ML20042E992
| ML20042E992 | |
| Person / Time | |
|---|---|
| Site: | Wolf Creek  |
| Issue date: | 12/31/1989 |
| From: | Bailey J WOLF CREEK NUCLEAR OPERATING CORP. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| NO-90-0141, NO-90-141, NUDOCS 9005070072 | |
| Download: ML20042E992 (131) | |
Text
{{#Wiki_filter:W44.F CREEK NUCLEAR OPERATING CORPORATION John A. BeHoy v6oe Pressere Nucteer Opershone April 30,1990 NO 90-0141 U. S. Nuclear Regulatory Commission ATTN Document Control Desk Mail Station P1-137 Washington, D. C. 20555 l
Subject:
Docket No. 50-482: Annukl Radiological Environmental Operating Report Gentlemen Attached is the Annual Radiological Enviroimental Operating Report which is being submitted pursuant to Wolf Creek Generating Station (WCGS) Technical l Specification 6.9.1.6. This report covers the operation of Wolf. Creek l Generating Station (WCGS) for the period -of January 1, 1989,- through f December 31, 1989. -i Very truly yours, -- [ 0 l John A. Bailey Vice President Nuclear Operations JAB /jra Attachment cci R. D. Martin (NRC). w/a D. Persinko (NRC), w/a D. V. Pickett (NRC), w/a M. E. Skow (NRC), w/a p( )( ) 1 5* A F DR ADOCk- 0:'o "j7i-, g e t o_ P.O. Box 411/ Budngton, KS 66839 / Phone: (316) 364-8831 [ m-g-,- (
Attachment-to NO 90-0141:- i M CMEK REICKERR GWar13G GEEGummi M CRER (BIButrDD Im mtm 1989 MBERL RAMufEEchL 1RRPIIGEMemL GWWEDG IGWGtr g ~.. ~ i I o l i i 1 J ..j April 30, 1990
ij - 4 i T 'INER & GEMBttS 1 2092 Lis t of 'Dables.................................................... -2. List of Figures................................................... 3 { rn w ucuan...................................................... 4 I. Prcummu Description..........................~............... 'S II. Discussion of Pasults....................................... 8 i ? III. Annual land Use Survey Results and Pwuimu Revisions........ - 13 IV. Monitorincr Prcummu Deviations............................... 14 V. EPA Interlaboratory Camarison P-Out-u Results.............. 17 t Tables............................................................ 18 Figures............................................................ 35 Appendix As . Sumnary tables in fonnat of NRC Radiological Assessment Branch 'Dechnical Position, Revision 1, November 1979........................... A-1 i Appendix B: - Individual Sanple Results...............,........... B-1 Appendix C: Wial Sanple Collections........... !.............. C-1 ~ e 1989 AleEBL RADTrrmifWs BWIIOGGBWL TIEUEDG REEUU NEE CREEK GERMUEDG SHEIN PAGE 1 OF 45 e t vc-,,* - =
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i LISF 2 'mIEJB 1 i M Table la 1989 Radiological Environmental Manitoring F N =u MTitng Schedule...................................... 18 M ling Iocation Numbers, Distances, and Table 2: Directions............................................. 21 Table 3: Gross Beta Analysis Results of Air Particulate Sanples................................................. 22 Table 4: Gama Analysis Results of Air Particulatn CPite. Sanples................................................ 25 Table 5: 19 8 9 TID Results....................................... 26 Table 6: Gross Beta Analysis Results of Drinking Water-. Sanples................................................ 28-r Table 6A: Drinking Water Sanples Tritium Analysis Results......... 28 - Table 7: Tritium Analysis Results of Surface Water.............. 29 Table 8: Gama Analysis Results of Sediment /SLoreline Soil. Sanples................................................ 30 'Ibble 9: Ganna Analysis 1%sults of Aquatic Vegetation-Sanples................................................ 31 Table 10: Results of 1989. Land Use Survey........................ 32 Table 11: Results of EPA Interlahnratory Wrison Tests........ 33 i L MIF GEEK GBEIREDG S'DEIN PAGE 2 OF 45 4 i L. ,e ..y
r e List & FIERIEi t t Figure 1: Airborne Pathway Sanpling locations -................... 35 Figure 2: Direct Baellation Pathway Sanpling locations........... 36 .i Figure 3: War-dOHA Pathway Ra iling Iocations................. 37-Figure 4: Ingesticm Pathway' RaTling Iocations.................. 38 Figure 5: Distant Sanpling Incations............................ 39 Figure 6: 1989 Airborne Particulate Activity Weekly Gross Beta Analysis Resulta..................... 40 Figure 7: 1989 Airborne Particulate Activity Indicator / Control Carparison.......................... 41 Figure 8: Operational TID Results Nearsite & Control location Averages.................. 42 Figure 9: Variation of Nearsite' TID Averages % of Control Incation Values.......................... 43 Figure 10: 1989 Drinking Water Analysis Gross Beta............................................ 44 Figure 11: Operational Tritium Concentrations Wolf Creek Cooling Iake............................... 45 i i ( N3E GEEK GIREMEDE SHEI(M PJGE 3 OF 45 l t u-e
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1 i i Intaxxhctim his represents the 1989 Annual Radiological Enviremental Operating Report 1 for Wolf Creek Generating Station (WOGS), located in Coffey County, Kansas, approximately five miles northeast of Burlington,. Kansas.. his report covers the period frm January 1 to Dooernbar 31,'1989. Fuel loading began at WOGS on March 12, 1985.- S e operational phase'of the Radiological Environmental Monitoring Pr%&-u began with initial criticality i on May 22, 1985, with the first detectable quantities of radioactivity j reported in plant effluents in June, 1985. his report contains a description of the Radiological Envirmmental Manitoring Fr%i-u conducted by Wolf Creek Nuclear Operating Corporation (WCNOC), results of sanple analyses perfomed by Teledyne Isotopes, a discussion of nonitoring ru,r-u results, a discussion of s@t-u deviations and revisions, and a discussion of the results of the Environmental. Protection Agency (EPA) Interlahnratory Conparison Fr%smu. Individual sanple results and a summary of results in the Nuclear Regulatory Camission (NRC) Branch Technical Position specified fomat are included'as appendices' to the report. ~ Tritium frm routine plant releases was detected in Wolf Creek Cooling Iake (WCEL) throughout the year. Activation products were detected in lake =ii=mt ()m-54, Co-58 and Co-60) and the algae sanples (Co-58 and Co-60) in the 4
- inte vicinity of the NCCL discharge cove.
Tritium was detected in a drinking. water.sanple at Iaroy in the first quarter sanple of 1989.. %e result was at background levels with a large standard deviation associated with the measurement. All other tritium sanples for the year at Iaroy were less than detectable. Tritium was also detected at two ground' water sanple locations collected the fourth quarter of 1989. %e ocmcentrations were well belcw the Technical Specification reporting levels. All nuclides detected in the Radiological Environmental Monitoring sanples were below applicable Technical Specification reporting levels'. s. 1989 AlemhL RBnTrrmtr4L ENVIRCIOGRE5E. @ERMTG REPGU MIF GEEK GEIEEUEDG SHEIGI PAGE 4 OF ' 45 1
? I. IWXEUWE IMElRIPTIM Radiological environmental sanples were collected according to the schedule in Table 3.12-1 of the Wolf Creek Technical Specificaticms sad Section 4.0 l' of the Offrdb Dose Calculation Manual. All sanples were collected by WC'NOC's Endfnmental Managenent Group and sent to '!41edyne Isotopes of Westwood, New Jersey for analysis. Table 1 lists sanpling pathways and frequencies of sanpling and analysis. -The following is a description of the sanpling and analysis pugeri by individual pathways. Airborne Particulates and Iodine: Iow volume air sanpling purps continuously collected particulate sanples 'on 47nm glass fiber filters; sanples were than drawn through charcoal canisters to collect I-131. Filters and charcoal onnisters were changed out weekly, labeled, and shipped to Toledyne Isotopes for analysis. Total sanple volune-used to calculate air concentrations was determined fran the average of the initial and final sanpling flowrate and the total time of collection. Gross beta analysis of the air particulate sanples was performed i approximately 72 hours following filter collection to allow decay of radon and thoron daughter products. Each filter was mounted on-a stainless steel-planchette and counted on an autanatic alpha-beta counter. I Weekly air particulate filters were acabined into quarterly caiposites for l each location and analyzed for genua emitting isotopes.on a Ge(Li) detector. Charcoal canisters were routinely counted in groups _of five to determine the presence or absence of-I-131. Positive indication of ah4de 'I-131 would i i have been supplementni by separate analysis of individual canisters for each location. Air sanples were collected fran the three sectors with the highest ground level D/Q, the nearby comunity of New Strawn, and a control location. i Distances and directions to sanpling locations fran the plant site are listed in Table 2; locations are shown in Figure 1 (nearby locations) and Figure.5-(distant locations). E 21 The thennoluminescent dosimeters (TEDS) used during 1989 were provided by Teledyne Isotvrse. The TIDs consisted of rectangular teflon wafers im g wgnated with CaSO4:Dy. Prior to placement in the field, the dosineters i-were annealed for at least cme hour at between 250 and 260 dagues centigrade, then placed in polyethylene pouches and holders containing 0.093 inches of wam. shielding to filter out low energy radiation. New field-i i 1989 JetERL RADIrrmTr'AL ENVIIDBENML TERMIIG REEGT NNE CREEK GEEERM21G SMFIN PKit 5 OF 45 + - - -, - - - - --.v ,,.,,am-- em,
L dosimeters were exchanged _with W dosimters and the exposed dosimeters were returned to Toledyne Isotopes for analysis. Freshly annealed control dosimeters were sent with the exposed TIDs to record transit exposures received during shipnent as well as system background of the TID raadar. Gamma exposures were measured on a Teledyne Model 8300 TLD randar; individual dosimeters were then re f rradiated with a known exposure fram a-Cs-137 source-and read again to detemine individual dosinater calibration factors. In general, TIDs were located 3-4 feet above the ground on utility poles; they were placed inside either plastic themostat boxes or fiberglass air particulate sanpler housings to protect them from moisture and tampering. 'No TIDs were placed at each location to provide duplicate measurments. TID locations are shown on Figure 2 (plant vicinity) and Figure 5 (distant). Table 2 provides distances and directions of each location from the WOGS site. BLtdK1 - Monthly conposite sanples of drinking water were collected by_ continuously drawing aliquota at one to two hour intervals. Grab sanples of surface water and ground water were collected cm a nonthly and quarterly basis, i respectively. All sanples were sent to Teledyne Isotopes for analysis. I All water sanples were analyzed on a Ge(Li) detector to'detemine if gamma mitters were present. In addition to ganna analysis, a radinthemical-analysis for I-131 was perfomed on drinking water a6d ground water sanples. Gross beta analysis was also perfomed on-drinking water sanples. i Tritium analysis was performed by liquid scintillation counting on a quarterly basis for drinking water and on a nonthly basis for surface water. Tritium analysis for ground water was performed quarterly by gas counting. l Drinking water sampling locations are at the water treatme.t statims for the towns of Burlington (upstream control location). and Iercy (downstream indicator location). Surface water sanpling locations are at the John Redmond Reservoir outfall (control),-Wolf Creek CooliIg Lake discharge cove (indicator), and' Wolf Creek Cooling Iake main dam (indicator). Ground water is sanpled from three wells located l hydrologically downgredient fram Wolf Creek Ccoling Iake and frun an upgradient control well. All water amnling locations are listed in Table 2 and shown in Figures 3 and 5. Incestion: Milk sciples were collected on a semi-monthly basis fItzn April through November (while milk animals were on pasture grass) and on a monthly basis 1989 AIGIORL RADImnrfTCRL ERWIRGREINmL OPERNEDG REPORP NTF CREEK GEM RNFING S M PION PAGE 6 OF 45
i the retainder of the year (when animals were en stored feed). Sanples were sent to 'mledyne Isotopes where radiochemical analyses for I-131 and t ganma analyses were performed on each sanple. Icoations are shown in Figures 4 and-5. Broadleaf vegetation aanples were collected nonthly during the gtwing season. Occasionally alternate sanpling locations were used when quantities of vegetation were limited,. such as early or late in the gtwing season or during dry periods. Additicmally, sanples of crops irrigated with water frun the Neosho River downstream of Wolf Creek Cooling Ialoe were collected during harvest. All vegetation sanples were sent to Teledyne Isotopes and analyzed by ganma spectroscopy. Icoations are shown in Figures 4 and 5. Fish sanples were collected semiannually with several recreationally inportant species being sanpled. Sanples of boneless meat portions were sent to Teledyne Isotopes and analyzed by ganma sghwoopy. Incations are shown-in Figure 4. All sanpling locations above are listed in Table 2'. Shoreline' Sediment ~ & Aountic Veaetatim: Semiannual sanples of shoreline WNant and aquatic vegetation were collected fran the discharge cove area (location "DC" on Figure.3) of iblf Creek Cooling Iake. Ganma analysis was perfonned en each sanple. i 'I d 5 4 IDE N GEEEMEIIG SDEIGi PAGE 7 OF 45
F II. DHEIEEEN & REKKES - Analysis results for all pathways are sumarized in Appendix A using the fomat described in IRC Radiological Assessment Branch Technical Positicm, Revisico 1, November 1979; results for individual'sanples are listed in Appendix B. In this section, results are discussed by pathway and analysis type. Operational results are related to control location results, p oo :s tional r values,-sources of radioactivity, and affluent releases when applicable. Trends or seasonal offacts seen-in the data are also discussed. Airborne Particulates and Iodine: Results of gross beta analysis of weekly air particulate filters are'shown l in Table 3. In addition, the four indicator locations are avara-i and plotted graphically with the control location in Figure 6. Finally, Figure 7 shows the relative variation of the indicator average as a peu. - tage of the control location results. Figure 6 denenstrates how closely the indicator and control locations tracked together. Results frcan the weekly analysis of charcoal filters for I-131 showed no-- canoentrations above the detection limit during the year. Results of the cuarterly gama analysis of air particulate filter cmposites are sumarized in 'Inble 4, which shows that naturally occurring Be-7 and K-40 were detected regularly, as was the case during gooperational nxmitoring. L No effects of plant operatica were seen via the a4*rne pathway' for the. year. .Tms_t i Quarterly ganma exposures measured at each location for 1989 are shown in Table 5. Values are mvmalized to a 90-day standard quarter. Results from TIDs located near the plant site (less'than _approximately three miles distant), which would be most sensitive to changes due to plant operation, were ccumbined into quarterly averages. 'Ibese nearsite averages, using locations, 1, 2, 7, 8,.9,'10, 11, 12, 13, 14, 18, 26, 27, 28,-29, 30, 37, and 38, are ccupared to control TID results in Figure 8. In addition, variation of the nearsite averages frcan the control location results are displayed graphically in Figure 9. 'Ihese figures also include >=oparational data for ccmpariscm. .l 19M M RADWN N N N MIF OtEEK GRERXfRG SB5'IGI PJGE 8 OF 45 u
s m l-Ib changes to area ganma exposure rates as a result of plant operation were identified, i A M Nater! Results of gross beta analysis of drinking water sanples are listed in Table 6; Figure 10 depicts these results graphically along with preoperational values for ocuparison, h gross beta results for the indicator locatim are slightly higher in Ot,+r*mr than the rest of the year. This is attributable to a shorter _than nomal decay time between sanple collection and sanple analysis. The autcznatic sanpler at this location malfunctioned, resulting in the nonthly sanple being split into two canposite sanples for the first and last weeks of the nonth. The value used for October in Figure 10 is an average of the ~ ) two sanples. collected. No significant difference between the indicator and control locaticms was found. Additicnally, no increase over ju.+pational concentrations was evident when evaluated graphically as in Figure 10. No effect due to plant' operation was identified in drinking water sanples by gross beta analysiu. 1 A positive tritium value for the indicator location was noted in the first quarter of 1989 (see 14ble 6A). She error associated with this positive value as'well as all rencining tritium analyses being less_than detectable for the remaining quarters isdicates the positive value was not significant or attributable to plant operatirm. No other radionuclides related to plant operation were seen at detectable levels. Surface Nater Tritium, attributable to WOGS operation, was detected in all surface water l sanples collected fram NCCL in 1989. A total of 588 curies of tritium were released to NCCL during the year. Measured cmcentrations are shown in Table 7. In Figure 11, NCCL tritium concentrations are plotted since NOGS began operation. It can be seen in Figure 11 (page 42) that monthly surface water tritium concentrations appear to be slightly increasing since plant startup. 1his is expected until the lake concentration reaches equilibrium. A peak concentration of 13,000 pC1/ liter occurred in November when the nonthly grab sanple was obtained while a batch release was in progress. Since the sanple point is close to the discharge structure ecmplete mixing had not occurred. She peak concentration is seen in Table 7 and Figure 11. \\ 1989 AIRE 0hL RADTrYmrAL ENVIRO 8EBBE OPEREFDEI REEWT NOW GEEK GERWIRNrDIG S'BEION PAGE 9 OF 45 i
=- o j All tritita omountrations measured were below applicable 'Dschnical )' Specification reporting levels.. Gross alpha, gross beta, and Sr-90 analyses (not part of the normal REMP surface water analyses) were performed on the April surface eter sanples for information purposes. Gross algha was not detected but positive results were noted for Gross beta and Sr-90. Gross beta activity levels are within the nomal range measured in drinking water sanples at Burlington and Imroy, indicating the measured concentrations are probably background concentrations and not attributable to plant effluents. '1he Sr-90 activity is most-likely due to fallout because its long halflife (29 years) and the absence of Sr-90 in routine plant effluents. '1here were no ganna emitters related'to plant operation detected in surface eter for the year. Ground Waters Tritium me detected at locations D65 and C49 in the fourth quarter sanple; the measured activities were 760 and 810 pCi/litar respectively. 'Itase cancentrations are below applicable Technical Specification reporting 1 limits. Beginning in 1988, a nere sensitive tritita analysis s ucaiure was used for sanples of ground water, enabling smaller quantities of tritium to be detected. '1he old detection limit es 800-900 pCi/ liter and the new detection limit is 100 pC1/litar. No gamma emmitters were detected in any of the ground water sanples analyzed. All milk sanples analyzed for 1989 contained naturally occurring K-40 at concentrations consistant with s + & tional levels. Yearly average concentrations were 1350 pCi/ liter at indicator location F-8 and 1340 pCi/ liter ai. the control location. Sanples at location F-8 were cmly available between February and June of this year and one sanple was available at indicator locatica F-1 in January. '1here were no indicator j sanple locations available after the first June sanple at F-8 (see Fwpmu Deviation section for explanation). o No other ganna emitters were detected and no plant related effects were identified during the year. [' Food & Garden Croos t Ganna analysis of broadleaf vegetation sanples revealed naturally oewrring ganma emitters K-40 and Be-7 at concentrations emparable to gamerational and background levels. 1989 AteERL RADItYnint%L ENVDOGENIE @ERNPDG RERRE WTE CREEK GENERATDG SmrIm PAGE 10 OF 45 j'
Cs-137 was also detected in a sanple fram location A-1 during July. The concentration was 0.0184 pCi/ gram. This cancentration for Cs-137 is attr2uted to fallout. S e range of fallout Cs-137 seen in preoperational sanples was 0.0131 to 0.0478 pCi/ gram. Also, Cs-137 was not released in. { airborne plant effluents during the third quarter of 1989. Finally, Cs-134 was not detecta$, _ although it would be expected in canparable quantities if the occurrence of Cs-137 was related to plant operation (Cs-134 decays with a shorter halflife than Cs-137; detection of Cs-137 alone indicates older fallout as opposed to newly produced fission products), i No other gamma anitters were detected for the remainder of the year, and no effects of plant operatim were identified. In addition to braodleaf vegetation, crop sanples were collected which - were irrigated with water frun the Neosho River below the W31f Creek Cooling lake outfall. Genna analysis revealed naturally occurring K-40 to be present in the aanples, with no nuclides detected due to plant operation. fithi Naturally occurring K-40 was measured in all fish sanples at concentrations i consistent with pwopeuational levels. i No other radimuclides were detected and no effects of plant operation were seen for this pathway, heli = nt/ Shoreline Soils Table 8 shows gamma anitters detected in Wi-nt and shoreline soil sanples i collected fran the discharge cove of Wolf Creek Cooling Lake during 1989. 1 In addition to the naturally ewing nuclides (Be-7, K-40, Ra-226, 2-j 228), several other radionuclides were detected. Hn-54, Co-58, and Co-60, seen mly in the Wi=nt sanples, are activation products whose presence is attributed to plant operation. Iie Cs-137 concentrations measured are considered to be primarily due to l fallout rather than plant operation since they are at or below-concentrations measured p p ationally. Also, Cs-134 was not detected, although it would be %%m:1 if the occurrence of Cs-137 was related to plant operation. t i Aauatic Veaetatim A cmbination of naturally mwing nuclides, fission products, and activation products were detected in algae sanples from the NCCL discharge cove during the year. Rooted aquatic vegetation was not available this year. A sumnary of the concentrations measured is-shown in Table 9. i NO2 CREEK GENERM' DIG S'5EIGN PAGE 11 0F 45
J ) l Naturally. occurring nuclides measured were Bo-7, K-40, Ra-226, and %-228. Activation products seen in the sanples were Co-58 and Co-60; both of these are attributable to operational releases. Fission product Cs-137 was detected in both algae sanples. While it is possible that operational releases nay have contributed to the measured levels, these levels are below concentrations measured p.wyraticnally. We detection of cs-137 in these sanples is therefore considered to be due-to fallout to a greater extant than to NOGS operational releases. i k i r 4 1 ? h e W N GEmmG Smmm PAGE 12 0F 45 ( -.e
m. r- -r. IJmo i- %ggr gnarum* AND MO3U81 NFISHEE h 1989 Annual land Use Survey was ocupleted in Ottnhar. Information as collected using a conbination of mailed survey forms, telephone contacts, and door-toh contacts. Results of the survey, showing the distances to the nearest residences, milk producing animals, and vegetable gardens within five miles of the plant site, are sunmarized in Table 10. '1here were no changes to the nearset residences in each sector. The closest residences to NOGS remain in Sectors A and Q. '1hese residences are 1.4 miles distant from the plant. Milk animals were identified in Sector G where previously none had existed. Milk animals are still present in Sector F although the distance to the nearest animal increased fr a 1.6 to 4.7 miles. Current identified milk-producing locations within five miles. frm the plant ares D-2 Milk not used for human consunption. l F-13 Milk not used for human consumption. G-6 Dairy cattle are removed fr m 5 mile radius during milk production. M-19 Dairy cattle are removed fr m 5 mile radius during milk production. One change was noted for the location of the nearest garden in each sector. t '1he nearest garden in Sector C is now at Iocation C-12,1.9 miles distant frm NCES. '1he previous distance to the nearest garden in this Sector was 2.0 miles. '1his change does not affect the current sanple locations. As in the past, it should be noted that dose calculations are performed for a W rne and liquid pathways for a hypothetical individual at the exclusion area boundary in the highest X/Q and D/O sector-(for.ai*rne pathways) and at the circulating water discharge point (for liquid pathways). Calculated doses are therefore not affected by changes in residence, milk animal, and broadleaf vegetation locations identified by the Annual Iand Use Survey. i - i i 1989 JealtaL RADTrrmir4L ERETIR(BBGBBBL WEIUEDG REEWT NOT CREEK GIBEEUEDG SBEION PKiB 13 OF 45 l
.~ IV. IEMPERIIG HEIEUM MFIXrIGE Airborne Particulates and Iodine l 1 All locations (9/20/88 - 5/16/89): - All air sanplers which were in the field during this time were calibrated with a nass flownster which was found to have an error of ~-11% when sent to the vendor for calibration. i 'Ihis does not confirm a problem with the air sanpler calibrations but it does indicate a potential problan nay exist with the calculated sanple volumes frun 9/20/88 - 5/16/89. A canplete review of the problen resulted. with a detemination the calibrations did not result.In a s wi-n deviation 6 i and did not have an adverse impact on the Radiological Environmental )bnitoring Pr i-n.- 'Ihe error associated with this problem was in a l w l conservative direction. An assessment was made to determine the offacts of the mass flownster calibration error upon the sanple volumes calculated for airborne particulates and radioiodines. It was deterndnad that all air sanple. volumes calculated during this; time frama could have been approxinately 11 percent lower than the true sanple voltanos. 'Iherefore, the reported concentrations any have been higher than the-true canoentrations since the - same activity level is divided by a smaller. volume of air. All of the l radiolodine results during this tine frame were-less than detectable and were well within the LID requirements of Tech Specs and are therefore unaffected by the potential error. t Location 2 (11/11/89 11/21/89): Air Sanpler NC-5981 was in service beyond its calibration due date of 11/11/89. Cutt w tive actions.have been initiated to prevent a recurrence of this incident. Air sampler m1thration due dates are now tracked on the RIMP schedule. 'Ihere is no basis to believe that the accuracy of volume calculations for these sanples was - l affected in any way by this event. Response characteristics for the flowmeters that are used with these aanplers generally are quite stable with r age. In addition, the flownetar on NC-5981 had been in actual field use for less than three nonths at the time that it exmaariaci its calibration due date. 'Iherefore, it is believed the calibration curve for this~ flownster was still' accurate and that recalibration of NC-5981 and recalculaticn of sanple volumes for the period in question was not warranted. l l; location 2 (12/12/89 12/19/89):. h sanpling punp motor seized naking it inpossible to calculate the aanple volume and resulting air ocncentration, h sanple filter was counted and results reported as total pCi. 'Ihe sanpling punp was removed from service, p H&lU. Incation 35 (1/4/89 - 3/17/89):- Che of the TID's at this location was lost due to road construction efforts. 'Ihe second TLD was found and i=arliately i re-installed on the utility pole. h Coffey County, Engineer was contacted i 1989 JenERL RADIntnrHCRL BlVIIOaENEL (PERMFDG REEUtr WWE OtEEK GIRERMFDG SMFICM PJGE 14 OP 45 . ~
y u l and requested to provide the road crews with a description of the TID boxes and instructions to avoid damaging the boxes. '1he nonitoring requirenant at this location was still met with the rainining TID. s t Incation 16 (4/4/89 - 7/5/89): - Ihe TID's at this location were missing, i probably due to an act of vandai M. Since acts of vandalism are beyond the. contw>l of WOGS and it appears to have been_an isolated incident, there were ) no ccu.u:cdvs actions taken. Icontion 21 (10/2/89 - 1/3/90): One of the TIDs at this location was apparently not renoved since when the TID was analyzed a negative dose was obtained and the wrong color label was an' the TID.. h nonitoring-requirement at this location was still met with the second TID. Drinkina Water: Location IM-40 (4/4/89 - 5/2/89): - h sampler had lost power at see time during the nonth and only collected a small fraction of the normal collection volume. A defective power outlet caused the loss of power. It is believed because of the small sanple volume the requirunant for a ocmposite senple was not met during April-(listed in 'llable 6 as N/A). '1he electrical outlet was repaired and the-sanplar was placed in service. On this same aanple the Gross Beta Analysis ~was not performed due to a personnel error in filling out the shipping fonn.~ An attenpt was made to correct this error by notifying the analysis vendor to perfctm the analysis on the stored sanple..Ihe-vendor notified NCNOC the sanple had been l misplaced and further analysis was not possible. Incation IW-40 (10/10/89'-;1/2/90): Construction activities caused numerous interruptions in sanpling at this location.. '!here were generally. four types of problems encountered during this periogl which were respcmsible for the sanpling interruptions: demolition of:the secxxid floor of the - building necessitated renoval of the sanpler, loss of power due to *=aring by construction personnel, rerouting of water through the facility by-passing the sampling inlet, and freezing of the sanple line during cold-weather. '1hese events represent deviations frm the sanpling program since a-rung to the ODCM monthly conposite sanpling of drinking water supplies shall be perfonned with time intervals between aliquots not to exceed two hours. Using this criterion, drinking water sanples collected fra IN-40 on 11/7/89 and 12/5/89 are not true catposite sanples due to the sampling interruptions experienced at that site.~ In addition, numerous interruptions. during December caused the nrmthly sanple to be unavailable due to insufficient volume (less than one pint) of water collected. Since construction activities at IN-40 were beyond the control of WCNOC, corrective. actions were aimed at maintaining.sanpler operability through as noch of the construction period as possible. ~ Normal sanpling was resumed 1/2/90. Incation BR-15 (10/3/89 - 11/1/89): '1he timer which controls the interval between aliquots malfunctioned and reset to 80 hours between collections. i. 1989 ABEEmL RADImmTr'AL ENVIIGODBERL TERNEDG REEGT WIF GREK GBEIEM'DG SDG'IGi PAGE 15 OF 45 .m,- e. ..--n, ..ne, .,-.-.~---m a- ,-~ -
This deviates frm the pw n which requires a ponthly canposite sanpling of drinking water supplies to be perfonned with time intervals between aliquots not to exceed two hours. The malfunction did not occur when the timar was positioned to the " minutes" moda rather than the " hours" made. The timar was reset for a sanpling interval of 60 minutes which corrected the problan, huh.L There were no deviations in milk sanpling; however,. the loss of indicator sanpling locations during 1989 needs to be mentioned. Indicator location F-I was renoved frm the program in January when the diary cow quit producing milk. This location was replaced with F-8 which had a milk producing cow. 2his indicator location was used until June whan the cow was sold and noved out of the plant area. Following the loss of F-8, there were no milk sanpling locations available frm which milk was used for hunnn ecmsunption within five miles of the plant site. t Sanples were still obtained and analyzed at the control locaticm in the event an indicator location became available during the remainder of the year. Food & Garden Croos: 1 Broadleaf vegetable aanples were not collected during April-1989 because they were unavailable at all locations. 2his was verified by visual inspection of the gardens on'4/25/89. Broadleaf vegetable samples were unavailable from Incations G-1 and R-1 l during August 1989. N spring crop of lettuce was depleted ~at R-1 while a fall crop of turnip greens at G-1 had not matured sufficiently. Broadleaf vegetable sanples were unavailable from Iccation A-1 during Septanbar 1989, h crop of swiss chard at this location had surv =*=i to insect infestation, No corrective acticms were necessay since the schedule directs these sanples to be collected "as available" during the growing season. Aauatic Veaetaticci l Rooted aquatic plants were not available during the routine sanple collection schedule. Algae was collected in place of.the rooted aquatic plants. She 00CM requiries a sanple of. rooted aquatic plants semi-annually therefore, this is a deviation frm the established sanpling schedule. l' Since this sanple is not required by NOGS 'Dschnical Specifications it will l_ be deleted fr a the ODCM, but rooted aquatic plants will continue to be l collected when available. 1989 JMERL RADImmrCAL ERWIIDGENEhL TERMIIG REEUU MIE CREEK GEIEREDG SHEIGi PAGE 16 OF 45 i
V. EPA INfEAB3UGGN GEE 98WK3i PEGU88 RIIBERS Teledyne Isotopes, contracted to perfonn analysis of radiological environnental sanples for NCNOC, participated in the EPA InterlaboratoLy Ccaparison Program during 1989. Table 11 shows inte m.m g ison test results received during the year.. 'Ihe table 2'.sts the sanple number and data, the sanple maita,.the nuclide or analysis type, the known value reported by the EPA, the measured value reported by 'mleuyne Isotopes (based on triplicate analysis), and the normalized deviation fran tho' known. (The normalized 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 normalized deviation larger than 13.0 gwvi.s followup j action to identify the cause of the discrepancy.) Results are listed in the table for _only sanple media and analysis types corresponding to those performed for NCNOC. j One of the 39 intemmwison results exo* a normalized deviatica of 3.0. Ba-133 results for water sanple #521 were lower than the EPA value. An investigation showed no reason why Ba-133 was low by 5.54 standard i deviation (std dev) while the other isotopes were all within i 2 std dev. 'the detector efficiencies and Ba-133 branching intensities were chh1 and - i found to be correct.. On 10/31/89, 300 ml of the original undiluted sanple were counted with Ba-133 having 43.9 i 5.8 pCi/1. L'Ibe next test for Ba-133 { (#530) was within the 3 std dev criteria for acceptable results. 1 No systamatic problems were identified for any sanpling maiia or specific analysis. l 'l 1989 JWEERL RADInrmTCRL EMDMBEMBL OPEWmW REPORE g NCEE CREEK GEBERA5'DG SMFIGE PJGE 17 OF 45 - l ~
. - _ _ _ ~ 1 S N EJC 1 i 1989 RADIf7MCE IBWIIGGENIE MEEKRDG FRIEUWE sneyLDs snumrm i EXPOSURE N(NBER OF SAMPLES SAMPLDG AND TYPE AIO EREQUEICY PAD 9&Y/ AND mrJJirTICN OF ANALYSIS SAMPLE SAMPLE LOCATICNS FREQUENCY AIRBCRNE Iodine & Indloator locations' Continuous operation Iodine canister. particu-at staticri ntanbers of sanpler with Analyze weekly for. lates 2, 3, 32, ~ & 37 m sanple collection as I-131. Figure 1; Ccntrol required by dust _ i location at statim loading but at least -~ Analyze for gross. 40 on Figure 5, weekly.- beta radioactivity not lese than=24 hours following filter change. Perform ganna isotopic analysis-on.each sample when 1 beta activity is greater than 10 times the yearly mean'of control-sanples. Perform = genna' isotopic i t analysis on. m - +1te (by - location) once per quarter. DIRECP 38 TLD locations-Quarterly at each-Ganna dose within 5-mile radius location quarterly of site (station numbers 1-38 on Figure 2) and two offsite locations (stations 39 & 40 on Figure 5); two TLDs at each' location, r b 1989 AleERL RADIrYMCAL EIWBUGEDHE TERMDG REPWT MIF CREEK GENERMDG SBG'Im PAGE 18 OF 45-l i
F 'IN KJC 1 L 1989 RADIm(nTN ]gIVDOBEBtmL 3 DEI'ITEDG HEXRAM l-SAggLDU nrsaRTER (cont'd) EKPOSURE NUMBIE OF SMPLES SMPLDG AND TYPE AND PREQUENN PN1%AY/. Ato tyr.T.prTIN OF ANALYSIS SAMPLE SAMPLE IDCA2'IWS ,_5)DUENCY e Surface Upstream sanple at Monthly grab sanple. Monthly gama + . location MUSH near isotopic analysis, the John Radmond - Monthly. tritium Reservoir spillway, analysis of sanples. fran Wolf caposite sanple. Creek Cooling Iake at locations DC and SP (see Figure 3). l Ground Indicator locations Quarterly Quartarly gama at C-10, C-49, D-65; isotopic and Control location at tritium analysis. 1B-12 (see Figure 3). Drinking Municipal water Anthly cmposite* Monthly gross beta supplies at - and gama isotopic Barlington (BN-15 analysis. - ( upstream) and Iaroy Quarterly tritium ( m-40 downstream) -analysis of i (see Figure 3) cmposite sanple. Shoreline One sanple fran Wolf Semiannually. Suniannual gama Sediment Creek Cooling Iake isotopic analysis, discharge cove,_ location DC (see j Figure 3). l Rooted One sanple fran Wolf Saniannually Semiannual gama Aquatic Creek Cooling Lake isotopic analysis Plants discharge cove, locaticn DC (see i Figure 3).
- Canposite n=nlLng is performed by collecting an aliquot at intervals-not exceeding 2 hours.
s l 1989 AleGnL RADTfY(UTf'AL ENVDOGGBtmL TERATDG REPGE r IGE OtEEK GENERATDG SDEIGi PAGE 19 OF 45 i' 1 4 6 ,,e v- ..-e 4. u eea-. ____,m
.i i l 'INEE 1 f i 1989 RADYrumir*AL BWDOWEBEIRL 3DIPIUtDG PIO3Udf SAMPLDG pfMENR (ocnt'd) f I EXPOSURE NWBm OF SMPLES SAMPLDG AND TYPE AND FRICUDCY PNIHRAY/ AND rYYJWW OF ANALYSIS SAMPLE SAMPLE IDCATIGIS _Ep00ENCY [ D GESTIW Milk Control sanple from Semim nthly when Gama isotopic and location S-3 on animals are on I-131 analysis of Figure 5. Indicator pasture; nonthly each sanple, sanples fran F-1 or at other times. F-0 on Figure 4..No: indic.:ttor sanple location existed after June. i Fish One sanple 'frun Wolf Semiannually Gamma isotopic Creek Cooling ieke, analysis on edible i similar control portions. sanple frau John Redmond Reservoir 1 spille y. l Food Broadleaf vegetation Monthly during Gama isotopic f Products sanples at locations
- harvest, analysis'on smilhle i
G-1 and A-1 on pcrtions. Fit 3ure 4;(location R-1 m y be used as alternate) control sanple at location S-4 on Figure 5. One sanple of crops At time of harvest Gama isotopic -b irrigated with analysis on edible Neosho River water
- portims, fran locaticos down-4 stream of the Neosho-l Wolf Creek Confluence I
(Incations my vary l fran year to year). l l l 1989 JeeGAL RAnTrutr:Tr'4L ERWDORIENEL WEEUEDG REPGtr i KEF GEEK GEINERATDG STRTIGi PAGE 20 0F 45 I
'INEA 2 e SIBIPLIDG IOCNI'KN EBEERS, DIRINGS (=flam) AIO DIRIK3' IGE location Distance / location Distance / Location Distance / j Number Direction Number Direction Number Direction TID and Air Particulate - 1 1.4/N-15 4.5/ESE 29 2.6/SSW r 2 2.7/N 16 4.2/E 30 2.2N - l 3 3.0/NNE 17 3.6/SE 31 '3.0/WNW 4 4.0/NNE 18 3.2/SSE 32 3.2/WNW 5 4.0/NE 19 4.0/SSE 33 3.7/WNW 6 4.4/ENE 20 3.3/S 34 .4.0/NW. 7 1.9/NE 21 3.8/S 35 4.6/NNW { 8 1.6/NNE 22 4.1/SSW 36 4.2/N. 9 2.0/ENE 23 4.5/SW-37 2.1/NNW l 10 2.4/ENE 24 4.1/WSW 38: 1 2/NW 11 1.6/E 25 3.6M 39 13.0/N 12 1.8/ESE 26-2.6/WSW 40 >15.0/WNW 13 1.5/SE' 27 2.1/SW l 14 2.6/SE 28 2.8/SW Ground Water Drinkim Water Surface Water B-12 12.2/NNE 'BW-15 3.9/SW MUSH 3.6/W C-10 2.8/W IM-40 10/SSE DC-0.6/WNW C-49 2.9/SW SP 2.9/S D-65 3.9/S i Milk and Food Products Irriaated Croos A-1 1.4/N R-1 2.1/NNW NR-D1 9.2/S G-1 1.6/SE S-3 >15.0/WNW NR-D2 >10/S- ~ F-1 1.3/ESE S-4 >15.0/WNW F-8 1.8/ESE c flah Shoreline Sediments Aauatic Veoetation NOCL 0.6/WNW DC 0.6/WNW DC 0.6/WNW JRR 4/W i t [ t J NIF CREEK GENERNI'DG SMI'EN PAGE 21 OF 45 I I j
'IREE 3 1999 AIR PARr100DGE SAMPU B (MDER IER AROLYSIS Imammt (M ) INDICA'KR IOCNTICNS DOICA'KR ST M ARD O WIROL Dh's C C Im 32 IDC 37 AVMUGE DEVIATICM IDC 40 1/3-1/10 0.041 0.042 0.041 0.046 0.043 0.002 0.042 1/10-1/17 0.032 0.033 0.036 0.037 0.035 0.002 0.021 1/17-1/24 0.032 0.032 0.035 0.037 0.034 0.002 0.034 1/24-1/31 0.043 0.044 0.047 0.050 0.046 0.003 0.046 1/31-2/7 0.051 0.038 0.048 0.055 0.048 0.007 0.048 2/7-2/14 0.036 0.040 0.036 0.045 0.039 0.004 0.039 2/14-2/21 0.039 0.037 0.044 0.043 0.041 0.003 0.040 2/12-2/28 0.043 0.034 0.044 0.045 0.042 0.005 0.041 2/28-3/7 0.033 0.030 0.037 0.043 0.036 0.006 0.037 3/7-3/14 0.021 0.027 0.036 0.041 0.031 0.009 0.026 3/14-3/21 0.015 0.025 0.022 0.021 0.021 0.004 0.018 3/21-3/28 0.024 0.025 0.031 0.032 0.028 0.004 0.025 3/28-4/4 0.024 0.022 0.027 0.025 0.025 0.002 0.022 4/4-4/11 0.023 0.028 0.027 0.029 0.027 0.003 0.026 4/11 4/18 0.030 0.025 0.042 0.041 0.035 0.008 0.038 4/18-4/25 0.037 0.028 0.037 0.039 0.035 0.005 0.034 4/25-5/2 0.030 0.020 0.028 0.029 0.027 0.005 0.027 5/2-5/9 0.028 0.027 0.029 0.030 0.029 0.001 0.027 5/9-5/16 0.027 0.024 0.044 0.032 0.032 0.009 0.033 5/16-5/23 0.025 0.022 0.025 0.025 0.024 0.002 0.026 5/23-5/30 0.033 0.029 0.031 0.031 0.031 0.002 0.033 ) 5/30-6/6 0.033 0.033 0.033 0.034 0.033 0.001 0.033 6/6-6/13 0.029 0.024 0.022 0.026 0.025 0.003 0.024 6/13-6/20 0.024 0.022 0.025 0.027 0.025 0.002 0.029 1989 ABEERL RADIrwomr'41 ggyInagegMBL WBUNDG REPORE M CRIIREC GBERNEDG BUEIGE PAGE 22 0F 45 i - i
'I N E R 3 1989 AIR PNtrICEME SRblPIJE GGE HM5L AlmLTBIS Insrumt (cont'd) 3 (pci/m ) INDICA'KR IDCATICNS DOICA'ITR SThNDhRD CCN1BCL DE E E IDC 32 Ifr 37. AVIEAGE DEC321Qi IDC _40 6/20-6/27 0.022 0.026 0.031 0.027 0.027 0.004 0.033 6/27-7/5' O.027 0.020 0.030 0.027 0.026 0.004 0.028 7/5-7/11 0.030 0.025 0.036 0.037 0.032 0.006 0.035 7/11-7/18 0.028 0.025 0.026 0.027 0.027 0.001 0.030 7/38-7/25 0.033 0.031 0.035 0.032 0.033 0.002 0.030 7/25-8/1 0.022 0.024 0.024 0.023 0.023-0.001 0.017 8/1-8/8 0.030 0.027 0.029 0.027 0.028 0.002 0.032 B/8-8/15 0.034 0.027 0.040 0.041 0.036 0.006 0.037 8/15-8/22 0.041 0.027 0.032 0.031 0.033 0.006-0.031 8/22-8/29 0.022 0 W6 0.023 0.020 0.022 0.001 0.020 8/29-9/5 0.028 0.031 0.031 0.030 0.030 0.001 0.028 9/5-9/12* 0.029 0.032 0.025 0.028 0.029 0.003 0.022 9/12*-9/19 0.031 0.031 0.036 0.031 0.032 0.003 0.038 9/19-9/26 0.034 0.031 0.031 0.022 0.030 0.005 0.018 9/26-10/3 0.040 0.036 0.042 0.033 0.038 0.004 0.036 10/3-10/10 0.054 0.052 0.039 0,055 0.050 0.007 0.047 l 10/10-10/17 0.032 0.032 0.035 0.038 0.034 0.003-0.029 10/17-10/24 0.031 0.044 0.036 0.042 0.038 0 006 0.036-1 10/24-10/31 0.037 0.049 0.021 0.028 0.034 0,,012 0.035 10/31-11/7 0.041 0.040 0.037 0.038 0.039 0.002 0.035 11/7-11/14 0.026 0.033 0.034 0.037-0.033 0.005 0.031
- 'Ihe filters at the centrol locatien (40) were actually changed out 9/13/89, 1989 All010hL RADTrutrurw. gwIgagegBEIE WHUn'DG RIWGtr l
WIP OtIEBC GBugun'DG sun'ICM PAGE 23 OF 45-l i m n-a a < ~
'INEA 3 1909 AIR PNtrICWJtER SABEW GOBS Istm. aMNtMIS MSIRB (amit'd) 3 (pCLAa ) DOICA'KR 10CATICNS DOICARR STNDRD 00NIROL DIGE El Igl_3 J.OC 32 10C 37 AVERAGE DEVIATICM IEC 40 11/14-11/21 0.041 0.048 0.043 0.046 0.045 0.003 0.043 11/21-11/28 0.043 0.043 0.043 0.045 0.044 0.001 0.041 11/28-12/5 0.027 0.037 0.034 0.037 0.034 0.005 0.037 12/5-12/12 0.037 0.032 0.040 0.043 0.038 0.005 0.039 12/12-12/19 3.6* 0.062 0.055 0.062 0.060 0.004 0.051 12/19-12/26 0.047 0.041 0.049 0.059 0.049 0.007 0.046 12/26-1/2 0.029 0.027 0.030 0.029 0.029 0.001 0.027
- Reported as 7btal pCi; sanple volume unknown.
Not included in indicator average. W CREEK GBERA5'DG SBETG8 PAGE 24 0F 45 J
- \\
'IRIEB 4 AIR PaltFrrYrJrm cugggrIgg gngsqJig GRBER AlmLYSIS Insanns 3 (,3Ci/m ) (CMRL) 'lSCKIPE 2B JgL2 JgL) LDC 32 7re 37 IDC 40 le-7 1st 0.0564 0.0560 0.0726 0.0732 0.0532 2nd 0.0654 0.0602 0.0745 0.0713 0.0814 3rd 0.0669 0.0606 0.0701 0.0613 0.0613 4th 0.0602 0.0662 0.0492 0.0536 0.0491 YA0 ist 0.00448 10 ND ND 2 2nd ND ND ND ND 0.00930 3rd ND 0.0103 0.0138 ND 10 4th ND 0.0120 ND 0.00933 ND 20 - Not Detected. No other gamma emitters detected. i M CREEK GEBEEUEDG 895'IG4 PAGE 25 OP 45 1
immut 5 1989 'tLD Innamt (aR/ Standard Omartar*) 1sT GwmR 2ND QUARTm 3RD QUMTER 4TH G RRTE IIrATION M M M M M M M M _= 1 15.6 0.3 16.2 0.3 15.7 0.5 16.1 0.3 [ 2 15.4 0.2 13.5 0.3 14.6 0.4 14.7 0.5 L 3 15.2 0.4 14.9 0.3 15.4 0.5 17.2 0.9 4 16.0 0.3 15.5 0.4 15.7 0.3 15.8 0.4 5 14.0 0.4 13.7 0.3 14.8 0.6 16.1 0.6 F 6 14.3 0.3 13.8 0.3 15.3 0.4 15.1 0.4 L 7 14.8 0.3 14.1 0.3 14.5 0.4 14.1 0.2 8 16.8 0.5 16.3 0.4 16.6 0.9 16.8 0.5 9 14.2 0.4 14.1 0.4 14.4 0.3 14.9 0.4 3 10 16.3 0.4 17.0 0.5 16.0 0.4 16.7 0.3 11 17.2 0.3 16.6 0.2 18.5 0.5 18.0 0.3 12 16.5 0.4 15.3 1.6 15.8 0.4 16.2 0.2 13 16.8 0.4 16.1 0.4 16.5 0.4 16.4 0.3 14 15.6 0.2 15.5 0.4 16.9 0.4 16.4 0.4 15 15.9 0.3 15.1 0.5 16.1 0.6 16.3 0.4 16 15.6 0.4 (1) 16.2 0.3 16.2 0.2 17 15.2 0.4 15.0 0.3 16.0 0.3 15.4 0.4 18 16.3 0.5 16.9 0.5 16.4 0.6 17.0 0.6 19 16.4 0.5 15.9 0.4 17.5 0.4 16.8 0.3 20 15.0 0.3 15.6 0.3 15.7 0.4 18.7 0.4 21 13.2 0.3 12.8 0.3 13.6 0.5 15.6 0.3
- 90 days par standard Quarter.
(1) TIDs lost due to vandalism. 1989 AleionL nanTrummar. IngIIOeeMAL OFIBUEIRE3 REFORT MIP OtER GBEBUEDG BUEIGI PN3E 26 0F 45
1RIER 5 1999 15m summrmt (cont'd) (um/ standard Quartar*) IST QUMtTER 2ND QUNmR 3RD QUNtTER 41H QUhRITR 1LrATim M M M M M M M M 22 15.7 0.3 15.4 0.3 16.0 0.5 16.3 0.3 23 14.5 0.3 14.7 0.2 15.5 1.0 15.9 0.2 24 15.4 0.4 15.1 0.4 16.3 0.2 16.8 0.5 25 12.7 0.4 11.5 0.4 13.4 1.2 12.4 0.4 26 14.5 0.6 13.3 0.3 14.3 0.2 13.9 1.2 27 15.8 0.5 15.3 0.4 15.8 0.4 16.9 0.5 28 13.9 0.5 13.1 0.3 16.4 0.5 13.6 0.2 29 13.5 0.5 12.6 0.4 13.5 0.4 14.0 0.3 30 16.1 0.5 13.8 0.4 15.0 0.4 16.2 0.2 31 15.8 0.4 13.8 0.4 15.3 0.4 14.7 1.7 32 14.2 0.2 13.6 0.4 14.2 0.3 15.4 0.5 33 17.2 0.6 15.6 0.8 16.3 0.6 17.5 0.3 34 19.0 1.1 15.1 0.4 16.5 0.4 16.3 0.6 35 17.9 1.0 15.0 0.5 15.5-0.1 16.7 0.2 36 16.1 0.4 15.4 0.7 15.8 0.2 36.5 0.4 37 15.1 0.4 15.2 0.2 14.5 0.2 15.3 0.2 38 17.9 0.5 15.9 0.5 18.6 0.5 17.8 0.3 39 16.3 0.5 14.8 0.5 16.0 0.4 16.3 C.2 40 14.4 0.2 12.4 0.6 13.3 0.3 14.5 0.7 41 15.6 0.4 15.3 0.5 15.6 0.3 17.5 0.3 42 10.8 0.6 9.3 0.2 10.5 0.4 10.4 0.3 43 9.2 0.4 10.3 0.3 9.2 0.2 9.8 0.2
- 90 days per Standard Quarter, i
MIX OtllEK GBEN5'DG SBE' IGE PAGE 27 0F 45
'seta 6 Uprimrre. gaint asesum (Russ EEm AsesrBIS puurum (pci/litar) IM-40 BW-15 JMQi (DOICAKR) .fCCM m 0L) JAN 6.5 1 1.4 7.2 1 1.5 PEB 7.1 1 1.5 7.6 1 2.2 MAR 6.1 1 1.4 7.5 1 1.6 APR N/A 13.0 1 2.0 MAY 6.0 1 1.5 1.4 1 0.8 JUN 7.3 1 1.5 7.3 1 1.4 8.8 + 1.6(1) JUL 7.0 1 1.3 10.0 1 2.0 ALG 6.2 1 1.3 7.1 1 1.3 SEP 8.1 1 1.6 7.9 1 1.4 OCr(2) 13.0 3 2.0 6.7 1 1.4 11.0 1 2.0 NW 7.2 1 1.5 7.9 1 1.5 DBC N/A 8.9 3 1.4 N/A - Not available. (1) Special grab sanple, not a nonthly canposite. (2) Construction activities at IN-40 caused two sanples to be pulled (10/3-10/10 and 10/25-11/7). 'JNER 6A ORDEQlE WGWL SieELES 4RITItal Jeg0rBIs puerum (pcL/litar) IM-40 BR-15 QUARTER (DOICAKEi ,(CCNIROL) ist 910 1 550 <900 2nd <700 <700 3rd <900 <900 4th <500* <500
- Does not include a Mr sanple.
1989 JessuhL mantrarmm. ENVDOODBtDL NIBUG'DG REPGtT W37 CREBC GBBBUE'DG 958'IG8 PJGE 28 0F 45
1REE 7 satimat unmut meertas 1RITHBE AMRutBIs yearnt (pcunter) IccATIm DC SP MUSH M fIlOICA2tR) (IlOICA20ti fm) 1/17/89 5700 1 600 5200 1 600 <900 2/21/89 4500 1 600 4000 1 600- <900 3/21/89' 4800 1 500 4600 1 500 <700 4/18/89 _4800 1 600 4800 1 600 <900 5/16/89 4600 1 600 5300 1 600 <800 6/20/89 5100 1 600 5200 1 600 <800 7/18/89 5700 1 600 5600 1 600 <900 8/15/89 5600 1 600 5200 1 600 <900 9/19/89 4500 1 500 4700 1 500 <700 10/17/89 5800 1 600-5000 1 600 <600 11/21/89 13000 1 1000* 6200 1 600 <800 12/19/89 7000 1 600 6200 1 600 <900
- This grab sanple was obtained coincidental to a batch release.
M N GBEBREDE 825T38 PAGE 29 CF 45
maa a SR)Dett/SDtEiDB SDIL Fint MIL DISCHRRE QWE m assaasIs numerna (pci/gman - dry @ ) nuts SAMPLE TYPE NUCLIDE CMCIMRATIW 4/18/89 Shoreline Soil K-40 9.75 1 0.98 Cs-137 0.0614 1 0.0151 Ra-226 2.22 1 0.43 228 1.10 1 0.11 6/20/89 Bottom Sediment K-40 12.0 1 1.2 Mn-54 0.0718 1 0.0330 Co-58 0.0445 1 0.0328 Co-60 0.272 1 0.039 Cs-137 0.325 1 0.039 Ra-226 2.53 1 0.51 2-228 1.42 1 0.14 10/10/89 Shoreline Soil K-40 9.78 2 0.98 Ra-226 1.66 1 0.41 2-228 1.03 1 0.10 4 10/10/89 Bottom Aa41=mt Be-7 0.654 1 0.295 K-40 10.9 1 1.1 Co-58 0.135 1 0.040 Co-60 0.294 1 0.045 Cs-137 0.342 1 0.043 Ra-226 2.17 1 0.47 2-228 1.06 1 0.11 i l 1989 JWWElhL RADIrvtrat%L EBRDG8EBEE WEUEDG REPORE MIF CREEK GBRUEDG BBEIGE iAGE 30 & 45 i L
l 'IRER 9 3 acome vranwza um wxx. oramanat mes seem anumsrs p==rna I (sci /9== - * @) l-JB2'E VE ZIRTIM TYPE NUCLIDE CONCllNIMTIM 6/20/89 Algae b7 0.153 1 0.041 l K-40 1.96 1 0.20-Co-58 0.0218 1 0.0032. I Co-60 0.0198 1 0.0050 i Cs-137 0.0385 1 0.0053 Ra-226 0.282 1 0.088 l 2-228 0.0891 1 0.0089 9/19/89 Algae b7 0.226 1 0.082 K-40 0.907 1 0.135 Co-58 0.0365 1 0.0095 Co-60 0.0394 1 0.0096 i Cs-137 0.0183 1 0.0086 + 2-228 0.0331 1 0.0137 I t h r l I t M G3E GEEMSG SMI'IW PAGE 31 OF 45
'IREE 10 ]MNWmt & 'BE 1989 IAID IEE fMMR DIRBOTICM DISTAICE (MILES) 30 NEAREST: SEC'KR IPCM PIANT RESIDBCE MILK ANIMAL GARDEN A N 1.4 NONE 1.4 B NNE 1.8 NONE 3.1 C NE 1.9 NCNE 1.9* D ENE -2.1 2.3 2.1 E E 1.8 NCHE 1.8 F BSE 1.6 4.7* 1.6 G SE 1.6 3.6* 1.6 H SSE 3.1 Inat 3.1 J S 3.3 ENE 3.8 K SSW 2.6 NONE 4.1 L SW 2.1 NONE 2.8 M NSW 1.6 1.3. 2.4 N W 2.1 NONE 2.6 P NNW 2.9 NCHE 2.8 Q NR 1.4 NCHE 2.3 R leM 1.9 NONE 2.1
- Indicates a change frun 1988 data, a
WIP CREEK GBERATDG SDERM PJGE 32 & 45
'IRER 11 PannrnN & BR IBBETAIKBUUURY (IEE9RIIKE8 'IMPIB SAM IRTE SAMPLE NUCLIDE EPA TELEm'NE KRM L,, TYPE RESULTS RESULTS DE/_, 502 11/25/88 Water (1) Gr. Beta 9.00 1 5.00 11.00 1 1.00 0.69 503 10/18/88 Water (1) Gr. Beta 54.00 1 5.00 53.33 1 2.52 -0.23 Cs-134 15.00 1 5.00 15.67 1 1.15 0.23 Cs-137 15.00 1 5.00 16.33 1 3.21 0.46 504 10/28/88 Milk (1) I-131 91.00 1 9.00 87.67 1 1.15 -0.64 Cs-137 50.00 1 5.00-51.33 1.53 0.46 505 12/9/88 Nater(1) I-131 115.00 i 12.00 106.67 1 5.77 -1.20 507 1/20/89 htar(1) Gr. Beta 4.00 1 5.00 ' 6.00 1 0.00 0.69 510 2/10/89 Water (1) Cr-51 235.00 1 24.00 245.67 1 11.72 0.77 Co-60 10.00 1 5.00 12.67 1 1.53 0.92 Zn-65 159.00 1 16.00 181.33 1 5.51 2.42 Ru-106 178.00 1 18.00 191.00 1 9.85 1.25 Cs-134 10.00 1 5.00 10.33 1 0.58 0.12 Cs-137 10.00 1 5.00 13.67 1 0.58 1.27 511 2/17/89 Water (1) I-131 106.00 11.00 98.67 1 0.58 -1.15 512 2/24/89 Water (1) H-3 2754.00 1 356.00 2866.67 1 251.66 0.55 515 3/31/89 Air Gr. Beta 62.00 1 5.00 65.67 1 1.53 1.27 Filter (3) Cs-137 20.00 1 5.00 18.00 1 1.00 -0.69 516 5/12/89 hter(1) Gr. Beta 50.00 1 5.00 52.00 1 1.73 0.69 517 4/18/89 Watar(1) Gr. Beta 57.00 1 5.00 53.00 ! 3.61 -1.39 Cs-134 20.00 1 5.00 19.67 1 1.53 -0.12 Cs-137 20.00 1 5.00 20.00 1 2.65-0.00 518 4/28/89 Milk (1) Cs-137 50.00 1 5.00 53.33 1 2.31 1.15 (1) - pCi/ liter (2) - pCi/kg I (3) - pCi/ filter i MIF CRIBK GBERM'DG SINt'KBE PAGE 33 CF 45 l 1
s eus 11 Insurma or epa nmBEABORa5EEtf G359AISKEI BBIS (cont'd) SAM DATE SAMPLE NUCLIDE EPA TELEDYNE 1001 _1. TYPE RESULTS RESULTS
- gy_,
521 6/9/89 Watar(1) Ba-133 49.00 1 5.00 33.00 1 3.61 -5.54 co-60 31.00 2 5.00 30.00 1 2.65 -0.35 Zn-65 165.00 1 17.00 165.33 1 0.58 0.03 Ru-106 128.00 1 13.00 113.67 17.50 -1.91 Cs-134 39.00 1 5.00 34.00 1 2.65 -1.73 Cs-137 20.00 1 5.00 22.00 1 3.61 0.69 522 6/23/89 Watar(1) H-3 4503.00 1 450.00 4466.67 1 152.75 -0.14 527 8/25/89 Air Cs-137 10.00 1 5.00 12.00 1 1.00 0.69 Filter (3) 528 9/22/89 Watar(1) Gr. Beta 6.00 1 5.00 8.00 1 0.00 0.69 529 10/20/89 Watar(1) H-3 3496.00 1 364.00 3433.33 57.74 -0.30 530 10/6/89 Watar(1) Ba-133 59.00 1 6.00 51.00 1 4.36 -2.31 Co-60 30.00 5.00 30.67 2.08 0.23 Zn-65 129.00 1 13.00 128.33 1 2.89 -0.09 Ru-106 161.00 1 16.00 139.00 1 15.72 -2.38 Cs-134 29.00 1 5.00 23.67 1 1.15 -1.85 Cs-137 59.00 1 5.00 61.67 1 1.53 0.92 (1) - pCi/litar (2) - pCi/kg (3) - pCi/ filter 1989 MMuhl. Immrummu. EDWDogennRI, CEgma'ac, REECIU' RLF CREEK GRERA5'DG SDE'KBI PJGE 34 OF 45
FIERRE 1 \\ lA 1 Y -~~~ ~ ~~~~ iiR f Bj l / h "I ? I Je] ) 4:/ M /X 6~ ~~ ~' %.1 r l \\ l /
- f14AO4 6
1 m c b ~ l / !'E ?># eI %7pjg [ [ ~~.....-- /L M // rw g, / ) ~ c ksa3 4 ' ,n yy c i AIRBORNE PATHWAY SAMPLING LOCATIONS
- - AIRBORNE PARTICULATE AND RADIOIODINE 1989 m unmaHCAL HerBuegamg, WEUtrDIG REPmr "NN PJGE 35 OF 45 I
s
FIGBtB 2 77,7_ ~~~~ iiR y B Q C a y
- 1 qsj
,p ~ ~~ 4e i...%pm y3 -e n /, if /1 4s/ a
)
1 n N k $5 ~~~ ~ '~~ E 3__ F 1 c m a. ... p( ( t s A y tr 9 ) / A; sq F h[jh la_ __ -- e 'y f ' -) g/ j \\' W!, f ~~~ ~~~ \\ ff .h 75 K s r ~- DIRECT RADIATION PATHWAY SAMPLING LOCATIONS e-TLD LOCATIONS 1989 AleguRL RADIGJ0GICE IBIHROBBEREE OPERMUG REPGtf WIP OWEK GREMEDE SBEIGI PAGE 36 OF 45
FIE5tB 3 \\ {A h Y -~~~ ~ ~~~~ MR j;, B
- M Xc
-J GN4 & ~~ p " <J A ' U/ W / X_" %,LT" j p ( l'~i ~~~ ~ "'* 6 N
- gc,.
T__ c 4 h L -~ 'j
- %fs!
h# ef s i ..) b \\ \\ [ g ~~~ n g/l;\\ w?~ 6A_) rk'
- k
.c WATERBORNE PATHWAY SAMPLING LOCATIONS
- -DRINKING WATER a-SURFACE WATER a-GROUND WATER v-SHORELINE SEDIMENT 4 AQUATIC VEGETATION 1989 MuunL naDImancnL sumosamum apunaams aspate M N N SMDON px;E 37 OF 45
FEDtB 4 \\ ~ ~~~~ jf -] 854 y f / a Y .d}..h ~ j" ) %.1 W/ /" /X ~ ~6 ~ Q '/-- -- ; +' ,= ~~~ ~ l~~i N aa d-i r L 14 ) L l k 1 j I x Ff / >%gd PW \\ WN 7 I iL 3 n.,, Y J m; n %d\\ fe 33" E INGESTION PATHWAY SAMPLING LOCATIONS i
- -MILK e-FOOD PRODUCTS E-FISH (WCCL) a-FISH (JRR) 1989 meeuRL nanmrtmr% annamesm8E OREUG3G REFORP MIF CRBIE GBegUGSG SUG'K31 PJGE 38 OF 45 l
l FIGets 5 i i 1 f S no w..,, 8 i L f ~~% ) j) 5 p s.a 1 em iss [ y I e, j I m / 'l = y s sar ) 1 y m t i 3 l l O / / -.i ^ l .-q*f; DISTANT SAMPLING LOCATIONS ,I
- -TLD 8-DRNKING WATER a-MILK
- -BROADcEAF VEGETATION /
IRRIGATED CROPS 1989 NEEmL RpnTrumir'AL BWHOSEBtmL TNUtrDG RERRE WIP OURIK GREEUEEDG SDetTWI PAGE 39 OF 45 i
lll I 1989 AIRBORNE PARTICULATE ACTIVITY WEEKLY GROSS BETA ANALYSIS RESULTS 0.08 0.07 - 0.06 - t I p I n: k O.04 l i ii n ... I h o.= o 0.01 - Q JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC D INDICATOR AVERAGE + CONTROL
FEIWEE 7 O D D -U O -W C O 6 0 g 2E D 0 3 h O -= U D 4 E U ~ g g. W U I D Ea 5 a d2 D. x 0 e Q g 3 D O U ~ D 5$ 3 c 2$ O 4 m t1 4 o D - m u D o y ) El R Z h M g D O 5 0 2 m O z M ~ Cl - E o D U g E 2 h D -M 5 go 0 -g ~ t D C Cl -m h) U h ~k 888888888888888888888 iisssiNsssiiN5siNss* E n'IVA 10 H.LM OD 40 M WIF CREEK GBBIA5'DG SDEKEl PAGE 41 OF 45 i A
ti lll l t OPERATIONAL TLD RESULTS (NEARSITE & CONTROL IACATION AVERAGES) 24 22 A h 18 - i k* D i G 14 - \\[ O j 12 - Q g' 10 - g a 3 - \\ 6 - 4 - 0 4 g - o ,*n 1985 1986 1987 1988 1989 0 NEARSITE AVERAGES + CONTROL AVERAGES PREOP RANGE ,..... -. ~. _
o ll i lll VARIATION OF NEARSITE TLD AVERAGES (% OF CONTROL LOCATION VALUES) 150 140 N a 130 ~s 120 g b o g Ig k 110 u o o O 0 0 oo o o ,0 o ooo oo o 0 0 o o 0 ,'- 0,0 m, 100 o a O z O 80 m O 70-e Q a 50 1980 1981 1982 1983 1984 1985 1986 1987 1988 1989 o (AVG /CNTRL)*100
I j11l g ) D t a0 N S o O O ISY Y ) L 8 A . S O RE N L ( A R D.o . A O R TA E A C I T T D E A O o. J N B I W SS o G O D.' . J N RG IKN 4 M IRD 0 A 9 89 1 O .6 M ) O0 P N OTG N 3 I - 3 o_ ,J LRU 5 4 3 2 1 0 9 s 7 s 5 4 3 2 1 o B 1 1 1 1 1 1 (LORTNO c o g t3,. \\G a l l E lIl 2k 3
FERBtB 11 ggnyg. = g-r ,7g i i I l 1 m I i i i !i x 1 i ii C i j! j i P I i t E l-i g l A M,i! i 3 i i p i i x i ~ mB l o5 j l l 2 l 4 L e i i Sli l k E l' ll,' l
- l
! N%I l I o 5 l -e e i El l. Eg ,i E- '4 a L o!I E l i i s w i 4 O D 1 i l b, h w 'o i E~ 4 g 2 i i o j i l i i i i
- l
-= fifffitfitieeie! Eqqqqqeeeauq.seqs
e.
a-. HEJEL43d I 1989 AletaL RADIfWanCE EB8VIIGSEBRE OPENIN3 REMBtr M QRERK GIBERA5'DG SDERBI PAGE 45 OF 45
APPBBII A IRBORRY 1 NILE DI PGSMS' W ISC RADIGIIRCAL Munumm8T IRABCE 'WimN PGIITEBI, REVISRBI 1, IGBEER 1979 I 1 1 i
1 terl#0euENTAL R49I0t9EICAL NONITORi4G P90EReft $455W9Y P lamme of Factitty teelf Crect nuclear Sectet me. Sie 50-4s2 tocatten of Fac6Iiiy Cef fey County. Eansas Repert6ag Perled w l Ige 9 Icounty.51ste) Analysis and tener llelt Medless or Pathway Total Nuter of All Indicator tocat tens tocat 6en eith M6ghest Annual Steam Centrol tocat eens Monrowt lee thster of Sampled of Analysis Setectlen
== useen (r) iname man (r) Nan (t) eeported p (theit of Straserement) Perfereed (Lt9)
- Range Distance and Directlens **Wange
- Wange Iteeserement s**
St at 6en no. 40 Air Eress (259) 3 34(207/207) 37 2.1 elleslues 36(52/57) 3)(52/52) O Particulate Beta (15-62) (20-62) (17-51) i ( x10-3,C /Co.n.) 1-131 (259) 7 -(0/201) N/A h (20) N/A -(0/52) 0 Se-7 1 64(16/16) 32 3.2 etles suet 67(4/4) 61(4/4) 0 (49-75) (49-75) (49-st) K-40 24 10(5/16) 32 3.2 elles suar 14(I/4) s.3( t/4) 0 (4.4-14) I tJ 54at tens 39 med 40 faternal its (336) Radiat ten Omarterly 0.05 0.17(300/300) 11 1.6 etles E 0.20(8/8) 0.16(16/16) 0 (d/ day) l (0.12-0.22) (0.18-0.22) (0.13-0.38) a 2 3 } IIsolnal Lsuer Ltelt of Setettten (l19) 4 Ilean and range based upon detectele measurements only. Tractlen of detectele measurements at specified locations 6s en46cated 6e parentheses (f) 6 1 -. -. ~.
I i l g 15h I t i I lli! 5 3 t t 1 I f 4 s _7 r i 79 te e~ I 5 - L 47 Se k4 e i \\ ~ vt x a: de a es se - I Y' g j e 3 g 4 e t =* _: J a s ) $s at es - = 14 n s+ I s i i 3 f et e s,,;: s i s j 5 1 I g g s 1 3 3 S i lIf i I aI = i i i e* 3 ~ ~ 4 4 4 i g j :I i -1 2 e E a v e e e I e. = = t 3 + s i w2 $ j S W C 'g y, I t I w] ~ ~ 4 2 3 i al h -s 5. :: 3 s e iEI 74 Ei fl E:
- 2 1=3 de es se e a
e
- A 8
I 5 g w 1 I U ) 's 1*3*i s j $ s e 4-
- s
-e 51 I W 3 3 it E %1 s}I 1332 j'~ ji 9 e a e a e g 1 r 1 -a = s
- n 5'
8 !Is J' 331_ iL eg le} la c ]* fil 1 2_in - _s PJGE A-3
- w
., - ~....
ENUINOISENTAL 8UWIOLOGICAL MONITORING P99Wl45 SWWWWtf samme of Facility Wolf Creet bcIcar Docket me. SIN 56-4w2 Location of Facility Coffey County, Kansas Seporting Period Annwel 1989 (County,5 tate) Analysis and Lemer Lleft Innelser of feedium er Pathisey Total Shamber gf All Indicator locattens te(at ten with Nighegt Agewel Stran Centrol tout tgag. NUnroutine Sangeled of Analysis Detection = nean (r) umme man (r) man (r) NeporteJ (Ignit of papaseremeet) PerforWPd (119)
- Range Distance and Directions **Wange
- % g fleasurement s**
Station 5-3 Milk 1-131 (20) 0.2 -(0/8) N/A N/A -(0/20) 0 (pCi/a) samme (2s) K-40 100 1281(8/8) F-8 1.8 miles ESE 134 F(7/1) 1335(20/20) 0 (818-1466) (1260-1460) (1200-1530) e 1 1 a i e meninal temer Limit of Detection (Lt0) fleen and range based upon detectatple measurements only. f rettien of detettable measureaments at spe(if sed letations es ande(ated en parentheses (t) .-. - ~, . ~.... -.. ~.~...
m' .M EevinoastmIAL RADIOLOGICAL StontiatimE PPOEANI Seseguty lease of f acility - Wulf Creek muclear Decket me. 'Sie 50-482 Location of f acility _ Coffey County. Kansas Reporting Period Annual I?9e (county.5 tate) Analysis and Lower Limit Shauber of fledium or Pathway - Total stumber of All Indicator locations location with Hieltest Annual plean Control tocations - 'aunroutine $mpled of Analysis setect ion
- flean (r)
E-Nan t r} Nan (r) - Reported-(unit of steasursetat) - Performed (tto)
- mange Oistance and airections *=aanse
- mange seessurement s**
so contros Sediment / Silt (pCl/g (dry welet) Gamma (2) Se-1 0.5 0.65( 1/2). K 0.6 mile kuu 0.65{I/2) 0 E-40 0.5 11(2/2) K 0.6 elle taas ~ 11(2/2) 0 M (11-12) '(11-12). Y sti-54 0.03 0.012(1/2) K 0.6 elle taas 0.072(1/2) 0 tn Co-58 0.02 0.089(2/2) K 0.6 alle taas 0.089(2/2) 0 (0.044-0.135) (0.044-0.135) Co-60 0.02 0.28(2/2) K 0.6 elle esas 0.28(2/2)- ~-- ~0 (0.27-0.29) .(0.21-0.29) Cs-137 0.06 0.33(2/2) K ' O.6 elle taas 0.33(2/2) 0 (0.33-0.34) (0.33-0.34) Ra-226 . 0.5 2.4(2/2) K 0.6 elle isIW 2.4t2/2) ~ 0 (2.2-2.5) ( 2.2-2.5) Yn-228-0.04 1.2(2/2) K 0.6 mile asas 1.2(2/2) 0 (1.1-1.4) .(3,g 3,4) b moninal Louer Lielt of Detection (itO) flean and range based upon detectable measurements only. fraction of detectable measurements at. spec sf sed locat sons ss indscated en parentfieses (f) .-;...,....,__n. . - - - - -. -~-
) f (. s s t e e n s f n e e oidm h t ee t rut r n eere e tros 0 0 0 0 ar s apa up ee p mERM n i . 5 de c t i a t c .a i c d o ) l n t f o i ( r s l e t o ng n i r an e s t ea C n t n R e 9* e o C "
- m i
9 t 8 ) a ) 8 ) 9 n f c 7 2 ) ) o 1 a ( ) / )2 )1 l e e 29 1 2 2 l M ng /- ( /2 /I d a en 25 1 2 - 2 - e u l ea (7 6 (7 (0 2 n a gR i 8 n . u =* 8 0 9.1 l.1 p f =.
- 9 (9 0
1( I( c a A n i -0 n A s e 5 Y n ps t e - t R s s - f R T e t el S d h c a o g e s st i r a s i 5 r H f s a a 8 - t f f 8 e O s e-8 n I tp P t l - 1 e A h s m t d e e e e e R g i n G o n w a l l l l r O N i_ i l l l u m~ e e e s R t n e P t r o c a 6 6 6 6 e o e i n G k p m t a 0 0 0 0 R c e a et I o R c ss e R D O .o al l C C C C b i l BO B L D B a f 4 tc 0 s e N a s t s n e L r n o d A a a ) i C e k e t .f I l t ac )~ o G c , a O u yt o f .n L n t 5 l ( o O n ) i 8 ) I t u y r ne t D e o t o eg 7 2 ) ) c A e C n t en 29 1 2 2 r ) / )2 )1 a R r u a u a / - ( /2 /1 F C y o c R 25 l 2 - 2 - f L e C i A f f ( d (7 6 (7 (0 T l f n 8 0 9.1 l.1 R o o I 9 (9 y s 0 1( 1( l E i C W l n l O o R y A l t y s t v i t n e l M t e E i .m s c i e n e a c t o r F a L i u F t) s f rf c9 a o f eoet e o w ti 6 4 ) m o e( 5 0 5 0 9 emon t D 0 0 0 0 tl te n t (b t d a a nr nt c aes oc o ti ie L sd tt s u ye ce h ) e 2 ed i S l s a r ( t yl ne en 7 6 8 9o aAf a 3 2 2 p l at r m 0 1 2 2 fu nof e m 4 o AT oP a s a h d G K C R T te ) l s t ea n ib e L y m e a e .g T w r n ur h u l a t s i a a o )' L P r S t d s de l n aa a. f h re e g n otf n l po i n e i eet e/m l 9 ma s e oe gl iSi rl y sp d h oCr e hP S((d M i ( l8 m p t
ENVIROl8EENTAL RADIOLOGICAL MONITORING PROGtApt 54petRRY Name of facility teolf Creek leuclear Docket No. Sim 50-482 l 1 Location of Facility Coffey County, Kansas Reporting Period Annual 1989 (County,5 tate) Analysis and Loser Limit stumber of Meditse or Pathway Total leumber of All Indicator tocations location with Highest Annual 90ean. Control tocations Roeroettne Sampled of Analysis - Detectierr
- Hean (f)
Wane "Mean (f) "Tiean (f) (Unit of Measurement) Performed (LLD)
- Range Distance and Strections ** Range
- It ange
. Reported 80easurements** N0 t.turwus. Wegetation, Gama (2) Aquatic 8e-7 0.1 0.19(2/2) DC 0.6 mile tsai 0.19(2/2) 0 (pC1/g wet (0.15-0.23) (c.15-0.23) weight) K-40 0.5 1.4(2/2) DC 0.6 mile tsai 1.4(2/2).. 0 (1.0-2.0) (1.0-2.0) Co-58 0.01 0.03(2/2) DC 0.6 mile tant 0.03(2/2) 0 (0.022-0.037) (0.22-0.037). Co-60 0.01 'O.029(2/2) DC 0.6 mile 1 sui .0.029(2/2) O p (0.019-0.039) (0.019-0.039) Cs-137 0.01 0.028(2/2) .DC 0.6 mile temi 'O.028(2/2) 0 y (0.018-0.039) (0.018-0.039). Ra-226 '0.2 0.28(1/2) DC 0.6 mile tant 0.28(1/2) 0 Th-228 0.02 'O.061(2/2). .SC 0.6 mile tauf 0.061(2/2) 0 (0.033-0.089) (0.033-0.089) 10cminal tower Limit of Detection (LLD) Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is. indicated 'in parentheses (f). _.c_.
- E- '
u._ --
,? INVIROSOIENTAL RADIOLOGICAL MONIIORING PROGRAM 5tsetARY Rome of f acility Wolf Creek bclear ~ Docket No. SIN 50-482 Location of Facility Coffey County, Kansas Reporting Period Annua! 1989 (County,5 tate) . Analysis and never Limit . Number of Medium or Pathway Total seusber of All Indicator tocations. location with Highest Annual Mean. Control tocations Nimroutine-Sampled of Analysis Detection
- Rean (I)
Name -
- Meean (f) **Rean (f).
Reported (Unit et Measurement) performed itLO)
- Range Distance and Directions **' ange
- Sange Measurements **
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1 WOLF CREFK NUCLEAR OPERATING CORP ~ EXPOSURE PATHWAY - AIR 80R8sE AIR PAR TICUL ATE & CHARCOAL FILTERS-STATION psU9tSER 03 - COLLECTION DATE MIO-COUNT A P FILTER MIO-COUNT CHARCOAL FILTER START STOP TIME GROSS SETA TIftE. 1-131 OATE DATE VettetE UselT5 OATE IPCI/CU.R.) .DATE IPCl/CU.R.) 08/29 09/05 3.00E OS CC '09/19 3.1 +-0.4 E 09/08 L.T. 3. E-02 09/05 09/12 3.llE OS CC 09/22 3.2 +-0.4 E-02 09/16 L.T. 2. E-02 09/12 09/19 2.97E OS CC 09/29 3.1 +-0.3 E-02 09/27 L.T. 3. E-02 09/19 09/26 3.09E 08 CC 10/06' 3.1 +-0.4 E-02 09/29i L.T.- 3.' E-02 09/26 10/03 3.12E OS CC 10/18 3.6 +-0.4 E-02 10/07 L.T. 3. E-02 10/03 10/10 2 89E 08 - CC 10/25 S.2 +-0.4 E-02 10/14 L.T. 3. E-02 10/10 10/17 3.IIE OS CC 11/03 3.2 +-0.3 E-02 10/22-L.T. 3. E-02 y 10/17 10/24 3.02E 08 CC.- 11/03 4.4 +-0.4 E-02 10/28 -L.T. 3. E-02 10/24 10/31 3.05E 08 CC 11/10 4.9 +-l.8 E-02 11/04 L.T. 3. E-02 10/31 11/07 3.00E OS CC 11/17 4.0 +-0.4 E-02 11/11 L.T. 2. E-02 11/07 11/34-3.07E OS CC 11/30
- 3. 3 +-0. 4 E-02 11/18 L.T.
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t' W N. N N N N N N N N N N N N N N> N N N J- = 4 O-9 G-9 9 e S e G 9 9 e e' O O' 9 e m o e e e. e 4 e t-e t t t t t e e a e E w w.- W W W W -- W. w dm31 . W w w w w .W W-w w w m *\\ e en W i e e. e e e.. e' e e e o e e 38%4 N m. N m N m-N. m' m m m m 'm e o e e e.. e W== g m N N m-m W W s 4 64 k- .h e-- e e e a e o e e e e e.. e o e o e e E w W e o e e-e o e o e e o e o e e e e. e a. d e ed e a d a me en d d -e a a a' a -a e >Iw Wi> m. - m.... m.-> N. m N m-e m m N 4 m m N e m m 2 O-m N N. t es 4 - % - m-a m e>gg a Fe N N N' m m e'G=9 e-e e e e en -
== 0 e e.9 O O 9. O e-OO. O e -O O E' e b 's N N N N N N -N N N a w N N;N S' = O : e O O 9 e -. e -. 9 - O e-O G N N N N N N-e.'9 9 9 9 q W w i t-I - 4. w w-w ww w w w ww w w w. w w 4-4 4-t t t t t - t t t t t e a ,l-w = a w w -w WE w mee iB wwE. 9 9 9 9 9 4 4 9 9 m m m M.. m 4 e m-i - = = s- >we. e e -e e e o e e e e-e e e e .O O O O-e weDi O O O 9 9 e e 9 9 O 4 O e i e o e e-es O N = W' 4 4 4 4 4. 6. t t t I e I e e a e .t. e i ' s==.: g m en.i . 9 0 9 + +, +, 9 e -$8 9 j W m Ep% i + w4 i -4 6 5 BOW OI E .w ab o e e ' > e 4 ' @ h 4 'N-m m .k b N > e i i m d. e e e e o e e e e o e e e o e W - - go. -e m-m e e m t e e m m N-m m s> 46 4' ~ N. N-.e m N i wB WE w 4 4 3 b d m ~ 1 3 > WW wg. W 4 m 4 m3 >. M~ O 4 N O F d m em--$- m m m 'd N .SW 5= WW N N O m m N O 9 N N' 9 m m = N. O e m WO e WE> i b m4 m m N N N N. 2 m M M -9 9 9 9 9 su c>o e O e e e O O e O e e e eo e O e e 1 w a = E = 4 lt M> m E4i U N N N O N O N N N N -W N N W M N N W-W W W W W W W W W W W W W W W W W l e I e e e e e e e G. e e e e e e e e e e e e e C e # O e e O e e e 9 e e e G S I e w w w w w w w w w w w w w w w w w 3 9 N N t 9 O m 9 q m e A O A
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E t W l >s - ' N. N. N. N N N N-N N N N N. .N N. N. N. N. N . i .. e b E W W. W 4 W W W W W W W b W W W W W dmh .-W s e-e e e e e e e s e s-e e s e e e e N N N N m m N m m. m .m N-m N en N m Wp-W W 6 e o e e e e e e e 4 e e e e e e .e 3 - h k. W e e e o e e e o e -e i e e e t a e d^ d a e a e a a e e d a a e d a 1 l 1 N p . >. e .e .e e N N e e - W3> N N N m. N N N .s se.>.- .k .h. h. e.
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I ew> N N N.. N N N N N N N N N N N' N N N N m e e e G 9 9 19-O O 9' O e - e O 'O e e e. m o a e a e e e e e e t t i e e a e- 'e e w E w _ w w w w W w w w w w w w w w w w w m e dMS 4mw. e. e e e e e o e e. e-e e e e e e e O8 % I m N m m m m m M N N N N t' m m m N m. wmmi .e ul - e e o e e e o e e e e -e e - i 4 &l e e e o e. 2 w t b b W W W W k h y 4-e. e e a e .e e e e e. e o e. e e o e e i l d e-d d' &'d' d d. & d 1 l 4 0 e - l twwL e. _-. -. ,N e m O e-N m-w._ O m N N m N m m a N O m N m I me- =%' ONO P P P P-O O .O - O-m m a m m N N" N N N m O O O e.m = m a m = m = m
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.j e 4 d836 0 O O G S 9 9 9 9 9 9 9 'O O O< O O O-h e e e e e e e te O N = ut i I e e e e e e t e e 4 4 t t - t t t ' am um &m%4 4 4 + +. + e + + 6 9_ w4' a me t 4 4 m &OWt m e e m N P e 4 m D' d m' m e O e p-Q 4 E w a&4 e e-e e-e e e e a e e e e e e e. e a w 4Ww m N m m e m m m. N m; m m e-e m-'e e e g> '44 4 wa 1 i dR .W il > > { t 4 4' G I W = 1 3
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wg a a WD > m. P N P 4 e e a m O k h 9 e > e N e h e S WW 1 m N N O m N O 9 m m m-m O O m N O m WO 4 WE>l emet S S S S O 9 m m m a m a N N N N m m Em OHOi O O O m -m a m m m a m m a m m m O O w a m E i 4 i I ] m 1 m 1 I v w w w w w w w w w w w w w w N w w w w w w w w w w w w w w w w w w w w s e 4 e e e e q e e e e e e-e e e e e e e e 9 9 9 e O O O .O O e O' e 9 e O O O I w W W W W W W W W W W W W W W W W N m > N m > e h m a e S 9 -m -N e m m 9 m m O e e, m e N m m m .m m 4 e e e o e e o e e e o e e e e e e e 4 m N N m m m m m m m m m m m m m m m e me m N D 4 m G h ( m, k k m e p N-p 4 W4Wu O m' = N O m m N' m 9 9 m N N O m = N 4- } MG>$ I-4>49 9 9 9 9 9 9 9 m m a m m N N N N 4 Omet O O e O m m m m m m a m m a m m .m-m m g w q w i w NM k N k 8 N O A 4 m m b 4 m e N d i m wNwe N o a m N O m m N m-m o m. N N O m a we=o g d>4 e 9 O O O O O O m m a m N N N 5 dme O O O O = m a a m
m m m a m = 0 N m = N N w = PEE Eh 12
8 U W H N m O = e e E E W = e sm3 (mw e Oe% m v>m a w -k 6 e 1 2 m J W I e 6 h 'I l SWW WRb O ImW SMS m-1 m O E i m i i E a E W N i O 0 w w e l g m-a w Me $4 e j st WDR m mO w kW el e >O 9 dOSI O 48 G N = w i 3 -em w m b e % ,t 4 W4 8 mm 4 4-4 m &OW G 4 2 W sh -o u e W Sum M 44 4 WfW sWW > g 34 4 g R& W = 3 > wW w 4 wg m Wws > m N GM WW m WO 4 WKW 4 I mW m .g &M Okei O W 5 m E 4 l m, b, m 'i O Iii e i O I4 l W 8, D m 4 0 N WSWI O >Gwi 4>4 m SMS O m DN l. O WWW I N We> d>4 N MO m W I PEE Ik 13 i 1 l
-- -~ - 1 ~ l N .ne.as. N. N.. N 'N N N-N .N A-w ~4 .N m N .N .N .N e. s t l - - E1 W-W W W W W Ws W W-W W W W-W W W W-W m - e a m3, -w e e-e .e. m *, N - m m m mm. e e e e e e e e e o e e. e -e .%i N m g. N N m m-W--1 wi 4 e o e e-e e e e e e o e o e e .o e e 2 =.i k- > > > > > > > > > > > >' >- > >- W e e-e- e e e - e e. e e e e o e e .e e e W J. a e a e e a e e d a e .d a a a a I i 1 1 - iWW m. - m.. -.- - -. - _. - m.. -- -- N . - -- ~ - - - ~ m. - ~ ~ ~... m'1 g-%- .N N. - N =. .. ' m m m m.- w [ e E I a I i 8 W-N N N. .N N. .N .N N. N.. N N N N N. N. N N N w .s .. W W W W W-W W W W -W W W W W W W W W W .3 .. e 3 WWE ......... -. m m' m m.... m
== a. >W e w.3 .e .e .o .e .e .e..e .o..e .e .o .e - e -e - o m ..e .e .o .e . ~ ~ w. W. W ...w .e .e .e..e.o .e .e : . ~ ~... m. m - - ~...... ei W e e w _e e e e e m m .e e e e . ~- m ~ ~ -m .m ~ W3 WE W W> E - >. E ') e - I = > wW w. > a .t-1 > = w > e N. m. ... m. -. ~ eWW ~ ~ - - ~.. ~ ~ - - ~.. W2 YS> l - - ~ ~ ~ ~
- m. m.
.m W. o m 1 8W = 3 i { -= w w w w w w w w w w w w w w w w w w Di w w w w w w w w w w w w w w w w w w 33............... W B W W W W S** 3 W'W W W W W W W W W - ~ S .m - g e e e o e e e e o e o e e o e e e. e N N N N N N N ~ ~ N N N N N m m N N . ~........... ..... ~ s> W.W u - - ~ m. - ~- ~. - ~ ~ -..- ~. >G>l i 3 .-.. g. g'% -. ~. ~ ~ N m. m m a g-. g 3 l .b O w m... - ~........ - -.. s v.. . - - ~ m. - ~ ~. - ~ ~. - - - ~ W.> g w>. 0 w.. N. .N N N m .m.a m C w = o = PAGE B-14 /
/ WOLF CREEK NUCLEAR OPERATING CoeP EMP05URE PATHWAY - AIRSORNE AIR PAR TICUL ATE & CHARCOAL FILTEks-STATION NUMBFR 37 CettECTION DATE mfd-COUNT A P FILTER MIO-COUNT CHARCOAL FILTER START STOP TIME CROSS SETA TIME t-131 OATE DATE-WOLtmeE UNITS DATE (PCI/CU.M.I OATE (pct /CU.N.8 05/02 05/09 2.99E es CC 05/24 3.0 +-0.3 E-02 05/12 .L.T. 2. E-07 05/09 e5/16 2.006 et CC 05/26 3.2 +-0.3 E-02 05/19 L.T. 2. E 05/16 05/23 2.00E 08 CC 06/0e 2.5 +-0.4 E-02 05/26 L.T. 2. E-02 05/23 05/30 3.32E OS CC 06/09 3.1 +-0. 3 E-02 04/04 L.T. 2. E-02 05/30 66/06 2.97E OS CC 06/23 3.4 +-0.4 E-02 06/10 L.T. 3. E-07 04/06 06/13 3.05E 08 CC 06/23 2.6 +-0.3 E-02 06/17 -L.T. 3. E-07 06/13 06/20 2.9eE 00 CC 06/28 2.7 +-0.3 E-02 06/24 L.T. 3. E-92 y 06/20 06/27 3.14E 08 CC 07/05
- 2. 7 +-0. 3 E-02 06/30 t.T.
3. E-02 y 06/27 07/05 3.45E OS CC 07/14 ~ ' 2. 7 +-0. 3 E-02 07/09 t.T. 2. E-02 07/05 07/11 2.64E GS CC 07/20 3.7 +-0.4 E-82 07/35 L.T. 3.. E-02 07/13 07/38 3.tSE OS CC 07/30 2.7 +-6.3 E-02 07/22 L.T. 3. E-02 07/1e 07/25 3.02E e4 -CC 08/06 1.2 +-0.3 F-92 97/29 L.T. 2. E-02 07/25 08/03 2.95E OS CC 08/l1 2.3 +-0.3 E-02 08/06 L.T. 3. E-02 08/01 08/98 .2.99E OS'- CC 08/I8 2.7 +-0.3 E-02 0s/12 L.T. 2. E 08/0s 09/35 2.99E OS CC OS/25 48
- -0.4 E-02 09/89 L.T.
3. E-02 08/15 08/22 3.05E 08 CC 09/06-33 +-9.3 E-02 08/25 L.T. 2. E-02 08/22 08/29 3.02E OS .CC 09/18-2.0 +-0 3 E-02 09/03 L.T. 3. E-02 Os/29 09/09 2.90E 08 CC 09/19 3.0 +-0.4 E-02 09/0e L.T. 3. E-02 l m ~.. _ _
S W i . N N N N N N N. N N. N N N N N N N N d = 0 9 9 9 O-O t. 9,'O. 9 9 9 G e e e e m e I e' S 4 6 i< 0 0 8 6 e t 4 4. t t 4 h E %. W W W. W WJ W W. W W W W W W' W-W W h m o L-dm3i gaW I e t-e e o e Q$ %I N. A m M m m. e e e e e e e e e e e 'm.' M M N-m 4 m m m m M Wmmi e W-g &i e e 4 4 4 e e e e e 4 e e e e e e 2 - i > -. >e W i e o e e e e e. e a a e d: a d e a a e e o e e e o e e \\ d. d a d a d d 1 I WW . _. -. ~ e. m.e N m. - WE> u = N N. 9-m M N O m. m N 9 9 m-M m e t ag n L>el e P P O O O O m m a m N N N N N m. m i 6: O e m a a m m m m a m. m m, m. m S-E i 1 i w a 8 W N N-N -N N N N N N N N N -N N N N N e e O 9 'O O e O O O -9 9 9 6 -O O-O W d i e t .t t t t t t t t n. I e -I e~.-W'W W e a = m W W W W W -W W W W W W W W-W W E h 54 e W .d WW e e e e e e 4 - e e o e e o e e e-e e W>E m M 'm 4-W' m d 4 M ~$. g - M mO me 4~ de3i O O O O O O O O 9 9 e O .9 9 9 g O et e > m W s e e i e e e 6 e a l' s e .6 e i e be%' am W m + 6 9 6 4 6 + 4 4 + 4 9 e 4: +
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m m a m a m = -m a m -e e' O wW W m G E 2 4 +> B N N N W N N N N N N N N W W W W W W W W W W y W W. W W W. W l e e e e e e e e e e B G e e e e - G-u O O 9 e O e e O e e e 4 O-
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W W W W W W W W W W W W W W W W i e N + m O N e m m m e e m > m - di 4 m O G 9 9 m m e 4 ' e 96 e e e e e e e e e o e e e e o. e - m N D4 m' N m m N m oh m N m m m m m M eR e N m O k e m m e N P 4 N W4W m m N 9 m m N m O m N N O = m N O MOW 4>4 P P S e O O O m m a m N N N N m OMO O O O m m a m m m a m m m a m m O E =>> ,e N m O d a h d m e N P 4 USW i O m m N O m m N m O m N N O m m M W4W I d>4 P P P O O O O O m m m m N N N N dMe O O O O m a m m m a m m a m a m = 0 W PEE B-16
UOL F CREEF NUCLEAR OPERATING CORF E XPOSURE FATHWAY - AIR 00088E AIR PAR TICUL ATE. & CHARCOAL FILTERS STATION NUMSER 40 CottFCTION OATE Rio-COUNT A P FILTER Mio-COUNT CHARCOAL FILTED START STOP TIME 59055 SETA TIME t-131 OATE 0 ATE vetteet UNITS OAYE (PCE/CU.M.) SATE IPCf/CU.M.3 01/03 08/10 3.07E Ce CC 6t/20 4.2 +-6.4 E-02 61/13 t.T. 1. E-02 et/te 01/57 3.93E Se. CC 03/26 2.1 +-0.3 E-02 03/18 L.T. 2. E-62 St/tf et/24 2.83E ee CC 02/02 3 4 +-o.4 E-62 '91/2T t.T. 2. E-02 02/24 01/33 2 92E es CC 02/10 4.6 +-e.4 E-02 02/03 L.T. 2. E-02 01/31 02/07 2.94E:ce CC 02/15 4.s +-o.4 E-02 02/10-t.T. 2. E-02 02/07 02/14 2.91E ee -CC 02/24' 3.9 +-0.4 E-62 62/19 L. T.' 3. E-82 42/14 .et/28 -2.92E es CC 03/03. 4 0 +-0.4 E-02
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4 1 APPIBOIX C - SPEIAL S195Ut OIZEETCBE i .' j i - ) i j i i - 3i 3 ~ i l i l l --mm-eim-ni sumsm e ei is im e map 6tpe au m,is e imme miei-menmin.m.,sua s mi em rmr um a i mu m annir u
~ LEll. 'Ihree additional TLD locations are nonitored which are not part of the Radiological Environmental Nbnitoring Frwaan. '1hese locations are 41, 42, I and 43 corresponding to Stringtown Cemetary, Baffle Dike A and Baffle Dike B. 'Ihe doses at 41 are 'v=marahle to the other nearsite locations but the doses-at the Baffle Dikes are consistently less than the other nearsite ~ i doses.. GN4E ANI!OLS: Game animal aanpling is not part of the Technical Specification required sw&-u but we do collect scne game animals for radiological analysis. This year an Eastarn Cui.Lxitail Rabbit was analyzed. The only nuclide detected en the sanple was naturally occurring K-40. The caplete analysis is included in Appendix B. i I i i 1 i PAGE C-2 I !}}