ML14190A505
| ML14190A505 | |
| Person / Time | |
|---|---|
| Site: | Dresden  |
| Issue date: | 05/31/2014 |
| From: | Teledyne Brown Engineering |
| To: | Exelon Generation Co, NRC/FSME, Office of Nuclear Reactor Regulation |
| References | |
| Download: ML14190A505 (136) | |
Text
...... IN : "
=0. o 50-237 50-249 DRESDEN NUCLEAR POWER STATION UNITS I, 2 and 3 Annual Radioioqical Environmental Operating Report 1 January Through 31 December 2013 Prepared By Teledyne Brown Engineering Environmental Services Exeton6 Dresden Nuclear Powr Station Morris, IL 60450 May 2014
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Table Of Contents I. Summ r and, n
sions.................................
ac I
II. Introduction....................................................................................................................
3 A. Objectiv of the RE MP 3
S. Implementation of the Objectives............................
.... 3 III. Program Descption......................................................................................................
4 A. Sample Collection......................................................................
4 S. Sample Analysis................................................
..... 5 C. Data Interpraon.........................................................................................
6 D. Program Exopons........................................................................................
7
- E. Program Changs.......................................................................................
10 IV. Resus and Discussion:
......... 10 A-Aquatic Environment.........
10
- 1. SurfaceWater.......
10
- 2. Ground Water.....................................................................................
11
- 3. Fish....................................................................................................
. 11
- 4. Sediment..........................................................................................
12
- 8.
IAmshe.
Envinment
............ 12 1.Ai ibo rPn.........
................................... 12 ab..AlrboIniote s
.13 a'n...
'13
- b. Food PrIoduiS 14 C. Ambient Gamma 14 D. Land Use Survey.........................................................................................
15 E. E D
15 F. Summary of Resut
-I Comparison rga...........
16 1
i "
Appendices Appendix A Table A-1 Appendix B Table B-1 Table B-2 Figure §-1 Figure 8-2 Radiologlcal Erwronmental Moitorinhg Report Summary (Meets requiremants of NUREG 1302)
Raog EnvironmetiW MAn#tung Program Annual Summary for the Dresden Nuclar Power Station, 2013 Location Designation. PlstAnq &lcin ad$
l Collection &
Radiologicl rni6 l)dontoring Program - Sampling Locations, Distance and Direction, Dresden Nuclear*Power'Statici,*2013 Radiological Envi t0Fn4 Monitoring Program -Summery of Sample Collection and AnalytlMethds, Drelden Nucear'Power Station, 2013 bresden-ý 6tAl MtnIner..
OSL Lmot.on, Fish, Water, Wnd Sediment Locations, 2013.
Dresden Station Fixed Air Sampling and OS.D Sites, Outer Ring OSLD Locations and Milk Location, 2013 Data Tables andFigures - Primary Laboratory Concentrations of Gross Beta in Surface Water Samples Collected in the Vicinity of Dresden NuclearPower Station, 2013.
Conoent*ions of Tritium in Surface Water Samples Collected in Vicinity of Dresden Nuclear -Poiw Station, 2013:
Concentiki~ons of Gamma Emitters in Surface Water Samples Collected in the Vicinity ofesden Nuclear Power Station, 2013.
C0o.centrations of Tritium in Ground Water Samples ColkO! in the
-Vicinity of Dresden Nuclear Power Station, 2013.
Concentrations of Gamma Emitters in Ground Water Samples Collected in the Vicinity of Dresden Nuclear Power Station, 2013.
Appendix C Table C-I. 1 Table C-1.2 Table C-1.3 Table C-II.1 Table C-11.2
Table C-11.1 Concentrations of Gamma Emitters In Fish Samples Collected In the Vicinity of Dresden Nuclear Power Station, 2013.
Table C-IV. I Concentrations of Gamma Emitters in Sediment Samples Collected in the Vicinity of Dresden Nuclear Power Station, 2013.
Table C-V. I Concentrations.of Gross Bets In AiW Particulate Samples Collected In the.Vicinity of Dresden Nuclear Power Station, 2013.
Table C-V.2 Monthly and Yearly Mean Values of Gross Oeta Conoentratlons(E.-3 pOl/cu meter) in Air Particulate Samples Collected in the Vicinity of Dresden Nuclear Power Station, 2013.
Table C-V.3 Concentrations of Gamma Emitters In Air Particuiate Collected in the Viciirty of Dresden Nucleaw Power Station 2013.
Table C-VI. I Concentrations of 1-131 I Air Iodine Samples Collected in the Vicinity of Dresden Nuclear Staton, 2013.
Table C-VII. I Concentratlos of 1-131 in MilkSamples Collected In the Vicnity of Dresden Nuclear Power Station, 2013.
Table C-VII.2 Concentrations of Gamma.Eniters I Mik Samples Collected in the Vicinity of Dresden Nuclerw Power Station, 2013.
Table C-VIII. I Cnoentrations of Gamma Emitters in Vegetation Samples Collected In the Vicinity of Dresden Nuclear Power Station, 2013.
Table C-lX. I Quarterly OSLD Reults for Dresden Nuclear Power Station, 2013.
Tabdle C-IX.2 Mean Quarterly 06WL Results for the Inner Ring, Outer Ring, Othe and Contd Locatiom for Dresden Nuclear Power Station, 2013.
Table C-IX.3 Summary of the Ambient Dosimetry Program-for Dresden Nuclear PoWer Station, 2013.
Figure C-1 Surface Water - Gross Be t-Station 0-52 (C) Collected in the Vicinity of DNPS, 2000 - 2013......
Figure C-2 Surface Water - Gross Beta - Stations D-54 (C) and 0-57 (C)
Collected In the Vicinity of DNPS, 2003 -2013.
Figure C-3 Surface Water - Gross Bets - Stations 0-21 and O-51Collected in the Vicinity of DNPS, 2000 - 2013.
Figure Ca, Surface Water - Tritium - Station 0-52 (C) Collected In the Vicinity of ONPS,2000 2013.
Figure C-5 Surface Water - Tritium - Station
-,54 (C) and 0-57 (C) Collected in the Vicinity of DNPS, 2003 - 2013.
Figure C-6 Surface Water - Tritium - Stations 0-21 and 0-51 Collected in the Vicinity of DNPS, 2000 - 2013.
Iii
Figure C-7 Ground Water - Tritium - Stations 0-23 and D-35 Collected in the Vicinity of DNPS, 2000 - 2013.
Figure C-8 Air Particulate - Gross Bets - Stations I-01 and D-02 Collected in the Vicinity of DNPS, 2000 -ý 013.
Figure C-9 Air Particulate - Gross Beta - Stations 0-03 and D-04 Collected in the Vicinity of DNPS, 2000 - 2013.
Figure C-10 Air Partculakt - Gross Oet -,"Station, D-07 and D-12 (C) Cotlected In S
- 'the VicinityOf DNPS, 2000 -2013.
Figure C-Il Ai.P..
....-Grsskt Stations 4
Figure C-1 Air ParticulNt --Grossea- $tstn 0-045and 010Collected in th
- l Vnity ofDNPS, 2000-2013.
Figure C-12 Air Particulate - Gross Beta -Stations 008 1and D-14 Collected in the Vicinity of DNPS, 2005 -2013.
Figure C-1 3
' Air Particuhate - Gross Bete --
SaIm
-13 arid'* Collecte in'the Vtcnfty of IDNPS, 2005 - 2013.
Figure C-14 Air Particulat --Gross Bet -- Stations b-55 and 0-56 Collected In the V.iciniy of DNPS, 2000- 2013.
Figure C-1 5 Air Particulate - Gibs Beta -
tatidn 0-58 ColWetd in the Vicinity of ONPS, 2011 - 2013..
C.*.
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Appendix D Inter-Laboratory Comprison-Progrand Table 0-1 Analytics Environmental RaRdkioeVty.Cross Check Program Teledyne Brown Engineeting, 2013 Table 0-2 ERA Environmental Radioactvity Cross Check Program...
Teledyne Brown Engineering, 2013 Table 0-3 DOEs Mixed Analyte Perfomance Evaluation Program (MAFPEP)
TeledYne Brown Engineefrng, 201,
- .,.," ~..............*
Appendix E Erratp Data.....
Appendix F Annual Radiolgcal Grndwater Protectlono rogram Report'(ARGPPR)
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Summary and Conclusions Thisport nthe Radiological Envir ental Monitoring Program conducted for the Dresden Nuclear Power Station (DNPS) by Exlon covers the peridd I January 2013 through 31 December 2013.
uring that time period 2,023 analyses were performed on 1,885 samples. In assessing all the data gathered for this report it was concluded that the operation of DNPS had no advere radiological impact on the environment.
In 2013, the Dresden Generating Station released toithe environment through the radioactive effluent liquid and geseous pathways approximately 55 curies of fission and activation gases, 33 curies of Carbon-14 itid apprfietely 24 curies of tMitium. The dose from both, liquid and gaseous effiuents was conservatively calculated for the. Maximum Exposed Member.Qf the public. The results of those calculations and their comparison to the allowable timits were as follows:
- 1.
Liquid Dose to a Member of the Public for 2013 Total Body: 1.22E-08 mrem which is 4.07E-07% of the 3 mrem/year limit.
Organ: 1.22E-08 mrem Which 1.22E-07%'of the 10 mrem/year limit.
- 2.
Gaseous Dose to a Member of the Public for 2013' '..
Total Body: 2.19E.02 mrem which is 2. IE-01% of the 10 mrad/ye limit.
Skin: 5.35E-03 mrnrm which is'2.68E-02% of the 20 mradlyear limit Organ (Pti"uAImodn*.):-. 9.22E-02 mrem.1SE-Ot% of the 15'°.-
mrem/yesr limit.
- 3.
Direct Radiation Pose to a Member of the Public for '2013 Total Body: 8.76E+00 mrem which is 3.50E+01% of 40CFRI90 Limit of 25 mremlyear (Whole Body and Organ).
Thyroid dose: 2.30E-02 mrem which Is 3.07E-02% of 40CFRI90 Limit of 75 mrern/year limit.
The doses as a refaut of the radiological effluents released from the Dresden Generating Station were a very small percentage of the allowable limits, with the exception of 40CFRI90 whole body radiation which was calculated to be 35.0 %
of the 25 mrmnVyr limit. The largest component of 40CFRI90 dose is attributable to BWR skyshine from N-16. This value is co i
calulated for the hypothetical maximum exposed member of the public.
Surface water samples were analyzed for concentrations of gross beta, tritium and gamma emitting nuclides. Ground water samples were analyzed for concentrations of tritium and gamma emitting nuclides. No anthropogenic gamma emitting nuclides were detected. Gross beta and tritium activities detected were consistent with those detected in previous years.
Fish (commercially and recreationally important species), and sediment samples were analyzed for concentrations of gamma emitting nuclides. No fission or activation products were detected in fish. Cesium-137 was detected In one sediment sample at a concentration consistent with levels observed In previous years. No power station produced fission or activation products were found in sediment.
Air partitouate samples were analyzed for concontations of 96a bet and gamma:emitting nuclides. Qrosw bete resui at the 1rdiccatof tloctons wer.
consistent with those at the ontr location.
s ihon or, ctivi products were detected.
High sensitivity 1-131 analyses w perorrned on W-W.1ir d
sa.Mples. AM results were less than the minimum dite*table activity fo 1-41S'."
Cow mik samples were analyzed for concentrations of 1-131 and gam ma emitt nucides. Al 14131 results wm e
6eew the minimum ilibie activity.
Conentatinsof naturally oc~currng -40 were found. N iso ratvto Cdciý oz nNr fission:
or "vaton Products were found:'.
Food product samples were anhly;Wd for concentratlonsof gamma emitting nuclides. No fissionr acvation products wore detected.
Environmental gamma radiation mi.surements were petorh*
,,arterly using Optically Stimulated Luminescent Dosimetry (OLO). Beginning in 2012, Exelon changed the type of doesietry'used for the Radiological Ehvironmental Monitoring Program (REMP). Optically Stimulated Luminescent Dosimetry were deployed and Thermolumindsbant Dosimetry (TLD) were dotinued. This change may result in a step change In readings, up or down, deperding on sits characterstc.
The relatie comprisn to control locations rmnainvalid.
OWIL technology is dlfferint thintha uied in a TLW but has the same purpose (to measure direct radiation).
I I,
II.
Introduction The Dresden Nuclear Power Station (DNPS), consisting of one retired reactor and two operating boiling water ractors owned and operated by Exelon Corporation; is located Ia Grundy County, Illinois. Unit No. I want critia in 1960 and was retired in 1978. Unit No. 2 Yint critical on 18 Juie' 1970. UnitNo. 3 went criticalon 02 November 1971. The site is located in northern Illinois, approximately 12 miles southwest of Joliet, Illinois at the conluee of the Des Plaines ant Kankakee Rivers where they fom' thelllinois River. A This rep( covers those analyses performed by T 9dyne Brown nen (TWE) and Landauer on samples collected during the period 1 January 2013 through 31 December 2013.
An asessment of the station's rsdioedive effluent monitoring resut W
and radiation dose via the principle paways of exposure resuitingfrom plant emissions of radioactivity including the nmadmum noble gasgammn and beta air doses in the unrstricted area, an annual summary of meteorological condition including wind speed, wind direction and atmospheric stability and the resultof the 40CFRI9O uranium fuel cycle dose analysis for the.caledar year are published in-the station's Annual Radioactive Effluet Release Report.
A.
Objeotive of the Radiological Environment Monitonng Program REMP)
The objecMes of the REMP are to:
- 1.
Provide data on measurable levels of radiation and radioactive materials in the sit environs.
- 2.
Evaluat the relationship betmrn quantities of radioactive material released from the plant and resultant radiation.doses to individuals from principal psaths of exposure.
B.
ImPlementtion of the Objece.
The Implementn of the objectives is accomplished by:,
I.
Identifying significanetexposure pathways.
- 2.
Establishing baseline radiological data of media within those pathways..
3,
- Continuously monitoring those media before and during Station
.. :,-operation to assess Station radiologica effects (if any) on man and the environment...
Ill.
Program Description A.
Sample Collection Samples for the DNPS REMP were dollected for Exelon NuclearWb Environmental Incorporated Midwest Laboratory (EIML). This section describes the general collection methods used by EIML to obtain environmental samples for Vie DNPS REMP in 2013. Sample locations and descriptions can be found In Appendix B, Table B-1 and Figures B-1 and B-2. The collection methods used.bElML-re listed Ih8Table
-2.
Agogai Envir~onmen
,.qM' The aquatic environment was fvaluated by perforihigradiological analyses on samples of surface-water (SV), ground WAter (GW), fish (FI) and sediment (SS). Samples were colled from three surfooe water locations (D-21, 0-52 and D-57) and cothposited for analysis. Control locations were D-52 and D-57. Samples were collected quarterly or more frequently from two well wate locations (0-23 and D-35)" -AN samples were collected in new unusedsplastic bottles, which were rinsed with source water prior to collection. Fish samples comprising the flesh of channel catfish, largemouth bass; common carp and freshwater drum were collected smiu at two locaut, D-28 and 046 (Contol).
Sediment samples composed of recently deposie substreib were collected at one location semiannually, 0-27.
Atmonohg nvtfoMeMnt
°'::*
The atmospheric environment was evaluated by performing radiological analyses on samples of air particulate and airborne iodine (AP/AI).
Airborne iodine and particulate samples were colledm at fourteen locations (0-01, D-02, D-03, D-04, D-07, D408,,0-10, D-12; D-14, 0"45, D-63, D-55, D-56 and D-58). The control location was D-12. Airborne iodine and particulate samples were obtained at each location using a vacuum pump with charcoal and glass fiber filters attached. The pumps were run continuously and sampled air at the rate of approximately one cubic foot per minute. The air fltters and air iodine samples Were replaced weekly and sent to the laboratory for analysis.
Terrestrial Eimea t
Milk (M) samples were collected biweekly at one control location (0-25) from May through October and monthly from November through April.
There are no Milking animals within 10 km (6.2 miles) of the site. All samples were collected in new unused two gallon plastic bottles from the bulk tank at each location, preserved with sodium bisulfite and shipped promptly to the laboratory. Food products (FL) were collected annually in September at five locations (D.Control, D-Quad 1, D-Quad 2, D-Quad 3 and O-Quad 4). The control location was D-Control. Various types of samples were collected and placed In new unused plastic bags and sent to the laboratory for analysis.
AmIA Gama RlUggin
- ° Beginning In 2012, ExeW changed the type of dosimetry used for the Radological Environmental Monitoring Program (REMP). Optically Stimulated Luminescent Dosimetry (OSLD) were deployed and Thermoluminescent Dosimetry (TLD) were discontinued. This change may result in a step change in readings, up or down, depending on site charactefistics. The relative comparison to control locations remains valid. OSLO technology is different than that used in a TLD but has the same purpose (to measure direct radiation).
Each location consisted of two OSLO sets. The OSLD locations were placed on aind around the DNPS site as follows:
An inner doconsisting of 17 locations (D-58, 0-101, D-102, D-103, D-104, D-105, -106, 0-107, D-106, 0-109, D-110,0D-111, D-112a, D-113, D-114, 0-115 and D-118) atornearthesite boundary.
An gWK djg-oonsistin of 16 locationis (D-201,0D-202;,0-203,0D-204, D-205, D-20W, D-207, D-206,'0.209, 0-210, 0-211,0-212,0-213, D-214, 0-21 5 anid D-216) approkdmately 5 to.10 km (3.1 to 6.2,miles) from the site.
Qft consisting of OSLO sets at tOe 13 -air sampler locations (D-01, D-02, D003, D-04,0-07, D-08, 0-1, 0),14,0--45, D-53,.D-55, 0-56 and 0-58).
The balance of one location (D-12) represents the control area!OSLD set.
The OSLOs were exchangod quarerly and sent to Lnda.er for analysi.
B Sample Analysis This section describes the general analytical metwodologimused by TBE and EIML to analyze the environmental samples for radioactivity for the DNPS REMP in 2013. The analytical procedures used by-the laboratories are listed in Appendix B Table B-2, In order to achieve the stated objectives the current program includes the following analyses:
- 1.
Concentrations of beta emitters In surface water and air particldates.
- 2.
Concentrations of gamma emitters in ground and surface water, air particulates, milk fh, fsedlment and vegetation.
- 3.
Concentratonsof Mtium in ground and surfae water..
- 4.
Concentration*of t31 in air and milk.
- 5.
Ambient gamma radiation levls at vrious, fte environs.-
C.
Data Interpreta..o, For the purpose of this report, Dresden Nuclear Power Station was considered operational at initial criticality. In addition, data were cpared to prsvki yars' opational data for consistency and trnding:..Several factors were Impotant in the interpeto of the data:
The lower limit of detection (LLD) wm defined as the smallest concentration of radioactive material in a sample that would yield a net count (above backgound) that would be detected with only a 5% probability of falsely concluding that a blank observation represents a "rear' signal. The LLD was Intended as a before the fact estimate of a system (incklding instrumentation, procedure and sample type) and not as an after the fact criteria for the presence of activity. All analyses were designed to achieve the required DNPS detection capsbiti for environmental sample analysis.
The minimum detectable concentration (MDC) is calculated the same as the LLD with the exception that the measurement is an after the fac estimate of the presnce of activity.
- 2.
Net A*tv't Calculation and ReBoMrina of Results Net activity for a sample was calculated by subtractirg background activity from the sample activity. Since the REMP measures extremely small changes in radioactivity in the environment, background variations may result in sample activity being lower than the background activity effecting a negative number. An MDC was reported in all Cases where positive activity was not detected.
Gamma spectoscopy results for each type of sample were grouped as follows:
For groundwater, surface water, and vegetation twelve nuclides, Mn-54, Co-58, Fe-59, Co-60, Zn45, Nb-95, Zr.95, 1.131, C9-134, Cs-137, Ba-140 and La-140 won reported.
For fish, sediment, air particulate end milk elevern nuc~ides;,
Mn-54, Co-58, Fe-59, Co-60, Zn45, NW-95, Zr-95, Cs-134, CA-137, Ba-140 and La-140 were re Means and standard deviations of the result were" calculated. The standard deviations represent the varIabi of measured results for different samples rather than single analysis uncertainty.,
D.
Program Exceptions For 2013 the DNPS REMP had a sample recovery rate greater than 99%.
Sample anomalies and missed samples are isted in the tables below.
Table 0-1 ISINQ F M LE AMALIfE Samope AP/N I
AP/I ww SW SW AP/I AP/I Location Code 0-10 0-23 D021 0-57 0.01 0-02,0-03 03101/13 03108/13 04/12/13 04/26/13 04/28/13 06/24/13 05/24113 Reason AP filter founrI damaeged; three holes In filter paper.
No-apparent reason for kx reading of 166.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br />.
No sample; home**ier absent Compositor pump pit flooded.
Supply,ne ftom river to composor mising.
Low reading of 163.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br /> possibly due to power oulage from storms Low reading of 163.9 hours1.041667e-4 days <br />0.0025 hours <br />1.488095e-5 weeks <br />3.4245e-6 months <br /> possibly due to power outage from storms.
Table 0-1 Ail C I I IA;v Z 1X,7,Jqj *47-711IT-711 Sample Location Collection Reason Type Code 0te AP/I D004 05/24/13 Low reading of 160.5 hours5.787037e-5 days <br />0.00139 hours <br />8.267196e-6 weeks <br />1.9025e-6 months <br /> posily due to power outage from storms.
AP/I 0-07 05/24/13 Low reading of 164.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br /> possby duelo powr outage from storms.
AP/I 0-08, 0.10 05124113 Low reading of 164.7 hwospossibly due to power outage from storms.
AP/I 0-56 0524/13 2m Low reading of 162.9 hours1.041667e-4 days <br />0.0025 hours <br />1.488095e-5 weeks <br />3.4245e-6 months <br /> possby due to powr outage from storm.
AP/I 0-58 05/24/13 Low realng of 152.9 hours1.041667e-4 days <br />0.0025 hours <br />1.488095e-5 weeks <br />3.4245e-6 months <br /> possibly due to power outage from storm.
AP/I 0.03 06/21/13 Low reading of 94.2 hours2.314815e-5 days <br />5.555556e-4 hours <br />3.306878e-6 weeks <br />7.61e-7 months <br /> possibly due to pow outage from storm; stabon notiied.
APII DOm 06/21113 Low reading of 60.7 hours8.101852e-5 days <br />0.00194 hours <br />1.157407e-5 weeks <br />2.6635e-6 months <br /> due to pump nmaunction; electric connections diolore possil due to lightning. ColectorrepacWd AP/I 0-04 06/2O13 No apparentreasoni for low reading of 145.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br />.
AP/I 0-04 07/12/13 No apparent reason for low reading of 159.0 hours0 days <br />0 hours <br />0 weeks <br />0 months <br />.
AP/I D-08 11/15113 No apparent remmon for low reading of 163.5 hours5.787037e-5 days <br />0.00139 hours <br />8.267196e-6 weeks <br />1.9025e-6 months <br />.
AP/l 0-10 11/15/13 No apparent meson for low reading of 163.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br />.
.1* *I '
I Table 0-2 I q F-i tl:L, l'!t][01 j ý i ý*I 4 OIWý IITIW !
Sample APNl AP/I AP/I AP/l APII ANI AP/I OSIM OSLD AP/I APII AP/I Location Coflection Rga~on Code 003 0-03 0-03 0-03 D-216-2 D.03 D-202-1 D-03 D-03 D)03 D-03 D-03 06/28/13 - 07/0/13 fNOeectrc"ty.
07/12/13 No elctwc unable to perform pump field check.
07/19/13- 08/02/13 No electricty.
08/09113 No electricity; unable to perform pump field check.
06/16/13 - 08/30/13 No electricity.
09/06/13 No electricity; unable to perform pump field check.
09/13/13 No electricity.
09/13/13 OSLD missingfield; 'oollector placed spr 121653.
09/0/13- 09/27113 Noeleticty.
0O27113 OSLO missing In field during quwtferl exchae; co placed 101"413 Noeew iiy unWabl topeor L umfieldcek 10/11/13 -10125113 NO electrcity.
11/01113 No electricity; unable to perform pump field c 11/08/13-11/22/13 Nolectrlcy.
11/29/13 N o.,.
N iciy..4ne tol
,perform p*mp f chck,,
12/06/1 -2/2W/13 Npp efcticity.e.
12/27/13Noelsctriciy; unable to perform pump field check.
AP/l AP/t AP/l AP/l 0-03 D-03 Each program exception was reviewed to understand the causes of the program exception. Sampling and maintenance errors were reviewed with the personnel involved to prevent recurrence. Occasional equipment breakdowns and power outages were unavoidable.
The overall sample recovery rate indicates that the appropriate procedures and equipment are In place to asure reliable program implementation.
E.
Program Changes No program changes In 2013.
IV.
Results and Discussion A.
Aquatic Environment
- 1.
Surface Water o'w Samples were composited or taken weekly and cmposi*td for analysis at three locations (D-21, D-52 and D-57). Of these locations only 0-21, located downmstra, could be affected by Dresden's effluent rmlas. The win analyses w*ar performed:
Monthly composites from all locations were analyzed for concentonsof gross beta (Table 0-4.1, Appendix C). Gross Beta was detected in afllsamples. The values ranged from 3.2 to 26.2 p0CUA. -Concenbutions deMtcted were consistent with those detected In previous years (Figures C-I, C-2 end C-34 Appendix C).
TAUm Quarterly composite from all locations were analyzed for tritium activity (Tiabl.
-l.2, Appendix C). "Three samples at indicator tation D.21 were positie for tritium. The values ranged from 475 to 687 pCi/L. Four samples at control station D-57 were positive for tritium. The values ranged from 618 to 6550 pCilL. Concentrations detected were consistent with those detected in previous years (Figures C-4, C-5 and C-6, Appendix C).
4110-
w,
., I
, ML-K.*
J A,
Monthly composites from all locations were analyzed for gamma emitting nuclides (Table C-.3, Appendix C). No nucides were detected and all required LLDs were met.
- 2.
Ground Water Qua*ely or more frequent grab samples were collected at two locations (D-23 and 0-35). These locations could be affected by Dresden's effluent releases and by sources upstram on.the Kankakee River. The following analyses were pformed:
AD samples were nayzed for tritium activity (Table C-I.1, Appendix C). Tritium was detected in twelve of sixteen samples.
The concentraton ranged from 218 to 414 pCil. Concentrations detected were Consistent with those detected in previous years (Figure C-7, Appendix C).
Gamma SRSUctm*
Al samples were analyzed for gama emtng nuclides (Table C-41.2, Appendix C). No nuclides were detcted and ar mqired LLDS were met.
- 3.
Fish Fish samls comprised of channel ctish, largemo
- bass, common carp and fewa drum were collected at,two locations (0-28 and D.46) semiannually. Location 0-28 could be affected by Dresden's effluent release. The following analysis was perokmed:
The edible portion of fish samples from both locations was analyzed for gamma emitting nudildes (Table C-411.1, Appendix C).
Naturally occurring K-40 was found at both. otion.ý,No fissio or activation products were detected.
- 4.
Sediment Aquatic sediment samples were collected at one location (D-27) semiannually. This downstream location Could be affected by Dresden's effluent releases. The following analysis was performed:
Sediment samples from the location were analyzed for gamma emitting nuclides (Table C-lV.1, Appendix C). Cesium-137 was detected In one sample at a RconIenratMon of`l87 pCkg dry The activity detected was consistnt withkthose detected. in previous years and is Nikely due-to fallout from aboveground nuclar,
weapons testi.. No other ion oractivation products were, detected.
B.
Atmospheric Environment I.
Arbome
- a.
Air Particulates Continuous air particulate samples were colaecod from fou
-elocations on a wely basis. The fouteen locations wete spat Ito four grups: O-t.sbsamplers (D601, D.
02 and D-03), Near-eld 6a lrs witMh 3.1 miles of the sie (D-04, DO7, D"45; 0-53, D-66 and 0-58), Far.4ield samplers between 5 and 10 km (3.1 and 6.2 miles) from the site (D-08, 0-10, D-14 and 0-55) and the Control sampler between 10 and 30 km (6.2 and 18.8 miles) from the site (0-12). The followhn analyses were perfiormd:
Weekly samples were analyzed for concentra',ios of beta emtes (Tabe C-V.1 and C-V.2, Appendix C)..
Detectable gross beta activity was observed at all locations.
Comparison of results among the four groups aid in determining the effects, If any, resulting from the operation of DNPS. The results from the On-Site locations ranted from 7 to 57 E-3 pCi/m3 with a mean of 20 E-3 pCi/mi.
The results from theNear-Field locations ranrd from 5 to 54 E-3 pCi/m3 with a mean of 20 E-3 pCi/m. The results from the Far-Field locations ranged from 8 to 63 E-3 pCI/m 3 with a mean of 21 E-3 pCi/M3. The resufts from the Control location ranged from 5 to 52 E-3 pCi/m 3 with a mean of 21 E-3 pCi/m3. Comparison of the 2013 air particulate data with previous years data indicate no effects from the operation of DNPS. In addition a comparison of the weely, mean values for 2013 indicate no notable differences among the four groups (Figures C-8 through C-14, Appendix C).
Ga1mmagwoefotbl Samples were comp**W quartry and analyzed for gamma emitting nuclides (Table C-V.3, Appendix C).
Naturally occurring We-7 due to cosmic.ray activity was detected in 53 of @4 samples and ranged from 37..5 to. 110 E-3 pCi/M3. Naturally occurring K-4-0 was detected in one of 54 samples at a concentration of 24.7 E-3 pCi/rn3. No anthropogenic nuclides were detected and all required LLDs were met. These samples were consistent with historical quarterly results. Al other nudides were less than the MDC.
- b.
Airborne Iodine Continuous air samples ware collected from fowteen locations (D-01, 0-02, 0-03, 0.04, D-07, D-08, 0-10, D-12,
.- 14, D-45, 0-53, 0-55, D-568 and -68)and analyzed
-. weekly for 1-131 (Table C-VI.1, ppendix C). All results e
wmlesa than the MDC forl1-131,.-.
- 2.
Terresial.I
- a.
Milk There are no Indicator locations within 10 kilometers of the station. Samples were collected from one control location (0-25) biweekly May through October and monthly November through April.,The following analyses were performed:
Milk samples from the location were analyzed for concentrations of 1-131 (Table C--VLI., Appendix C). No 1-131 was detected and all required LIDs were met.
Each milk sample was analyzed for concentrations of gamma emitting nuclides (Table C-V1I.2, Appendix C).
Naturally occurring K-40?0ctivity was found in all samples.
No other nuclides were deftote1 and a09 required LLDs were
,met.
L-
- b.
Food Products.
Food product samples were collected at five locations (D-Contol, 1-Quad 1, 0-Quad 2, D-Qua4d3 and D-Quad 4) wihen available. Four locations, (O.Quad 1, -Quid 2',.....
0-Quad 3 and D-Quad 4) could be affected by Dresden's effluent releases. The following analysis was performed:
Samples from aN locaions were analyzed for gamma emitting nuclidi (Table C-MIl.I, Appendix C). No nuclides were detected and all required LLDs were met.
C.
Ambient Gamma Radiatio Beginning in 2012, Exolon changed the type of dosimetry used for the Radiological Enviro1m Monitoring Program (REMP). Optically Stimulated Luminescent Dositmey (OSLD) were deployed and Thermolunnewent Doswimy (TLD) were discontinued. This change may result in a stop change in readings, up or down, depending on site characteistics. The relative companson to control locations remains valid. OSLD technology is different than that used In a TLD but has the same purpose (to measure direct radiation). Forty-six OSLD locations wer established around the site. Results of OSLO measurements are listed in Tables C-IX.I to C-IX.3, Appendix C.
MostOSLD meauement wre below 30 mR/quarter, with a range of 22.6 to 38.7 mRlquarter. A comparison of the Inner Ring, Outer Ring and Other locations' data to the Control Location data, Indicate that the ambient gamma radiation levels from the Control location (D-1 2-01and D-12-02) were comparable.
D.
Land Use Survey A Land Use Survey conducted on August 28, 2013 around the Dresden Nuclear Power Station (DNPS) was performed by EIML for Exelon Nuclear to comply with Section 12.6.2 of the Dresden Offiste Dose Calculation Manuat (ODCM). The purpose of the survey was to document the nearest resident or industrial facility, milk producing an"in
, and livestock in each of the sixteen 22 % degree sectors within 10 km (6.2 miles) around the site. There were no changes required At the DNPS REMP as a result of this survey. The results
,thi survey are summarized below.
D ein Mi from
."e"DNPS Reactor BUM=ld.
Sector Residence.
Livestock" Mk Farm Mf
.. MR" Mies A N 1 S. -..
- 1.
BNNE C NE DENE EE F ESE G SE HSSE KSSW LSW MWSW N W PWNW QNW RNNW 0.8 0.7 1.1*
1.0 0.6 0.5 0.5 3.3 3.6 5.8 3.5 3.7 2.6 0.8 60.
1.7 I&0 i...
a1
.3 0.5 E.
Errate Data Teledyne Brown Engineering (TBE) provides data results [activity, uncertainty and minimum detectable concentr a i (MDC}]. We are required to calculate the MDC.using a ipllerof4.68.
4.66'"
MDA =
A 2.22 (v)(y) (a)(e)
Where:
. 3
- ,..m At = counting time for sample (minutes)
I = background rate of instrument blank (cpm) 2.22 = dpm/pCi or: 2.22 x 10 dpm/pCi v = volume or mass of sample analyzed y = chemical yield
£= efficiency of the counter The formulas for calculating the acti*ty, ufcertaintyand C
contained in the software of the counting equipment. For the gamma system, when the new detector number 08 was added to the system in January 2012, the default value of 3.29 was uLWtoca.ltculated the'MDCs on detector 08. The activity! and unceftnty were not 'affected. The multiplier has been Chg from 3.29 the required 4.66.
When the MDCs are recalculated using 4.66,. the MDC values will Increase by 41.6%. The greatest impact will be on the short-,ived nuclides which have an LLD requirement, e.g. 1-131, Ba-140 and La-140. Which means there could be some missed LLDs which will be Identified in the Errata Data Appendix table of the 2013 annual report. This is not a reportable Issue for the NRC. There is also the possibility that naturally produced nuclides that wre detectod would become a n4 c, e.g, Th-228, Th-230, etc.
F.
Summary of Results - IntMr'bordary. Campafson Program The primary laboratory analyzed Evaluation (PE) samples of air padrule, O'r iodine, milk,sodil, vegetaon and watWe matrices (Appendix 0). The PE sampl,,supplie b Analytics Inc., Envirnmental Resource Associ (ERA) and DOE's d An*lyt Pef Evaluation Program (MAPEP), were evaluated igainst the followi pre.
set acceptance critea:
- 1.
Analytics Evaluation Crit.
Analy' evaluation-rea provides a ratio of lborory results and AnalyW' known value. Sinos flag values are not assigned by Analytics, TBE-ES evaluates the reported ratios based on Intemral OC requirements, which are based on the DOE MAPEP criteria.
- 2.
ERA, Evaluation Criteria ERA's evaluation report provides an acceptance range for cntrol and wa*!rng lims with issocieW flag values. ERA's abceptance limits are established per the USEPA, NELAC, state specific PT
-.16-
program requirements or ERA's SOP for the Generation of PeormAnce Acptance Limits, as applicable. The acceptance limits are either determined by a regression equation specific to each analyte or-a fixed percentage limit promulgated under the appropriate r~gator document.
- 3.
DOE Evaluation Cr1tea48 MAPEP's evalu*a*inreport provides an,
.ceptane,ranewth associated fn values.
The MAPEP defines three levels,Of performaonce; Apaeptabe (Nag = "A'), Acceptable with Warn (flag.=
) and NWt Acceptable (flag = 14-). Performance is considered acceptable when a mean result for the specified arialyte is
- 20% offte reference value. Perfo n Is ccetaewithwaming when a; mean rest* falls In the range from.20% (o`0%
0f the reference value (ie.,-20% < bias < 30%). If the bras is. grater than 30%, the For the TOE laboratory, 178 out of 185 analyses performed met the specified acceptance criteria. Seven analyses (Sr-89 and Sr-90 in milk, Co-S?, Zh-85 ohd:S90 in soil, Cs-1 34 in air particulate and Sr-90 in vegtat~n two ta*warning in a rowJ) did not meet the spSedW accptacecriteria, or Infternal Q eurmnsfor the fOoll"M reason:
- 1.
Troyne Brown En's Analytics Sepmber 2013 Sr-89 in milk rsu of 63.9 pCi/L was lower than the knwmn vakuof 96.0 pCU/L. The failure was a result of analyst error and was specific to the Analytics sample. Client samples for the associated time period ware evaluated and no client samples ware affected by this failure. NCR 13-15
- 2.
Teledyne Brown Engineerng's Analytics September 2013 Sr-S0 in milk result of 8.88 pCi/L was lower than the known value of 13.2 pCi/L. The failure was a result of analyst error and was specific to the Analytic sample. Client samples for the associated time period were evaluated and no client samples were affected by this failure. NCR 13-15
- 3. & 4. Teledyne Brown Engineering's MAPEP September 2013 Co-57 and Zn.O5 in soil were evaluated as falling the false positive test.
While MAPEP evaluated the results as failures, the gamma software listed the results as non identified nuclides. The two nuclides would never have been reported as detected nuclides to a client. MAPEP does not allow laboratories to put in qualifiers for the submitted data nor "less than" results. MAPEP evaluates results based on the relationship between the activity and the uncertainty. MAPEP spiked the soil sample with an extremely large concentration of Eu-152, which was identified by the gamma software as an Interfering nuclide, resulting in fgrr.
activity results that were evaluated by MAPEP as detected Co-57 and Zn-65. No client samples were affected by these failures. NCR 13.14
- 5.
Teledyne Brown Engineering's MAPEP September 2013 Sr-90 In soil result ofe64 Sq/kg was higher than the known value of 460 Sq/kg, exceeding the upper control limit of 598 Sq/kg. An inconrect Sr-90 result was entered Into the MAPEP database. The correct Sr-90 activity of 322 Bq/kg would have been evaluated as acceptable with warning. No client samples were affected by this failure. NCR 13-14
- 6.
Teledyne Brown Engineering's MAPEP September 2013 Cs-134 in air particulate activity of -0.570 Sq/sample was evaluated as a failed false positive tet, based on MAPEP's evaluation of the result as a significant negative value at 3 standard deviations. A negative number would never have been reported as a detected nuclide to a client, therefore no client samples were affected by this failure.
NCR 13-14
- 7.
Teledyne Brown *flgel',
MAPEP September 2013 Sr-90 In vegetation result was dvt lue to two low warnings In a row. It appears the September sample was double spiked with carrier, resulting in a low activity. With a recovery of around 50%
lower, the Sr-90 result would have fallen within the acceptance range. No client samples ware affected by this issue. NCR 13-14 APPENDIX A RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT
SUMMARY
Ila ll blank
TABLE A-I RADIOLOGICAL ENVIRONMFNTAL MONITOING PROGRAM ANNUAL
SUMMARY
FOR-DRESDEN NUCLEAR POWER STATION, 213 NAME OF FACUATY:. DRESDEN DOCKETNUM3ER:
9010 3237*5044 LOCATION OF FACILfTY:
ORRIS EL RE6TU4G PERIOD.
ANNUAL 201, IICATOR CONTSM W0CAT11N Wire HG=f ANNUAL MEAN (M)
LAWAMNS LOCATiON MEDIUM OR TYPES OF NUMBIER OF REQUIRED MEANM()
MEAN(
MEAN(M)
STATION #
NUMSER O
PATHWAY SAMPLED ANALYSIS ANALYSIS LOWERLIM (F)
(F)
(F)
NAME NONROUTINE (UNITOF PERFORMED PERFORMED OF DETOCtON RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
M.ESUIR M ETS SURFACE WATER
(,CvL'Lr)
OR4B H-3 36 12 36 GAMMA M144%
C"o 4
8.3 (12/12)
(S.bfl4) 200 60 (314)
(47516n7 Is 411) is
<LLD 30
<LLD Is 4"I 30
.LD is
<LLD 8.5 (23124)
(3.2n6.2) 2567 (4/8)
(618/6350) 3.6 (12112)
(42n.12O) 2567 (4/4)
(611aw")
D-)2 CONTROL DESPLAINES RIVER-UPSTREAM 1.1 MLES ESE OF SITE D-51 CONTROL KANKAKEE RIVER AT WILL ROAD 2.0 MILES SE OF SITE 410D
- 410,
'liD
<LLD
<LLD
<LLD 0
0 0
0 0
0 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOWltGCAL ENVIRONMENTAL MONITORING PIROGRAM ANNUAL
SUMMARY
FOR DRESDEN NUCLEAR POWER STATION, 2613 NAME OF FACELl.: DRESDEN DOCKET NUMBER:
51s9~
S607 &. 249 LOCATION OF FAC'lJTY: MORRlS IL REPORTING FERIOD:.
ANNUAL 2013 B401CATOM CONTROL LOCATION WTIH IGUF ANNUAL MEAN (W)
IOCAtiONS LOCATlON MEDIUM OR TYPES OF NUMBEROF REQUIRED MEAN (M)
MEAN (P)
MEAN(M)
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSIS ANALYSIS LOWER UMlr (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREN (LLD)
MEASUREME SURFACE WATER ZRJ-30
.4m
-Lm 0
(pCl/UTER) 1-131 h
CS-134 CS-137 BA-140 LA-140 Is
<LLD 15
<li.D Is
,LD IS 4"L
<LLD 0
0 0
0 0
0
<LAD GROUND WATER (PCIYITER)
H-3 16 16 2000 312 (12t16)
(218/414)
NA 312 (12/12)
(212/414)
D.23 INDICATOR THORSEN WELL 07 MILES S OF SITE GAMMA MN-.4 15
<LLD NA 0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PAREN17HESES (F)
TABLE A-I RADIOLOGICAL ENVRNMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRESN NUCLEAR IPOWER STATIN 2013 NAME OF WACIIJTY: DRESDEN DOCIWT NtUMDER:
410 90037 & WS24 LOCATION OF FACILITY: MORRE IL EmarIo NG rWxm ANNUAL2W INVIATeS COF4ThOL WCATION UG=ES ANNUAL MEAN (M)
IOAWAIMMS LOCATIO MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN (M)
MEN()
MEAN ()
STATION 0 NUMBER OF PATh1WAY SAMPLED ANALYSIS ANALYSIS LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETBETION RANGE RANGE RANGE DITANCE AN DI]RECTION REPORTED MEASUREMENT)
D)EASUREMENTS GROUNDWATER CO-8 Is 41lD NA 0
OPCVUTER)
NOMS 7R.95 14131 CS-134 30
<LLD Is 4L.D 30 4LL 15 41D 30 4wD 15 4mD 15 4.LD NA NA NA NA NA NA NA 0
0 0
0 0
0 0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMESIr AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRESDEN NUCLEAR POWER STATION, 2013 NAME OF FACUTYM: DRESN 9C T NUMBER:
s001 W237 & 524 OCATION OF FACILTV: momi IL REPOfTING MURIOD ANNUAL 213 RCAWTM CONUO LOCATIWN WIN UW ANNUAL MUMAN M)
LOICATIONSM LOCAnOM MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN(M)
MEAN(M)
MEAN (")
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSIS ANALYSIS LOWERLINrT (F)
(F)
(F)
NAME NONROU7TINE (UNM OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
OJD)
MEASUREMENS GROUNDWATER.
CS-137 Is 4
NA 0
(PCI/LITER)
BA-140 LA-140 GAMMA MN-54 FISH (PCI/KG WE')
8 60 41D Is
<LLD 130
<uD 130 4m 260 4m 130
<LLD 260 4m NA NA 0
0
<LLD CO451 F&-59 4m 41D 4111 0
0 0
0 0
ZN-4S 0 THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRESDEN NUCLEAR POWER STATION, 2613 NAME OF FACILITY: DRESD)EN DOCKET NUMDER in.4)7 m
£ 249 LOCATION OF FACILITY: MORRIS IL FJOKnING WRNOD ANNUAL I131 INH01CATOI ONTRiOL LOCATION TM nflGiMST ANNUAL MEAN (M)
LOCATIONS CATION MEDIUM OR TYPES OF NUMBER OF REQUIRED MEAN (I)
MEAN (M)
MEAN(M)
STATION#
NUMBER OF PATHWAY SAMPLED ANALYSIS ANALYSIS LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(LLD)
MEASUREMENTS FISH NB-g5 NA
<LLD
<LUW 0
(PCIJKG WET)
ZR-95 CS-134 BA-140 LA-140 GAMMA MN-4 NA 41D 130 4
<LID NA 4<D NA
<4L NA
<4W NA
<4ID
<LLD
<LLD
<LLD
<LLD 4JLD 0
0 0
0 0
SEDIMENT (PCVKG DRY) 2 NA NA 0
0 CO-58
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRMESDN NUCLEAR rowER STATION, 2313 NAMIE OF FACILITY: DRESDEN DOCKET NU'L-
"s "S237&w249 LOCATION OF FACILH
- MORR IL fEIOlTING PfE310 ANNUAL 2N3 IP4ICATOS C01UM.
LCATMIWN M GWST ANNUAL MEAN (N)
WC*ATUON LOCATION MEDIUN OR TYPES OF NUMBEROF REQURD MEAN (M)
MEAN(M)
MEAN (T)
STATION #
NUMBERF o
PATHWAY SAMNL ANALYSIS ANALYSIS LOWER Lgwf*
(F)
(F)
(F)
NAME NONROUTINE (UNOF PERFORMED PERFORME OF DETECTION RANGE RANGE RANGE DISTANCE AND DIREC*ION REPORTED MEASUREMEPM (LLD)
NMASURE11 SEDIMENT FE-39 NA 4<lb NA0 (PC[JKG DRY) 6%
ZN40 N845 7R.95 CS-liED CS-137 BA-140 LA-140O NA
<LLD NA
<LL NA 4W NA
<*LLD ISO
-am IN IS?
NA
<LWD NA NA NA NA NA NA NA NA 0
0 0
0 0
0 0
0 167 (1/2)
D-27 INDICATOR DRESDEN LOCK AND DAM - DOWNSTREAM OLS MIlU NW OF SITE
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARENTESES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRESDEN NUCLEAR POWER STATION, 2313 NAME OF FACIIJTT: DRESDEN IDOCET NUMBEL 5"9 56237 & W-249 LOCATION OF FACDTfr: MORRIS IL RKWORTING PERIOD:
ANNUAL 253 INW40ATC CONTR LOCATmm wnu HNIWG T ANNUAL MEAN (0)
-OAIN LOCATION MEDIUMOR TYPES OF NUMMROF REQUIRED MEAN (N)
MEAN(N)
MEANM()
STATION #
NUMBER OF PAThWAY SAMPLED ANALYSIS ANALYSIS LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORMED PERFORMED OF DETECION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT (LLD)
MEASUREMENTS AIR PART.CULATE GR.
714 tO 20 21 21 D0 c
IN.I.ATOR 0
(E-3 PCI/CU.METER)
(E660661)
(m/7 (03/53)
(5632)
<LL (53/53)
(7/32)
PRAIRIE PARK 3.8 MILES SW OF SITE GAMMA MN-54 54
",.4 co-"s FE-"
CO-6 ZN45 N854 2R45S NA
<LLD NA 1D, NA
<LLD NA dIJD NA
<LLD NA
<LD NA
<LLD
<LD 4<1.
0 0
0 0
0 0
0 4*W
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECWIIED LOCATIONS IS INDICATED IN PARENTHESES (F)
TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL SUMMARV FOR DIRESDEN NUCLEAR POWER STATION, U13 NAME OFIFACILIT: DRESDEN DOCiCE NUMBERI 56410 so.1
& SW249 LOCATION OF FACILITY: MORNS IL KPORT*iG VERIODM ANNUAL213 U4I1CATOlR CONIW)L LOCATION WnU HGIGUET ANNUAL MEAN (N) lWCATONS LOCATION MEDIUM OR TYPES OF NUMBEROF REQUIRED MEAN (M)
MEAN (M)
MEAN(M)
STATION#
NUMEOF PATHWAY SAMPLED ANALYSIS ANALYSIS LOWER LIMIT (F)
(F)
(F)
NAME NONROUTINE (NITrOF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEASUREMENT)
(um)
MEASUREBMEJTS AIR PARTICULATE........
CS-134 so
<LLD
<IJLD 0
(E-3 PCI/CU.METER)
'S CS,-137 BA-140 LA-140 GAMMA 1-131 NA
<LL NA
<LLD 4Wm 4,LD
<LL 0
0 0
AIR IODINE (E-3 PCLICU.METER) 714 max (PCI4JTER) 1-131 20 20 70
<WLD I
NA NA NA NA NA
<LLD 0
0 GAMMA
.4m 0
0 CO-so
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMEITS AT SPECI LOCATIONS IS INDICATED IN PARENThESES (F)
TABLE A-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL SUMMARV FOR DRESDEN NUCLEAR POWER STATION, 2010 NAME OF FACILMIT: DRESDEN SOCKET NUMBER-341 9136m &.149 LOCATON OF FACILITY: MORRIS IL REPOrU4NG MAIM ANNUALM UN4ICATOR COMM LOCAWJ*MIOW WIG WT ANNAL MEAN*R) 1A)CATMS LOCATON MEDIUM OR TYPESOF NUNM OF REQUIRED MEAN (M)
MEAN(M)
MEAN (M)
STATION #
NUMBER OF PATHWAY SAMPLED ANALYSIS ANALYSIS LOWER IAMIT (F)
(F)
(F)
NAME NONROUTINE (UNITOF PERFORMED PERFORED OF DErB~CfON RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED IEASU)EMEN (LD)
MILK
~
FE-59 NA NA
<lD0 (PCIiTER)
CO.60
'0 Zlt4" CS-134 NA NA NA NA NA NA NA NA Is NA Is NA 60 NA Is NA
<LLD
<LLD 4"I 4"A 4mA 4"
<LLD 4"I 0
0 0
0 0
0 0
0 BA-140 LA-140
' THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DIlECTABLE NIEASUREME*I*S AT SPECIFIED LOCATIOIS IS INDICATED IN PARENTHESES (F)
TABLE A-i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRESDEN NUCLEAR ]OWER STATION, 2113 NAME 0OF FACILIT: DRESDEN EX3CIET NUIIER.:
9"-10 586W & 50-249 LOCATION OF FACMLT: MORIMS IL REROR*iNG FERODk ANNUAL *23 INICATOR CONT1OL LWCATIN WnHI T ANNUAL LMEAN K)
LOICATIOM5 KOAWATI MEDIUM OR TYPESOF NUMBER OF REQUIRED MEAN (M)
MEAN (M)
MEAN (M)
STATION #
NUMBEROF PATHWAY SAMPLED ANALYSIS ANALYSIS LOWER LIMIT (F)
(F)
NAME NONROUTINE (UNITOF PERFORMED PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AN DIRECTION REPORTED MEASURT[IO (LLD)
MEASUREMENTS VEGETATION GAMMA 10 (PCViKG WET)
MN-54 0
NB-"
7R45" 1-131 NA
<Lw NA
<4D NA
<4LD NA
<LLD NA
<LLD NA
<111 NA
<LLD 60
<LLD
<LLD
<LLD
<LLD
<am 4m 0
0 0
0 0
0 0
0
- THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PARmNTHSES (F)
TABLE A-I RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ANNUAL
SUMMARY
FOR DRESDEN NUCLEAR POWER STATION, 2013 NAME OF FACILITY: DRESDEN DOCKET NJMDER 50416 S.237 & 5024 LOCATION OF FACILITY: MORRIS IL REFORTiNG 3EROD.
ANNUAL2013 INDICATOR CONIVOL LOCATION WnI KIGWST APNNAL MEAN (1)
LOCATUMN IOICATION MEDIUM OR TYPES OF NUMMEOF REQUIRED MEAN (M)
MEAN (M)
MEAN (M)
STATION #
NUMBER O PAThWAY SAMPLED ANALYSIS ANALYSIS LOWER LIMrT (F)
(F)
(F)
NAME NONROUTINE (UNIT OF PERFORNM PERFORMED OF DETECTION RANGE RANGE RANGE DISTANCE AND DIRECTION REPORTED MEA S)
(LLD)
MEASUREN S
VEGETATION CS-134 60
'"Am
<W 0
(PCI/KG WET)
CS-137 s0 4m NA
.4m NA
<LLD NA 302 (357/357)
(22 A1&7) 4LD 4Wa 0
0 0
0 LA-14 DIRECT RADIATION (MUI-ROENTGENam)
OSLD.QUARTERLY 365 29.1 (m/)
(24.6033.1) 35.5 (4/4)
(32.1/3&1)
D-1 10.4 INDICATOR 0.9 MILES SSW 0 THE MEAN AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES FRACTION OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS S INDICATED IN PARENTIESES (F)
A 4
..1~
.4,.
- 1 A -~
- t~
S.9
.~
3 *~t
- ~1' Intsntionafly Iefl aInl
A.- wig DB LOCATION OESIGNATION, DISTANCE & DIRECTION, AND SAMPLE COLLECTION & ANALYTICAL METHODS
We. donifysft %tbwan
TABLE B-I:
RaMdoo* Envtrmental Iding Proaran -Samwpng Loca DtmnOe and Diection.
Dresden Nucler Power Staon. 2013 Locaion Locaion Destiptn DsFo eDcm a
on From Sita 0-21 l Rver 9 EJ&E Brlp (ndicor) 0-52 OesPlnee Rir at We Road. Upsam (con=tr) 0.57 lwnkdee River at Wi Road (contrl)
B G
- idAl WaS.,
0-23 ThoMrn WaO. Dreen Road In*dicar) 05ODresdmn Lok and Oam (dicator)
C.
An - wlolw I Mmo 0.25 Fins Pam (0on0l) a-ml almauiAtea ig"odn 0-0t D)-02 0-03 043 0-07 046 0-10 0-12 D-14 0-45 D-63 D455 D-4 D-48 Onsmt shwton I (Indcator Onsits StatOw 2 (fndcat"f Onslie Stawo 3 (IndWator CoMb~sRoad, on Stion propety(lnicio Clay ProducWs nDm Flon Road (Vftoor)
-u~
Roed Prairie Forks "Idcao" Goose Lake Road, Gooes Lawi Vileg (Indcaor)
-um ROaK Usb (con"s)
Cantf Sftma GhWWn (WKVC0f)
Mcfinle Mods Road, ChennW=o "and"~r VON Rosdý Hjowck (Inift o)
Ridge Roa Unocke (ndicator)
WN Rood, WNdleMhe (INdOcAto)
WIN Rood, Mwa (Inictsor)
Oresdon PWool 1 minnai Rivr Omubuwn (Indicao)
Duomine Rihv, Upow (cdom" 1.4 mOle WNW 1.1 mils ESE 2,0 miles SE 07? miss S 0.7 ndesSW 0.8miNHW 0.8 nm NW 0.3 miles UNE 0.4 MeS S 0.68meW 3.6 mfes sW 3.5 mes $SW 10.5 miles NW 3.7 mils NE t.7 al ENE 2.1 mikeaSSE 4.3 mIes N 1.TmflsSE 1.1 mine ESE 0.9 mnes NNW 1.2 miles ESE 0.8 miles NW 2.6 mnes NE 3.2 m*sl SSE 3.9 mnes SSW 1.0 moe NNW 12.8 mies ENE D04 0-27
'InM R"ver at ODreden Lack ad DaOn. DowmsMrm 0 A cNN r)
Quadrat I Quadrat 2 Qudmnt 3 Qu01lr10 4 Contrd Cats Loolmer Robrt Paglan Jim Bloorn J.D. Camlolim GlmOOCk Fan B-i
TABLE 8-1:
Radlolo0k3 Envlonmmnwt Mo*tl* Program - Sampling Lcions, Distance and Dhftmo Dresden Nuclew Powe Station, 2013 Location Locaftin Descipion Distence & Direction From Sfte H.
Enwroamental Doedmayr -OSLD 4-8-1 and.2 0-101-1 and -2 0-102.1 and -2 0-103-1 aid -2 D-104-1 and -2 D-1051 and -2 0-106-1 and -2 D-107-1 and -2 D-106-I and -2 0-109-1 Nd -2 0-110-3 and -4 D-111-1 and -2 D-112A-1 mnd -2 D-113-1 mad -2 D-1 gland -2 0-115-1 amnd -2 D-1t6-1 and -2 0-201-1 and -2 0-202-1 and -2 D.203-1 and -2 0-204-and.2 0-205&1 and -2 D-206-1 and -2 0-207-1 and -2 0-20t aind -2 0.2091 Ond -2 0-210-1 and-2 0-211-1 and.2 D-212-3 ewd -4 0-213-1 0n0d-2 0.214-1 end -2 0-216-1 and -2 0-216-1 eid -2 OfeLiocallon, 0-01-1 and-2 D.02-1 and-2 D.03-1 and-2 0404-1 rid -2 0-07-1 mnd -2 0.-1 and -2 0-10-1 and -2 0-14-1 and -2 D.45.1 and.2 0D63-1 and.2 O-W6l and -2 0-56-1 mnd -2 0.61-and -2 1.1 mili ESE 1.0 mils N 1.3 m NesNE 1.2 mles NE 1.7 Mnes ENE I.5 miln E 1.1 miMes ESE 1.4 mile SE 1.9 miles SSE 0.8 miles $
0.9 mils SSW 0.64 Mkes SW 0.7 mbleWSW 0.9 miles W 0.9 mIre vWNw 0.8 miles NW 1.0inoes NNW 4.8mMiles N 5.1 MOues NNE 4.7 mil*e NE 6.0 mes EWE 4.0 miles E 35 mie ESE 4.2 mile SE 4.9 mie SSE 4.1 miles S 4.9 miles 88W 4.8 mles SW
.0 miles WSW
- 4. mil* W 5.0 miles WWW 4.8 mlest W 4.9 mRs NNW 0.8 miles NW 0.3 mils NNE 0.4 miles 0.8 miles W 2.6 MIN S 3.6 miles SW 3.7 miles NE 1.7 miles ENE 2.1 miles SSE 4.3 mles N 1.7 miles SE 1.1 miles ESE 10.5 miles NW Onabo2 Onalte3 Comin Roadaon Staon e
Clay Prod Dresden Rood Road PRaiNN PWkS Goose Lae ROW, Goore LAI Via CeOr Stret Chwnnto Mdane Woods Road. Chgmhn Wi Rout Hdo*
Ridge Road. Unoodw Wi Road. Wlldfhmer WiU Rood, MaInM D-12-1and -2 Lisbon 8-2
TABLE B-2:
Radioogcal Environmental tmntong Program - Summu l Sample Collecton al MWal lMM0I06s, Dresden Nde Powe S
, 2013 sample Anatl Sunt vMshd Ced.on Prcedure Nu e
Sample Sime Anao" Procdr Number Mlodkim Surface Water Gammadn Spechuecapy Moneftl Nopo EIML-SM-1 Envkhm fte bncorpved 2 90ma IM1, TUE-207 Goaina emye"n ample or monly
- MIk, at.crsly Lambors rooenpN rasic e anwwyui
'FF-m from sof fMaw Wo sapems.
19!. TBE-2023 Conuopo'g of eanonm EM.-COMP.01 proceure JW c o
______~~vA ualwd mmol sonples surface WaSe Gross BeamM.
coroslet EIML-SPM-i. EnvkmuimW IPncopormted 2 gallon TUE. T31-2000 Gross A~ft =Mdlo 6e orrmonuly Mdoshw Lsomry Sanpin Procedure.s pos t
u aMcly invadous ml compoele frm *,,j Manu TN. 1w2m0 CorrpWa of sample IIML.COFAP4I procedure for iopudn Surface Water TdMMu Ournteld peiteo EIML-SPM-1, Enviromnolo mweadle 800W TUBE-2011 Tumi analysis in 1muvttly P. A pMONOt MIfif Lolorst SWampin Proceicres Obwdg vealr by UWM WdttOWn TV1,1TK-2023 ComfpoW% nof samples EML.-COMIMO prcmi for os welr a mmm e
GrouuM Wae Gam Spectmmc Qum-te,,*
sanpes.
EML-4.Sf., Efmnetm l imorporaed 2 geon TOE 11-20O Ganrmn ei" Mol Lam -
V Proceiues u
De mulyis Ground Wale TOMa Queleygrobserrles.
EN&-SPM-, Er~mmiWnha Inorpmad 500 md TV, 1BE-2011 Tiban andysis in MIdfut"Lsoalawy $anuormProcedures uhdirir YuAorboy "ud schirblion Fish Gammam Specuoeacp SmnlsOcUeietdc ENVL4PM1., EurwitmeuM kopore 1000pmi (wo TUE. 1M.2007Gomm wM"tn ovm*d via Mkrnea Lsorala SwMnpb Procaieduresata anahlysi
@lcotidigor Oiliver Momus Sedirment Gammao Spectroecopy SoeWoinua Erb WML-PM-I, Envkwouentt hico pora
-Id 500 gram. (dry)
TBE. T9E-2007 Gam ams
-eOtW Leabortor Somir Proedre "dwac e anlyi Mmmiu
TABLE 8-2:
Radiologlc Envokmmw Molor"ig Proam - Summrmy of Swrple Csollonim and Aalyti ds, Dreosdn iclow Pow Stan, 2013
~-Pn Bo"-V 4 : 1
,.04#
i to
- p.
~
rk~
I b~
-~
~
Im
A L ---
Ak*
alo--u m
Wk I~rs r~m R`k-w
'om m"-.
Figre S-t Dredn StuMon tw ftn O8LD U* oc
, Fih. Worn ed Sednmnt Lomon, 2013 B-s
O 9
I I
I U
U-
-~-~umuain.a
" &Mom 9 MLos"
- 1Lomm Fgn B-2 mroen Saion Fld Air Sonpong man OSLO 8Its, Outmi Ring OSLD Locaons d Mlk Locabon. 2013 B-6
APPENDIX C DATA TABLES AND FIGURES PRIMARY LABORATORY
- 0
.1 1*
In~sn~onle ft blank
Table C4.1 CONCENTRATIONS OF GROSS SETA IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION, M013 RESULTS IN UNITS OF PCI/LITER t*2 SIGMA COLLECTION rkwftf 0-21 D42 0-67 01/04113--
01/25.13 02(01113 - 02022/13 -
03/01/13 - 0/2/13 0415/13 - 04/2I/13 0/03/13 - 011113 06/07/13 - 06W8/3.
07/06/13 - 07/26/13 05102/13-08/30/13 0~4/3 - 0010/13 r 11101113 - 11r13 12106/13 - 12127/13 10.5 -*22 7.1 t 1.7 5.0 1 1.8 7.4 a 1.6 18.4. 2.5 7.5 a 1.6 7.4 1 1.7 8.3 t 1.8 5.2 a 1.8 9.8
- t.8 7.1 1 1.5 7.9
- 1.7 12.0 Z 2 7.6
- 1.7 8.9
- 11 (1) 9.6 a 1.8 9.0 Z 2 9.2 a 1.7 9.2 a 1.8 e.9 a 2.0 4.2 a 1.6 6.4 a 1.0 8.2 a 1.6 10.2 a 1.9 6.8 2 1.9 13.5 t 2.2 12 a i.e 0.4 a 1.7
- 5 i.8 26.2 a 2.9 7.5 a 1.7 5.2 a1.8 (1) 5.7 a. 1.6 7.0 a 1.5 0.8 a 1.6 MEAN 8.5 a 7.0 8.6 a 3.9 8.3 a 13.0 Table C4.2 CONCENTRATIONS OF TRITIUM IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF PCI/LITER
- 2 SIGMA COLLECTION "I1 4-52 0.7 0ou134IS -
3/26113 04105/13 - o0r2/13 0710513 - 00r27113 104/13 - 12/27/13 MEAN 667 a 159
< 193 663 a 138 475 a 139 M08 a 232
-c 194 4165
'=160 1i00 a 183 618 a 153 2000 249 2567 Sa43 THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-1
TAW C4.
CONCETRATONS OF GAm MA
-r.r wE SURFACE WATER SAMPLES COLLECTED IN TME VICINITY OF DREEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF PCIUJTER
- 2 SIGMA SITE COLLECTION W-84 CO-GS F0-9 Co.&
Zn.5 Nb-t6 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 01/25/3 - 02122M3
<c4 3
-c7
-c3 c 7
ýc4
<7 c 9
<3 4
<22
<7' 02213 - 03I2913
< 5 c 5 1 i2 5
< 11
' 6
- 10
- 13
' 4
< 6
< 31
< 11 03r2W13 - 042613
<6
<4
<12
'5 c10
<4
'7
<13
<4
<5
<32
'8 04/213 -
W31i13
- 5
< 6
< 10 85 411
< 7 11
- 13
' 5
< 5
- 37
' 10 05131113 -06 1OV 3
<4
<4
<7
<4
-8 c4
<8
-9
'4
'4
'19
-8 028I13 - 0712f13
< 5
' 6
< 13
' 4
' 11
< 5
- 10
< 13
< 6
< 6
- 32
< 10 07/26=13 -083013
' 6 6
' 13
-c
- 11
< 6
< 11
'13
< ' 5 5
< 33
< 12 OW3W13 - 027113
'5
-'4
< 10
< 6
< 10
' 6
< 7
<15 c 4
< 5 c 31
< 10 09027113 -1012513
-0 6
4 11 45 49
'8
< 10
< 13 45
-'5
< 29
< 10 102 11M13 45
<6
< 11
-5
' 11
<5
-<9 1 14
-'5
' 5
- 32
- 12 11r213 - 12127113
< 3 43 7
c 3
- 7
'4 6
< 14
- 3
'3 27
< 9 2
MEAN 0-62 01/04f13-01=2/13
<2
'2
'4
'2 c'3
'2
-3
-6
<2
'2
<12
<3 02f01113 - 02/22/3
-c3
-c3
-c6
-c3
< 5
< 3 c5
<9 c 3
<c3
<18s
< 5 0=/1113 - 03MW13
< 4
-c4
<8
< 3
-<8 44 47'
<11
<4
< 4
< 24 c<5 04~i513 - 04~/13
<6
-6
-12
<5
'12
<7
<9 414
'6
'6
<32
-9 05D313-5131/13 56
' c 10
< 5 0
- a 5
' 9
' 14
<5
< 5
' 29
-'8 06007113 -02l3
'4
'4
<9
,4
'9
'4
<8
<10
'4
<4
'23
'8 075/13 2613
- 6
< 5
'c 13 4C6 a 10
' 6
< 12
' 14
< 5
< 6
< 30
< 13 O0Bi2J13 - 0w3013
<3
<5
'8
'4
-7 c5
'9
'11
'4
<4
'24
<10 09W13 -0V27113
'4
-'5 9
-C5
' 10
'5
< 10 412
'4
'5
-'28 c 10 10f0413 - 10253
< 7
< 6
'1
's
- 7
' 13
' 6
- 9
< 15
< 5
<5
- 34
' 13 11101/13 - 11r213
' 4 c 5
< 9 c 4
<'8 a
5 9
' 14 4
<5
<27
< 9 120813 - 12027113
< 3
< 4
- 8
'3 6
- 4
-0 a
c 14
' 3
- 3
< 28
' 9 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION
Table C4.3 CON -ENRATIONS OF GAMMA IITTERS IN SURFACE WATER SAMPLES COLLECTED IN THE VCINITrY OF DRESDEN NUCLEAR POWER STATON 2H013 RESULTS IN UNITS OF PCIIUTER
- 2 SIGMA SIE COLLECT1ON Mn-64 PERIOD Co-GB F*-8B CoO br-OS WA*O Zr-OS 1-131 Cs-134 Cs-137 BOA-40 La-140 01/25113 - 0222r13
'4 02/22113 - 03r29/13
< 4 03/29113 - 04128113
< 5 04/2~13 - 05/31/13
< 6 05131113 - 0612813
< 3 0618M13 - 07M26113 45 07r2/13 - 06/30/13
< 4 06130113 - 0W27113
' 4 09127113 - 10025113
< 5 10125/13 - 111213
'4 11/2W13 - 12027/13
< 3
'0
'~
- '9
'4
'4 45
-<4
'5
'5
'c5 45
'4
<4
<8
'8
< 12
'7
' 10
< 11
<(11
<'11
, 10
< 10
'4
'3
'5
'5
'3
-5
'6
,'4
'4
'4
'8
'5
-7
<4
<9
'4
'10
'5
<12
<6
'7
'3
'10
-C
<9
<5 c11 06
<7
'4
<8
'13
<4
'7
<9
'4
<9
<11
<4
-10
'13 U
5
-9
<13
<6
'6
'9
'3
'10
<12
'4
<9
<13
'4
-c9 c %
<56
<8
'13
'5
-7 c11
'3
<8
<14
<3
<5 28
-¢9
<4 24
'8
'4
'24
'8 5
431
<11
<6 c33
-11
<3
<21
'6
'6
<36
'9 5
<. 30
<10
'4
- <35
<10
-5 1<28
<11
<4 27
'10
'4 c 27
'9 MEAN (1) SEE PROGRAM EXCEPTONS SECTION FOR EXPLAATION
Tdle C41.1 CONCENTRATIONS OF TRTJ IN GROUND WATER SAWPLE COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF PCI/LITER
- 2 SIGMA COLLECTION D-23 D.35 01111113 - 01111113 02/07/13 - 0210710 03/08/13 - 03/08/13 04/11W13 - 04/0113 05/1013 - 05/10/13 08=14/13 - 06/14/13 07/12/13 - 07/12113 00109/13 - 060W13 0913113 -0W13113 10/11/13 - 10/11/13 11108113 - 111)6/13 12/13113 - 12/13/13 MEAN 218
- 125 414
- 120 250 a 116 (1) 265 118 3865 123 311 a 129 223 t 134 302
- 116 286 a 134 351
- 135 321
- 115 365
- 141 312 t 131
< 185
< 176
'104 4182 A
(1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-4
Tabin C-12 CONCENTRA11ONOF GAMA EMITTEMS IN GROUND WATER SAMPLES COLLECTED W THE VICINITY OF DRESDEN NUCLEAR POWER STATIOCK Ml)
RESULTS IN UNITS OF PCIIL/TER
- 2 SIGMA SITE COLLECTION PERIOD Mn44 Co-G8 Fe-G CoG0O Zma6 PbB Zr4B 1-131 Cs-134 Ce-137 80-1,40 LIA-140 D-23 01/11/13 - 01/11/13
<6 02107113 - 02/07/13
' 3 03106113 -
3I/13
'3 04119113 - 04/1913 (1) '6 0S16113 - 05M/113
<3 06114/13 - 06114/13
<3 07/12/13 - 07/1213
' 6 0610613 - 08M061$
< 5 09113/13 - 06113/13
< 4 16I1113 - 10611/13
- 2 11106113 - 11/08113 46 12M1Y313 - 12F13113
' 7 MEAN D-36 01111113 - 01111113 8 a 04/12M13 - 04112113
< 3 07/12/13 - 07111213
' 6 10111/13 - 10111/13 4 2
'c4
'3
'3
'c6
-3
'3
'5
<6
'4
'2
<6
,8
-11
<4
'7
<3
'8
'4 1 14
<6
'8
<3
<6
<3
< 15
'5
<13
<6
. 10
'4 c4
'2
<13
<6
' 12 86
'8
<3
< 10
<4
<5
<2 Doom
-7
'7
< 11
<6
'6
< 11
<11
<9
'4
< 11
'1t2
< 11
'6
<12
'3
'a
'3
'4'6
<3
'3
'6'8
'5
'2'6
'7
'6
-3
'6
<2 SV 14
'6
'9
<6
<9
< 10
' 14
<6
'8
<5
'7
<11
< 14
- 11
' 14
<7
' 14
'3
'11
'10
'14
, 13
' 10
'4
'3
'3'0
<3
'3
'5
'5
'4
'2
<5
'5
'3
-5
'2
'4
'3
'4
'5
'3
'3
<5
<5
'4
'2
-6
'7
-c5
'3
<4
-2
'23
'6
'21
'7
'32
'10
'20
'7
<'18
'86
<41
'9
'33
' 13
<27
' 10
< 19
<6
'34
'9
'31
< 12
-32
' 10
'28
'10
<31
<14
,' 19
'6
-5
'3
<5
-c2
'9
'6'8
'4
' 14
<14
'12
'11 MEAN (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATiON
Tabb C-I1.1 CONCENTRATIONS OF GAMMA EMITrERS IN FISH SAMPLES COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION 2013 RESULTS IN UNITS OF PCIAKG WET
- 2 SIGMA SITE COUZICTM NINK6 C048 FoSS Co40 Zn-45 fW-9 Zr-Os C*434 Cs-137 Sa1040 U4-40 Da8 ofeDatr n
Loo ows Commn Carp
-~q B~d 0510113 c 65 0510113
- 75 10I13
' 60 1OW13
- 62 MEAN 05601/13
' 35 0S U13 c 75 1(0M13
< 61 102J13
< 67 c98
-'57 c59
< 149
'248
< 145
< 135
'C59
'72
'64 4 119 175
< 110 125 S86
< 105
<45
-76 130
< 168
- 101
- 141
'61
<74
<43 C58
-70
<84
< 44
-c72
< 1196
- 1250
- 480
- 548
< 122
< 440 4 150
<168 046 Channe Catfih Com Corp Common Cop 6
~Lugsmo, Bass
- 41 c 114 4 35
< 73
- 03
< 190 8
as
-148 oc67
-147 061
<70
- 140 117
< 147
'48
'64 062
-'76
< 175 4114 4132
'35
- 74
'57
'U8
<36
-'76
-62
<64
-4 52
" 1154
< 504 "6M7
'249
<c264
" 153
" 182
Tabs C4V.1 CONCENTRATIONS OF EMITTERS IN SEDIMENT SAMPLES COLLECTED PS THE VICUTY OF DRESDEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF PCA(G DRY t 2 SIGMA SITE COLLECTION Mn-64 CO.8 F.
Co04 Z"5 Nb.95 Zr-05 Cs-134 CI-137 S1440 La-140 PERIOD D-27 05M1 W3
'57 1WO4I13
'94 MEAN
'62
<1560
-8
'134
-71
<8 9 49
-52
<533
< '2
< 228
- 128
'184
' 121
< 170
- 87 187 104 8<
778
< 213
<279
£3
. I
Table C-V.1 CONCENTRATIONS OF GROSS BETA IN AR lARTICULATE SAMPLES COLLECTEO IN THE VICINITY OF ORESIDEN NUCLEAR POWER STATION, W013 RESULTS IN UNITS OF E-3 PCI/CU METER
- 2 SIGMA COLLECTION PERIOD GROUP I I
GROUP II Iv-u1 LUW LK4
-07 0-4 ID-53
- m U60a 01/04113 -01111/13 40 t 6 37
- 6 38 t 6 38 t 6 46 t 6 01111/13 -01/18/13 26 5 5 22,6 30*5 26
- 5 24*5 01118/13 - 0126113 16 t 4 18*5 17 t 5 21 t 5 21 t 5 01=25/13 -0201/13 33
- 5 30 t 5 386 *5 36 t 5 27
- 5 0210113 - 02f0W13 31
- 5 31 t 5 28*5 26
- 5 36 6
020/13 - 02/15/13 15 *4 21 t 5 22*5 16
- 5 18 t 4 02/15113 - 02/22/13 20 t 4 16 t 4 19 t 4 19
- 4 16*4 02=2213 -03101113 15 t4 13
- 4 14 *4 16* 4 l *4 03/01/13 - 03A0W/13 12
- 4 9* 4 10 t 4 14 t 4 9
- 4 03W0813 - 0315/13 18
- 5 17
- 165 15 t 5 17 *t5 03115/13 - 032/13 20*5 18/ *4 17 14 17 t 4 18
- 4 03r2213 - 032913 8
- 4 7t4 8*4 11*t4
<5 03W2913 - 04W513 22
- 5 20
- 4 20* 5 1? *4 15*4 040513 - 04"12/13 11
- 4 13 *4 12*4 11 t 4 t3 *4 04012/13 - 04/1913 8
- 4 8* 4 8
- 4 6
- 4
-0 v 4 04/1013 - 04126113 13
- 5 11 *4 13
- 5 17 t 5 20 :6 5
04113 - 0603113 13*4 22*t 5 246* 5 22
- 5 158*4 05603113 - 0/10/13 13 t 4 11 *4 17 t 4 12 *4 13 *4 05110/13 - 05I17/13 15*4 18 t 4 19 *4 19 *4 13 24 05/17113 - 06124/13 (1) 17 *4 (1) 15 *4 (1) 17-*4 (1) 17 *4 (1) 14 *4 05r24/13 - 05/31113 13 5
14*5 11* 4 14
- 5 11 t4 05/311t3 - 067/13 9 t 4 86 *4 10*4 9
- 4 12 *4 06107/13 - 08/14/13 16* 4 16* 4 18 *4 16 t4 19 *4 0614/13 - 06121113 13* 4 15 *4 (1) 14* 7 12* 4 16
- 4 06021/13 - 06/28/13 17 *4 14
- 4 (1)
(1) 14
- 5 12
- 4 062/13 - 07105/13 13* 4 12*4 (1) 9 *.4 10
- 4 0710113 - 07/12113 14* 4 19*5
. (ly (1) 19s 8
15 t 5 0711213 - 07119113 11 *4 10* 4 (1) 8*4 13 *4 07/19113 - 071263 16 *4 14* 4 (1) 19t*
4 15 *4 07125/13 - 08=2113 18 *4 14* 4 (1) 20 *4 19 *4 06102/13 - 08/09/13 16* 4 18 *4 (1) 18* 4 14 *4 08109/13 -08/1/13 17
- 4 17* 4 (1) 19* 4 18*t 4 08/16/13 - 0O2313 27
- 5 29 t 5 (1) 29
- 5 29 t 5 0823/13 -06/30/13 27t5 26* 5 (1) 24*65 271*5 06/30/13 -0910/13 13*
- 4 14 *4 (1) 15* 4 18 *4 09/06/13 - 0913/13 34 5
43 6
(1) 34 t 5 36 t 5 09/13/13 - 020/13 2D 4
20 4
(1) 20 t 4 16*4 0920/13 - 0917/13 17 *4 15 *4 (1) 17 *4 15 *4 0107/13 - t/4I13 23* 5 24
- 5 (1) 23
- 5 24* 5 10/04/13 - 10/11/13 21
- 4 18 t 4 (1) 21
- 4 23
- 5 10/11113 - 10/16/13 21 *4 22
- 5 (1) 24 *5 2 *t 5 10/18/13 - 10/25/13 16 *4 16* 4 (1) 16*4 18 *4 10/613 - 11101113 21 t 5 28* 5 (1) 21 6
5 2 *6 5 11101113 - 1108/13 22* 4 21
- 4 (1) 22,4 27 /5 11/06/13 - 11115/13 20
- 5 17
- 4 (1) 16
- 4 17*t 4 11115/13 - 112/13 16
- 4 17* 4 (1) 1*6 5 21*t 5 11122/13 -
/29/13 20 t 4 18 t4 (1) 23
- 5 21 t 4 112/13 - 12106/13 38
- 6 40
- 6 (1) 44* 6 38
- 6 12/06/13 - 12113/13 37*5 29
- 5 (1) 42* 5 39 t 5 12/13113 - 12120/13 26
- 5 30 *5 (1) 31
- 5 32
- 5 122013 - 12/27113 24
- 5 2365 (1) 26
- 5 24
- 5 12f27/13 - 01103114 29 t 5 25
- 5 (1) 30
- 5 22*5 q0'1'O 39
- 6 23
- 13* 4 27*5 23*5 20*5 17
- 4 10
- 14 8*4 17 t 5 18
- 4 8*4 24
- 5 12
- 4 12
- 4 15 *5 21
- 5 16 *t4 16
- 14 17 *4 10 *4 17 *4 14 *t4 10 *4 11 *4 19 t 5 9*4 15
- 4 17 *t4 14
- 4 19 */4 30 *5 23*5 10
- 4 33
- 5 18*14 16
- 4 18214 21 *4 24*6 16 t 4 23*t5 22 *4 18
- 4 13 *4 22*t5 42*6 39 15 26* 5 20*5 20*5 41
- 6 33 *86 40*6 268*t5 27
- 6 22*5 17*65 1+*5 17*5 23
- 4 31
- 5 31 5
24*65 33 *5 34*5 20*65 19*5 20*5 19*4 19*4 18*4 15 4
10*4 12 *4 12*4 15*4 13*t4 11 5
158*
13*5 17*4 20*5 17*t4 8*4 6*4 9.4 20 4
18 t4 14 4
13*4 14*4 13 4
8*4 5*3 8*4 11* t4 15* 65 14 *65 24 *5 18*t4 18
- 4 14 *4 12 *4 12*4 17*24 15*t4 13*4 10*t 4 (1) 13*t4 (1) 16 *4 13*24 9* 4 13*4 11 *4 10*t4 14*t4 18*4 17*4 186*4 11*14 14*4 10*4 14 4
12*4 12
- 4 11*4 12*4 14
- 4 176 16* 5 16*4 10*4 10*4 11*4 14*4 16*4 14*4 16*4 16*4 17*4 15 4
14 *4 16s*4 18 *4 16 *4 15*4 28 *5 29*5 27 *5 26*5 26 *5 26*65 11 *4 16 *4 14 *4 38* 5 32*5 360*
5 20*t4 18*4 14*4 19 *4 15 *4 18*t4 20*65 20*65 20*5 22*t 5 24 *5 20*4 21 *4 24*5 23
- 5 15*4 186*4 168*4 22*5 21 *65 25*5 26*5t 24+/-5 25*t5 21
- 5 16 4
17 *4 18*5 10 5
21 *5 17*4 20 *4 24*5 41 *6 43 *6 39*6 36
- 5 38
- 5 38t5 29 *5 30
- 5 26*5 24*5 25*5 25*5 25*5 23*5 28*65 MEAN 20 t 18 20
- 17 20 t 22 21 t 19 21 t 10 19 t 17 20
- 18 20
- 18 20 t 18 THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-9
Table C-V.1 CONCENTRATIONS OP GROM SETA I AIR PARTICULATE MNIFLES COLLECTED IN THE VICiNiTY OF DRESDEN NUCLEAR POWER STATfON, M013 RESULTS IN UNITS OF E-3 PCI/CU METER *12 SIGMA COLLECTION PERIOD I. J_
I I
__t. GROUP III 0D8 0-1 lzuenz - UIM13 wt. I 01/04/13 0111113 42 6
01/11111
- 01/18113 22 6
01118/13 -01/2613 17 i S 01126113 - 02101/13 35 *5 02101/13 - 02J08/13 26 5 S 02/08/13 - 02(16/13 18
- 4 02/15/13 - 0=213, 13*4 02,22/1r -
301/13 (1) 9
- 4 03101113 - 03108/13 9 t 4 03108113 - 03115/13 17
- 5 03/1513 - 03/2213 19
- 6 03/22/13 - 03/29M13 7
- 4 03rM913 - 04/05113 20
- 4 04196113 - 04112113 15 *4 04/12/13 - 04/19/13 8 t 4 04/19113 - 04/26/13 20
- 5 04/26/13 - 06=08/13 22
- 5 05M03/13 - 0601/13 18
- 4 0561/13 - 05/17/13 17
- 4 05117/13 - 05124/13 (1) 15
- 4 05W4/13 - 05/31/13 13
- 4 05/31/13 - 06107113 10
- 4 08107/13 - 06M14/13 21
- 4 06114/13 - 06/21113 (1) 16
- 7 06021113 - 06/28/13 17
- 4 o06/213 - 07106113 10
- 4 07105113 - 07/12/13 17
- 5 07112113 - 07119113 9
- 4 07/19113 - 07)M13 15 t 4 07/2r/13 - 08,12/13 18
- 4 08102113 - 06109113 14
- 4 06109113 - 08/16f13 1S *4 06/16113 - 062313 33 fB 06/23/18 - 08/3W13 26.* 5 08/3913 - 0910613 15 4
09106113 - 09/13/13 33 0W133 - 0291M3 23 0 6 09/29113 - 0917/13 19 i 4 09/2713 - 1004/13 17 1 4 10104/13 - 10911/13 23
- 5 1/111/13 - 19118/13 23 & 5 10/18/13 - 1912511 18
- 4 10/25113 - 11101/13 26
- 5 11/01/13-1106/13 25
- 5 11106113 - 11/15M13 (1) 17
- 4 11115113 - 11/22/13 23
- 5 11/22=13 - 11129113 21
- 5 11/29113 - 12106113.
41
- 8 12106113 - 12/13113' 39
- 5 12/13/13 - 12/29113 31 t 5 12F20/13 - 12127113 29
- 5 12127/13 - 01103/14 25
- 5 z al: -
1 1 4426 24*5 22*5 33*6 33 5
18 *4 17 1 4 (1) 11 *4 17 5
19 *4 8*4 18 *4 12
- 4 10 4
16 5
18 *4 12 *4 15
- 4 (1) 13
- 4 13 t 5 11
- 4 22*4 132 4 14 *4 13 *4 18
- S 12 "4 IS *84 17 *4 152&4 18
- 4 27+/-5 26*5 18**4 34 5
18 *:4 18 *:4 20*t5 22*5 26*5 15
- 4 25 5
(1) 18
- 5 20 *5 20*t4 48t6 38
- 5 29*5 23*t 5 21
- 5 40*6 25 5 28 5
17 *4 17
- 4 11 *4 11 *4 16
- S 20*4 6*4 17 4
13 *4 9*4 12
- 5 21
- 5 14
- 4 14
- 4 17 *4 12 *4 15 *4 18 *4 13 *4 12 *4 14
- 4 18 *5 12 *4 17 *4 15 *4 17
- 4 16 *4 26*5 32*5 11 t4 38+/-5 19 *4 15 t4 25*15 21 *4 27285 13 *4 20*5 19
- 4 19 t 5 21 *S 18 14 42*6 33*5 29*t5 23*5 29*5 20 t 9 9.6w Y,8 35*6 26 5 15 54 28*5 17 *4 19 *4 12 *4 11 *4 17 *6 20 5
9*4 20*4 14 *4 864 14 *6 2628 14 *4 16 *4 16 "4 10 *4 10 *4 17 *4 IS
- 5 13 *4 12 *4 9*4 102 4 15 *4 14 *4 19 *4 32*5 2425 22,5 40*6o 2024 18
- 4 28 1:5 21
- 4 23*5 17 *4 18
- 27*5 26 5
15*4 20*4 39*6 38*5 26*5 26
- 5 28*t5 I
lwp 37*6 22*5 19
- 5 27 5
34*5 19
- 5 17 *4 13 *4 10 4
15 *8 19
- 5 7*4 21 *4 9*4 5*3 12 *5 16 4
14 24 16
- 4 16 t 4 16 *5 15
- 4 18 *4 14 *4 15 *4 11 *4 21
- 5 12 *4 16 *4 17 *4 172 4 18 *4 32*25 29 *5 15 *4 38*5 23+/-5 15 *4 21 *5 25 5 24*5 17 *4 22*5 22*t5 15 *4 20 *4 43*6 39 5 264*5 26*5 24*.5 MEAN 21 18 21 2 19 20 t 18 21
- 18 THE MEAN AND TWO STANDARD DEVIATION ARE CALCULATED USING THE POSITIVE VALUES (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-9
Tm C-V.,
MONTNLY AND YEARLY MEAN VALUES OF GROS BETA COUCENIRKTIO0 1d AIR PARTCULATEMK S
UPLS COLL THE VCUMSY OF D E W L POVARF STATION, 2H3 RESULTS IN UNITS OF E-3 PCI/CU METER
- 2 SIGKM GROUP I - O#ITIE LOCATIONS m m GROUP I - NEAR-FIELD LOCATIONS COLLECTION MIN MA *M4AE*.
OROUP II - FAR-FIE.D LOCATIONS COLUECTIONH-*,L MIN MAX MEANA p~p
_At GROUP IV-CONTROL LOCATION COLLECTION AMN MAX MENd+/-
PFRIM2m PERIOD PERIOD im-1ý owammmb----
12'2W12 - 0m1113 02=011/3 - 0=11/13 03/01/13 - 03/2613 03/23113 - 061)313 06=03/13 - 05131113 05/31113 - 06/26113 061613 - 06102/13 06102/13 - 06130/13 01/3=13 - 10W04/13 11101113 - 11012113 1112/113 - 0A14 1126112 - 01=03/14 1i 13 7
8 to18 10 16 13 1s 16 23 57 33*2 31 20 113 20 13 *9 24 14
- 11 19 15 *5 16 13
- 7 19 14 *6 29 22 12 43 22 *19 26 20*8 22 19*5 40 30t12 112=2W1
- W0=/13 02101/3 - 03101/13 0310/13 - 03O2613 03/613 - 06/0W3/
063/13 - 06131113 0612113 - 06=0 OL12613 - 06102/1 06W213 - 0612611 CM613 -
10106113 10AW13 -
11101/13 1110/13ll - l1lM613 11/2613 - 01/0314 13 10 6
5 9
9 8
14 10 15 13 20 64
.224 36 20* 14 20 13t8 24 15 10 19 14
- 19 13
- 20 14 *7 30 22
- 12 39 21*t16 26 21*
7 27 20*7 44 31 15 120M12 - £D01113 0210113 - 03M01M13 01=113 - 03WOWS13 0310313 - 05/03/13 0M1/13 - 05231113 0631113 - 06rj8/13 0860f/13 - 06=13 086/113 - 1~04/13 10106/13 - 11101113 11101113 - 111it3 1112W13 - 0113/14 1I 9
6 a
I0 10 14 11 13 15 21 53 33
- 25 38 19 *116 20 t4*10 29 16t10 18 14*4 16 15
- 6 33 23 *:13 40 22*16 27 21,*8 27 21 t7 46 32216 12M12 - 02101113 0a21/13 - 03Mt/13 03=1/13 - 0/2W13 03=26113 - 06W)3/13 06013 - 06131/13 05/31/13 - 06113 0626113 - 06/13 0S=13 - 408313 0613613 - 1004/13 104/13 - 11/01/13 11101113 - 11/26113 IM/AWM
- 01/03/14 10 52 31 *27 13 34 20 18 7
19 13 10 6
21 13 12 14 16 16 2
14 16 16 *2 11 21 16 *8 17 32 24 t 15 15 36 22 17 17 29 24 10 15 22 20 7
24 43 31*18 S
52 21 18 I;
7 57 20 *1$
1126-12 -01/0/14 6
14 20
- 18 1221/2 - 010314 6
53 21
- 16 12=12 - 0103/14
Table C-V.S cO a ITRATIO9U OF GAMMA EMITTERS IN AIR PARTICULATE SAMPLES COLLECTED IN THE VICNITY OF DRESDEN NUCLEAR POWER STATION, 21t3 RESULTS IN UNITS OF E-3 PCIICU METER
- 2 SIGMA WfE COOLECflO PmRon Mn64 co-S FeaS Co-SO Zn65 1b6 Zr-95 Cs-134 Co-137 ale-140 tla-140 0140 1W~1
-IZW13 03129/3 - 06M2/3 06M213 - 1OG4/3 104/13 - 01IM4 MEAN
-2
'2
<3
-3
<2
-2
<3
£ 0-02 12W212 - 03rA13 03r2813 - 0812813 081813 - IORMf3 1041W3 - 01JM14 MEM D-03 12r2812 - 0302813 03/28113 - 06B13 0812811
- 10O4I3 1~0/3 - 61MR/4 D.04 12F2812 - 028W13 03ROM13 - 0812813 06r2813 - 1OW3 10Mf3 - 01ý314 MEM 0.07 12W2812 -03.M813 03W213 - Ord/28113 0612813 - 1~3/1 10AW/13 - 0103/14
'3
'3 (1)-
(1)
'3
'4
'2'5
'3
'4
'3
'4
<3 d3
'3
'4
'4
'5
'5
'3
< 6
'3
'3
'3
'3
<7
'5
-8
'6
'9
'4
'7
- 10
'8
'8
' 15
'7
< 14
<10
<8
- 10
-7
<2
<2
'3
'4
'3
'2
'3
'3
'2
'3
'6
'2
'3 43
'3
'3
'5
'7
<8
'9
'5
'5
'8
<c6
'8
'3'3
'3
'3
,c3
<3
'3
'4
'4
-4
'4
-5
'4
'4
'3
'3
'4
<3
'5
'7
'6
'6
-5
,c 6
<6
'5
'9
<2
'3
'2
<3
'2
<3
'4
<3
'3
'3
'3
'2
'4
'3
'2
'2 c3
'2
'2
'3
'2
'3
'2 43
'2
'3
'3
'4
'2
'4
-3
'3
'3
'2
'75
'45 863
<40
'So
'84
'56
-<80
'72
'72
-c56 c73
' 110
'c46
- 21
'17
'29
' 21
- '28
- 20
'c21
- 21
- '28
'24
<'21
-'23
'c12
'7'7
<6
-'9
'7
-c5
'7
<6
'7
'7
'5
'8
'6
'6
'7-'6
'3
'3
'3
'3 (1) SEE PROGRAM EXCEPTOW S$ECTION FOR EXPLANATIOW
TabSe C-V.3 CONCENTRATIONS OF GA A EMTERS IN AIR PARTICULATE SAMPLES COLLECTED I THE VICVSTY OF DRESDEN NUCLEAR POER STATION, M3 RESULTS IN UNITS OF E-3 PCIICU METER
- 2 SIGMA WTE COULECMO p~m 1*I44 CoGS0 F.89 coao zn.65 Nb-95 Zr-OS Ce-134 Cs-137 Ba-140 La-140 flflfl44Iflflk.~%I,.Sdtiat eq 4
4 03r2W113 - 06=n813 MOM8/1
- 104/13 1lDAfl3 - 01103/4 MEAN hi D-10 12/28/12 - 03213 03129113 - 0828113 08r28/13 - 10104013 101t413 - 01103/14 D-12 12 M8/12
- 03M2913 03/A213 - OVA"2813 06128/13 - 10I1l3 10109413.-01103/14 D.14 12/28112 - 03/29W13 03a9/13 - 062V/13 062r113 - 104/13 104/13 - 0113,14 D-45 12r2812 - 03M9113 03r29/13 - 06/8/13 06/8113 - 1004/13 104/13 - 01014 (3
(3 (4
c2 (3
(3
'3 (3
'2
<2
'4
'3
'2
-2
'3 (3
<2
'2
<3
,'.1
'3 (3
'5 (3
'4
'3
'3
'4 (3
'3
'5 (3
'3 (3
'3
'4 (3
(4 (5
(11
'14
<10
'9
- 12 (7
(9 (5
(8 10 (10
<8
-c12
'6
'3
-6
'10
< 12
'3
'3
'2
'3
'3
'3
'3 c3
<2 (4
'c2
'2
<3 (2
43
'3 (3
-4
'7
'6
'7
':7
'6 c5
'4 (7
<6
'9 (5
'6
'6
'6
',7 (5
'8
' 11
,'3
<3
-5
'4
<5
'3
'3
'4
'3
'3'5
'4
-3 (3
'3
'3
'3
'3
'5
'7
'4
'-9
'7
<6
'-5
'6
'8
'4
'5 (7
(7
-'5
'6
'7
'5
'4
<6
,10
'2
'2
-'4 43
'3
'3
'3
'3
'2
'3
'4
<2
'3
'2
'3
'3
<2
'3 (3
'3
<2
'4
'3
'3 c2
'2
'3
'2
-2
-4
'2
'2
'3
'2
'2
<2
'2
<3
'91
'c67
<77
,c9S
-43 e68
'47
-72
'50
<73
'57
< 116
<52
'62
'54
<73
<65
'35
'28
'22
'24
< 31
'48
<'17
<34
< 17 (37
- '27
'40
<23
<48
< 19
<29 428
<31
<'31 MEAN
Table C-V.3 CONCENTRATIONS OF GAMMA EMITTER8 N MR PARTICULATE SAMPLES COLLECTED IN THE VICIlTY OF DRESDEN NICLEAR POWER STATION, 2013 RESULTS IN UNITS OF E-3 PCIICU METER 1 2 SIGMA UAn44 Co.6B F69 Qo4O B11.
Nb.0 6 Zr4S C84134 Co-137-.
sm-lb SITE COLLECTION PERIOD 0.63 12=28112 - 03029t13 03129113 - 0612813 06M2813 - 10104113 10A1/13 - 01103/14 La-140 MEAN
'.1 D-66 13128112 - 032913 030M13 - 06128113 06/28/13 - 1004113 10C4/3 - 01t03114 MEAN 06 212812 - 032W13 03M2913 - 06M2r113 06/26/13 - 10104113 10fl413 - 01103114 MEAN D-8 12W28112 - 03M29/13 031213 - 0612813 061813 - 1~34/t3 1~10413 - 01103/14
'3
'3
'3
'2
,c 2
'1
'2
<4
'4
'2
'3
'3
<2
<4
'3
<3
'4
'4
'4
'3
'3
<1
'3'6
'5
<3
'4 35
'3
'I'9
. 11
< 13
'9
.0'6<7
,'6
<4 414
< 11
'8
'10
'11
'5
'2
'2<2
'3
'3
'3'3
'2
'2
'3
'3
'3
'3
<4
-1
'9
'9<c6
. 10
<8
'6
<5
'6
'3
< 6
<5
< 11
<3
'7
'9
'6
'4
'3
<3
'5
-4
'3
<4
'3
'1
'2
<5
'5
<4
'5
'5
'3
'7
'6
-5
'10
<5
'5
<3
'3
'2
'4
'3
'3
'3
<3
'3
'2
'2
<4
'74
'67
<2
'2
'2
'2
'67
< 107i "45
<46
'38
- 25
'24
<16
<28
< 11
<'15
- 17 436
-27 c 13
- 38
'57
<12
'4
<S
'9
'8
'5
'7
-6
'2
'2
'3
'4
'2
'4
'3
'2
<1.
'2
'3
'3
'2
'3
'3
<3
<35
'46.
- 141.,
'65
,< 781 83.
'44
Tabe C.VI.i CONCEIITTIOM OF 1-131 IN AIR IODINE SAM" COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF E-3 PCIICU METER *:2 SIGMA COLLECTION GROUP I I
GROUP 11 I
II IIImm I
PERIOD 041 17Zf=IZ -U111J41¶ Ic I0 01104113 - 01/1113
- 17 01/11113 - 01118/13
< 17 01/18/13 - 0125/13
< 10 01/25113 - 02001113 c 14 02/01/13 - 02W813
< 11 02/0=/13 - 02/15/13
- 21 02/15/13 - 0222/13
- 9 02122/13 -0310113
' 30 03101113 - 0308/13 c 9 03/08/13 - 031113
< 41 03115/13 - 0302/13
< 11 0322/13 - 0312/13
< 28 03=2913 -04/05/13 14 04/05/13 - 04/12/13 438 04/12/13 - 04119/13 c 11 04/19/13 - 0418/13
< 11 04M28/13 - 05/03/13
- 13 05/03/13 - 0511013
< 37 05f10/13 - 05/17/13
- 17 08/17/13 - 054/13
< 15 (1) 054/13 - 05/31113
- 15 05131113 - 007/13 c 9 0e/07113 - 08/14/13
' 11 08/14/13 - 060211t3 c 13 06/21113 - 06r28/13
< 7 06/20/13 - 07/5/13
' 31 07/05113 - 07/12/13 c 23 07/12/13 -07/19/13
- 31 07/19/13 - 07=2/13
< 15 07/8/13 - 0&/02/13
< 64 08/02/1 08/09113
< 15 08/09/13 - 08/16/13
< 35 08/16/13 - 08/23/13 c 52 083/13 - 030/13
- 11 0/30/13 09/08/13
' 25 09/0/13 - 091131 3 25 09113/13.
o09Q/13
< 40 091O013 - 09127113
' 63 09127/13 - 10104/13
- 42 10104/13 - 10/11113
- 67 10/11/13 - 10/18/13
< 60 10/18/13 - 10=25/13
< 57 0/25/13 - 1101/13
< 25 11/01113 - 1/08/13
' 69 11/08/13 - 11/16/13
< 17 11115/13 11=22/13
< 54 11/22/13 11128/13
' 25 11/29/13 2/06/13
< 70 12/06/13 12/13/13
' 28 12/13/13 - 1210/13
< 65 12120/13 - 12127/13
< 66 12/27/13 - 01/03/14
' 32
-C44
-c4
< 40
< 43
-43
-43
'27
<27
<3M
<35
-29
<29
<'81
' 61
'23
-23
<12
'30
'24
'24
- 41
< 18
-29
<29
'27
'27
'25 425
- 38 438
'29
-29
-20
'20
'34
-34
'35
'35
'46
-46
'27 (1)
-27(1)
'39
-39
'24
<24
< 28
< 28 435 460(1)
C1O (1) c 31 (1)
-6 0 (1)
-3 1 (1)
, 38 (1)
-6 4 (1)
-c 40 (1)
, 35 (1) 5 53 (1)
' 27 (V)
' 65 (1)
'c 10 (1)
- 41 (1)
-83 (1)
- 42 (1)
< a6 (1) 69 (1)
'56 (1) 6*5 (1)
- 60 (1)
- 45 (1) 5 54 (1)
- 60 (1)
'70 (1)
- 65 (1)
-c as (1)
< 30 (1)
'3S0 (1)
'43
<43
-'26
'43
-28 862 423
'30
'24
' 41
-30
' 10
<24
-38
- 29
- 20
'34
-37
<46
- 28 (1)
'39
'24
<28
-34
- 23 (1)
- 64 (1)
- 31 438
'64
-c39
- 35
- 52
- 27 c64
-25
- 41
-'24
<42
<67
'57
<64
'69
'45
-54
'60
'70 867 c65
-68
-'32 07
'43
'41
<26
- '35
'30
'60
'23
'c30
'24
-40
'30
<26
-c25
- 15
<'20
'c34
'42
- 45
- 27 (1)
<39
'24
<28
-'35
<20
' 31
'62
- 31
'38
'64
'40
<c 40
<35 4'53
'c27
-c65 425
-41
,65
'42
<so
'60
<70
<e5
'54
.60 4'70
< 65
'c32 Q-45 G-53
'40
'39
'32
'34
'30
'39
,24
<34
'26
'45
-35
'27
'34
'36
-22
'27
-40
, 15 436
<30
'45
'34
'23
' 11
<'23
'35 458
'37 c38
'47
<'33 c28
'c43
'26
'39
'25
<50
'c35
'62
<59 462
'46
'c45
-68
'68
'68
<27
':36 6 1l
'30
<30
'21
'32
'22
- 17 c 21
<19
'37
'44
'27
<'18
<34
'24
' 31
'30
'37
-25 433
'30
'40
'26 (31
'27
'19
'56
'39
'37
'46
'35
'29
<41
'31S66
-'33
'48
'58
'34
- 46
'66
'60 c52
'63
<44
'45
'67
-70
<64
<65
-25 04m
<c ;3v
'30
' 21
<34
<22
<39
, 17
< 21
'19
'37
<44
'27
<18
'34
<'23
,'30
<30
'(35
'27
'33 (1)
'30
<40
<27
-c31
'27 S35
<37
'36
' 19
<35
'29
' 41
' 31
'33
'48 458
'34
<46
'60
'52
'62
- 44
'45
<70
-67
- 64
<65
<60
<30 436
< 21
' 18 422
'39
< 17
-21
' 19
'35
'44
'27
' 19
<34
'23
'c30
-29
'35
'27
'-c3 (1)
-30
-40
'27 431
'27
'35
<56
<37
<36
'46
'35
< 12
' 17
-c30
<56
'33
<20
<58
< 18
<46
-27
'60
<52
'62
'44
<45
< w
'70
<66
'64
- 65
'60 m
MEAN (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-14
Table C-VI.1 CONCENTRATIONS OF 1-131 IN 0Nt KOIE MPLUS COLLECTED U THE VICINITY OF DREODEN NUCLEAR POWER STATION, W013 RESULTS IN UNITS OF E-3 PCI/CU METER
- 2 SIGMA COLLECT"O GROUP III LGROUP W PEROG D-W 0.10o 0-14 0-01 1W./* 1 1 1
- f w
o a uemt I
Ic 4 - 1.
I T 4 %
- a i- -
,#110413 - 01/1113 4 16
- 40 c 40 c 30
<40 01111/13 - 0/18113 c 29
' 29
<28 c 37
'29 01118R13 - 0t2/13
- 14
- 32
- 33 422
' 33 01/213 - 02101/13
- 38
'3 38
<38
- 34
< 38 02101/13 - 020813
- 13
- 30
< 30
< 23
' 30 0208/13 - 02/1/13
- 15
< 39
- 39
< 38
- 39 02/15/13 - 022213
' 10
- 24
'c 24
- 18 c 24 02=2213 -03101/13 c 15 (1)
- 34 (1)
'934 c 21
- 34 03101/13 - 030813 c11 26
- 28 c 19
- 20 030/13 - 03/115/13
' 19
'45
< 45
'37 c 45 03/1513 - 03/22/13
-1 S
- 35
- 34
-46
'35 022/13 - 03/29/13
<11
-27
- 27
'27
< 27 03/2913 - 04M08/13
< 17
- 33
' 34
' 20
'34 04~13 /12/13
-c16
' 38
< 38
< 34
< 38 04/12/13 - 04/19/13 9 0
< 21
- 22
- 23
< 22 04/19/13 - 042613
< 11
'27
' 29
- 31 c 27 042/13 - 06A03/13
- 17
- 40
'40 c 30 c 40 05/03/13 - 0510/13
'- 42 I18
- 43
'937
- 43 05110/13 - 05M17/13
' 15
'36 437
'27
< 38 05/17/13 - 524/13
- 31 (1)
< 30 (1)
< 30 433
' 13 05/24/13 - 05131113
' 19
' 48
'45
< 30 c 44 05131113 0-/07/13
' 35
< 35
- 14 c 38
- 34 08107/13 - 0614/13
' 10
- 24
- 23
' 27
'23 0/14/13 - 06/21/13
< 64 (1)
'24
< 25
'33
- 25 06/21/13 -0/2813
' 20
< 28
' 23
'27
' 23 06/2/13 - 07/0513
' 38 c 36
- 38
'35
'c 38 07/05113 - 07/12/13
< 62
-58
-c8 se 4
07112/13 - 07/19/13
- 29
< 29
'29 414 c 29 0711/13 - 07/13
' 38
< 37
< 37
- 38 c 3 07/2/13 -060213 67
<5 c 58
< 47
' 5 08102/13 - 010/13
-40
'34
<34
'38 c34 08109/13 - 0816113
- 44
- 44
- 43
' 26
'43 08/11813 - 083113
- 44
- 44
- 48
- 43
'46 06/23/13 - 06/30/13 27
- 26 c 26
' 31
- 28 0813013 - 0/0113
<65
'39
<37
-c5 s30 095/13 - 091313
'25 425
-25
-35
-25 0W13/13 -06/2 13 c 57
- 57 6 57
' 49 c 56 09/2013 - 027113
- 65
< 53
- 51
' 58
' 53 09/27/13 - 104/13
' 20
' 28
- 20 35
- 28 10/04113 - 10111/13
< 68
-c6
-64
- 46
- 68 1011113 - 10118/13 53
< 53
' 53 c so
- 53 10/18/13 - 10=5/13
' 22
- 52
< 50
< 57 651 10/25/13 - 11/01113
-6
'0 5c6
- 59 c 55 c 56 11/01113 - 110/13 52
' 22 c 52 c 63
- 52 11106/13 - 1115/13
- 47 (1)
< 47 (1)
- 48
< 46
< 45 11/18113 - 11/22113
- 45
- 45
'45
' 45
- 19 11/22/13 - 11/9113
<60 W
' 66 68
< as 6 68 11/29/13 - 12W06/13
' 66
< a6 c 28
<61
- 66 12106/13 - 12/13/13
< 69
'6 as68
'69 s
6c 12/1/13 - 12/2013
< 58
- s 58
-56 65
-'58 12/2013 - 12/2713
< 87 c 67
< as 4C69 S
67 12/27/13 - 0103/14
< 48
- 48
< 49
- 63
'49 MEAN (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-15
Table C-.I1 CONCENTRATIONS OF 1-131 IN MLK SAMPLES COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF PCIULITER 12 SIGMA COLLECTION 01/0411 02/07113 03/07/13 04/04/13 05102/13 05/16/13 05r30113 06/13113 06/27./13 07/1113 07/25/13 06/06113 08/22/13 0915/13 0911/13 10/05/13 10/17113 10031113 11/14/13 12=05/13 CONTROL FARM D-25
-4,: 0.5
< 0.7
'c 0.7
- 0.8
< 0.7
' 0.7
' 0.6
-'0.6
< 0.8
- 0.6
- 0.7
- 0.7
- 0.6
' 0.8
'0.9
'0.8
< 0.9
- 0.6
< 0.7
- 0.8 MEAN C-16
Table C-Vi.2 CONCBItRATIOSSOF GAMMNA ENTTERS EUU( AWP*S" COLUf CYID UTHEVICINTY OFDRESDU UCLAR OW
- SttATIO, 3
RESULTS IN UNITS OF PCYIJTER
- 2 SIGMA SE.C.OLLECMON Mn-44 Co48 FbeM co4O Zn45 W-05 Zr-95 CS-134 CS-137 88-140 La-140 D-25 01/04113
< 7 0207113
'5 03107113 4 5 04~13
<6 05M13
'5 05M16113
- 6 05130113
- 6 06113/13
'6 08027113
'5 07112M13
'5 0715W13
-6 M1rOS3 7 7 S 061223
'6 010113 a6 101/13
<6 10/10/13
<2 10131113
<7 11/14113
<5 1205113 1 7 4<8
'6
'6
'5
-6
'7
'5 47
'8
-<6 45
'6 47
<7
'7
'7 C2
-7
'6
'6
'20
- 14
- 13
< 14
'15
< 15
< 13
' 15
< 14
'16
< 10
<14
< 13
-14
'6
' 16
' 15
- 17
< 10
'7
<6
'8
'7
'7
'7
'8
'7
<S
'7
'7
'6
'9
<8
'7
<3
'7
<6
-C9
'16 q8
-11 c7
- 13
'6
'12
<6
'14
<7
'13
<5
'13
-7
< 13
<7
-'10 45
< 13
-7
'15
'6
'10
-5
< 15
<7
'14
'7
'15
'7
'14
'7
'12
'6
,'15
'6
- 13
' 10
' 10
' 13
< 11
'9
'9
<11
' 10
<9
- 11
<13
'c9
' 13
- 11
' 10
-4
- 14
- 12
' 12
'5
'5
'5
'6 C5
'5
'6
'S
'8
'4
'6
'6 c5 46
'6
<a
'2
'6
'4
<6
-7
-5
'0
'6 86
'6
<7
'5
'6
'7
'5
'6
-C6
< 6
'2
<7
'6
'7
<46
-16
-'39
'9
- 38
< 7
- 46
< 12
- 40
< 12
-44
<13
< 27 a6
'28
'9
<'3
<10
'31
<8
'44
- 14
- 49 t13
'38
'6
'39
-11
'42
<11
'45
'8
'42
- 15
- 51
< 14
'45
<9 MEAN
TabIs C-VI.t CONCENTRATIONS OF GAMEMA TTERS IN VEGETATION SAMPLES COLLECTED IN THE VICINITY OF DRESOEN MICLE.R POWER STATION, 2013 RESULTS IN UNITS OF PC$JKG WET 12 SIGMA SrTE COLLECMONW fa.6 Co.6B F49 CoO-6 Zn4S Nb-W Zr495 1-131 CS-134 CB-137 Ba-140 La-140 PoWma 09W1413
'11 09H4113
'c10 fAEAXN
'9
, 10 c28
<13
<24
-11
<31
<17 32
'12
<21
<49 c9
<10
'23
'49
<10
-11
-20 c54
-9 4
'11
-21 451
<9 410
<91
<30
<102
' 21
<93
'25
< 90
<25 04OUAD i emus MUM1
'10 citqe 0W13113
'10 412
'27
'14
' 11
<28
<12
'27
< 12
-24
<11 MEAN DQUAD 2 ambs 0914/13,
- 9
< 10.
- 25
' 10.
.18
- 10 09114f3.
'10
-c11
'29
< 13
'28
<11 2
as D.OUA 3
&Stws sprfb MUMI1
-10 RPuhss 091413
'9 OQUAD 4 cowbq 0W14113
< 7 Cwrots 0&M4I13
< 11 411
- 27
- 10
< 21
< 11
< 13
' 30
' 14
' 28
' 12
-7
'20
'8 c17
<9
< 16
< 44
< 14
- 35
< 14
' 17
- 41
< 8
<20
'51
<11
- 15
<44
<8 422
-,,45
'9
-14
'38
<6
<27 c58
<12
'9
<79
-24
'10
-9
-'2B
- 20 93
<19
<11
-96
'22 16
<61
< 11
< 120
'18
-28 MEAN
Table C4X.1 QUARTERLY OSO RESULTS FOR DRESOEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF MREMIQUARTER t 2 STANDARD DEVIATIONS STATION MEAN JAN - MAR APR - JUN JUL -SEP OCT -DEC D-01-2 31.4
- 4.1 33.1 28.7 32.9 30.7 D,02-1 334
- 1.4 33.2 33.1 34.4 32.9 D.02-2 34.0
- 3.3 35.2 32.0 35.5 33.2 D.03-1 27.6
- 6.3 28.9 25.5 31.4 24.5 0-03-2.
27.5
- 4.8 26.4 24.2 29.9 27.6 D-04.1 32.4
- 5.2 33.0 29.4 35.6 31.7 0.04-2 31.1
- 2.2 31.1 30.2 32.6 30.3 0407-1 30.2
- 5.6 31.3 28.4 33.0 30.0 0.07-2 30.7 a 5.2 31.7 27.6 33.7 29.6 0-06-1 31.8
- 5.0 31.5 28.8 34.9 31.9 0.08-2 31.9
- 4.3 31.9 29.2 34.4 32.2 0-10-1 31.7 a 5A.
33.2 28.7 34.3 30.8 0-10-2 30.7 a 6.3 32.5 26.4 33.5 30.5 0-12-1 29.3 1 5.4 28.8 28.5 33.1 26.8 0-12-2 26.9 a 3.9 29.2 24.6 27.4 26.2 0-14-1 28.4 a 5.0 30.4 25.5 30.6 27.2 0-14-2 29.9 a 4.7 30.6 28.5 32.0 30.4 0D45-1 32.9 a 7.5 34.5 29.1 37.4 30.6 D-45-2 33.6 a 6.0 34.1 30.9 37.0 33.3 0-53-1 27.9 a 3.1 26.2
?5.9 29.6 27.8 D-53-2 27.2 a 3.8 27.9 25.1 29.5 26.3 0656-1 30.9 a 1.4 30.6 30.8 32.0 30.5 045&2 29.7 a 7.4 31.5 24.9 33.4 28.6 0.W6-1 26.2 a 3.9 27.2 24.9 28.4 24.3 0-56-2 26.7 a 4.1 28.2 25.0 28.7 24.8 0.5-01 28.3
- 4.2 28.5 24.2 27.6 24.7 0-58-2 27.0 a 6.3 28.0 22.9 30.4 26.6 0-101-1 31.5 a 6.7 33.3 27.9 34.2 30.7 D-101-2 29.0 a 6.4 28.8 25.3 33.1 28.7 0-102-1 32.3 t 5.5 33.2 29.3 35.6 30.9 0-102-2 32.0 a 4.3 32.6 28.9 33.9 32.4 0-103-1 30.1 a 5.1 31.4 27.7 33.0 28.1 0-103-2 30.1 a 4.3 31.0 27.1 32.1 30.2 0-104-1 31.2 a 5.5 33.9 27.9 32.9 30.1 0-104-2 33.5 a 6.2 344 28.9 38.7 32.1 0-105-1 30.2
- 5.8 31.6 26.1 32.8 30.1 0-105-2 31.6
- 4.5 32.3 28.4 33.6 32.0 0-106-1 28.8 a 6.0 30.5 25.8 31.1 27.6 0-106-2 27.0 a 5.6 28.4 23.6 30.0 26.1 0-107-1 26.5
- 4.9 26.0 24.1 29.1 24.7 0-107-2 28.0
- 4.4 28.4 25.8 30.9 26.9 0-108-1 31.9 a 3.9 32.3 29.3 34.0 31.9 0-106-2 28.5 a 4.8 27.6 27.1 32.1 27.2 0-109-1 30.6 a 4.6 30.0 27.6 32.9 31.7 0-109-2 31.5 a 5.3 32.1 29.0 35.0 30.0 0-110-3 33.3 a 4.1 33.8 30.4 35.3 33.8 0-110-4 35.5 a 5.2 36.7 32.1 38.1 35.0 0-111-1 34.0 a 4.0 33.4 32.0 36.8 33.9 D-111-2 31.1 a 4.9 31.8 30.3 34.1 28.3 C-19
Table C4X.1 QUARTERLY OSLO REULTS VOR DRESOEN NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF MREMIQUARTER t 2 STANDARD DEVIATIONS STATION MEAN
-.%Or%1 JAN-t!AR APR - JUN JUL - SEP OCT - DEC 0-11a-1 28.1 i 5.3 0-113-2 30.0 *.8 0-114..4.
28.5:* 4.9 0-114-2
".29.1 15.2 0-115-1 31.0 t*4.9 0-115-2
'31.9*13.7 0-116-1 33.0 t 6.9 0-116-2 33.6
- 5.6 0-201-1 34.7
- 4.9 0-201-2 35.3
- 4.7 0-202-1 31.6
- 4.7 0-202-2 31.A 2.1.
0-203-1 bi:f1'44.8' 0-203-2 29.7
- 3.4 0I204-1 29.0 *.6.2 0-204-2 27.0 a 5.3 0-205-1 28.3
- 6.0 0-205-2 29.5
- 0.7, 0-206-2 302 a 4.4 0-207-1' 26.4
- 3.5 0-207-2 30.0 a 4.2 0-208-1 26.5 9
3.9 0.208-2 26.6 3.4 0-209-1 26.0 a 8.1 D-209-21,
.26.9-4.7 0-210-1 3Q.1 *6.1 0-210-2 20.9
- 4.6.
0-211-1.
30.6 6.4
- 0-211-2 '30.6
- 4.6 0-212-3 27.0
- 4.4 0-212-4 282
- 3.8 0-213-1 27:2 *.0 D-2134 26.4*6.3 0-214-1 33.0
- 7.7 14-2 31'.0 9.0 0-215-1 34.1 42 0-215-2 33.1 32
..0-216-1
- 20.5 a 2.9 D-216-2 31.9,3.7 0-112A-1 28.3 *82 0-112A-2
.29.9 4.9 29.5 30.3 28.9 30.6 31.7 31.1 32.7 34.6 34.0 36.7 32.7 31.1 31.9 31.6 30.8 28.5 30.3 28.7 29.6 30.9 29.0 30.1 28.1 26.5 272 27.9 31.4 29.8 30.3 31.2 29.5 28.7 28.4 27.6 34.7 33.9 342 34.4 29.8 32.6 27A 30.8 26.1 25.6 26.4 27.6 30.2 29.1 29.6 32.7 32.6 26.1 30.9 27.6 28.1 25.6 24.6 24.5 26.9 27.1 27.5 25.6 27.8 24.0 23.8 22.6 24.3 26.5 26.8 28.5 26.1 24A 26.8 22.9 23.2 30.1 26.0 31.0 32.0
. 27.9 29.7 23.1 26.8 31.5 33.1 31.5 32.0 33.4 34.5.
37.5 36.2 37.4 36.7 33.1 33.5 30.7 32.3 30.0 31.0 33.6 32.9 32.8 29.7 32.8 27.9 27.9 28.6 29.6 33.5 32.1 34.4 33A 27.9 30.7 29.6 29.3 37.7 37.2 35.5 34.4 (1) 312 32.8 32.6 25.1 30.6 27.2 27.5 31.3 31.7 32.5 34.0 (1)
(1) 32.6 30.9 31.1 28.4 27.3 25.1 27.2 28.8 30.6 29.7 20.0 20.1 25.8 25.2 26.8 25.8 28.9 30.7 29.0 29.5 26.1 26.7 27.9 25.6 29.6 26.3 35.5 31.4 30.8 34.0 29.7 29.2 (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-20
TABLE C4X.2 MEAN QUARTERLY OSLO RESULTS FOR THE INNER RING, OUTER RING, OTHER AND CONTROL LOCATIOIM FOR DRES NUCLEAR POWER STATION 2813 RESULTS IN UNITS OF MREMWQUARTER A 2 STANDARD DEVIATION OF THE STATION DATA COLLECTION PERIODn INNER RING
- 2 A13 OUTER RING OTHER CONTROL PERIOD JAN-MAR APR-JUN JUL-SEP OCT-DEC 31.2 t 4.6 27.4
- 4.8 33.3
- 4.9 29.9
- 5.4 30.7'15.1' 27.2
- 5.6 32.3
- 6.7 28.9
- 52 31.3 t*4.6 27.7
- 5.1 32.9
- 5.1 29.8
- 5.3 29.0
- 0.6 26.6 t 5.5 30.3 t 8.1 26.5
- 0.8 TABLE C-IX.3 LOCATION
SUMMARY
OF THE ANuIOfl DOSIMETRYRoGRA~R FOR DRP NUJCLEAR ISTAIOqM1 RESULTS IN UNITS OF MLEotbUARTER SAMPLES PERIOD PERIOD..
PER.OD MEAN ANALYZED MINImU MAXIMUM -
t2 8.D,0 INNER RING OUTER RING OTHER CONTROL 136 22.9 125 22.6 es 24.2 8
24.6 38.7 37.7 37.4 33.1 30.4 a16.5 29.7 a 6.6 30.4 :k 6.3 28.1 **5.1 INNER RING STATIONS 101-1,0-101-2, D-102-1, 0.102-2, 0.103-1,0.103-2, 0.104-., 0.104-2, 0.105.
-105-2, 0.106-1, 0.40&2, 0.107-1. 0.107-2, 0.108-1.
0.105-2. 010-1, 0-109-2, 0.110-3, 0-110.4, 0-111-1.0-11-2, 0.112A-1, 0.112A-2. 0.113-1, 0.113-2, 0.114-1,0.114-2, 0.15-1, 0-115.2. 0.116-1, 0.116-2, 0.D661. 0.58-2 OUTER RING STATIONS - 0.201-1.0.201-2, 0.202-1, 0.202-2,0.203-1, 0.2032, 0.204-1, 0.204-2, D-205-1, 0.205-2, D-205-1, 0.206-2,0.207-1,0.207-2,0.206-1, 0-208-2, i-206-1, 0.209-2, 0.210-1, 0.210-2, 0.2111-1, 0-211-2, 0.212-3.10-212-4, D-213-1, D-213-2, 0.214-1, 0.214.2, 0.215-1.0-216-2.
t26-1, 0-216-2 OTHER STATIONS - D-01-1, DI-01-2, D-02-1, 0.02-2 0.03-1.0403-2, 0.04-1, 0.04.2, 0.07-1.0D07-2,0.08-1,.-08-2, 0.10-1, D-10-2.0.14-1, 014-2, D-45-1,0.45-2, 0-3-1. 0, ", D-4551.0.55-2,0 6-1,0-6-2 CONTROL STATIONS 12-1, 0-12-2 C-21
FIGURE C-t SURFACE WATER -GROSS BETA - STATION D42 (C) COLLECTED IN THE VICINITY OF DNPS, 2000 -2013 D42 (C) Oe nusier at WIN Road 16 14 12 10 6
4 2
0 01-28.00 11-10-02 08-23-05 06-08-06 03-19-11 12-30-13 DUETO VENDOR CHANGE IN 2005. ' VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MOC VALUES AFTER JULY 2005 C-22
FIGURE C-2 SURFACE WATER. GROSS BETA -STATION D.54 (C) and D47 (C)
COLLECTED IN THE VICMTY OF DNPS, 2003 - 2013 044(C) KWuhe Rver 14 12 10 6
4, 2
547f(C) KuV**R~yur* SN RW 32 20 24 20 16 12 8
4 01-12-11 0748.12 DUE TO VENDOR CHANGE IN 2005. < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY 2005 D-64 LOCATION REMOVED FROM PROGRAM JUNE 28.2007 AND REPLACED WITH 047 C-23
FIGURE C4 SURFACE WATER - GROSS BETA - STATIONS 021 and 041 COLLECTED IN THE VICINITY OF DS 2000 -2013 001 Iwlofs Ruvr a am lem 30-25 20 10.o 0-04-27-07 08-27-06 12-28.08 04-30-11 12-31-13 "4 Duusdw Lack & OMm 12 10 8
4 2
0 L 01-28-00 08-2-01 03-31-03 10-30.04 08-01-06 01-141.08 D-21 PLACED INTO SERVICE ON MARCH 30, 2007., REPLACED 041 D-61 LOCATION REMOVED FROM PROGRAM JUNE 29,2007 AND REPLACED WITH D-21 C-24
FIGURE C.4 SURFACE WATER - TRITIUM. STATION D42 (C) COLLECTED IN THE VICINITY OF DNPS, 2000. 2013 D02 (COf PlMMs River at Will Road 600 400 300 200 100 0 4-03-31-0 12-30.02 09-2Mw05 06-29"06 03-30-11 12-28-13 DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY 2005 C-25
FIGUME C4 SURFACE WATER - TRITIU
" STATMON 0D44 (C) AND D47 (C) COLLECTED IN THE VICINITY OF DNPS, 2003 - 2013 0-44 (C) Kalake River 800 TOO 600 5OO 300 200-100-0 03-28-03 02-03.04 12-11-04 10.1i.06 08-27-06 07-0-07 Locatien
-oimd l
3wrWwd Stmw (BD-t0) 7M0O 5000 400=
30=0 1000 0 4-2W:.
12-20-0 02-21-08 04-24-09 06-28-10 08-28-11 10-29-12 12-31-13 DUE TO VENDOR CHANGE IN 200, c VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY 2006 D-57 NEW STATION JULY 24.2006. REPLACED 0-.4 ON JUNE 28, 2007 C-26
F-UE C4 SURFACE WATER-TRITAUM - STATION 0621 and 041 COLLECTED IN THE VICINITY OF DNP, 20W - 2013 041 ranes Riwv*V.JS*Wp 700 300 0
06.9.0 10-1".0 0203-10 05-4-1 09.1-12 12,29.13 041 ONSSLO*&Oui 2OO0 1800 1600-1400 1200 1000 4W0 2W0 0-03-140 10-18-01 11-2344 06-12-0 D-21 REPLACED 0-51 JUNE 29. 2007 D-51 LOCATION REMOVED FROM PROGRAM JUNE 29,2007 AND REPLACED WITH 0-21 C-27
FIGURE C-7 GROUND WATER - TRITIUM! - STATIONS 0-23 and D45 COLLECTED IN THE VICINITY OF ONP, 2000 - 2013 m43 Thomon WoW 1000 200.
DIU"dM9tAA and un 400.
350-300 250 200 150 100 50 0.--
014--00 10-25.02 05-11-06 05-28.0" 03-15-11 12-30 DUE TO VENDOR CHANGE IN 2005, < VALUES ARE LLD VALUES JANUARY THROUGH JUNE 2005 AND MDC VALUES AFTER JULY 2008 C-28
FIGURE C4 AIR PARTICULATES - GROSS BETA - STATIONS 0-01 *W D.02 COLLECTED IN THE VIClMMY OF ONP, 2000 - 2013 0.41 Ohms Iumo I 40.01 11 I
I 30.0, 20.0.
II *11 10.0 1 1 NjV
.Z 0.0 01-08-00 10a.02 08-13-05 06.31.0.
03-9*.11 01-04-14 042 nsft. Smui I
I 50.0 40.0 30.0 20.0
'10.0 0.*0*--
014*6-102"-02 08-13.05 06-31-08 03-19-11 01-04-14 D-02 No samples; powr was ralWe an 00-16-06.
C-29
FIGURE C4 AIR PARTICULATE$ -GROSS BETA - STAT1ONS 043 and 044 COLLECTED IN THE VICINITY OF DNPS, 2000 - 2013
.osSoSISIMIS 60.0 50.0 I
40.0 30.0 20.0 10.0 0.0 4-01-0800 10-26.02 06.13-05 06-31-08 03-19-11 01-04W14 046 CoWs. ftu en MUon Prouuly I,
50.0 40.0 30.0 20.0 10.0 0.0 4-01408-00 01-04-14 c-so
FIGURE C-10 AIR PARTICULATES - GROS BETA -STATIONS D-07 and D-12 (C) COLLECTED IN THE VICINITY OF DNP, 2000 -2013 DsP Cluy PlpilcU OlammtfIld,",e I
120.0 110.0 100.0 00.0 80.0 70.0 00.0 60.0 40.0 30.0 20.0 10.0 0.0 01-06-00 10-25-02 08-13-05 05-3108 03-10-11 014M-14 D-12 (C), QWWi ft",
WkN I
80.0 70.0 0O.0 50.0 40.0 30.0 20.0 10.0 0.0 014840 10-26-02 06-13-05 05.31-08 06-10-11 01-04-14 C-31
FIGURE C-1i AIR PARTICULATES -GROS BETA - STATIONS 045 and D-3 COLLECTED IN THE VICINITY OF ONPI, 2000 - 2013 0-45 MW ley Woods Road, ChanMon I
U 70.0 60.0 50.0 40.0 30.0 20.0 10.0 0.0 01.08"0 10-2-02 08-13-05 05-31.8 03-19-11 01-04-14 D4SUV~ininlkoho1w I
0.0 i i
i 014)6-00 10-26.0 08-13-05 05-31-08 08-19-11 01-04-14 C-32
FIGURE C-42 AIR PARTICULATES - GROSS BETA - STATIONS 046 and 0-10 COLLECTED IN THE VICINITY OF ONPS, 2006 - 2013 70.0 60.0 0.00 200 "ftWWMW*ftLW*fP 60.0 v 60.01 I
40.0 30.0.
200-0.0 01-0745 10-25-06 08.11-06 06-29-10 03-16-12 12-31-13 C43
FIGURE C-IS AIR PARTICULATES - GROSS BETA - STATMON 04I3 and D414 COLLECTED IN THE VICINITY OF DNPS, 2006 - 2013 0-15 Minoclw 50.0 40.0 130.0 20.0 Y.*,
0.0 i
01-7-06 0747-06 01544,06 07.0446 01-0147 07-01-07 D.14 C~U8r'u, ChVhumNm 60.0 40.0-S20.o0:
k 10.0 0.0. 4-,
01407.
10-25-06 "06-11-0 05-29-10 03-16-12 12-31-13 0-13 TAKEN OUT OF SERVICE JUNE 29.2007 AND REPLACED WITH 0-56 C-34
FIGURE C-14 AIR PARTICULATIES -GROSS BETA - STATIONS D-0 and D.U COLLECTED IN THE VICINITY OF DNPS, 2006t2613 70.0 00.0,
60.0 30.0 20.0.
- 4a A
U
.m 0
m0mW UMb9 h 60.0 40.0 30.0 ja2o.o 20.0 10.0 0.0 4-07-25"08 01-20"0S 07-17.09 01-12-11 074&9-12 01-04-14 0-55 NEW STATION DECEMBER 30, 2005 REPI.ACED D-13 JUNE 20,2007 D-56 NEW STATION JULY 25,2008 C-35
FIGURE C-1S AIR PARTICULATES - GROSS BETA - STATION D48 COLLECTED IN THE VICINITY OF DNPI, 2011-2013 0.8 WmI Rawa Mmama 60.0 50.0 I
40.0 30.0 20.0 10.0 0.0 06-03-11 12-09-11 06-16-12 12-21-12 06-28-13 01-03-14 w~ ~~'"
cc' D-48 NEW STATION IN MAY OF 2011 C-36
APPENDIX D INTER-LABORATORY COMPARISON PROGRAM
Jnlsntionaly left blank
TAN.A D-1 ANALYTI R
4Y1R0lMENlTAL OAACI'Y C
CHECK PROGRM IPAM0 iOPF 2 ld~fi~fO~tl~flROPMWti Known mm0 (q)
MwOfthear Nm~be Ofti Unbs~ Value e)Value (b m8Jna~thru Evaluation (d)
March 2013 E10477 E10478 E10480 E10479 E110481 Mm Sr-GO 1-131.
C4.141 Cr461 Cs-134 Ca-I 37 Co."O AP 03.141 Ce-134 Ce-137 W-45 Charcoal 1-1311 sr-so Milk 1-131i Ce-141 Ca-I 37 0348e Ue-54 AP 03.141 Cr-SI Ce-134 C*4I37 CO-M.
Zn-9 0.490 Charcoal 1-131, PCUL PCUL PCUL PalL PM pm PaK PCVI pai 120 99.7 9.21 11.0 87.1 100 16 187 463 472 201 214 262 266 200 208 215 208 266 252 311 301 364 400 96.3 95.86 264 241 123 108 142 136 112 108 115 106 139 129 163 153 212 204 90.1 92.6 Pa/L 1640 180 1.20 0.84 0.07 0.90 0.96 0.94 0.98 0.96 1.03 1.06 1.03 0.96 1.00 1.10 1.13 1.04 1.06 1.08 1.08 1.07 1.04 0.97 0.97 1.16 0.93 0.97 0.92 1.01 0.94 0.95 0.93 0.90 1.04 1.01 0.97 1.00 1.07 1.09 1.07 1.06 1.16 1.14 1.24 1.05 0.96 A
A A
A A
,4A A
A A
A A
A A
A A
A A
A A
A A
A June 2013 E10M4 610545 E10547 E10546 pC&L 110 PCUL 16.6 pCUL 92.6 PalL 631 pOOL 253 palL lie pCUL 143
,/L 67.1 CUL 171 pan.
125 pCUL 220 pCUL 169 PCI 56.8
- pCi Ift pI 86.2 pa lot pCa 62.7 pa 125 pa 85.7 pa 116 pCl 86.5 Is.0 17.0 95.6 90.4 250 125 151 94.0 172 120 217 175 50.7 157 78.4 94.6 56.9 108 75.0 136 1-10 69.7 A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A w
A A
TABLE D-1 ANMLYTh EMV1Ot4MMNTAL RAOOOACTIVfVY CROM CHECK PROW"A TELEOWI SNOW 21"NRWG S
(PAW lOF 31 M
Nwnber-Mdtril Vau nw
- -W
-iU E l at.n MonUh*'ear I-Nwfter....
Moft__ NudI.....
LfJntt
.vwwlu(4 a)
V OA () _IJEAovi vlao June 2013 E10549 Water Fe-OS 8eptsmber 2013 E10648 E10647 E10672 Milk Mik Sr-69 Sr-90 1-131 Ce-141 Cr-41 Cs-134 Cs-137 Co-Os Fe-SB Zn.6 Co-80 PCiUL 1610 1610 PC.L 83.9 96.0 pCi/L 8.88 13.2 PCI/I PCUL pCI/I PCI/I PCl/L POCL PCI/I PcI/I PCI/L PObL PaI PCI PCA PCI pCa PCA PCI pCI POI 93.9 96.3 272 180 125 105 136 125 264 187 208 143 106 97.0 116 99.6 219 166 277 172 131 108 139 130 268 196 223 139 105 86.5 112 105 214 18 AP Ce-141 Cr-SI C@-134 Ca-137 Mn-S4 Fe-SO Charcoal 1-131 Weter Fe.SO E10648 E10673 PCI 76.3 71.7 pC/
1790 1690 pCOL 97.3 03.8 P
13.3 12.0 1.00 0.67 0.67 0.96 0.98 0.87 0.95 0.97 0.99 0.98 0.90 0.96 0.93 1.03 1.01 1.12 1.04 0.94 1.02 1.05 1.06 1.06 1.04 1.03 0.93 0.91 1.00 0.91 1.00 1.04 0.99 1.06 1.02 0.96 0.97 1.17 1.08 1.01 0.94 0.98 1.14 0.85 1.00 N(1)
N (i)
A NA (2)
A A
A A
A A
A A
NAA(2)
A A
A A
A A
A A
A Deoember20113 E10774 E110776 E107"?
Milk Sr-.6 Sr-SO 1-131 Ce-141 Cr-SI Cs-134 Co-137 Co-se Mh64 Fc-So Co.S0 PCI/I PCI/t PCI/I PCI/I PCI/I pCI/I pGI/L PCI/I PCI/I PCUL pCI pCI Pei pci pCI PcI pci 89.7 99.8 297 129 126 116 167 117 757 141 85.1 278 123 102 84.4 132 101 o6o 118 96.1 110 297 142 126 112 16s 110 741 147 88.0 238 114 101 89.9 136 88.3 595 118 AP Ce-141 Cr-51 CS-134 Co-137 Co-S8 Mn-54 Fe-S9 Zn-65 Co-60 D-2
TAKLE 0-1 ANALYT"CS RNMV RAOIOACMITY CRMS CHECK PROGRA TELSONWOR0 WNIoUhEMMGa3
""$GPM03 Id~filfl@tl~i epofWm xnon RtOO (a)
MonhiV~w Na gbe Mar Nuclide Unis Value (a) VoAlue(b IpEAJsftc Evetution (d)
December2013 E10776 E10778 Carcoal 1-131 Waist FP.l pCi 84.7 80.5 PCA 2010 1910 1.05
.'1.05 A
A (1)
(c)
(C)
UffitSr-8R90- hvfAmwaa~
f~ was ffvfN mp !w~agms6 ss byv~t wNOR13-18 The solv~e was not~a spo ~bCo141.
The AAn*at Imaw vat* Is sWlo 1W of te pow~mo pessatiiin ft smoed~ibyuu,*I~emx I Vom~mfmoasnnm n~dN6 0-A do dog OF AnW$t sv~akmfn baed on TUE blwat OC Oft A&Aor*staW. roqWIodmtab WI m~owt okfOLOO>01.20.
IAcvspftW~b
.whyiafg uedDStU.~O~O~f2.
N
- ItAcmaptabb uos,.as"il
~iV
?d D.3
TAmE 04 IRA eNVIRONMENTAL RADOOACMVOY CROSN CHMCK PROGRAM
?WLISYWO OWN BEiNG. 201$3
.t kunfcaon po(a) V
- A* cepta
.E....
May 2013 RA0D43 MRAD-18 Water Sr-69 Sr-90 50-133 CI-134 Or-B 1-131 U440 W.!3 Filr Or-A Sr-9O Dw133 CW-134 Calt37 Co40 Zn45 Or-A Or-S
!..131 U46t W4.3 FlW Or-A pCI/L 4.3 CY 19.3 pCItL 61.9 PC)I.
40.9 PCUA 44.0 pCUI 61.9 VCMI 202 pCIL 34.2 PCI/I.
18.0 pCI/I.
23.6 pCIt.
60.4 pCI/.
3970 PCIl Lost durin proceang 41.3 31.6-48.4 23.9 17.2 - 28.0 82.1 69.0-90.3 42.0 34.2 -47.1 41.7 37.0 - 48:'
66.9 59.3-75.0 160 170-222 40.8 21.1-51.9 21.6 13.0-29.7 23.8 19.7 -28.3 61.2 49.6-67.9 4050 3460-4460 A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A A
November2013 RAD-4 MRAD-19 pCiA.
25.6 pCVI 14.3 pCV 6
57.2 pCM.
63.3 pCVL 201 pCVL 104 PCIL 361 PCUL 29.5 pCIU.
30.1
-OM/
23.1 SpCI/.
6.531 pC~U 33.0 21.9 16.1 54.2 86.7 206 102 333 42.8 32.2 23.6 6.24 17700 14.4-28.2 12.6-21.6 44.7-59.9 71.1-95.4 166-226 91.8-114 300-369 22.2-54.3 20.8-39.9 19.6-28.0 4.70-7.44 1500- 19500 83.0 27.8-129 (b) Th. ERA IWm ft o to 10% of ft0spwn*
p wIin mf ftndW a d"U,
byn*MftnWi (C) ERA ovauan:-
A-acoqeab.
Ropwbd mOWS stfs wf g KW" OWLgIM MA,,not a t5ab/e.
R rwfoe m
ftm oi*dUvI Ocon GE,,finck * *b-n.
Rqood*meusw Sin wflMW Mew ConieJm endouei of Mae WwTag/UM*
D-4
TAIE D.3 0018 MOME MNALYTER PERFOUMNCE SVALUATMO PROGRAN (MAPIP)
TEM~le xafE SMMUONER6,31 "Ple 10I tdenflctlo Raofted --KNOW AcCiepitan Month/Year Number Modias Icd Unjt Val (a) Value (b Ramse Evaluaton (c March 2013 13-MWW29 13-GIW2S 13-M48W 13.RdF28 Water Cs-134 Cs-17 Co-57 Co.00 K-40' Sr-90 Zn4S WaSW Gr-A-Gr-B So01 004I34 Cs-437 co-sT K-40 Sr4O0 zn465 13-GeF28 1349M AP Cs-134 Cs-137 0o.00 C*40 Zn-45 AP Gr-A Gr.8 Vegaton Cs-134 Cs-t37 Co.07 Co.65 Sr-SO ZPAS W@ta Cs--134 Cs-@37 Co-57 Co.60
'4-3 Mn-54 K-40 Sr-g0 Zn45 Water Gr-A Or-B Sq/L 21.0 24.4 Sq/.
0.0446 8q&.
28.3 30.9 18.2 19.586 Sq/.:
50s 607 SqI.
26.7 27A Sq/.
2.09 Sq/.'
10.6 10.6 q/IL 29.2 30.4 SBq/.
2.74 2.31 SOqI.
15.6 13.0 Sq/k 859 687 SBqf 633 567 S/g 0.=5 736 691 sq/kg 0.671.
Bq/kg 714 626.3 Sq/kg 442 628 S
1057 99 Sq/sample 1.73 1.78 SQsinmple 2.73 2.0 S/smpe 2.38 2.38 q/aIple 0.0302
&$W"epl 4.36 4.26 Bq/amnple 1.43 1.49 Bq/sample 3.14 3.13 Sqsmple 0.767 1.20 Bq,/mple 0.871 0.85
/mple
.0.107 Sqftwaple 7.39 8.87 S/ample 9.87 8.66 Sq/swam 6.06 5.85 Sq/smple 40.0104 Bq/smple 1.28 1.64 BSq/ample 6.84 6.26 W
29.1 30.0 ISq/.
34.5 31.6 q/.L 0.0358 Sq/I 24.6 23.568 Bq/L 2.45 Sq/.
0.0337 Sq/.
0.193 q/.L 9.12 7.22 Sq/L 38.1 34.6 Sq/I.
1.13 0.701 Wq/I 7.61 5.94 17.1 -31.7
.(1) 21.6-40.2 13.89 -26.43 355-659 19.2 - 35.6 (1) 7.4-13.7 21.3-39.6 0.69 - 3.93 6.6-19.5 621 - 1153 41.1-763 (1) 484-896 437.7-812.9 440-816 697-1204 1.25 -2.31 1.62-3.38 1.65 -3.07
- ()
2.6-65.54 1.04-1.94 2.19-4.07 0.36-2.04 0.43-1.26 (1) 4.81 -8.93 6.08-11.28 4.10- 7.61 (1) 1.16-2.13 4.38-8.13 21.0- 39.0 22.1-41.1 (1) 16.61 - 30.65 (1)
(1)
(1) 5.05-9.39 24.2 -45.0 0.210 -1.192 2.97 -8.91 A
A A
A A
A A
A A
A.
A A
A A
A A
A A
W A
A A
A A
A A
A A
A A
A A
A A
W A
A A
A A
A A
A W
A A
A September 2013 13-MNW2 13.-fW29 D-s
TAMAE D4 DOOS MWISO ANALY.S PEPOANCE IVALUATIOM PROOGRM (MAPEP)
IM*ROW" a Im l~m ms5 RepOfttd KNOW tI 3M Value m Value eB*
R no*
Evaluation I I&~lhivor Idmha Uadle i
September 2013 134MaS29 son Cs-134 Sqflg 1150 1172 CS-137 aft/k 1100 97?
Co-57 oqf 670 C430 Sqlkg 602 481 Mn-54 Sqk 758 674 K-40 8Sqt 796 633 S-r0 fq" 664 460 Zn-U45 9qlk 210 13M-dF29 13-GF29 134WM AP CS-134 CO-137 Co-67 W.40 Sr-S0 Zn4S AP Gr.A Gr-B Vegeta Cs-134 C84137 Co-G7 8r-4 zn-Os qlswnale
-0.570 Bq/amnple 2.85 2.7 Sq/mple 3.30 3.4 Sq/ample 2.41 2.3 Sqsmpe 3.65 3.5 Bq/ample 1.40 1.81 Sq/ample 2.90 2.7 Bq/ample 0.872 0.9 Sq/ample 1.67 1.63 Sqsmple 5.29 520 Sqfsmple 7.48 6.60 Bq/Wample 0.0129 Bq/eutpl 0.0623 Bqampne 8.78 7.88 q/sample 1.6 2.32 Sq/smple 3.18 2.63 820-1524 684-1270 (1) 316 - 686 472-876 443-823 322-SM8 (1)
(1) 1.9 - 3.5 2.4-4.4 1.6 - 3.0 2.5-4.6 1.27 -2.35 1.9-3.5 0.3-1.5 0.82-2.45 3.64 -6.76 4.62 -858 (t)
(1)
&.52-10.24 1.62-3.02 1.84-3.42 A
A N (2)
A A
w N (2)
N (2)
N (2)
A A
A Aw A
A A
A A
A A
A w
(I) FpoW PC&"s (2) Sat Co.57 £Zn S Wsbygmwsm vmmnot At4P5Pma~da~astebi*
K f
po*
te A tpcmombu of Eu-152 we*s *ibad n U il le minig bObmun h mM I
Gerrn a u
uMb oe Unm
- dIna a nWt l-cs IAP t
W Alw did ns to ewfnoer dsruWomnuU NCR 1W4 l StO
& kn mo*ut s e
wo m bd to AMPE. AcW nm*wto 332
APEPrvaAmfd Uh..4 STOa U9Wfd mpovs bit.DN dnW auw'ps weom M c by M sema' NCR 1W Vogeteftn SrS0 - Ii aps~mW fta UscesweawwWb;
,ae
&WOW
-' iAeqpe ewaih~gnN1* aw a M~obU~a
- NLCR 1Wf
()Ttjr&*amDwuEnqkinsdng#W mwAtUeh
()The M4PEP~ammw~i vM qsWtoIOOU E thp~wiuivposwth Uwrna~nwaswmiO bypAmluela@dW (c) DOEAMPEP vakmdo Awaoopahda bWhamepffi
- 0~ wan*9 Nw
?Jmocemaab D-6
APPENDIX E ERRATA DATA
iftnftlohly left blan
Due to an Incorrect setting on gamma detector 0C, 3.29 rather tna 4.66 was used in fte MDC calculatIon. Nonconfomisnoe 13-07 was initiated and corrective actions have been implemftd to address this issue. AN samples counted on detector 08 were repwoessed using the correct calculation. As a result, all MDCs for these samples have Increased by 41.6%. The previously reported activities and uncertaintles were not affected. In some cames, the increased MDC resulted in missed LL.
All samples with MDC* affected by this Issue are listed below. The samples with missed LLDs are shown in the tble for 2011, 2012, and 2013. All other required LLDs wre met.
&I
2011 I START I END I
J RQUMRD REVISED CLIENTIP DATE mo3 AARXmoD
.c~
f~
.40110D.02 I
W30/11 I 1I3OW1I I AirPoeltictuts 14011DW.5 I 0t30/I I 12=1i I IAirPaticulate r T___
- Required LLDs were achieed.
E-2
2012 START END REQUIRED REVtSED CUENT 10 DATE DATE MATRIX
,N PE MOC MDC uNMrs 1Q12D-12 12/30/11 03/30,12 Aiiculate 1012 D-45 12130/11 03130/12 AWr PaitUlIM 1Q120-55 12/30111 03/30/12 ArParicult 435
/13.12 01/13112 GroundWatw 1-131 415
<17.1 Rc, 0.35 01/13/12 01113/2 L &40
<16 s15.29 0-67 01127112 02/24/12 SuwfaWater s
D-25 03/01/12 03/01/12 Milk mD tV-loN-11es 0320/12 03r212 ROM 2Q12 0-07 03/30/12 06/29/12 AlrParticulate D-23 05/11/12 05/11/12 Ground WaW 1-131
-15
<1i g/L D-23
'51112 06/11112 Gmund Water La-140
-15
<15.2 OC/L 0-26 06/17/12 05/17/12 Milk 0N-SW-DN-103 06/21112 0621112 RGPP 1-131
-15,
<21.08
/
DINMW4)WN116I 05/23/12 05123112 RGPP 1-131
<15
<19.63 pCU.
DN-OSP-107 06129/12 _
j2 RGPP O
-0N-101.,...
069/12 05129/12 RGPP 1-131 015
.18.658 C/L NwS4DN11*s O1012 o6 2
RGPP 1-131
<15 4919.87 ICR DN-DSP-132 06106/12 08012 RQPP 1-131
<15
<21.14 1CUL 0-25
,0/26/12 o6r26/12 Milk t C
3012 D-48 06/29/12 09/26/12 Air Particut 3012 06/29/12 09/26/12 Air Paii*cut C
0-25 07/13/12 07/13M2 Mk La-&40 015
<10.43 R-25 08/0912 06/09/12 Wk C
DN-SW-DN,1161 06/22/12 0822112 RGPP 1-131 015
'16.6 DCUL DN-OSP-107 08/27112 08/27/12 RGPP 1-131
<15
<19.14 D-25 09/06/12 09/06/12 Milk D-CONTROL Po) 09/16/12 09/16/12 V
t D-QUAD 3 mew) 09/22/12 09/22/12 Vegetailon C
C 4012 D-02 12 I 12/8/12 Air Partlcukfte C
,412 0-66 09/26/12 12/26/12 Air Partculate C
C 0-25 10/18/12 10/18/12 MRi La-140
<15
<1627 pC/L DN-MW.DN-1081 10/23/12 10/23/12 RGPP 1-131
-15
<21.2 oCi/L DN-W
-1081 10123112 10/23/12 ROPP La-140
'15
<20.36 pCi/L ON-DSP-108 10/24/12 10/24/12 RGPP 1-131
<15
<17.93 pci/L DN-DSP-108 10/24/12 10/24/12 RGPP La-140
<15
<18.69 PCVL D-67 10/26/12 11/30/12 SurfaceWate C
C DN-MW-DN-124S 1030/,12 1,0/0/12 Ground Water 1-131
-16
<17.16 pCVL D-25 11/01/12 11/01/12 Milk La-140 015
<17.01 pCi/L
- Required LLDs were achieved.
E-3
2012 START END REQUIRED REVISED CLIENT ID D.:E DATE MATRIX NUCLIDE MC
, MDC UNITS 0-21 11/30/12 12M20/12 SurfmWturW 1-131 "15 s 19.04 CI.,
D-21 11/30/12 12/28/12 Surfbc.Watsr La-140 015
'17.67
,/.
D-25 12/07/12 12/07/12 Milk IWN-)N-141 12J21/12 1201t12 RP1-431
<l1.
-40.06.
PCYL
- Required. U-s were achieved.
E-4
2013 START END IREQUIRED RISED GLIENT ID DATE
... PAIRT MATRIX NU*CUDE'
- AMC, MDC LUNTS D-25 01/04/13 010413 01043 Mk LO-140
-cis
<16.26____
0-25 03107/13 10/07/13 Milk "Required LLDs were ghieved.
anw spo
, let blan
- ~
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t A
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- ~Jr 4~i~.2 7
APPENWIX F ANNUAL RADIOLOGICAL GROUNDWATER PROTECTION PROGRAM REPORT (ARGPPR)
- F
- .tf a*
,,,tblan
- 7. ~*.
Docket Mo 510 20-37
"-249 DRESDEN NUCLEAR POWER STATION UNITS 1, 2 and 3 Annual Radiological Groundwater Protecion Program Report 1 January Through 31 December 2013 Prepared By Teledyne Brown Engineering Environmental Services E~e1on
+/-
Dresden Nuclear Pow Strion MOMns, IL 60450 May 2014
Intmn~ I0 blmw*
Table of Contents I. Summary and Conclusons..............................................................................................
1 II. Introduction.....................................................................................................................
2 A. Objctiv of the RGPP.................................................................................
3
.8. ImplementtMM of n
t Objectivs.................................................................
4 C. ProramD SCp 4
D. C
- erw of-Tr m (-
ý
..... 4 I. Program Descripon......................................................................................................
5 A. Sample A ly 5
B. D ata i r on...............................................................................................
8 C. Sac ground Ana 7
- 1. Backgroun Concentratro of Tritium................................................
7 IV. Results and Discussionrt..................................................
9 A. Groundwater Re**ts....................................................................................
9 B. Surface Water esft.......
11 C. PrecIpitma onW ssiwim s...............................
- 0. Dr"ng W e We# survey.........................................................................
12 E. Summary of Resuls - Intraborato C
program............
........ 12 F. Leaks, Spills, and Releases.
12 G. Trn..........................................
12 H. Inesg o 12 I. Action T*. n........................................
Act.ions*
a.ken
-i-
Appendices ARGPPR Appendix A Tab.
Table A..1 Location Designation Radiological roundwater Protection Program -.Sampling Locations, Distance and Direction, Dresden Nuclear Power Station, 2013 vaum Secuity-Related Inforuaion:- Maps of the;Dresden Nuclear Power Station have been withheld from public disclosure under 10CFR2.390 and N.J.S.A. 47:IA-1.1 A
ARGPPR Appendix B Data Tables Table sI.1 Concentations of Tritium, Strontium, Gross Alpha an:,
Gross Beta in Groundwater Samples Collected in the V.cinity of Dresden Nuclear Power Station, 2013.
Table B-4.2 Concentrations of Gamma Emitters in Grondwaer Samples Collected in' the Vidrty of Dresden Nuclear Power Station, 2013..
Table 6-1.3 Concentrations of Hard-To-Detects in Groundwater Samples CoIecte4 In the Vicinity ofDreeden Nuclear Power Station, 2013.
Table 841.1 Concentrations of Tritium in Surface Water Samples C410olecd in the Vicinity of Dresden Nuclear Power Station, 2013.
Table 8-11.2 Concentrations of Gamma Emitters in Surface Water Samples Collected In the Vicinity of Dresden Nuclear Power Station, 2013..
Table B-Ill.1 Concentrai*ofs of Tritium in Precipitation -Water Samples Collected In the Vkiinity of Dresden Nuclear Power Station, 20137 0. '
4
- ii -
L
.Suiwny andCoceln Dresden Station is situated on approximately 600 acres of lanW that borders the Illinois River to the north and the Kankakes River to the east. This land Is referred to as the owner-controlled area. The Dresden power plant itself takes up a small parcel of the owner-controled area and Is surrounded by a Security fence. The security fence defines what is known as the ProtectedAAre (PA).
The Dresden power plant has experienced leaks from underground lines and spills from systems containing radioactive water over its 50 yew history. These iwfntshave created a number of areas of localized contamination within the PA. The liquid scintillation analyses of groundwater in many of these areas show measuable cocentrons of tritium (H-3).
Dresden participated in a flsetwide hydrogeologic iainduring te-summer of 2006 in an effort to charactei gundwar movement at each site. This-Invstigon also compiled a list ofhe histric spilsand leaks as well as a detailed analysis on groundwar hydrology for Dresden Nuce Genertion Station. ComiiMg the brtur concentration In a locally conteminated arms with the speed. and rection of groundwater in the vicinity can produce a contaminated, grounrw!1 plums projection. If the plume of contaminated gmundwater passes through the path of.a groundwater motring well, it can be anticipated that the tritiumconcenratin hi
.th weft will increase to some maximum concentration, then decrease over time.
The fleetwide Hydrogeologc In on Report (HiR) shows that goundwater movement on the Dresden site is wery slow. In addition, ther is a confing rock layer, the Maquoketa Shale layer, about 55 feet below the surface that impedes oundwater movement below this depth.
Dresden has a domestic water system that is supplied by two deep wells (1500 feet deep) that were installed about 50 years ago south of the PA. Samples taken from domestic water supply have never shown any detectable tritum carcentration.
Tritium has a halflife of 12.3 years. This means that 40yare from now 90% of the tritium on site today will havedecayed away to more stable elements. Given the limited volume of contaminated groundwater on site, radloacive decay, slow groundwater movement and dilution efffcts, the-condulsion of the HIR is-that the operation of Dresden Nuclear Power Station has no adversoradiological impact on the environment As a result there is little potential for contaminated groundwater on site to affect off-site drinking water.
111. - ktroduction Radloloaicat Groundwater Monltor9t ProaMm MRee):
Dresden has a Radiological Groundwater Monitoring Program (RGPP) that provides long-term monitoring intended to verify the fleet-wide hydrogeologic study conclusions.
Dresden uses deweoped groundwater wells and surface water sample points In the RGPP."
The Dresden RGPPws=established in 200 and them hae been no significant changes to-this program. This program does not impact theopeation of the plant and is independent of the REMP.-
Developed groundwate r
wells areelthat were Insalled specifically for monitoring groundwater. These wells are equipped with screens and are properly sealed near the surface to avoid surface water Intrusion. The wells were designed in accordance with appropriate codes and developed in accordance with appropriate standards and procedures. Dresden has;groudwaellr monioring wellsidentifiKd as "shallow" (depths from 15 to 35 et),-nmedftW (depths from 35 -to 55 fet) and "deep" (depths beyond 100 feet).,-.All wells installed to a depth greater then 100 feet ("deep" wells) were found to be dry and removed from the RGPP. Surface water sample points are ident sample-locatins In the station's canals and cooling pond.
There are 98 sampling poinitin the RGPP:
Dresden has 47 deIloped groundwater monitoing ellst within the Proed Ares (PA). Somewf thesewes form a ring just inside the security fence and the remaining wellswere installed rna underground plant system piping that contains, radioactive waer.
Dresden has 30 developed groundwater monitoring wells outside the PA the majority of which form a ring just within te perimeter of the property.
Dresden has 11 surface water monitorng locations on the owner-conVolled area sampled as part of theDresden RGPP.
Dresden Me 4.precipitation peter monitoring locations sampled as part of the Dresden RGPP.:.Anadditional 8 locations were studied in 2011 through 2012, but only 4 locations are currently permarnetly, a part of the RGPP program.
Dresden has, 6,sentinel wells..' These-wells are not constructured to code or developed to a standard. The majority of these wells are idle and only used for qualitativetroubleshooting.
"2-
The Dresden stespwfi RGPP procedure Identifies the historic 'event that would affect the individual RGPP sample results. This procedure identifies threshold values for each sample point, which If exceeded, could be an indication of a new spill from an above ground system or a new leak in an underground pipe containing tritiated water.
The RGPP sample points are currently sampled on a frequency determined by the well detection category in accordance with site document EN-DR-408-4160, Dresden RGPP Reference Material. During 2013, there were 578 analyses that were performed on 251 samples from 74 sampling points.
Sentinel Wells, sometimes referred to as "baby wells are wells that were installed to monitor local shallow groundwater; typically in associated with a historic underground pipe leak. These wells are not constructed to code or developed toe.,tandard, Most sentinel wells are from 6 to 12 feet deep and consist of 2" PVC pipe without screens.
These wells are categorized as idle wells and are used only for troubleshooting purposes.
Dresden has tw basic storm water runoff sewer systems within the PA: one storm-system routes to the east, then north and discharges into the Unit I intake canal, the second storm-system routes to the west, then north, through a large Oil/Water Separator and discharges to the hot canal. Both the Unit I intake canal and the hot canal eventually route to the cooling pond. The Dresden Station RGPP has eight RGPP surface water sampling points to monitor these sysms.
A.
Objectives of the RGPP The Objective of the RGPP is to provide long-term monitoring intended to verify the fleet-wide hydrogeologic study conclusions. The objective of the site-specifi RGPP is to provide indication of shot-term changes to groundwater trtium con tations within the PA.
If isotopic results of groundwater samples exceed the thresholds specified in this procedure it could be an indication of a new spill from an above ground system or a new leak in an underground pipe containing Vitiated water.
Specific Objectives include:
- 1.
Perform routine water sampling and radiological analysis of watW from selected locations.
- 2.
Report new leaks, spills, or other detections with potential radiological significance to stakeholders in a timely manner.
- 3.
Regularly assess analytical results to identify adverse trends.
"3-
- 3.
Take necessary correc* e actions to protect groundwater resources.
B.
Imnplementatim of the Objetves
.J, Dresden Nuclear Power Station will conlinue to perform routine sampling and radiologcl analysis of water from selected locationts 2..
-Dresden Nuclear Power StaWn ho implemented procedures to identify end re' W ornewleaks, spills, or ote detections wih-potential radiological
.'sin~ficance in' a timely nmaner.
- 3.
Dresden Nuclear Power Station staff and consulting hydrogeologist assessanlytcal results on an ongoing bains to Identfy adverse trends.
- 4.
If an adverse trend In groundmwae onit~orin analytical results is ide d, further I aon wI be u en: If the neao n
Identifies a leak or unideniid spit.cor actions will be Implemented.
C.
Program esciption Drsden al Groundwaer Monitorin Program (RGPP) that' Povi ornq4m moaaft k
ded to ve*
th fleet-wide hydrogeologic study conclusions. Drosden tomw 8 developied groundwater web and surface water sample oints In ft RGPP.
1.... SampleCollection Sample locations can be found in Table A-1, Appendix A.
Water samples are collected in accordance with the schedule delineated in the Dresden site-specific RGPP procedures.
S Analytical laboratories are suboj to Internal quality assurance S
-programs, industy croesoeck-programs, as well as nuclear industry sudit.. Station peonnel. reviw and evaluate the analytical results.
D.
Charctrmstics of-.Tritium (H.-3)
Tritium (chemical symbol-H-3) is a radioactive isotope of hydrogen. The most common form of tritium is tritium oxide, which is also called "tVitiated water." The chemical properties of tritMum am esmmetilly those of ordinary hydrogen.
Tritiated water behaves the same as ordinary water in both the environment and the body. Tritium can be taken into the body by drinking water, breathing air, eating food, or absorption through skin. Once tritium enters the body, it dsperse quickly and Is uniformly distributed throughout the body. Tritium is excreted primarily through urine with a clearance rate characti zed by an effective biological half-life of about 14 days. Within one month or so after ingestion, essentially all tritium Is cleared. Organically bound tritium (tritlum that Is incorporated in organic compounds) can remain in the body. for a longer period.
Tritium is produced naturally in the upper atmosphere when cosmic rays strike air molecules. Tritium isalso protuced during nudles( wmpons explosions, as a by-product in reactors producing electricity and In special production reactors, where the isotopes lithium-7 and/or boron-lO are activated to produce tritium.
Like normal water, tritiated water Is colorless and odorless. Tritlated water behaves chemically and physically like non-tritlated water in the subsurface and therefore tritiated water will travel at the same velocity as the average groundwater velocity.
Tritium has a half-lif of approdmately 12.3 years It decayspottamoousiy to hellum-3 (31H.). This radioactive decay rolee a beta pulft (low1n1rgy electron). The radioactive decay of tritium Is the wota of the heMlth risk from exposure to tritium. Tritium emit very weak radiatio Od leavethe body ' -
relatively quickly. Since tritium is almost always found as water it goes directly into soft tissues and orgns. The associated dose to them tissues Is gonerally uniform and is dependent on the water conrte of the specfi tissue.
UL Progrm DesPUion A.
Sample Analysis This section describes the general analytical metoologies Wued by Teledyne Brown Engineers (TBE) to analyge the environmental samplfs for radioe*t1ty for the Dresden Nuclear Power Station RGPP in 2013.
In order to achieve the stated objectives, the cuttfet program includes the following analyses:
- 1.
Concentrations of gamma emitters in grotndwOs. and surface water.
- 2.
Concentrations of strontium in groundwater.
- 3.
Concentrations of tritlum in groundwater, surface water and precipitation weter..
- 4.
Concentrt0ons of gross alpha and gross beta In groundwater.
- 5.
Concentrations of Am-241 in groundwater.
- 6.
Concntmaons of Cm-242 and Cm-243/244 in groundwater.
- 7.
Concentrations of Pu-238 and Pu-2391240 In groundwater.
- 8.
Concentations of U-2331234, U-235 and U-238 in groundwater.
- 9.
Concentrations of Fe-55 in groundwater.
- 10.
Concentrations of N1.63 in grudwatr.
B.
Data Interdfaion Ills radiogical data collected prior to Dresden Nuclea Power Station becoming operational wet9 used as a basel with which thes operaionl~date were compared. For the purpose of this report, Dresden Nuclear Power Station was cseredoperationalt initialcrtclity. Severa factors waee I ttn t Imtn the interptation of the data:-
- 1. -LK M iQM an t~nimUMu The Lower Umit of Detection (LLD) is the minimum sensitity value that must be achieved routinely by the analytical parameter.
2.
LIT The estimated uncertainty in measurement of titlum in environmental samples is frequently on the order of 50% of the meaurement value.
Statistically, the exact value of a measurement is expressed as a.
range with a stated level of confidence. The convention is,to.report results,with.a 95% level of confidence. The uncertainty comes from calibration standards, sample volume or weight measurements, sampling uncertainty and other factors. Exelon..
reports the uncertainty of a measurement created by statistical process (counting error) as well as all sources of error (Total Propagated Uncertainty or TPU). Each result has two values calculated. Exelon reports the TPU by following the result with plus or minus t the estimated ample standard deviation as TPU that is obtained by propagati all sources of analytical uncertainty In measuremnents.
Analytical unceitainties ar reported at the 96% confidence level in this report for reporting consistency.with the AREOR;.
Gamma specrslp resut for each type of ample were grouped as falows For groundwalter nd surfa&e water 14 aulides, Be-7,,KMO, M*54, CO-58, Fe659, Co-60, Zn-4,NAb-O6, V-96,11-131, Cs-134, CsW137, Ba-140 and La-140 were reported.
C.
B*akground Analysis A pre-operationl radigical nvro al monitoring program (pre-operational REMP) was conducted to establish bckround doactivi leve prior to operation of the Station. The. mviwrunmenu media sampla and nae during the pre-operational REMP were a tmdphrI1 radiation, fAOut domestxc water, surface water, marine lif and food sfs. The results of the moi
- were, detailed in fth report entled, Environmenta RadiologicaW Monitori for Drndn Nuclear Power Nudar Power Station, Commonwealth.Edison Company, Annual Report 1986, May 1987.
- 1.
BackGround Conacentratof Tritium The purpose of the following discumlon is to summarize.
bacgrod meurmesof tritum:in various media performed by otwS. Addiol detal mn" be fou by ecnultn referenoce (CRA 2006)..:*
- a.
Tritium Production processes both cmic and suberranMean, as well as from anthropogenic (i.e., man-tmad), ourmes. In the upper atmohere *Cosmogenlc tritium Is produced from fth bomb ent of stable nucies and combines with oxygen to form tritlated water, which wilt then enter the hydrologic cycle. Below ground, lithogenlcW tritium is produced by the bmArdmntof natural lithium present in crystalline rocks by neutrons produced by the radioactive decay of naturally abundant uranium and thorium. Lithogenic production of tritium Is usually negligible compared to other sources due to the limited abundance of lithium In rock. The lithogenic tMtum is introduced directly to groundwater.
A major anthropogenic source of Mritium and strontium-O comes from the former atmospheric testing of thermonuclear weapons. Levels of tritium In precipitation increased lnfficantly durng Me 1960.sn early.196s, and, er with additional testing, resulting in the release of significant amounts of tritium to the almosphere. The Canadian heavy water nuclear power reactors, other commercial poWer reactors, nuclear research, and weapons production continue to influence tritium concentrations In the environment.
- b.
Precipitation Data PreAIpitatUon samples are routinely collected at stations around the world for te analysis of tWum and other radionuclides. Two publicly available databases that provide tritium concentraiorns in precipitation are Global Network of Isotopes in Precipitation (GNIP) and USEPA's RadNet detabase. GNIP provides tritium precipitation concentration data for samples collected woldwide from 1960 to 2006.
RadNet provides tritium precipitation concntratio ditaf6X samples collected at stations throughout the U.S. from 1960 up to and including 2006. Based on GNIP data for sample
- °*
stations located In the U.S. Midwest, tritium concentrations peaked around 1963. This peak, which approached 10,000 pCi/L for some stations, coincided with the atmospheric -
test"in of thermonuclear weapons.
Tritium concentrations In surface water showed a'sharp decline up uhtil 1975 followed by a gradual decline since that time. Thitium-concentrations in Midwest precipitation have typically-ben below 100 pCi/L since around 1986.
Tritiumconcentrtions in wells may still be above the 20W' pCilL detection limit from the external causes described
.8-
majority were installed in areas of historic spills or close to piping containing tritiated water (Table 8-1. 1, Appendix B).
IMDI&m Samples were collected and analyzed for strontlum-89 and strontium-G0 activity (Table B-1.1, Appendix B). Stronthun-89 was not detected in any of the samples. Strontium was detected at a concentration greater than I pCi/L at two sampling locations (DSP-108 and MW-DN-105-S). The concentrations ranged from 1.5 to 4.9 pCi/L.
C.
.1i Gross Aloha gnd Gros §Mt Wdisove MAn Suonded)
Gross Alpha and Gross Beta analyses in the dissolved and suspended fractions were performed on groundwater samples throughout the sampling year In 2013. Gross Alpha (dissolved) was detected in ten groundwater locations. The concentrations ranged from 1.3 to 15.6 pCi/L.
Gross Alpha (suspended) was detected in one groundwater location at a concentration of 1.0 pCi/L. Gross Beta (dissolved) was detected In 32 of the groundwater locations. The concentrations ranged from 2.7 to 46.8 pCi/L. Gross Beta (suspended) was detected in one groundwater location at a concentration of 30.2 pCUL. The conoentrations of Gross Alpha and Gross Beta, which are slightly above detecable levels, are considered to be background and are not the result of plant effluents.
Gammna EmM Naturallyocc(ung K-40 was detected in two samples. The concentrations ranged from 37 to 65 pCi/L. No other gamma emitting nuclides were detected (Table 8.4.2, Appendix 0).
Hard-To-Detect analyses were performed on two groundwater locations to establish background levels. The analyses included Fe-55, Ni-63, Am-241, Cm-242, Cm-243/244, Pu-238, Pu-2391240, U-233/234, U-235 and U-238. The isotope U-233/234 and U-238 was detected at one of the two groundwater monitoring locations. The concentration of U-234 was 1.0 pCi/L and the concentration U-238 was 0.39 pCi/L (Table B-1.3, Appendix B). The concentrations detected are considered background.
All other hard-to-detect nuclides ware not at oentrations greater than their rspective MDCs.
above. Water from previous years and decades is naturally captured in groundwater, so some well water sources today are affected by the surface water from the 1960s that was elevated In tritium.
- c.
Surface Water Date Tritium onntkalon re roIneymeasurqd In large sufaice water bodies, including Lake Michigan and the Miss. ssippi River. Illinois surface water data ware typically ess Mthan 100 pCUiL.
The radio-analytical laboratory is counting tritMum results to an Exelon specified LLD of 200 pCl/L. Typicolly, the lowest positive measurement will be reposted within a range of 40-
.240 pC11L or. 140 t 100 pCUL. These sample results cannot ibe dnguhe as differeMnt from ba ound at th IV.
bauft fl4011s 0
r Dresden Station W
Intat aRadlologicuf Groundweler Prohmcton Program
.,5 (RO M in 2.006*:,.-
A.
Groundwater Results Samples were collected from on-site wells throughout the year in accordance with Dresden's RGPP. Analytical results and anomalies are discussed below.
Ttium oMnentraMt*on S:n-the shallOwand intrmldte aquifer are stable or decreasing over time. Trium
- oncentrtons in MW-DN-124S and MW.-DN1 241 continue to be closely monitored for the eO plume in this area. The few wells that exceed the United States Envronmental, Protection4 Agency (USEPA),drinking war standard (and th Nuclear Regulatory. Commission.ReportingUm'.t).of 20,000 pCl/L arm located onsite and are not available as a drinking water source. Although tritium is detected in.a large number of these wells, it is important to note that the S.
Surface Water Results a
Samples werecollected from eleven surface water locations throughout the year In accordance with the soation radiological groundwater protection program. Analytical result and anomafles am discussed below.
Titium Samples from a locations were analyzed for trtium a*ct (Table B-11.1, Appendix B). Tritium values ranged from the deection limit to 4,740 pClfi.
The mesurabl concenatns of tritium are from an upstream source.
Samples were not analyzed for strontium activity (Table 541.1. Appendix Samples wer not analyzed for Gross Alpha and Gross Beta In 2013.
QUMn EMiters fto gam'ma emitting nuctDdes were detected (Table 8-11.2, Appendix B).
Samples were not analyzed for Hard-To-Detect analyses in 2013.
C.
Precipitation Water Resuts Samples Were colt from 4pion waterlocationshoughout the year in accordance with the station radiological groundwater protection program. Analytical results and anomalies are discussed below.
Samples from 4 locations were analyzed for tritium activity (Table B-ill.l, Appendix B). Tritium was not detected in any samples.
D.
Drinking Water Well Survey No drinking water well surveys were conducted In 2013.
E.
Summary of Results - Inter-Laboratory Comparison Program Inter-Laboratory Comparison Program results for TBE are presented in the AREOR.
F.
Leaks, Spills, and Releases There were no leaks, wills or releases of radioactive material in 2013.
G.
Trends The elevated tritium concentrations are expected for the wells in the vicinity (MW-DI-124S and MW-DN-1241) as the plume continues to reside in this area.
Overall, tritium coNcentrations In the shallow and Intermediate aquifers are decreasing over time.
H.
Investall*i*ns No additional invtigatin conducted In 2013.
I.
Actions Taken
- 1.
Compensatory Actions No compensatory actions were mquired in 2013.
- 2.
Actions to Recover/Reve Plumes No actions were taken in 2013 by Dresden Station in an effort to revere plume movement.
APPENMDI A LOCATION DISTANCE
~ft blank
TABLE A-I:
Radlologicl Grmunmdwaw Pklon Prowgr
-Sewnp Locns.
Dresden Nular Power Station. 2013 kse Site Type Location DSP-105 DSP-106 DSP-107 DSP-108 DSP-117 DSP-121 DSP-122 OSP-123 DSP-124 DSP-125 DSP-128 DSP-147 DSP-148 DSP-,149R DSP-150 DSP-151 DSP-152 DSP-lBS DSP-154 DSP-156 DSP-1674l DSP-1 67-M DSP-1 57-S DSP-1S684 DSP45-DSP-ISO-DSP-159-4 DSP-1SO-M OSP-I59-S MW-OW-101-l MW4-3NI01-8 MW-OS-102-l MW-DN-102-$
MW-DN-10 MW4DNI03-S MW4)WN-I044 PA~N43I05S4 MW4ON 1084 MWJOW4107-8 MW4-N-1084 MW-ON-1094 LWW4)Wi0O-S MW-ON-1104 mwz"O1-84 MWI-ON-ll-S SMWV.DW112-l MW-ON-112-S MW-N-113-l MW-DN-i13-S MW-ON-i4IW MfqW-DN1i4-MW-DN-i1Gl MW-ON-ItO-S AM-DN-li1-4 MW-ON-Its-MW-ON-I 17-I MW-4N-I18-S MWiON-I 19-I MW-ON-I 19 LwOW4N-120-1 MW-ON-12D-S NW-DN-121-S
-doWeN Monitoring Wel Monitoring Wel Monitoring Wall Mortm" Wdt Mmwtm~w Mmtmor w"
M-O&
Wd Mwnto"Wel
-rorWell Mo-m" WeN Mmotomgwd Moitoring 0Wel Mon-dng Well Monitoring We Mmftm*wd Monito* *e
-bdo WON Mmtb"Wd
-ox We' Moro" wal
-mong We mo,-ng WON m
nlWell
-ox Wel Monitorft Was mo-t WON mon-o Wea UMwtodnW V Modnf Wel M-~r we' Monmor" Wal kmtormo wea
-mo Wel
-KQWall Mmortng Wed mo-i Wei Mrn*
We' Mwft"odnWe Monitot Wea mo-~o" Wal Mwlorgrng We' Monitoring We' mMoitoringWell Mwftodng Wel Monitoring Weil Monitoring Wev Mwnitodn Wag Moiorn WONl 30 fa O of the eO wl of the EM Shop as fm em Ofaemla of EM Shop 9 feet east of th easO Unit I Fuel Pod wel 40 ft et of the Unit I Sphwe Northemst o Unit I Sphwe 625 fog wet of Ros W1de 72 feet north of 2 InteCank fenoe 50 feet north of the Radsm Tank Farm Northeast corner of the Unit I Off-gas Budng 9 fet south of Flcr Drain Collector Tank Nortst morn of the Unit 2A CST 21 flet fs ofth nol t
l ed* I d
Tramning Buddin 328 foot wat of Teemery Bridge 130 fat southemat of the Flow Rean Sttion Wkli 35IMso*th bysouhMwst ofth 138 KV yod Wm 85 OW easof an enoheao rwof the UnIt I Spent Fuel Pool*pd 65 flee north of the now east Corer of the Storeroom 210 fed south by souhsMt Of the sohea orner of A#Mkte We Guge 10IMO fetas of toe soufthest corner of "qi hydrogen tank farm fenoe 33 feet vat of the tnack 166 last eas of the Seourtty Checkpoin 70 ft eat Mby mtl ofte nof wst oner of 138 KV yard fnce 25 fee Wsoi of the south edge ofte Emple Pk" lot 25foe mouh of t so*thedgeo of te En m Parn
[lat 26 fee south of
- t south edge of the Employee Park lot 63 fet we of the Kan*keae Rkw, 33 fot west of the cider trk o3 be west of the Kmakee Rir, 33 fet west ofhe ftCier US*
50OWeewest oftgo KiernwskeRlwr 33 fogweetof decindertraic 250 faet wet of de Thorsen house; 450 ft south of the plant accen gel.
250 feet west to. Thomn houwe 450 It so9th of the plat s gin 251 fIe t of the Th1rn hous; 450 ft south of the plant acOs gofs W0 feel north of the Unit I Diesel Fuel Sor8a 60 eat north of t0 UWit I Diesel Fuel Omp 12 fe south ofm to el cormne oft. MUt DS Builng 13 W south of the southeast conW of the MUDS Bulling 280 feet west ofthnortwt corer of N-GET Siding 2811fe0wst ofte nort cornr of N-GET Bailng 50 foet north of RaPit Tank Farm 65 fet north of th norteast ainer Of the Storeroom 76 fat north oift 2/3 I etl Cmel fen*; ea of the Unit I Intlm Canol is feed Vat by soaa of the unlt I CST 7 fet smemst of the soa&iwst cor* r of I Unit I Cfwhouw o feel north Of Chemistry Baiin 8 feet north of Chemlay BuIdng 265f west olft Ws Waer Tremel (WWT) aln 25 fee wes offt. Wasb VAWae Tenent (WWT Sailin 9 feet east of t Floor Drain Collector Tban 100 fee south of t.hemOwnsty Buldln 100 fed south ofthe Chemnistry B&"Vn 90 fIee VIst of th w
orner ci th. AmtrsMo BUildin 91 foe wWest th soiit cor n oft he Aftkntm Bidin 50 f*el east of t. Unit I Clean DOam ln d WOW" Tank S fee* ouMtwest ofth Radon* plsH Dept west aco doors 11 fet south oa Insbtrumen Menltaence Shop 12 fast south of Inhsment Melintance Shop 76 fet south of*dt Calgon Buli roUl-ip door 75 feet outM of th Clgaon Buid rol.-p dOr 35 feet aSt by nmthmest o ft. Unit I Stuck Southeast oon of the Unit I Fuel Pool 20 fat ee by northeast of the Unit I Sewage E*jtor Bulling 21 fet east by norlhest ofthe Unit I Sewagp Eeco Builing 45 feet north by nothest of te RoSS Bridge rIlng 46 fee north by nortteast of the Ross Brdge railg 7 feel west cthe dirt road, 42 fee ast ciofthe 345KV yard fenc A-1
TABLE A-1:
Radlologlat GrournctWar PFrotMM PMr n - Ssm" Location.
Dresden Nuclear Powr Station. 2013 Site Sits Type MW-ON-1224 MW-MN-22-S MW4N-1234 MW.D)N-123-S MW-DN-124-MW-ON-124-S MW-DN.125-S MMION26-S MW-ON-127-S MW4DN-134-MW-DN1-135-6 MW4D134 MV-DI4-137-S MW-DN-140-S MW-DNW141-S MMM-MD11 DSP-131 DSP-1132 SW-)WON-I SW-4DN-102 SW-ON-los SWV-DN104 SW-ON-lOS SW-ON-log0 FYI-I PW-2 MW-3 FW-4 FW-5 FW46 MW7 FW-8 FW-0 FW-10 FWI-11 FW-12
-MO Wag Monitoring Wall Monitoring Wal
-ra" WIN
-~t Wall Mw"n wen Monit" weng Mo-well Mwtntorkv V"
-ro WON Mwo wen Mo-o" Well Surwoe Watw Sa1*m Water Sufmt Wer stofe Watew Surma Wter Sufma Water Surmae Wiaer prcpiiton Precohatlici Prcptton Prcptton 150 met north of Collins Roed northeast of the G.E. Fuel Storge Facility 180 feet normh of Coins Road; northest of the G.E. Fuel StoMgp Facilty 400 feet wat of the Thorsan house; "t of the Cold Canal 400 met west of the Thorsen house; wst of the Cold Canal 10 foet south of the "d nroen ting tanks 10 feet south of the lquld nitrogen neang tanks 40 fet e t of 2M3 CST 15 fet south odffece around Unit 2/3 A CST and B CST (outside of fenc) 20 fee south of Unit 3 HRSS 20-t Nom of Mausoleum uldin 20-ft Ent of Mausoleum Suildig 14.5-ft Sout of MMaMIUew Buildin 20-ft Ws od Mausoleum Bukkn East of MW 0t4N10,1 at SW orner ouidLe of 2/13 ab hous North of 'A' Wase Tank nexd to 213 main chime P
located betosen Condensate Stae Tanks.
Storm water -35 ft NE of the Unnt 23 ha*ng baW 150,000 galon does, fuel S tank W
tofthe hot canal en-uncdene Sesft Black Storm waar-M tNE ofthe Unit I Sphere. The w ewr linthe m'lde ofthe road with a old covr (no slots). Them Wm two other sem In the vicinity h4th solid covers on thm. but bath have the ward'SANTARY" an tf cover. The wowr Is ft SE of the Unit I dieal full tusI shed.
Unit 203 In~ft (DSP50) at the Rosa Brk~e Unit 203 ODischag (DSP20) at the Telemetry Bridge Unit 2/3 MUM Cal at the OMicawge to the Intake Canal Cold Cnl (OSPS3A) at the Coo" Tor wallkcwy Wkge Hot Canal (DSP34) at the Cooin Tower walkway fbid Cooling Pond - Pol It at the sest aid od the Covered Obdg.
40 fee southwest of Unit 2M Off-ps r Bilig acceu doa, north and Of uAI*l 80 et East of Con Pe-c Trailer South of Stock Truck Bay rollup door Southeat comer of Unit 3 RB Inelock Ent of Unit 24 Inuta Roes bater Nort of Unt I Chimney Souths of Unit 2 TB Tucway Souwest corne of 2J3 CST on fMen South of MUDS Suiling on Seountly faoe AZ tw ftnce at the northwast corner of the SOO BSiling 30 fet east of thes ea wall of the EM hop ast ft stanchion for RGPP wall DSP-lOS 60 fmet soculeast of the southwes corner of the Admin Building an the aseurity fence A-2
DATA TASSFlS
- 1. 1,
. 11
ý Inftsnfouil mft blan
TABLE 34.1 CONCENTRATIONS OF TR11rUM, STROWNI, GROSS ALPHA, AND GROSS BETA IW GROUNDWATER SAMPLES COLLECTED iW THE VQINITY OF DRESDEN NUCLEA POWER STATON, 013 RESULTS IN UNITS OF PCILITER
- 2 SIGMA COLLCTBON SiTE DATE H.a Sr.M St-G0
&A (DiMl Gr~A I&1a flr.a vl 0*
ar-fl M~ull DSP-105 DSP-105 DSP-105 DSP-106 DSP-106 DSP-100 OSP-10e OSP-107 DSP-107 DSP-107 DSP-107 DSP-108 DSP-108 DSP-108 DSP-108 DSP-108 OSP-10l DSP-122 DSP-122 DSP-122 DSP-122 DSP-123 DSP-123 DSP-123 DSP-123 ISP-124 DSP-124 DSP-124 DSP.124 OSP-125 DSP-125 oSP-125 DSP-125 DSP-123 DSP-147 DSP-148 DSP-148 DSP-148 SP-.148 DSP-149 (R)
OSP-14, (R)
DSP-149 (R)
DSP-149 (R)
DSP-150 DSP-150 DSP-10 DSP-150 DSP-151 DSP-151 DSP-151 DSP-151 06/13/13 06/15/13 10123/13 03M04/13 06/13/13 08/15/13 10W2313' 03104/13 0M/13/13 08/15/13 10123113 03/04/13 0611311 06113/13 06/13113 07/31/13 08114/13 10/23/13 02027/13 0610613 06/13/13 1022/13 03(4/13 06107/13 08/14/13 10M2313 0217/13 05/14/13 08l16H13 10/25/13 03/06W13 0M5/13 08/12/13 1025/13 06/10/13 06104/13 03O06/13 06e/13 03/16/13 10/2=/13 03f08/13 0/0eW13 05/19/13 10/2M113 03105/13 06/13/13 08/15113 10124/13 03/05/13 06/13/13 08/15/13 10/24/13 4M1
'170 252-t 116 N184 2490 a 311 2310 a 251 220D 269 1830 a240 2900 a.351 2860 a 336 2560 t-305 2530
- 305 746 t 157 017
- 150 9O a 146 801 a 144 529 a 139 650
- 143 1090
- 172 797
- 143 791 *150 1960 a213 1720 a 224 1820 a 232 1830 220 1350 D 0 4160
- 459 3680 a 413 360 446
< 105 277 1 119 250 A 118
' 179
< 16
< 171
- 194 312 a 123
- 178 292
- 122
- 1I6 464 a 128 107 a 118 244 a 116
- 1Ig
< 166
- 169
< 182 I 1g9
<160
- 168
- 178
' 7.8
- 1.0
' 1.2
' 7.8
, 3.2 c 4.0 S0.8 c0.7
' 0.8
- 0.4
- 0.4 6.1 a 1.2
- 1.3 4.2 a 1.1
- 1.3 7.3 a1.3
'1.5 12.3 a1.5 '1.5
- 0.8 1 t.0 1.6
- 0.7 ' 1.4 1.5 t 0.4 1.7 a 0.7 2.4 a 0.7 < 7.9
< 0.9 1.2
- 3.9
< 2.0
,c 0.9
- 1.7
'0.6
- 1.7 11.8 1.5
-1.6 37.2 a 63
- 3.8
- 1t0
- 6.8 B-I
TAKLE 94.1 CONClIfI RATIONS OF TTflOUM, StRONTIUM, GROSS ALPHA AND GROCA ETA IN GROUNDWATER SAMPLES COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION, 3913 RESULTS IN UNITS OF PCI/LITER 12 SIGMA COLLECTION InAyr
+
RrJI9 11r,,
1 l lý 4
1.. Irliall I'll! !I "
a l 112 111
-12 t 1 4 lillillim
!:I
ý;
loollillippIC-6 "'
,"I DSP-IN6 DSP-lie DSP-ie4 DSP-I157-S U DSP-1 594 DSP-1 59-S MW-45-I014I MWD-14 MW-DN-101-S MW-DN-101-S MW-DNl01
.MW.D MW.OtI102-I MW-D MW-OIl2-MW&-DN-02-S MW.O4-102-S WJ-DN-102-S MW-ONl034 1W3W04-S MWDN10' MWON-09-S NW-DN-1074 WVIDN-1 074S MW4DN-l07-S MW-O-lB-MW-O-lS-MN-DN-1084 MW-DN-10114 MWV43-l094 MW-NI 04 MWIO-04 MW I
S-l9 MW-DN.109-S MW-DN-109-S MW I
lBS MW4ON-I104 03106/13 06/03/13 08/191t3 10/'28/13 0611 0113 06/10113 06/11613 06/11613 03/04/13 06107/13 06114/13 10123/13 03/04/13 0W107/13 06/14/13 10123/13 0M106/13 06114/13 06118113 10/26113 0310O/13 06114/13 0/116/13 10/26113 06110/13 06110/13 02/27/13 06113/13 10122/13 03/05113 06113/13 08/15/13 124I13 06103/13 03l05/13 06113/13 06/11613 10/21/13 03/04/13 06/07/13 08/14/13 10/2/13 02/27/13 06106113 06/13/13 10/22/13 02/27/13 0~6/013 06113/13 10122/13 02/27/13
< 194 204 a 116
<178 253 a 118
'168
< 167 310 a 134 854
- 153 940 *151
-3.6 6M5 a 147 631 a 149
'176
<171
< 3.5
'193
'176
< 172
< 167
< 7.2
< 190
' 179
'- 176 S166
'0.2
'187
-c 109
,' 164
< 187
< 170 261 a 115
'180
'178
- 7.4
-1IN
'9.1
'161
< 6.6
< 191
'3.8
'172 306
- 124 250 t 118
' 161
' 177
< 170
- 3.4
<'168
'190
<169
< 3.8 541 t 148 689
- 157
- 186
< 169
- 3.7
' 193 201
- 128
-c1IS
' 0.8
< 1.3
<1.5
< 0.3
' 0.7
< 0.7 4 0.6
' 0.7 12.3 a 1.5
'0.8 9.9 a 1.5
<1.7 3.6 0.0
'1.6 43.2 a 9.2
< 5.5 1.3 a 0.6 ' 0.5 15.6
- 9.3 - 1.9 4.9 a 0.8
' 0.9
' 0.9
. 0.5
-0.0
< 0.8
- 0.7
' 0.5 40.6
< 0.6
< 05 12.9 a 1.4
<1.6 2.7 a0.8
< 1.0 15.7 a 1.9
<1.4
- o0.9
'2.7 6-2
TABLE 84.1 CO#4CENTRA1N OF TRmUM. STRONW~lM GROS ALPHA. AND GROs aWA wN aROUOWA7ER SDUlPLSS COLLETED IN THE V1CWTY OF DRESDEN NUCLEAR POWERt STATION 201 RESULTS IN UNITS OF PCIALITER
- 2 SIGMA COLECTION SrrTE DATE 14-Sr'-SO Sr-90 Gr-A 081i)
Gr-A (Ss)
Gr.B (DIM) Gr-B (Sue)
MW-ON-T1O-04' 6/-
MW-ON-110-I 08/13/13 MW-DN-1104 10=22/13v MW4)IN-ll-S 02027/13 MW4ON-110-06/06/13 MW-N-110-S 06/13/13 MW-ON-l1-8 10=22/13 MW-ON-111-S 02r27113 MW-w-1il-S 06/14/13 MW-ON-ll-S 09116/13 WI-DN-1Il-S 10l25/13 MW-ON-1124 02127113 MW-ON-1124 06/08113 MW.ON-1124 06113M13 MW.DN-1124 10=22/13 MW-ON-112-S 02127113 MW-ON-112-S 06/06/13 MW-ON-1 12-S 06/13113 MW-ON-112-S 10=22013 Mw-ON-I113.1 03/05/13 MW.ON-113.I 06/14/13 MW4-N-1I13-1 06/16/13 MW-ON-113S-I1 i0413 MW-ON-113-S 03/08/13 MW-ON-1I13S 06M14/13 MIW-N-113-S 08/16/13 MW-ON-113-S i0W24/13 MW4-N-114-I 03/M6/13 W.-ON-1144 06/0M/13 MW-DN-1144 08M13/13 MW-ON-I14-4 10121/13 WION-114-S 03A0513 MW-ON-I14-S 06/06/13 MW-ON-I14-S 08/13113 MW-ON-I14-S 10/21113 MW-ON-115-1 03/08/13 MW-N-115-4 06/13/13 WV-ON-116-I 08115/18 MW-ON-1154 1024/13 MW-ON-115-S 03/06/13 MW-0N-115-S 06/13/13 MW-ON-115-S 08=15/13 MW-ON-I15-S 10124/13 MW-ON-1164 02/27113 MW-ON-1164 06/07/13 MW-ON-I16-I 08/14/13 MW-ON-116-I 10/22/13 MW-DN-116-S 02a27/13 MW-ON-I16-S 06/07/13 MW-ON-116-S 08/14/13 202 2 117 1685 4172
- 183
- 190 365 1 34 351
- 122
<C 173 232 a 130
- 185
- 170
- 173 C 102 C 172
- 170
- 1.82
- 176 4 166
- 6.8
< 17
- 169
- 8.0
<160 5600 a 607r 7900 a 83 5150 *+/-60 7100 a 755
' 176 206 a 117 4 190
- leg 433 a 131 355 a 122
- 143 272 a 127
-c 174
- 166
- 190
- 171 216 a 123 220*'*117 45.2 1270 a 194 1210 a 179 403 a 134 430 123 c4.2 254 1 128 I
- 0.7 c &.9 4 1.3 C 0.4 87.2
&.0 a 12 4 3.6
- 1.3
< 0.8 CI6
- 0.7
- 0.8 1.6 a 0.9 < 0.5 3.6 a 1.8 < 0.5 11.2 a 1.4
< 1.4 18.6 1 1.8
< 1.4 1-3
TABLE 84.1 CONCENTRATIONS OF TRITIUM, STRONTIUM, GROSS M.POA, AND GROSS BETA IN GROUNDWATER SANMPLS COLLECTED IN THE VICINITYOF DRESDEN NJCLEAR POWER rSTATION, 2013 RESULTS IN UNITS OF PCI/LITER *2 SIGMA COLLECTION SIT6 o
I-a.
I S&r-Sr.10 Qr.A MAI~ Qr-A (20AM Gr-k rIma ar.B tsuav,z SITE
- OATE, MW-ON-iI18 MW4ON-itS-S MWVON-I 19-MW-ON-i 104 MW-DN-I1694 MW-ON-lie-S MIWCIN-I 19 MV4W-ON-i 6 MW4ON-116 LWV-ON-122-I MW-DN-1 22-8 MW-ON-124-I MW-DN-1244 MW-O-i244 MWI-ON-124-MW-DN-124-8 MW-N-124-S MWN-1I24-S MWJ-ON124-S LM4WI26-125 LIW-DN-126-S MW-ON-125-S fM4X&125-S MW-ON-126-S fANN-1264 MMV&N126-4 MV4W-NI28-MW-ON-I 28-8 LiW.ON-12?-S MW-N127-8 MW-ON-127-MW-DN-127-S MW-ON-i 344 MW.ON-i34-S MMW-Ni 344S MW-DN-134-S LM-NI 35-S MW-ON-136-S LW-DN-135-S MW4DN-135-S MW-DN-136-S MW-DN-136-10122/13 03/04113 06/13/13 06/11/13 10/3/13 03/04113 08!/07/13 09/14/13 10/23/13 03A04/13 3R/02013 06/07/13 06/14113 102"3/13 08110/13 06110/13 03/06113 08114/13 09/16113 10r25113 03106113 03M913 06514113 0=/16113 10r25"13 03/06113 06/14113 06116/13 10/25/13 03IM513 06114113 06116113 10r"413 10/24/13 Rooumt 03/05/13 0614113 08115113 10124113 03AW913 03109113 06116113 10026113 03/09/13 06/04/13 08/19113 10/28/13 03/09113 06/04"13 320 1
126 1370 a 194 594
- 135 343 a 132 345 1
129
< 169
' 7.7
'0.7
'0.7
-1.2
' 0.5
$Atl.4 '1.6 23.0
- 1.9
<1.4 422 122 '3.6
< 186 313 t 122
. 181 3.6
- 1.7 1.0 t 0.7 6 8.4 c 09 40.8
- 2.8
- 0.8
- 1.6
'159 190
- 175
- '168
'165 43500 43700 23100 8750 1m
<'173
. 1.0
'0.6
< 0.7
. 0.6 15.5
- 1.3
' 1.7 8.1 a 1.4
'1.4 33.4
- 3.9
' 2.0 121 a 1.6
-1C6 a 4390 '7.9 a 190 ' 7.6 4410
- 4100 Z
23-0 V9.7
- 711
- 7.2 ami0 a8m
-c 0.7
-' 0.9
, 0.6
' 0.7
' 3.4
<1.7 255 t 110
'7.6
- 189
<176 1150
- 178 615t 138
<8.4 389 a 133 W
t 157 936 a 162 283 a 124 413* 127 <8.0
' 0.8
< 0.9
' 0.9
- 1.8
< 0.6 12.7
- 7.2 < 1.5 S192
- 175
' 175
-c178
< 173
- 172
- 161
' 178
- 173
< 177
- 162 1 2.4 4 1.7
'0.5
'0.9 5.4 a 1.3
'1.3 35.4 *t8.
-3.9 11.2 *2.5
- 1.6 10.1 a 1.4
- 1.6 7.6 t 1.4
- 1.8 11.6 t 1.4
< 1.7 16.8 a 1.6
- 1.6 13.8 a 1.8
'1.0 11.6 t 1.7
'1.6
< 6.9
' 0.7
' 3.4
- 0.7
- 7.2
' 0.8
- 3.8 U
0.9
- 7.5
< 0.9
- 4.5
'0.9 B-4 2.6
- 1.4 c 0.5 2.6 a 1.1 < 1.1 4.2
- 1.3 ' 0.5 c 2.3 c 0.4 3.3 2.1 ' 0.5
TAKLE "I.1 CONCENTRATNS OF TRIUM, STRONTI, GROSS ALPA AND GROSS eTA IN GROUNDWATIR SAMPL COLLECTED WN THE VICWT OF DRU W CAAR POWER STATION, 2013 RESULTS IN UNITS OF PCI/LITER 12 SIGMA COLLEC~nON DATE SITE MW.DN.136 MW4D-13S MW04O-137-S MW4-MD3d-13 MW.Oti137-S MW4DW1374S MW4DN-1404
,N14)wu VADW140.3
'*ra14043 MW*41404S MW.ON-1414S
'044:M141-S MWMMN141I4
.MW4)W141-8 W.3 ar.m9 Sr-W arA inhil A&A I ntdrm illhi flrEA IAu*1 71
~T
~~1Wu 08/18/13 10r. 13 O06l0613 1IS3 08/t3/13 01062/13 02406113 08/13/13 10=2/13 02/2713 06/*131 10F22/13
' 178
,c173
- 176
<c 160
' 178
'leg7416 0
1740t 23
' 6.0
- 0.9 8.5
- 4.0 c 0.8
< 1.6 c 1.3 40.6
'7.8
-C 0.8 6.6 t 3.8 1.5 46.8 t 6.5
' 3.6 7.4 t 1.6 4 2.0 17.7
- 4.9 30.2 2 3.6 16.8 t 1.3
<1.8 1510 a 200 1170 a 167 50 141 1160 a 163 2300 279 c3.9 707 a 149 1280a 186
- 0.7
'0.8
' 0.5 9'
'I 4.
B-s
TABLE B-2 CONCENTRATIONS OF GAMMA EMITTERS IN GROUNDWATER SAMPLES - -
COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR.POWER STATIO, 2013 RESULTS IN UNITS OF PCI/LITER *t2 SIGMA -
SITE COLECTION
':e0-7 K-40 Mn-4W CO-68 F~O CblD Zn.65 Nb-OS
&45O 14131 CS-134 Cs-137 IMI-140 U4-40 DSP-105, 08A1313 DSP-lOS 1MUM11 0SP-106 08615H13 DSP-105 t0QrM3 OSP.106 "
03"M43 OSP.106 "
0/3/13 OSP-108 08115113 DSP-1OB 10123r 3 DSP-10" 03113 ISP-107 08M3/1 DSP-S07 08W11513 DSP-107 03104113 DSP-SOS 0613113 DSP-106 07131113 DSP-SO 01111 DSP-OB 1
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TABLE 8-1.2 CONCETATIONS OF GAMMA EUTTERS IN GROUNDWATti SAMPLES COLLECTED IN THEViCINITY OF DRESDENUIICLEARPOWER STATION, 2H3 RESULTS IN UNITS OF PCIiLITER t12 SIGMA Sime COLLECTION Be-7 flATE
.K40O Mn.84 Co)-GB FaMG Co
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0614113 MW-CN-12,4 1025113 MW-tMN-124-06114113 MW-ON-124-8 10W2913 MW-ON-125-8 06114/13 MW-&N-126-8 06114113 MW-DN-127-8 01'1/413 MW-DN-134-S 03105113 MW-11-134-S 104113 MW-4N-135-S 03/05113
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TABLE 8-42 CONCENTRATIONS OF QAM EIIITTERS IN GROUNDWATER IAUMLES COLLECTED IN THE VICINITY OF DRESOEDINUCLEAR-POWER STAION, 2013 RESULTS IN UNITS-OF PCULITER t 2 SIGMA SITE COLLECTION BW-7 1K-0 n-64 Co Fe,.69 Co.0 Zn-b6 Nb-SB Zr-B 14131 Ca-134 Cs.-137 Sa-140 La-140 DATE t
MW-DN35-S 06W0413
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TABLE 84.3 CONCENTRATIONS OF HARD TO DETECTS IN GROUNDWATER SAMPLES COLLECTED INTHEVICINITY OF DRESDEN NUCLEAR POWER STATION, 213 RESULTS IN UNITS OF PCIIUTER
- 2 SIGMA SITE COLLECTION Arn-241 Cm-242 Cm-2431244 Pu-238 Pu-23924 flAT*
U-234 X-236 11-M3
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TABLE 04.11t CONCETRATIONS OF TRITIUM IN SURMACE WATER SAMPLES COLLECTEO N TME VICINITY OF ORMOEW NUCI.LE POWER STATION0 MI RESULTS IN UNITS OF PCI/LITER t 2 SGMA SITEMw OSP-131 DSP-131 DSP-131 DSP-132 OSP-132 DOSP-132 DSP-132 sWDN-101 SWO0N-101
,SW-ON-lol PN4WIOI.0
'SW-DWN102 SW-DN-102 SW4DN-102
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COLLECTION DATE 06/18/13 08/13/13 o 10/21/13 "03108tl3 06/15/13 08113M13 10021113 031*/13 06103/13 08/19113 10/28113 03106/13
- 10/28/13 03I013 06103113 08/19113 10W28/13 03108/13 06103113
- 06/19/13
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- 200 405
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- 309 733 t 184 488
- 125 4-
- 525 2630
- 312 870 t 101 551 t 128 4630
- 520 2660
- 314 775
- 157 569
- 127 4010
- 457 2M60 t 334 I'
B-IO
TABLE ".1.2 CONCENTRATIONS OF GAMMA EMIER IN SURFACE WATER SAMPLES COLLECTED IN THE VICINITY OF DRESDEN NUCLEAR POWER STATION 2013 RESULTS IN UNITS OF PCI/UTER t12 SIGMA SIT COLLECTMO 89-7 K40 Mn.54 Co-SB P.6 Co4iO Zn45 Nb95 Zr-95 1-131 CS-I 34 Cm-137 Ba-IS0 La-140 DATF DSP-132 061 613 D44N-W.O410I 06=313 DN-SMW-O-~102 113 ON-SW-OS-103 0610313 ONW-SW-VN1 0603113 OD-W-Dtd105 06=313 DNON-SW-W-lf 06IMf3
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TABLE 5411.1 CONCENTRATIONS OF TRITIUM W PRECIPITATION WATER SAMPLES COLLECTED IN THE VgCNIY OF DR8OE NUCLEAR POWER STATION, 2013 RESULTS IN UNITS OF PCI/UTER 1 2 SIGMA COLLECTION 81 ODATE FW-10 FW-11 MW12 0807113 06/13/13 00/14/13 (160
,c 160 8-12