04/08 2.0 +-0.3 E-02 03/26 L.T. 3. E-02 03/24 03/31 3.01E 08 CC 04/15 1.8 +-0.3 E-02 04/02 L.T. 3. E-02 03/31 04/07 2.83E 08 CC 04/21 2.2 +-0.3 E-02 04/12 L.T. 2. E-02 C4/07 04/14 2.66E 08 CC 05/01 2.2 +-0.4 E-02 04/I8 L.T. 3. E-02 (8) C4/14 04/21 2.'92E 08 CC 05/07 7.2 +-2.4 E-03 04/23 L.T. 2. E-02 I

(C) 04/21 04/29 05/08 2.4 +-0.7 E 00 TOTAL PCIO5/02 L.T. 7. E 00 i

(Al DUPLIC?TE AMALYSIS (8) Sampler pump salfunction i

(C) Sampler pump malfunction; results reported as total pCi per filter.

l

WOLF CCEEE NUCLECO OPE?oTING CORD E"P05UR E PST HWAY - CI200RNE AIR PARTICULATE g CHARCOAL FILTERS STATIDW Num8ER 32 COLLECTION DATE M IO-C OUNT A P FILTER MIO-COUNT CMARC"At FILTER START STOP TIME GRD55 BETA TIME I-131 0 ATE DATE VOLUME UNITS CATE IPCI/CU.M.9 OATE IPCI/CU.M.)

. ....==- - -

... -- ==

04/28 05/05 2.95E 08 CC 05/22 2.1 +-0.3 E-02 05/11 L.T. 4 E-02 05/05 05/12 3.04E 08 CC 05/26 3.4 +-0.4 E-02 05/15 L.T. 3. E-02 05/12 05/19 3.03E 08 CC 06/04 2.9 +-0.3 E-02 05/22 L.T. 2. E-02 05/19 05/26 3.01E 08 CC 06/05 1.5 +-0.3 E-02 09/28 L.T. 3 E-02 05/26 06/02 3.04E 08 CC 06/12 1.6 +-0.3 E-02 06/05 L.T. 2. E-02 IA105/26 06/02 3.04E 08 CC 06/12 1.6 +-0.3 E-02 06/08 L.T. 3. E-02 06/02 06/09 2.99E 08 CC 06/19 2.5 +-0.3 E-02 06/12 L.T. 2. E-02 06/09 06/16 2.91E 08 CC 06/30 2.2 +-0.3 E-02 06/20 L.T. 3. E-02 k' 06/16 06/23 3 04E OS CC 07/08 2 8 +-0.4 E-02 06/28 L.T. 3. E-02 H

'" 07/13 2.3 +-0.3 E-02 07/03 L.T. 2. E-02 06/23 06/30 3.03E OR LC 06/30 07/07 3.04E 08 CC 07/23 2.5 +-0.3 E-02 07/11 L.T. 2. E-02 07/07 07/14 3 01E 08 CC 07/31 2.1 +-0.3 E-02 07/21 L.T. 3. E-02 07/14 07/21 2.96E 08 CC 08/05 3.0 +-0.4 E-02 07/23 L.T. 3. E-02 07/21 07/28 3.06E 08 CC 08/07 3.4 *-0.3 E-02 08/01 L.T. 3. E-02 07/28 08/04 2.94E 08 CC 08/17 2.5 +-0.3 E-02 08/06 L.T. 3. E-02 08/04 08/11 3.01E 08 CC 08/21 3.1 +-0.4 E-02 08/16 L.T. 2. E-02 08/11 08/18 2.90E 08 CC 08/28 2.9 +-0.4 E-02 08/20 L.T. 2. E-02 08/18 08#25 2.94E 08 CC 09/03 2.7 +-0.3 E-02 08/27 L.T. 2. E-02 IAI OUPLICATE ANALY115

I WOLF CCEE3 MUCLEC3 OPEMTING COap ENP050tE Pt.TMwAv - at:80aME AIR PARTICULATE & CHARCOAL FILTERS 51ATION MUM 8tR 32 COL L ECT IDM OATE MID-COUNT A P FILTER MIO-COUNT CHARCOAL FILTER START STOP TIME GROS $ SETA TIME I-131 OATE DATE VOLUME UMITS DATE IPCI/CU.M.9 04TE (pct /CU.M.)

=- _

_=.= __ . - . . =-.- . -

- - = - = - -----

08/25 09/01 2.98E 08 CC 09/18 2.4 +-0.3 E-02 09/04 L.T. 3. E-02 09/01 09/08 3 05E 08 CC 09/22 3.9 +-0.4 E-02 09/11 L.T. 3. E-02 09/08 09/15 2.94E 08 CC 09/24 2.9 +-0.3 E-02 09/17 L.T. 3. E-02 09/15 09/22 3.07E 08 CC 10/02 2.5 *-0.3 E-02 09/24 L.T. 3. E-02 (A909/15 09/22 3 07E 08 CC 10/02 2.1 +-0.3 E-02 09/26 L.T. 1. E-02 09/22 09/29 3 03E 08 CC 10/08 4.5 +-0.4 E-02 10/01 L.T. 2. E-02 09/29 10/07 3.71E 08 CC 10/20 2.1 +-0.3 E-02 10/11 L.T. 1. E-02 10/07 10/13 2.58E 08 CC 10/23 2.6 +-0.3 E-02 10/17 L.T. 2. E-0,2 10/13 10/20 3.12E 04 CC 10/27 3.8 +-0.4 E-02 10/25 L.T. 2. E-02

  • 10/20 10/27 3.19E 08 CC 11/04 3 3 +-0.3 E-02 10/30 L.T. 2. E-02 10/27 11/03 3.06E 08 CC 11/16 3.0 +-0.4 E-02 11/06 L.T. 2. E-02 11/03 11/10 3.02E 08 CC 11/19 3.3 +-0.3 E-02 11/12 L.T. 2. E-02 11/10 11/17 3.10E 08 CC 11/25 2.8 +-0.3 E-02 11/21 L.T. 3. E-02 11/17 11/24 3.05E 08 CC 12/02 3.2 +-0.4 E-02 12/01 L.T. 2. E-02 11/24 12/01 3.11E 08 CC 12/10 2.8 +-0.3 E-02 12/04 L.T. 2. E-02 12/01 12/08 3.00E 08 CC 12/17 4.2 +-0.4 E-02 12/12 L.T. 2. E-02 12/08 12/15 3.03E 00 CC 12/73 1.7 +-0.3 E-02 12/19 L.T. 2. E-02 12/15 12/22 2.93E 08 CC 01/05 4.T *-0.4 E-02 12/25 L.T. 2. E-02 (Al DUPLICATE ANALYSIS

-a WOLF CCEE3 souCLEAR OPE 2CTissG COA 7 EMP05umE P^.THeeay - atroomesE Ata PARTICULATE & CHARCOAL FILTERS ST AT IOes 88UM9ER 32 COL L E C T IOce DATE MI D-COUsef A P FILTER MI D-COUsef CMARCOAL FILTER START STOP TI#E GROSS BETA TIME t-131 OAYE DATE VOLUseE Use t TS DATE (PCI/CU.M.) DATE (PCI/CU.M.9

. . - - - _ = - _ _..... _....... ....- - - .- _ . _ _ _ - - - - - - _ _ . . . . _.. . . ....- .......

12/22 12/29 3.0SE 08 CC 01/08 3 1 +-0.3 E-02 01/04 L.T. 2. E-02

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1 WOLF CCEE2 teUCLECQ OPE 20Tla6G C0t?

EXPOSURE PATHWAY - At:80RNE als PamTICutaTE & CHa4 Coat FILTERS S tat ION soum8 E R 37 COLLECTION OATE M I O-Coussi aP rtLTER MIO-C OUe6T CHARC0at FILTER STami STOP TIME ca055 SETA TIME l-131 DaTE OaTE YOLUME UNIT 5 DaTE (pct /CU.N.9 DaTE SPCt/CU.n.3

.........--- - - - - - - _ - - _ _ - - - - - _ = _ - . . . . . . . - - . _ _ . - - __... .......

04/28 05/05 3.02E 08 CC 05/22 2.8 +-0.3 E-02 05/11 L.T+ 4. E-02 05/05 05/12 3.00E 08 CC 05/26 3.4 +-0.4 E-02 05/15 L.T. 3. E-02 05/12 05/19 3.12E 08 CC 06/04 3.0 +-0.3 E-02 05/22 L.T. 2. E-02 05/19 05/26 3.00E 08 CC 06/05 1 2 +-0.3 E-02 05/28 L.T. 3. E-02 C5/26 06/02 3.04E 08 CC 06/12 1.8 +-0.3 E-02 06/05 L.T. 2. E-02 06/02 06/09 3.00E 08 CC 06/19 2.5 +-0.3 E-02 06/12 L.T. 2. E-02 06/09 06/16 3.15E 08 CC 06/30 2.0 +-0.3 E-02 06/20 L.T. 3. E-02 06/16 06/23 2.96E 08 CC 07/08 2.6 +-0.4 E-02 06/28 L.T. 3. E-02 4

c 06/23 06/30 3.03E 08 CC 07/13 24 +-0.3 E-02 07/03 L.T. 2. E-02 06/30 07/07 2.87E 08 CC 07/23 2 5 +-0.3 E-02 07/11 L.T. 2. E-02 07/07 07/t* 3.0tf 08 CC 07/31 2.2 +-0.3 E-02 07/21 L.T. 3. E-02 07/14 07/21 3 04E 08 CC 08/05 3.0 +-0.4 E-02 07/23 L.T. 3. E-02 07/21 07/218 3.02E 08 CC 08/10 4.0 +-0.4 E-02 08/01 L.T. 3. E-02 64907/21 07/28 3.02E 08 CC 08/07 4.1 +-0.4 E-02 08/03 L.T. 4 E-02 07/2P 08/04 3.06E 08 CC 08/17 3.5 +-0.4 E-02 08/06 .t.T. 3. E-02 08/04 08/11 2.98E 08 CC 08/21 3.3 +-0.* E-02 08/16 L.T. 2. E-02 08/11 08/18 3.03E 09 CC 08/28 2.3 +-0.3 E-02 08/?O L.T. 2. E-02 04/18 08/25 3.02E 08 CC 09/03 2.5 +-0.3 E-02 08/27 L.T. 2. E-02 tal 00PLICATE ANALYSIS

l l

WOLF COEE3 WUCLEAR OPE 30 TING COA 7 EX PO5URE DATMway - al2n0RME AIR PARTICULATE & CHARCOAL FILTERS .

STATION NUM8ER 37 COLLECTION DATE MI D-C OUNT A P FILTER MID-COUNT CMa# COAL FILTER STAa! S T OP TIME GROSS 8 ETA TIME l-131 DAT5 DATE VOL UME UNITS DATE (PCI/CU.M.I DATE (PCI/CU.M.)

. ......... ...._-= _ - - -

l 08/25 09/01 3.01E 08 CC 09/18 2.6 +-0.3 E-02 09/04 L.T. 2. E-02 09/01 09/08 3.05E 08 CC 09/22 4.3 +-0.4 E-02 09/11 L.T. 3. E-02 09/08 09/15 2.99E 08 CC 09/24 2.7 +-0.3 E-02 09/17 L.T. 3. E-02 09/15 09/22 3.32E 08 CC 10/02 2.5 +-0.3 E-02 09/24 L.T. 2. E-02 09/22 09/29 3.26E 08 CC 10/08 4.2 +-0.4 E-02 10/01 L.T. 2. E-02 09/29 10/07 3.82E 08 CC 10/20 2.2 +-0. 3 E-0 2 10/31 L.T. 1. E-02 10/07 10/13 2.74E 08 CC 10/23 2.9 +-0.3 E-02 10/17 L.T. 2. E-02 10/13 10/20 3.33E 08 CC 10/27 4.1 *-0 4 E-02 10/25 L.T. 2. E-02

[3 10/20 10/27 3.28E 08 CC 11/04 3.6 *-0.4 E-02 10f30 L.T. 2. E-02 o

10/27 11/03 3 32E 08 CC 11/16 2.6 +-0.3 E-02 11/06 L.T. 2. E-02 11/03 11/10 3.43E 08 CC 11/19 3.2 +-0.3 E-02 11/12 't.T. 2. E-02 11/10 11/17 3.33E 08 CC 11/25 3.3 +-0.3 E-02 11/21 L.T. 2. E-02 11/17 11/24 3.31E 08 CC 12/02 3.6 +-0.4 E-02 12/01 L.T. 2. E-02 11/24 12/01 3.40E 03 CC 12/10 2.9 +-0.3 E-02 12/04 L.T. 2. E-02 12/01 12/on 3.35E 08 CC 12/17 3.* +-0.3 E-02 12/12 L.T. 2. E-02 12/08 12/15 3.09E OF CC 12/23 1.8 +-0.3 E-02 12/19 L.T. 2. E-02 12/15 12/22 3.06E 08 CC 01/05 4.3 +-0.4 E-02 12/25 L.T. 2. E-02 (All2/15 12/22 3.06E 08 CC 01/05 4.1 +-0.4 E-02 12/29 L.T. 4. E-02 (Al DUPLICATE AgaLYSIS l

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wCLF CCEEO seuCLEA4 OPEXYING COR)

E MP0504 E P ATHWAY - A l# DOA NE Alp PARTICUL ATE & CHAaCOAL FILTERS ST A f low seusse FR 40 totLECTID4 OATE M 10-C OUNY A P FILTER MID-COUNT CHASCCAL FILTER STA4T S T OP TIME C#055 GETA TIME I-131 DATE 0 ATE VOL UME UNITS DATE SPCI/CU.M.B OATE (pct /Cd.M.9

................. _ _ - ==__ __ ......._- . .= _==.__ ---- =__ __ - ..... ..... ==

12/30 01/06 3.04E 08 CC 01/26 2.0 +-0.3 E-02 01/11 L.T. 2. E-02 01/06 01/13 3.02E 08 CC 03/2* 3.0 +-0.3 E-02 01/15 .L.T. 2. E-02 (A301/06 01/13 3.02E OS CC 03/29 3.0 +-0.3 E-02 01/18 L.T. 3. E-02 01/13 01/20 3.10E 00 CC 01/31 3.0 +-0.3 E-02 01/25 L.T. 2. E-02 Ol#20 04/27 2.9fE 00 CC 02/05 2.0 +-0.3 E-02 01/2e L.T. 2. E-02 08/2T 02/03 3.2tE 08 CC 02/20 1. 8 +-0. 3 E-02 02/09 L.T. 2. E-02 02/03 02/10 3.20E 08 CC 03/03 1.T +-0. 3 E -02 02/15 L.T. 2. E-02 02/10 02/1T 3.15E 08 CC 03/04 3.3 +-0.4 E-02 02/20 L.T. 2. E-02

[3 02/1T 02/24 3.13E 00 CC 03/09 2.0 +-0. 3 E-02 02#20 L.T. 2. E-07 to 02/24 03/03 3.06E Os CC 03/24 2 3 *-0.3 E-02 03/05 L.T. 2. E-02 03/03 03/10 3.tlE 08 CC 03#24 2.4 +-0.3 E-02 03ste L.T. 3. E-02 03/10 03/17 3.00E 08 CC 03/26 3.0 +-0.4 E-02 03/21 L.T. 1. E-02 03 PIT 03/24 3.01E os CC 04/08 2.0 +-0.3 E-02 03/26 L.T. 2. E-02 03/24 03/31 2 9ff Os CC 04/1S 1.9 +-0.3 E-02 04/02 L.T. 2. E-02 03/31 04/07 2.93E 00 CC 04/23 2.3 +-0.3 E-07 04/12 f.T. 1. E-02 04/07 04/14 3.09E 08 CC 05/01 2.0 +-0.3 E-02 04/18 L.T. 2. E-02 04/14 04/21 3.03E 09 CC 05/04 2.9 *-0.3 E-02 04/23 L.T. 2. E-02 04/21 04#8e 2.86E Os CC 05/08 2.T +-0.4 E-02 05/02 L.T. 2. F-02 1

(A) DUPLICATE ANALYSIS

asot F CCEE3 seUCLE sa OPEOCTING C04)

EMP05URE CCTMwaV . CI:soteeE AIR PamTICUtaTE A CManC0at FILTFR5 5 f aT I O88 seUset E R 40 COL L E C T t og caTE mtD-C004T aP FILisa MIC-Consesi (MaeC0aL FILTER STami STOP TIME G8055 SETA TIME I-131 DaTE DaTE VOLUME Use t T 5 DaTE (PCI/CU.m.) DATE (PCf/CU.#.9

......... ......... _--- .................. .- _ . . . . . = .... ...... . . __. ..... .. _ ..........

04/28 05/05 3.02E 08 CC 05/22 2.1 +-0. 3 E-02 05/11 L.T. 2. E-02 05/05 05/12 3.04E 08 CC 05/24 3.7 +-0.4 E-02 05/15 L.T. 2. E-02 05/12 05/19 2.97E 08 CC 06/04 2.8 +-0.3 E-02 05/22 L.T. 2. E-02 05#19 05/24 3 02E 09 CC 06/05 1.7 +-0.3 E-02 05/20 L.T. 2. E-02 05/26 06/02 3.03E 08 CC 06/12 1.7 +-0.3 E-02 06/05 L.T. 1. E-02 06/02 06/09 2.94E 09 CC 06/19 2.5 +-0.3 E-02 04/12 L.T. 1. E-02 06/09 06#16 2.9tE 08 CC 06/30 2.4 +-0.3 E-02 06/20 L.T. 2. E-02 T

to 06/16 06/23 2.96E 08 CC 07/08 2.4 +-0.4 E-02 06/28 L.T. 2. E-02

" 06/23 06/30 2.93E 08 CC 07/13 2.5 +-0.3 E-02 07/03 L.T. 1. E-02 fab 06/23 06/30 2.93E 08 CC 07/13 2.4 +-0.3 E-02 07/07 L.T. 4 E-02 06/30 07/07 2.92E 09 CC 07/23 2.4 +-0.3 E-02 07/11 L.T. 1. E-02 07/07 07/14 2.9tE 08 CC 07/31 2.6 +-0.3 E-02 07/21 L.T. 2. E-02 07/14 07/21 3.03E 08 CC 08/0S 3.4 +-0.4 E-02 07/23 L.T. 2. E-02 t

! 07/21 07/28 2.95F OS CC 08/07 3.3 +-0.3 E-02 08/01 L.Y. 2. E-02 07/28 09/04 2.9tE 08 CC 09/17 3.1 +-0. 3 E -02 08/06 L.T. 2. E-02 08/04 08/11 3.0tf 00 CC 08/21 3.4 +-0.4 E-02 08/16 L.Y. 1. E-02 08/11 09/38 3.00f 08 CC 08/28 26 +-0.3 E-02 08/20 L.T. 8. E-02 08/18 08/29 2 93E 08 CC 09/03 2.7 +-0.3 E-02 09/27 L.T. 1. E-02 tal DUPl. IC af f ansaLYSIS

WOLF CCEE3 88UCttaa OPE 2cTING Coa?

EuPOSURE PATMwAY - AIRD0thE AIR PARTICUL ATE & CwanC0at FILTERS STATION soumatR 40 COL L E C T low DaTE M I O-C oum f aP FITTER M I O-C O UN T CMapCoat FILTER START STOP TIME GROS 5 SCTA TIME I-131 DaTE DaTE WotumE UmlTS DATE fPCI/CU.M.) DATE (PCI/CU.M.)

---.. ........--.--- .....--..___-- --.--.. ......=--- _ __ - -_--._ . --- ==-- -

08/25 09/01 2.96E 08 CC 09/18 2.6 +-0.3 E-02 09/04 t.T. 1. E-02 09/01 09/08 2.92E 09 CC 09/22 4.4 *-0.4 E-02 09#11 L.T. 2. E-02 09/08 09/15 2.94E Os CC 09/24 3.0 +-0.3 E-02 09/27 L.T. 2. E-02 09/15 09/22 3.01E 08 CC 10/02 2.6 +-0.3 E-02 09#24 t.T. 2. E-02 09/22 09/29 3.03E 08 CC 10/05 4.3 +-0 4 E-02 10/01 L.T. 1. E-02 09/29 10/0T 9.S3E OS (C 10/20 2.5 +-0.3 E-02 10/11 L.T. I. E-02 10/07 10/13 2.SOE 05 CC 10/23 2.8 +-0.4 E-02 10/17 L.T. 2. E-02 k' 10/13 10/20 3.OTE 09 CC 11/02 3.8 *-0.4 E-02 10/2S t.Y. 1. E-02 to

'" E-62 10/30 L.T. E-02 10/26 10/27 3.00E 08 CC 11/04 3.6 +-0.4 3.

10/27 11/03 3.03E 08 CC 11/12 3.7 +-0.4 E-02 11/06 L.T. 3. E-02 11/03 11/10 3.01E 08 CC 11/19 3.1 +-0.3 E-02 11/12 L.T. 2. E-02 11/10 11/17 3.05E OS CC 11/23 2.9 +-0.4 E-02 11/21 L.T. 1. E-02 tal11/10 11#17 3.05E 04 CC 11/25 3.2 +-0.4 E-02 11/24 L.T. 3. E-02 11/17 11/24 3.00E 08 CC 12/02 3.2 +-0.4 E-02 12/01 L.T. 1. E-02 15/24 12/01 3.0TE 05 CC 52/10 3.2 +-0.4 E-02 12/04 L.T. 2. E-02 12/01 12/05 2.90E OS CC 12/17 4.2 +-0.4 E-02 12/12 L.T. 2. E-02 i 12/05 12#15 3.09E 08 CC 12/23 1.7 +-0.3 E-02 12/19 L.T. 9. E-03 12/15 12/22 3.02E OS CC 01/05 "4.2 +-0.4 E-02 12/25 L.T. 3. E-02 i GA9 DuPtlCATE AmatV585 1

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WOLF CREEK RUCLEAR OPERATIOG CORPORAT10m EXPO 5URE PATNWAV - AIRBOR4E THERMOLUM1mESCERT 0051 METERS (net mR/ day)

STAT 10m FIRST QUARTER SECOND OUARTER THIRD QUARTER FOURTH QUARTER

  1. DMafR 01/07/87-04/01/87 04/01/87-07/01/87 07/01/87-10/01/87 10/01/87-01/05/88 STA-01 0.188 2 0.002 0.178 2 0.003 0.191 2 0.002 0.183 2 0.002 STA-07 0.178 2 0.006 0.170 t 0.013 0.167 1 0.002 0.169 2 0.007 STA-03 0.175 t 0.003 0.170 2 0.008 0.188 1 0.008 (A) 0.180 1 0.006 STA-04 0.183 1 0.003 0.177 1 0.007 . 0.208 1 0.004 C.186 t 0.004 STA-05 0.175 t 0.004 0.169 1 0.007 0.160 1 0.020 0.175 t 0.004 STA-06 0.171 2 0.003 0.164 2 0.004 0.178 a 0.002 0.171 a 0.002 STA-07 0.157 2 0.001 0.153 1 0.003 0.174 1 0.004 0.158 1 0.002 3,

STA-08 0.174 2 0.003 0.170 1 0.008 0.179 1 0.005 0.172 2 0.004

[3 STA-09 0.203 a 0.006 0.166 2 0.005 0.174 1 0.001 0.170 t 0.004 STA-10 0.189 1 0.006 0.178 1 0.007 0.195 t 0.004 0.185 1 0.002 STA-11 0.201 1 0.007 0.193 2 0.007 0.199 2 0.002 0.199 2 0.002 STA-12 0.198 2 0.004 0.177

  • 0.004 0.185 2 0.003 0.191 1 0.003 STA-13 0.182 2 0.006 0.175 1 0.004 0.163 2 0.018 0.191 2 0.005 STA-14 0.196 2 0.004 0.188 1 0.007 0.191 2 0.002 0.189 1 0.001 STA-15 0.191 1 0.001 0.179 2 0.004 0.196 t 0.005 0.195 2 0.007 STA-16 0.187 2 0.004 0.179 1 0.004 0.193 t 0.007 0.188 1 0.004 STA-17 0.184 1 0.003 0.185 2 0.011 0.186 1 0.009 0.189 2 0.009 STA-18 0.193 1 0.006 0.192 1 0.004 0.162 2 0.041 0.195 2 0.005 STA-19 0.192 2 0.006 0.182 1 0.008 0.196 1 0.003 0.184 2 0.005 STA-20 0.189 t 0.008 0.181 s 0.004 0.190 1 0.003 0.190 2,.0.002 (A) Co15ection date was 01/06/88 for location 3.

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A-32 I

WOLF CREEK huCLEAR OPERATING CORPORATION EXPOSURE ?ATHWAY - AIR 80RNE THERM 0LUMINE5 CENT DOSIMETERS (net mR/ day 1 STATION FIRST QUARTER SECOND QUARTER THIRD QUARTER FOURTH QUARTER NUMBER 01/02/87-04/01/87 04/01/87-07/01/87 07/01/87-10/01/87 10/01/87-01/05/88 STA-01 0.192 1 0.008 0.170 1 0.002 0.191 t 0.012 0.180 2 0.004 STA-02 0.170 1 0.008 0.153 2 0.005 0.171 t 0.011 0.172 i 0.006 STA-03 0.204 i 0.003 0.184 1 0.005 0.185 t 0.005 (A) 0.171 2 0.004 STA-04 0.191 1 0.003 0.169 i D.002 0.186 i 0.005 0.184 i 0.004 STA-05 0 179 1 0.001 0.156 1 0.005 0.178 0.007 0.164 1 0.006 STA-06 0.181 i 0.007 6.159 1 0.002 0.187 i 0.004 0.168 2 0.003 STA-07 0.165 t 0.008 0.152 t 0.004 0.168 i 0.003 0.160 1 0.001 STA-08 0.175 t 0.004 0.160 t 0.005 0.182 i 0.003 0.173 i 0.004

), STA-09 0.176 1 0.006 0.160 1 0.004 e

0.177 i 0.009 0.166 1 0.003 Ej STA-10 0.188 2 0.002 0.171 1 0.004 0.203 1 0.004 0.183 i 0.003 STA-11 0.203 1 0.006 0.188 2 0.003 0.212 1 0.007 0.200 1 0.003 STA-12 0.185 t 0.006 0.174 1 0.007 0.193 2 0.004 0.201 2 0.001 STA-13 0.208 2 0.007 0.170 1 0.00/ 0.198 i 0.007 0.189 2 0.005 STA-14 0.196 i 0.004 0.174 1 0.003 0.201 1 0.005 0.192 t 0.005 STA-15 0.196 2 0.001 0.175 2 0.005 0.192 1 0.008 0.183 1 0.005 STA-16 0.196 1 0.003 0.175 1 0.005 0.192 1 0.010 0.197 1 0.003 STA-17 0.240 1 0.018 0.168 2 0.004 0.190 2 0.005 0.190 0.005 STA-18 0.203 1 0.006 0.181 1 0.004 0.202 1 0.004 0.200 2 0.019 STA-19 0.197 i 0.004 0.170 2 0.008 0.192 1 0.005 0.200 2 0.006 STA-20 0.189 1 0.003 0.173

  • 0.005 0.196 0.005 0.199 1 0.005 (A) Collection date was 01/06/88 f ar location 3.

WOLF CRt'EK NUCLEAR OPERATING CORPORATION EX?OSURE 7.* AIR 8ORNE THERMOLUMINt: .,0SINETERS (net ama.;y)

STATION FIRST QUARTER SECOND QUARTER THIRD QUARTER FOURTH QUARTER NUMBER 01/02/87-04/01/87 04/01/87-07/01/87 07/01/87-10/01/87 10/01/87-01/05/88 STA-21 0.164

  • 0.002 0.145 2 0.002 0.152 1 0.007 0.163 1 0.0'03 STA-22 0.172 1 0.004 0.155 i 0.007 0.208 1 0.01/ 0.220 t 0.013 STA-23 0.180 t 0.002 0.163 i 0.003 0.182 1 0.002 0.193 1 0.017 STA-24 0.188 1 0.003 0.170 1 0.005 0.182 i 0.002 0.189 i O.006 STA-25 0.142 i 0.004 0.133 1 0.004 0.150 1 0.002 0.168 i 0.025 STA-26 0.187 1 0.008 0.159 i 0.005 0.174 1 0.007 0.176 1 0.002 STA-27 0.196 1 0.006 0.166 i 0.004 0.189 1 0.005 0.192 1 0.007 ao STA-28 0.160 t 0.006 0.153 i 0.003 0.161 i 0.009 0.151 x 0.002

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A-51

t0LF CREEK NUCLEC4 OPERATING CORP EXP350RE PATHW3Y - INGESTION NILK t PCI/ LITER 1 STATION NUMBER 5-3 DATE COLLECTED 01/13 01/13 (A) 02/10 03/10 04/14 1

RADIOCHEMICAL ANALYSISt I-131 L.T. 4. E-01 L.T. 3. E-01 L.T. 5. E-01 L.T. 3. E-01 ,L.T. 4. E-01 GCMMA SPECTRUM ANALYSIS:

CE-7 L.Te 1. E 02 NR L.T. 5. E 01 L.T. 5. E 01 L.T. 4. E 01 Q-40 1.63+-0.16E 03 NR 1.34+-0 13E 03 1.19+-0.12E 03 1.28+-0 13E 03 00-54 L.T. 1. E 01 NR L.T. 5. E 00 L.T. 5. E 00 L.T. 4. E 00 CO-58 L.T. 1. E 01 NR L.T. 5. E 00 L.T. 5. E 00 L.T. 4. E OC FE-59 L.T. 2. E 01 NR L.T. 1. E 01 L.T. 1. E 01 L.T. 9. E 00 CO-60 L.T. 1. E 01 NR L.T. a. E 00 L.T. 5. E 00 L.T. 5. E 00 24-65 L.T. 2. E 01 NR L.T. 1. E 01 L.T. 1. E 01 L.T. 1. E 01 NS-95/ZR-95 L.T. 1. E 01 NR L.T. 5. E 00 L.T. 5. E 00 L.T. 5. E 00 RU-103 L.T. 1. E 01 NR L.T. 5. E 00 L.T. 6. E 00 L.T. 5. E 00 4U-106 L.T. 1. E 02 NR L.T. 5. E 01 L.T. 5. E 01 L.T. 4. E 01 l I-131 L.T. 2. F 01 NR L.T. 8. E 00 L.T. 1. E 01 L.T. 8. E 00 3* CS-134 L.T. 1. E 01 NR L.T. 6. E 00 L.T. 5. E 00 L.T. 5. " 00 Ln C5-13T L.T. 1. E 01 NR 6.94+-4.02E 00 L.T. T. E 00 L.T. 4. E 00 LA-140/8A-140 L.T. 1. E 01 NR L.T. 4. E 00 L.T. 7. E 00 L.T. 5. E 00 1 CE-141 L.T. 2. E 01 NR L.T. 9. E 00 L.T. 1. E 01 L.T. 8. E 00

) CE-144 L.T. 1. E 02 NR L.T. 4. E 01 L.T. 4. E 01 L.T. 3. E 01 4

QA-226 L.T. 3. E 02 Nr L.T. 1. E 02 L.T. 1. E 02 L.T. 9. E 01 1 TM-229 L.T. 3. E 01 NR L.T. 1. E 01 L.T. 1. E 01 L.T. 8. E 00 l

l tal DUPLICATE ANALYSIS 1

4

== == m O O se O *e C O -e O O O O O == N O O OOOOOOOOOOOOOOOOOO I

W WWWWWWWWWWWWWWWWWW 4

es e e e e e e e e e e e e e e e e e e e e e o e c == c ** e e e > 4 4 e e t ** 9 I

O e eO e e e o e e e e e e e e e e e e

% > >d>>>>>>>>>>>>>>s=>

e 4 e e e e o e e e e e e e e e e e e e e O .e .6 ** ao me .6 e .e .e .e ad .o e me .6 ed .e .6 .o

    • ==mOOOOOOOseOOOOO O O OOOOOOOC000OC000CO e

W WWWWWWWWWWWWWWWWWW m

se o e e e e e e e e e o e e e o e e e e m eO4*P4944mke4enm9e 0

N e eN e e e e e e e e e e e e e e e e N > >m>>=>>>>>>>>kt=>>> >

e e e e e e e e e e e e e o e e e e e e O me .e ** J .e .e .e .o J .e .e .e a e .e .6 .e .e .e

= ** ==m O O O O O O O seO O O O Ose N O 4 O COOOOOOOC000OO00OO w I W WWWWWWWWWWWWWWWWWW N

en A e e e o e e e e e o e e e e e e e e e a e 9 O 4 9 e t 9 4 t m 4 + 4 4 9 4 == m O 8 W2 N

  • O =* e e4 e e o e o e e e e e e e e e o e O ==  % > >ae>>>>>e=>>>>>>e->>>

2> e e e e e e e e o e e e e e eee e e e

== e O .e .e os .e .o a .e .e .e .e d .e .e .J .e a .o .6 .a

>W m 40 0 32

  • e W ==

& a a ** == m O O as O -e O O == O O O O == == N ==

0I u' w O COOCOOOOOC000000OO

> et I c> W e= E We WWWWWWWWWeuWWWWWWWW e3 4 .6 .e 3 m W3 == % 2 =e

., E E ==

  • e e o e o e e e o e e e e e e o e e W> W 2 d e O em e se 4 == c 4 e e 4 4 e == 4 se m D4 & C 6 26 == N
  • w > se e e >= e e e o e e e e e o e e gw 4  % > > N > e.e(=>ee > e.e > > > > > > > > e.e Wg >. e e e e e e e e e e e e e e e e e a e e WD e O 6 .d en .e ed .e .e e .e .e .e .e .e .6 .e .a .a .e .e E+

WO E N

.4 W *e =s

  • O O O O O O O se O O O O O == *e O C O OOOO000OOOOOOOOOOG 3 8 W WWWWWWWWWWWWWWWWWW M

es e e e e e e e e o e ee e e e e e e e N

  • O 4 4 e t 9 d e 4 e e e tP= m 9 e i

N e eC e e e e e e e e e e e e e e e e

% > > m > > > 9= > >= > > > > > > > > > >

d S e e e e e e e e e ee e o e e e e e O .6 .e ** e .o .e sd J .J e .e e ao ed .a me .6 .e me es se e M.e

    • e e e > am

> .o e me 4 >

4 2 .6 2 4 4 4 2 O E e W s D C

> 4 K t W W W > c as es W *e W P 0 4

.e I W 8 4 W me W 6 6 e **

O Z e N  % .J V W  % f* 4

  • P= O **
  • 4 e &

C *e 4 d E P O e e O O .e m m e e e N N 3 W == m E > 0 e e e 4 4 e as se m se se == ee se N N O

> O es 2 f 9 0 0 4 e a e e te g g e g g a e 4 4 4 4 W 4 2OWO2e$3iee4WW4 3 =

Q E = 0 mWEWEUN2as=WWsWWar 4 A-53

m mmOOmomOOmOOOOm=Nm O C00000000000000000 0 -

W WWWWWWWWWWWWWWWWWW t

n e e e e e e o e e e e e e e e e e e o m 40kem>N>>49e>>memm i

e

  • N e oc e e e e e o e e e e e e e e e e

% > km>>>>>>>>kkkp>>>>

e e e e e e e e G e e e e e e e e e e e O d dadaddddddeddadddd e.

m amOOOOmOOmOOOOOmNO O C00000000000000000 0

W WWWWWWWWWWWWWWWWWW N

N e e e e o e e e e e a e e o e e e e e m <Ott99m4cte4 4494me 4

N

  • m e eO e e e e o e e e e e e e e e e e

% > MN>>>>>h >>>>>>>>>>

e e e e e e e e o e o e e e e e e e e e O d Judadeddddeddddded a mMOOmomOOmmOOOmmNm O C00000000000000000 t

W WWWWWWWWWWWWWWWWWW G

m A e e e e e e e e e e e e e o e e e e e a m 40cem4=4>4m444meNa O 8 v2 e

  • O N e *N e ee e e e e 4 6 e e e e e e e om  % > WO>>>>>>>>>>>>>>>>

27 > e e * * *

  • e e e * *
  • e e o e e e e

=+ O & daddddeadaddadd&&&

e= W m 40 0 OE

  • e W=

es e a a mmOOmonOOmmOOOmmNm Os W w O C00000000000000000

> e t n> g = E W WWWWWWWWWWWWWWWWWW el 4 .J d D m W3 m  % 2 m dZ E m o e e e e o e e e e o e e o e o e e e v> v 2 e eOcememedd=44Padam 30 & C 0 20 = f

  • w > a e e t. e ee 6 e o e e o e o e e e e e NW 4  % > km>>>>>>>>>>>>>>>>

Es > > e o e e e o e o e e e e e e e e e o e WD w O d & a e d a d e d d a d *a d e d d e d (f 91 90 to E N JW m mmOCOOOOOmOOOOOmWO O O C00000000000000000 U C W WWWWWWWWWWWWWWWWWW N

m o e e e e o e e e e e *

  • e e e e e e m WOttPfedef>ffe@t=9 4

4

  • N e em e e e e e e e ee e e o e e e e

% > km>>>>>>>>>>> >>>>>

e e e e e e oe N e e ee e e o ee e e C d anaadedadeedadaadd H

M N M =

m M M >

> d 4

4 2 3 4 4

O E W d D 0

> 4 5 4 V W > @ m W V @ l

& "E W l 4

& W L d e o T M N

% me 4>Om44e u u O N 4 490DecOCammt44NN W = m g mocee44F==mmmmmmNN

> Q w I ff f i a e 4 4 0 la t I t i 6 8 9 4 4 t 4 W 9 FOWC2eD3eee4WWg2 '

O E

  • O CWEQ%QNE68mWUdMUm>

i A-54

l i

l a a amOOmomOOmOOOOO-Na 4 O OO0000OC00000000CO '

= 0 w w w w w w w w w w w w w w w w w w 'ad A

me o e o e e e e e e e e e e e e e e o e N e O e f so f me e c & > f @ c P e =e re i

e

  • N e eN e e e e e e e e e o e o e e e e

% > >m>>>>>>>>>>>>>>>>

0 e e e o e e e e e e e e e e e e e o e

    • .6 .e ** ee .e d .o .6 .a .e .e .a ed .e .a .c .e .a .e
    • == m O O O O O O O == O O O O O ** N O O OOOOOOOOOOOOOOOOOO e

W WWWWwWWWWWWWWWWWww M

-e e e e e e e e o e o e e e e e e o e e m mom *P4effmf444>meee 8

e

  • N e em e e e e o e e e e e e e e e e e

% > >N>>>>>>>>>>>>>>>>

0 e o e e a e o e o e e o e e o e e o e

    • .e .e ** .a .e me .6 .6 .e .J .o .6 .e & .e .e d .o at me ** m O O O O == O O == 0 C O O O ** a= O O OOOOOOOOOOOOOOOOOO I

w wwwwwwwwEwwwwwwwww t

me 16 e e e e e o e e e e e e e e e e e o e a N *O4ee****rm>fec>mee C I u2 m

  • O **
  • ek e e e o e e e o e e e e e e e e C ==  % > km>>>>>>>>>>>>>>>>

Z> O e e e e e e e e + e e e e e e e e e e

    • m *= .a a =* .e er .e .e e at me .e d me ao .e .e e me me

>u m OC D MF a M w ==

4 m E .= *= m o O O O == 0 C == 0 O O O O == N O O 8 w w o COC00000aO0000000O

> e i er > w == E w wwtswwwwwwisWWwwwwww

%14 .e .e D &

w3 == % 2 se

.e 2 E == a e e e o e e e e e e e e o e e e e e v> w I m 4 O 4 e e d se e e M N v

  • r P m ee e D4 'a 0 1 2 gg O e w > N e oe e oe e o e e e o e e e e e e e rf w 4  % > >d>>>>>>>>>>>>>>>>

wa > P e e e e e o e e e e o e e o e o e e e wD M 3 .e me *e .e .no .e .e e me me .e .e ao .6 .a e .e .mt me er 34 VO tb wM

.e w == == m O O == 0 == 0 O == == 0 O O == = N =

4 O OOOOOOOOOOOOOOOOOO

.5 I w wwwwwwwwwwwwwwWwWW 4

=e e e e e eee e e e e e e e e e e e m > 0 > > a= > N e e Pe ** e P.e e N P* N N 8

9 4 O e ee o e e o e e o e e e e e e e o e

% > > m > > > to >>>>>>>>D'>>>

P e e e e e e 4 e o e e e e e e e e e e O .e .e ** .e .e .e me .e .e e .e as .e .e as .e me .e ee Se se e e se en e e M > ==

> ad d 4 4 2 .e 2 4 4 4 E O E 4 w .e D C

> d W 4 W W W > O == >

w == V P 6 4 ee K w l 4 Y me

.s w b K t O E w ms  % a w v %ee 4 > 0 ==

  • e e e6 O == 4 4 e e C e e C o me m
  • 4 4 d N N =

w ==O m T > 0E C e1 ef 494I9l== ** m == == == *= ** N N O k ** e I t iI ** I i f I I I i =

4 4 6 4 W # 2CwCEeDDI ee4wwd Z d O m == c e w a v s v N E e a ==U V .6,w w a >

A-55 1

m

==

O .* m O O = 0 = O 0 e O O O O O eN O 6

OOOOOOOOOOOOOOOOOO W WWWWWWWWWWWWWWWWWW N

es

& e eeeeeeeeeeeeoeeeee a m C e ol in e == c ce to an e e e 4 4 9 4 == e vE e

  • O O e em e ee oe e e e o e e eee o e O ==  % >

2> N e

> N > > > > ee > > = > > > > > > > > >

== e me .e e e e e e e e e 0 0 e e e ee e e e

>W #3 J oe me e d ed ee ed & me e .e me eJ ed .c ae .e 41.3 0 41 E ** e E ==

a er s ==

    • m C CO OO O O==0 O O O O**N O OI W E O C0000000000000000O

> e 4

() >

42 4 ag ee as E W WWWWWWWWWWWWWWWWWW W3 ==

me Qa

  • e me me K E em e eeeeeeeeeeeeeeeeee v> v 2 m 4O d 4 P
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  • wW

= >

4 N

e se ee e e o e e e e o e o eo e a

>Ok>>>>>>6->>>>>>>>

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> == e eoeoeeeeeaeeoeeoee e ** ,e ee ** ad .0 =d me me d .e .a .e me ne e ea se .e e Li e v O.

6 4m

.e W me m O O O O == O O as O O O O == = N O O O 3 0 OOOOOOOOOOOOOOOOOO W WWWWWWWWWWWWWWWWWW fm ao e e e e e e e e # 4 e e e e e 0 e m W O t 4 9 e ** 4 e 4 9 4 e 4 .0. d .4. e I

O

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.e e 4 2 I 4 4

O E W -e 3 O

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W == Q 9 0

.e E W t 4

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M Q %m4 4 M o ne t d e W .O.

=

m t 4 + e 9 C am e c o ** m m 4 * + N N

> O ** 2 > C e er e 4 4 e == == m == = == == se N N 0 4 0 0 e e e e i t se 8 i e I t t t 4 4 o a == 0 a g W e20WOEe336He4WWWX e at E v m W ad I a a == W W .e w w a >

A-56

I 1

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1 &

5 C

w Cw E~

e. >

>4 43 w er O = C W4

& a > a == O N N N N N N N = N N N N N == 0 O O I = s W C000000 OOOOOOOC00O O O e 9 i e6 ee e e e e e 0 0 0 0 5 >

4 4 M

E WWWWWWWWWWWWWWWWWW N ** f N W ee W3 W c MP N + m ==

s

.,o K 3  % e e e e e ee e o ee e e e e e

. > == 3 == 0 N N e N e m m N e m ev v v .ee.OO 4 of w Q 4 e a e I e

& w & en k e4 e e o e w > N e ** eW e e e e e e e eee e e O es a gW 4  % m se > S > tm > > > > k > W e- > > $ em Ws & O e e e e e ee e e e e e e e e e e e ND n e ** e 9 e 4 .6 .e ed ao me d o d e ,e .e .n ew en aa wC Wm aw == es N N N N N N N se N N .m N N em O O O OOOOOOOOOOOOOOOOOO 3 t 0 9 0 t 9 e e et 9 e e ea WW se W W W W W eW the W W W W W W uf W W e e ed es se ** an e e e o e e # e e e e e e e e e <* e N O esNeN4mkN>mOf 9 MOO 9 0 0 8 4 + * **

N ee e e o ee o e eo em o eeet

% t- O e- > p > > > > > > > se > > > O O e e i e eeee e o e e e e e ee e e O .e ee d e .e .d .e .e .a a a .e = .a .o .a N en en e

me w

J e

3 g

O E W 3 O

> a o 4 w > c ee W w e e

.* W t 4 J 6 a e 0 e N  %

v %me + > O ee d d e e 4 et e o er e O O m m 4 4 e N N W E k O e e e d 4 e se == m == ee =e == ** N N

> E 4 f I t t e e i I t es 0 0 I e i e f e e W t 2CWORe33eeeeWW41 O O e W t u th w N 2 m a *= v v .d w w a >

A-57

WOLF COSE2 8eUCLE*3 OPE 2ATING CORD E M PO5 UR E P ATHW AY - AOU AT I C SHOREliast SOIL IPCI/GM ORY I STATIDW MUM 9ER 4R CaTE COLLECTED 05/26 CamM3 SPECTRUM ANALYSI5:

SE-T 2.80+-1.45E-01 C-C@ 1.30+-0.13E 01 mm-54 L.T. 2. E-02 C9-SS L.T. 2. E-02 PE-59 L.T. 5. E-02 C0-68 L.T. 2. E-02 24-65 L.T. 4 E-02 48-GS/2R-95 L.T. 2. E-02 CU-183 L.T. 2. E-02 CU-104 L.T. 2. E-01 I-131 L.T. 6. E-02 C5-134 L.T. O. E-00 C5-137 4.03+-0.97E-92 3,LA-140/8A-140 L.T. 5. E-02 s CE-141 L.T. O. E-02

$$CE-144 L.T. 1. E-01 ca-226 1.17+-0.31E 00 TM-228 7.97+-0.80E-01 RA-228 5.71+-0.84E-01 l

l i

l

au me O N sm N N N N N as N N N N N me me N me 4 == O0OOOOOOOOOOOOOOOOO w> 0 4 I I 0 i t 0 0 0 0 4 8 0 0 0 0 1 4 WWWWWWWWWWWWWWWWWWW D P e ** @

O *e m N m 4 e e e e e e e e e e ee e e e e e e O

NOe=0mNmNNNeNNNmmemmo eae e

>W 4 **

  • N e= e e me d e o e e e e e e e e e e e e as

%C >eoe>>>e>>>>>>s=>>>c oC e e e e e e e o e e e e e e e e e e e

== a me *e m =e .o ao .a .e .6 .0 .e .e ad ad .e ad on .6 en W as C N se N N N N N a= N N N N N *e ** N as

== 0OOOOOOOOOOOOOOOOOO

> 0 0 0 0 0 0 t a 0 0 0 t 6 4 I 6 8 I e WWWWWWWWWWWWWWWWWWW D MOW >

O N4N 9 L 4 e e e e e e o ee e e o e e e e e e e a N O =e O J N 4 N N N e N N m t ee 4 4 O O O I I I I W >W e * *

  • N> e e e oee e ee

(* v %C OO

>mee>>>>>eo eNeee o e ee

>>>>>>>>m e e e o e e e eo e oe e o e e e o e E .= v

= = > == == E .d on N ee .d .a o .d e .a a .a ao .e d .e ao .o en

>e >

e3 e v vO 3

  • O We O 6 e > a O O N N N N N #m m N N m N N N N me se O t a W 0000000C0000OCOO00 1 3 e a e t e e e 4 e e e e e e e e e a> E W W W las W W W W W W W W W W W W W W e eN ee 2 E D e N m == m W 3 C o a NNee a6 > == N

.42 ==  % e

  • O e e e e ee e oe e e e e u> > == E O O O O se O ** 4 4 e N > 0 ,eee.egO D4 e v O e e a e s e ae R& > & a= mW ** 4 $ $ e e$

w w > Ne ePeeee e e e e eee eo e 9 as as W O 4 %O m =* O e > e > > > > > > d > ke > mN We w > d .4 e o e e oe o e e o e e e eae e ea WD > e O4 N N N N .d M .i.d.a.# w ed > d.d.d f N 2 ae UC 4 M s nn. W O O M M N m N m m N N m N m N N me N O == 000OOOOOOOOOOOOOOO 3 > 0 t e 4 e I # 1 I e f 8 e e i e 4 W the les W W W W W W W W W W W W W W W D me e et O **==

  • g e e oe e o e e e e eeo e e Oe O, O o e 4 as e se e d # N 4 0 e oe e as8 as O e t e 6 mW eo e ee N> em oe e e e e o e ee eoeee

%o m e > > > e.e >>>>>>m>>>eO e e eoe o e e e e o eo ee e e ew 4O OE ee ne J .e .d .e .e e .o .0 me .d me .0 4 .a N > 2 N

e em i e e

==

> e

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W e 4 e t c e e %ee

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W t > O e e e 4 e e == an e == *e =e == == N N == C

> t t* e e e e e e e e me e e e ef e e e 4

O e W 8 3QWC2e3DIee4WW42e O eW EwwwN2ss=WWwWuske a

4 A-59

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WW WWWWWWWWWWWWWWWWWW

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% 4> >>=>>>>>>>>*>>=>>>>>>=

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m WW WWWWWWWWWWWWWWWWWW O

% 4

& m a s e e o e e o e e e o e e e e e o e e er O .* N memmef>+eme***emee OW I I UE m +

at O e e e e eoe e e e o e e e e o e e e t.) O  % e> >>=>>>=>>>>=>>>=>>>>>>=

2G N e e e e e e e e o e e e e e e e e e e e er ea c t c o 4 .J .e .a .a .J .e .e ad .J .o .e .J .o .4 .a .J .J .J .e E kW **

Q> er 3 ff C W = m WD >

ew 4 er ec N O1 3 W W O e g>

e e C

@ ** E > w 0 44 2 .J O

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> E U R O g C d == e6 0 0 3 L er == 4  %

C m* > 0 e WW 4  % > #

W >= *e er er er & er a W af er er er er er er er er er er er er e E W m O EE EEEEEEEEEEEEEEEEEE .J UM b WO O L **

nk M .e

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O WW WWWWWWWWWWWWWWWWWW E O

% @ U N e e e e e e e e e e a e e e e e e e e e O ** 4 m 4 m m e 4 P* f 4 m e f 4 e @ N e > 0 8 9 **

4 +

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W#JLF CREEK NUCLEAR OPERATING CORPORATON Bart D. Withers er e w cw rie. ome.,

April 29, 1988 WM 88-0114 U. S. Nuclear Regulatory Commission ATTNt Document Control Desk Washington, D. C. 20555 ,

Subject:

Docket No. 50-482: Annual Radiological Environmental Operating Report Centlement Attached is the Annual Radiological Environeental Operating Report which is being submitted pursuant to kolf Creek Generating [

Stacion Technical Specification 6.9.1.6. This report covers the operation of Wolf Creek Generating Station for the period of January 1,1987, through Decen.ber 31, 1987.

Very truly yours, ,

~LA Bart D. Withers President and '

Chief Executive Officer BDW/jad Attachment cet B. L. Bartlett (NRC), w/a R. D. Martin ( NRC), w/a

?. W. O'Connor (NRC), 2 w/a

' \

PO Box 411 i Burhrvpon, KS 66839 / Phone: (316) 364 4831 M E%W Opportrwy Empeyer W TCVET u -_-__-_ _ --_.__-- - _________-_____--__________ _ _____ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ - - _ _ _ _ _ _ _ _ _ _ _ - - - _ _ _ _ _ _ _ _ _ _ - - _ _