RBG-34-917, Radiological Environ Operating Rept,Jan-Dec 1990
| ML20073H363 | |
| Person / Time | |
|---|---|
| Site: | River Bend  |
| Issue date: | 12/31/1990 |
| From: | Harrington M, Odell W, Reed M GULF STATES UTILITIES CO. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| RBG-34-917, NUDOCS 9105070087 | |
| Download: ML20073H363 (55) | |
Text
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A GULF STATES UTILITIES COMPANY
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April 30, 1991 RIG- 34,917 File Ibs. G9.5, G9.25.1.5 U.S. Nuclear Regulatory Ccnmission Document Control Desk washington, D.C. 20555 Gentlenen:
River Bond Station - Unit 1 Docket No. 50-458 Enclosed is the Annual Radiological 111vironnnntal Operating Report for 1990. 'Ihis report is submitted in accordance with Subsection 6.9.1.7 of Appendix A ('Ibchnical Specifications) to River Ivmd Station License Ntrnber NPF-47.
Sincerely,
,f5h y!n, ,r 0 ftet- W. H. Odell Manager - Oversight River Dend Nuclear Group
. J
' /WJi/pj Enclosure cc: Mr. Robert D. Martin, Regional Adntinistrator U.S. Nuclear Regulatory Ctmnission 611 Pyan Plaza Drive, Suite 1000 Arlington, TX 76011 l NRC Resident Inspector l P.O. Box 1051 St. Francisville, IA 10775 l
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e i RADIOLOGICAL 1:NVilt0NMI;NTAL Ol'l: RATING REl' ORT ltlVER llLND STATION FOR Tile OPEllATING Ptit10D Januar y 1 1990 - December 31, 1990 Cornplied by:
.- ,,,.AA2. I McGehee Reed Rad. Environmental Analyst Edited by: Reviewed by:
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t Michael A. Harrington
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l Edwin M. Car gikT Y ~~_ - . -
Supvr. - Envitonruental Services Director - Itadiological Programs Approved by:
y b Philip 'D Graham Plant Manager
RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATINO rep 0RT POR 1990 Ahrtirsi i
During 1990, a land use census and radiolosleal environmental monitoring were conducted in the vicinity-of River Bend Station (RDS). As part of the monitoring program, the RBS Environmental Setvices Group participated in an interlaboratory comparison. program with 97.4 percent of analytleal results within control limits. The land use census revealed 4 salient chances in receptor: locations since 1989, and the census was expanded to add meat animal receptor locations wlthin the 8 km range. Seventeen monitoring exceptions occurred out of a total effort of 1754 samples collected and 2339 subsequent analyses performed. Fourteen c of these exceptions -involved Technical Specification requirements, although none had significant impact on program quality. . Although well below the required detection limits, slightly elevated (relative to baseline data) levels of Cesium-137 were sporadically measured in Eboth Indicator and cont rol , media; these concentrations were presumably attributable to the'1986 incident at Chernobyl, Russia. The orily measurable increases. In radionuclide activity or levels of radiation attributable to plant operation, in the vicinity of RBS during 1990, appear 4
-to.have been expected low levels. In the 11guld discharge line and traces of airborne I-131 due to small amounts of failed fuel -in the boiler-reactor, i The levels of activity measured in airbornr. media and in the 11guld discharan were below the required LLDs .and. hence substantially belon Technical Specification reporting levels. Thus the 1990 Radiological Environmental Monitoring Program substantiated the adequacy of source control and effluent ,
p monitoring at River Bend Station.
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I HlVER llEND STATION ,
RADIOLO0lCAL ENVIRONMENTAL OPERATING REPORT FOR 1990 1611LLE MN1 Hill Page 1.0 I NT R O DU CT I O N . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 2.0 RADIOLOGIAL ENVIIt0NMENTAL MONITORINO PROGRAM (REMP) .............. 4 2.1 Purpose /Dases ............................................. 4 2.2 Environmental Radiation Expor.ure Pathways ................. 4 2.3 Land Use Census for 1990 .................................. $
2.4 ' Interlaboratory Comparison Pr ogram Result s for 1990 . . . . . . . 12 2.5 Program Exceptions ........................................ 12 3.0 INTERPRETATION OF REMP RESULTS ................................... 15 3.1 Summary of Operational REMP Results ....................... 15 3.2 Comparison of Operatlonal and Daseline REMP Results ....... 20 3.3' Comparison of REMP Results with Operatlonal Controls ...... 22 '
. APPENDICES A. Listings of 1990 REMP Resilts i
11 . Summary of Preoperat ional REMP_ (llaseline) Results 1
11
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l RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT FOR 1990 l
LL6L9LE1.@RCS Page Figure 1. Far-fleid Radiological Environmental Monitoring Locations .................................... 2 Figure 2. Near-field Radiological Environmental Monitoring Locations .................................... 3 r
LIST OEEELS Page Table l1. Radiological Environmental Monitoring Program ........... 6 Table 2. Results of: Land Use Census ............................. 11
, ' Table 3. U3 EPA Intercomparison (Cross-check) Program Participation Results for 1990 ......................... 13 .
- Table 4'. Monitoring Program Exceptions-in 1990 ................... i4 Table 5. Radiological Environmental Monitoring Program Summary .................................. .............. 16 Table 6.. ' Summary Comparison of Liquid Effluent-Quantitles/ Concentrations and REMP Discharge Line Monitoring Results ................................ 23 f
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.. e RIVER BEND STATION
, _ , _ _ RAD 1QLO_01 CAL ENVIRQEM6L OpIMlF0_ rep 0RT_ [Q11 1990.
1.0: IFlBQlEC11gh This Annual Radiological Environmental Operating Report for the period of :
January 1 through December 31, 1990, la submitted in accordance with Technical '
Specification 6.9.1.7 of Appendix A to River bend Station License Number NpF-47.
River Bend Station (RBS) is a 936 MVe General Electric boiling water reactor located in West Feliciana_ parish, Louislana, 4.1 km southeast of St. Francisville 3
-(Figure 1). -Waste heat from RBS is dissipated via a system using four mechanical draf t cooling towers which draw makeup water f rom the_ Hississippi River, 3.3 (air) km to the west._ Blowdown from the normal cooling tower system dilutes low-level liquid radioactive waste and is discharged to the Mississippi River through a 4.4-km buried pipe located downstr eam of the intake structure (Fig. 2). Gaseous radioactive ef fluents are released through the main plant exhaust - duct, t he fuel ,
building exhaust duct, and the radwaste building exhaust duct.
The area within a 16-km radius of RBS includes substantial portions of' West Feliciana, East Feliciana, and pointe'Coupee parishes, as well as small portions of East.and West Baton Rouge parishes. Most of the land in this area is devoted, in about equal proportions,' to forests and agriculture (pasture, verlous crops).
Wetlands, streams / takes, and urban / improved lands comprise the remainder of the immediate vicinity of the plant. - Besides St. Francisville, (4.1 km northwest),
human population centers near RBS are New Roads (10 km southwest) and Jackson (12 km northeast)._ Industrial f acilities in the immediate vicinity of RBS are Lambert Redi-Mix Company (1.8-km north-northeast); James River Corporation paper -Hill (5 'i km south)l Big Ca.lun No. 2 power Station (5 km southwest); and the Coips of Engl-neers concrete casting yard (5 km west).
The area within an 80-km radius of RBS'contains all or portions of 19 Loul- _;
sinna parishes .and . five Mississippi counties. This area has generally the same
. makeup as that of the immediate vicinity of RBS, although wetlands, agricultural
. lands, and urban / improved lands are relatively more extensive (at the expense of
.foiested lands) in the southwestern and southeaster n quadrants. _ Baton Rouge, -
centered at, about._38 km_ southeast, is the _only large city _ in the general vicinity of RBS.
During 1990, radiol _ogical environmental monitoring in the v.icinity of RBS was Lperformed 'by' the Gulf _ States litilities Companv-(OSlf) Environmental Services Group
_with support from the Plant- Staf f ~ - Radf ulogical programs Section in maintain-Ing/ calibrating air samplers and in reading / annealing thermoluminescence dosimeters. -
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RIVER BEND STATION RADIOLQQ1.Q&g,fNVIRONMENTAL OPERATING REPORT EQR__1190 2.0 RADIOLQQlCAL ENVIRONMENTAL MONITORING PROGRAM (RbfP) 2.1 PurD2se/ Bases i
The Radiological Environmental Monitoring Program (RDIP) was established to e provide representative measurements of radiation and- of radioactive materials, resulting from RBS operation, in those exposure pathways and for those radionuelIdes that lead to the highest potential- exposures of members of the public. The RDiP implements- Section IV.B.2 of Appendix I of 10CFR50 and thereby supplements the radioactive effluent monitoring program by verifying that the measurable concentra-tions of radioactive materials and levels of radiation are not higher than expected
- on the -basis- of the effluent measurements and the modeling of the environmental-exposure pathways. .
The REMP applies the concepts of indicator vs. - control and preoperational vs. operational intercomparisons to verify the adequacy of source controls and resultant human radiation doses. In addition to 100FR50, Appendix 1, the program i is based on guidance provided in the Nuclear Regulatory Commission's Radiological Branch Technical Position, Revision 1', November 1979, as well as NRC Regulatory Guides 4.1 and 4.15, 2.2 Environmental Radiation Exposure Pathways Elemeats of the RDiP monitor indications of the impacts of gaseous (airborne) ,
and liquid effluents released from River Bend Station. The specific methods used in monitoring. the pathways by which these effluents could lead to human exposure, based on existing. demographic information, are:
HUMAN EXPOSURE PATHWAYS (A) ' Airborne Pathway MonLLati nn Media
- Immersion Dose (external) Air Samples (Particulates and Radiciodines)
-Ingestion Dose (internal)- Vegetation / Food Crop Samples
- Air. Samples _
.(B) Direct T,xposure Pathway - M2nitorinn Medi.g External Dose Thermoluminescence Dosimetry (TLD) Area Monitors l- 4; g -N'=T'v'767-*Y wr ge v'sermaa-=P'-'1*ge'7y--y -ar,s.g-er3.,q-g_ew.g me--p.e4.mu.q.-g#y.--wm- e y q .ps .a .ew9,4a -+my w..qw-pt,g,wSe,e-mis,.w.,%e,m,-e w 44myevy.sg.m-elui.-,g r.p ypm -p-w---- w--ggs,,vr q,ggamy,.ygi ' u w e r-Ty g -s-.t1.ww
- - - . - . - - - - . - . - - . - - _ . - - - - - . - . ~ . _ .
RIVER BEND STATION RADlQLQQICAL ENVIRONMENTAL OPERATING REPORT POR 1990 (C) Vaterborne Pathway Monitorinn Mesj.i.a Ingestion Dose (internal) Surface Water Samples Groundwater Sample Drinking Water Samples Fish / Invertebrate Samples Shoreline Sediment Samples Immersion Dose (external) Surface Water Samples ._
Shoreline Sediment Sampics Site-related dispersion characteristics, demography, hydrology, land use, anticipated source terms, and the exposure pathways outlined above were considered in the selection of the sample media, campling and. analysis frequencies, sam-pling/ measurement-locations, and types of analyses. These criteria were used to establish both the-preoperational and operational phases of the RDIP.
The program that evolved during the preoperational 'oaseline) monitoring l phase incorporates all of the elements in the RBS 'rechnical Specifications (3/4.12.1, 3/4.12.2, 3/4.12.3) plus special study criteria, and is illustrated in Table'i and Figures 1 and 2.
2.3 LLnnd tise Qgpsus'for 1990 The 'arinual land use census .was conducted during the 1990 growing season in accordance with RBS Technical Specification 3/4.12.2. Table 2 summarizes the results-and notes changes in nearest receptor locations within 8 km f rom those identified in the Radiological Environmental' Operating Report for 1989. !
The 1990 ' census identifled residences within 8 km - of the RBS renEtor -
containment.-In all _ sectors except L (SW) and M (WSW). The nearest resident in sector M (WSW) was . beyond 8 km In 1990 versus.-4.3 km' in 1989, and the nearest resident ~1n sector P (WNW).was at 3.7 km in 1990 versus 4.1 kai in 1989.~ In sector-E (E), the garden identif f ed in 1989 was discontinued, and in sector 11 (SSE) a new -
garden was established for 1990 : The gardens identified in sectors P (WNW) and Q-
- (NW) are- the onsite gardens established in the sectors with the highest catculated annual average ground : level -D/Q. These gardens are REMP. indicator' locationsfor
- broadleaf vegetation (Table 1,. Fig. 2).
No dairy ~ animals were found w'ithin 8 km of RBS during the 1990_ census.
' llistorically, there had never been enough dairy sites to accommodate the minimum
~ RBS Technical- Specification requirements for analysis of milk (3 locations.within -
l5.km), so monitoring of broadleaf vegetation has.been performed from.the outset.
OSLI_ began a survey of meat animals within the 8 km radius of RDS during the-1990 census.. This _ initial survey identified beef herds in-all sectors except.L
-(SW).
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4 RIVER IlEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT l'OR 1990 TA11LE 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (Page 1 of 5)
Exposure Pathway Sample Point Description. Sampling arni Type and Frequency Alldistr JanDit_ Dia1anch And p.itn G 12!t. CRlitG119tLEI2Wt11Cy . O f AtuLhph, Airborne samples from 9 locational Patticulates and Radiolodines INDICATOR STATIONS Ad. River Bend Training Continuous air Aampler Charcoal cartridgel Center; 1 7 km N. with filter collection analysis weekly for weekly or au required radiciodine.
by dust loading. which. farticulate filtert ever in more frequent. analysis weekly for Stone beta and gamma tuotopic activity (3) following filter changes.
Compoalte particulate filters analysta Adl. River bend Station "
quarterly for gamma North Access Road acrona from lootopic activity, plant entrancei 0.6 km NNW.
APl. Near River Bend Station " "
Onsite Carden #1; 0.9 km WNW.
AQS2. " "
St. Francia Substation on US Hwy. (Bus.) 61 in St.
Franciavllle; 5.5 km NW (nearest community location).
CONTROL AND SI'ECIAL INTEREST STATIONS (1)
A1.C . Parlange Power Center " "
in Oscar; 20 km SW (Control).
Atl. Itiver Bend 8tation cooling - " "
tower yard; 0.6 km NNE. (2) '
AKS. River Bend Station River " "
Access Road;_2.8 km SSW.,(2)
ACS. CSU 5ervice Center compourut " "
in Zachary; 17 km SE. (2)
Alt h . -koof-of CSU Offlec Building, " "
l- North Blvd., Baton Rouge; 40 km i 855. -(2)
I' Direct Radiation- Measurements from 44 locationat INDICATOR-STATIONS' TAl. River Bend Training Thermo ttaminescence Camma dose monthlv Center; 1.7 km N. . domineters -(TLpa); and quarterly. (3) deplopment/ retrieval-monthly and quarterly. (3)
TA2. CSU Utility pole $246 " "
- at Jct. of La. ilwy.-10 and West reliciana Parish Road (WF) 2 in Elm Park; 8 km N.-
- tdt.- River Bend Station cooling. " "
tower yard; 0.5 km NNE.
TB2. Stub pole at Jct. La. Hwy. " "
- l. 965 and Audubon Lane (WF 17);
5 km NNE.
r t
7C1. Stub pole a' Jet. . U$ Hwy. . "
l- 61 and Old liighwuf 611 1.7 km NE.
TC2. Stub le along La. Hwy. 966 a "
. 0.6 km S. o Jct. La Hwys. 966 and 9651 7 km NE.
TDI. 150 m " -"
- 8. of .Jct.
stub kT tmle along 7 arx1 U$WI Hwy. 7, 61; -
1.6 km ENE, 6.
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RIVER DEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT POR 1990 TAllLE i RADIOLOGICAL ENVIRONMENTAL MONIT0ltlNG PROGRAM (Par,e 2 of 5) trposure Pathway Sample Point Descriptlun, 6ampling and Tyge and itequency
.AtidLkt 30ap,lt ll1AintlCtatiLilittEllD(L CulltClintL.llituutitty _DLt.In&lysta__,
Direct Radiatton TD2. 8 tub pole along 1.a. Thet moluminenrence Gamma do#4e monthly (continued) Hwy. 966. 4 km S. of Jct . doetmeters (TLDa); and quart erly. (3)
La. Hwys. 966 and 9654 6.3 deployment /tetrieval km F.NE. monthly and quarterly. (3) 721. Stub pole along WF 7 " "
i km B. of Jct. WF 7 and US Hwy. 611 - 1.3 km 8.
ft2. Cratal Power Center on La.
Hwy. 66, 2 km N. of Jet. 1.a. Hwys.
68 and 9641 10 km 2.
TF1, stub twile along WF 7 1.6 km " "
- 6. of Jrt. kr 7 and US Ilwy, 61; 4.3 km tst.
TF2. Or. La. Hwy, 954. 0.6 ks N. of Jet. La. 954 and U6 Hwy. 61; 6 km 1:ht.
Tcl. Stub pole along WF 7. 2 km S. " "
of Jct. WF 7 and US Hwy. 61; 1.6 km St.
TC2. Telephone Imle at gate to " "
Marathon Tank Farm on US Hwy. 61 near Delombrel 7.5 km St.
Titi. 8 tub pole at Illinois " "
Central Culf RR croneine of WF 7 (near Cranta bayou); 1.7 km Est.
TH2. First telephone pole on La. " "
Hwy. 964 N. of entrante to James River Corporation paper mill!
5.5 km sst.
TJ1. Stub pole near Itiver Bond " "
Station gate 823 on La. Hwy. 965; 1.5 km 8.
TJ2. Large tree along River Road. "
100 m N. of James River Corporation intake structureg S.8 km 8.
TKl . - CSU utility pole 8L10174 on " "
La. Hwy. 965. 20 e 8. of R86 River Accean Road; 0.9 km asW..
TK2. Stub pole at Jct. La. Ilvya.
414 and 415; 6 km BSW.
TLt. second utility pole on La. " "
Hwy. 965 8. of former ICG RR l crossing; 1.0 km $W.
TL2. Secogni utility pole along La. Hwy. 415 E. of Loutstana and '
Athaname RR croaning incar Patin's Dthe);-9.5 km $V.
TM1. First utility pole on La. " "
! crossing: 0.9 km WSW.
TH2, Utility pole along La. Hwy. "
- 981, about 3 km S. of Jct. La.
l-Hwyn. 961 and 10; 4.2 km kSW.
l ll- TNI. Utility Dole along La. Hwy, " "
l 965, between Rbs gatea $13 and #14, i 0.9 km W.
l.
TN2. Utility pole with electrical '" "
[
i-meter near vest bank ferry landing
[ - ( La . Hwy . 10); 6 km W 7
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RIVER llEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REP 0ltT l'Olt 1990 TAllLE 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (Page 3 of 5) 2xposure Pathwav Sample Point Description, 8an,giling and Type and frequency
.Aldl9EJtdRL .MA1A11ERM.l!1LtEt12tL CulltEuu!LhtWtut!
_ stl.Attelyfts _
Direct Rattiation -- T P l . Nemr River Bend Statton Thermoluminescence Gamma done monthly onette Garden it; 0.9 km WNW. doalmetera (TLDs)! and quarterly. (3) deployment / retrieval monthly and quarterly. (3)
Stub pole ebout 1.8 km N, " "
TP3 of former 100 RR trestle on Tunica Street. Sentern outaktrte of St. Ptr.nclaville; f.3 km WNW.
TQl. C$U property sign along La. " "
Hwy. 96$ atout 1 Km N- of RBS hurth Access houd; 1.4 km NW.
702. CBU gole at Jet. of North " "
Commerce and American Beauty Streeta, St. Franctsvillel 6.9 km NW.
TRj. RB8 North Accome knad acroes from " "
plant entrancel 0 8 km f4NW.
TR2. rwot "acockTree Road,along aboutnorth 1.8 kmside of VF
- t. of Jet,2 kr 2 alwl US Hwy. Gli 8 km NNW.
CONTROL AND 6PECIAL INTEREST STATIONS (1) s TAC. Telephone pole along US Hwy. 01 " "
about 200 m N. of Hamilton Station Water Tower, near Wakefieldt 18 km N.
TEC. Stub tote at Jet. of La. " "
Hwy. 955 and Midway Road 4.6 to N. of Jct. Le e Hwys. $$$ and
$G41 10 km E. (2)
TLC. Parlange Power Center in O part 20 km $W. ,
705. Utility pole at gate to tant " "
Louisiana State Hospital in Jacksoni 12.3 km NE.
TGS. 05U Service Center comimund in-Eacharyl 17 km St.
THS. Roof of GSU Office Build- " "
ing, North Blvde. Baton Rouse; 40 km $5E.
TKE. 'RBS River Access Road!
2.8'km SSW. (2)
_TLS. Utility polo near false River "
Academy algn at edge of New Roadal-9.9 km SW.
TQSl.- -Behirut Pentecostal Church -- " "
(opposite West Feligiana Hospital) near Jct. US Hwy. 61 and Ferdinand Street 1 4 km NW.
TQb2. St. Francia Subbtation on " "
US Hwy. (Busineam) 61 in St. Francia-ville; 5.8 km NW.
7053. Utility pole at Louiniaria " "
State Penitenttary dairy, near
. Angolan 35 km NV. (2)-
TRS. Stub pole at Jct, of WF 2 " "
and US Hvy. 61, near baina (West Feliciana High School); 9.2 km NNW. (2) 8
. _ - . -~ _ - -.- - - .- - - . - - - - . - . - . - - -
RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT FOR 1990 TABLE 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM I (Page 4 of 5)
Exposure rathway $ ample point Depeription, $amplingt and Type and f r equency and/or Sa d L A 1Ab h ant.fi1 M u1L C911K110tLif.trunne.y ,_91 ADAl%EED Waterborne SORFACE WAttk (4) 3 $WU. Hlasiaalppi River Weekly graba composited Monthly coepoaltet about 4 ks. upst reas f rom over monthly ani gamma tootopic, J the Rbs 11guld discharge, quartetty perioJ0. tritium (3) and near I.a. Hwy. 10 ferry beta analyala ($grona
). ,
oronning. Quarterly ctoposet&t <
tritlum analyals. ;
SWD. Himalanippi River about 4 km downat roam f rom RBS liquid discharge, near paler mill.
D t. . Rhs liquid dincharge line "
Hourly graba compoalted line at blowdown control monthly and quarterly, structure along Rivet Acevas Road.
l.RINRINC WATER (G)
Nearest downstream water Weekly graba compoalted Hunthly c<mponite t supply IH-10 bridge in over monthly and Daton Rouge. 53.9 km down. quarterly periods. fammaluotopicdgross ritium (3) an atteam from RBS liquiti dia- beta analyala (6),
charget people's Water sera Quarterly compositet vice Company in Donaldsonville, tritium analyala.
13h river km downstream from kB5 liquid discharge.
CROUNDwATER WD. Upland Terrace Aquifer Quarterly grab. Croar. beta, gamma well downgredient from plant, isotopio and trattian about 470 m SW. analyaec quarterly. ($)
WU. Upland Terrace Agulfer " "
well upgradient from plant.
about 470 m NN5 (controll.
-5HORELINE 6tD1HENT SEDD. East shore of Hinsin- f,emiennual grab. Gamma isotopio analyala alppi. Rivst about 4 km downs nomiannually.
stream from plant near paper mill.
S t:DLf. East shore of Hients. " "
sippi River about 4 km up-stream tros plant Hwy, 10' ferry. ($)neart.a.
Ingestion F15H AND INVERTtBRAft$
FD. One sample of each of' 8emiannually or Gamma taotopic snalyata three commercially and/or rec- acanonally when on edible p rt(swl neu - ,
reationally important specien available. cnntLlly or measonally. -
from downstream area influenced by RBS liquid discharge. (7) l'U. ' One- aample of each of " "
three commercially and/ or rec-reationally impurtant apecisa from upatream ases not intluen-ced by RDS llgold discharge i .(control). 8.s PRODUCE (8)
C1/C2. Two samples of each of Hunthly during growing Camma isotopic and three different kinds of leafy meanon. 1-131 analysea vegetables from onsite gardens monthly.
near the alte boundary in areas of highest calculated avetage fround-levelD/Q; I km WNW and
.1 km NW.
l- GQC. One sample of each of *hree " "
i different kinds of leaf y vegetablea
- l. from 1.a. State Penitentlary at l: Angola; 35 km NW (control).
9 e
i l
l t
, , _c . _.. ,. . - _ _ . _ . , _ - _ _ .___._ _ . . - - . - , - . - . - - , - . - - . ~ . . . _ _ _ _
RI'!ER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 00R 1990 TABLE 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (page 5 of 5)
EDIIS_t (1) For purposes of data summary, comparisons, and discussion, the sampling locations designated as "Special Interest" are treated as indicato stations if they are within 16 km of RBS and control stations if they are beyond 16 km.
(2) Sample / measurement location not required by RBS Technical Specifications--(not identified in ODCM).
(3) -Sampling and/or analysis frequency greater than required by RBS Technical Specifications and ODCM.
L(4) The upstream (control) sample is taken at a distance beyond
- influence of _ the plant . discharge. The downstream (indicator) sample is taken in an area beyond but near the mixing zone.
(5) Gross beta analysis not required by RBS Technical Specifications and ODCH.
(6) Drinking water sampling / analyses not required by RBS Technical Specifications aad ODCM. (No drinkina water pathway exists
'due to extreme distance to nearest intake). The upstream surface water sampling location (SW) is used as a " control" .
for drinking water analyses comparisons.
(7) Preferred species are river shrimp (tlEGlatEhlm Alt 19nc), blue
' catfish (1s13h}gs h1LCA11ts), and f reshuter drum ( Aplodinginti gLunnieng); if. these are unavailable, other edible species may-be substituted.-
(8) No irrigation pathway exists due to t.he extreme distance of nearest domestic water intake (see Note 6);. leafy vegetables are- sampled and analyzed because -of limited availability -of milk samples.
10-
_ . - . ~ . . . . _ . . _ , .,___-.._u- -, _. , , _ . - _ , _ . . _ _ , . - _ _ . . _ . . . _ _ _ _ _ _ __ .a
RIVER BEND STATION RADIOLOGICAL E:WIRONMENTAL OPERATING REPORT POR 1990 TABLE 2 RESULTS OF LAND USE CENS ,
Nearest Range Nearest Range Nearent F.ang e Nearest Range Jggior ReAMenge (km) JudC J Lo ) Jt L iltai titaLAnimalI _.DAl A (N) Jonce 1.8 Jones 1.6 - - Davis 1.9 9 (NNE) Dreher 1.6 Harvey 1.8 - - Harver 1.8 C (NE) Magee 1.5 H gce 1.5 - -
Daniel. H. 1.7 D (ENt) Lambert 1.4 Daniel, t.l. 1.6 - -
lambert 1.0 2
t (E) BicLham 2.2 - - - Daniel. E.1. 1.2 F (Est) Shelton 3.4 tisworth 3.6 - - Dantet. E.I. 1.2 G (SE) Milla 6.6 n111s 6.G - -
Rickham 3.5 H (SSR) Koffman 1.7 Koffman 3 1.7 - - Daniel, d.i. 3.0 J (S) Bliss 1.8 Bliac 1.8 - - Daniel, E.1. 3.5 K (SSW) Culltory 7.4 Guillory 7 -4 - - Daniel, E.1. 3.5 1 ($W) - - - - - - . -
2 Langola M (WSW) - - - - - 5.0 N (W) Lacost 6.1 - - - - Langols 5.0 4
P (WNW) Dietrich 3.7 Gsu il 1.0 - -
Hardovin 7. 4 0 (NW) ninmer f.3 CSU 42 1.1 - - Cavin 1.3 5
R (NNW) Young 1.7 tonroe 3.0 - -
Klein 2.4 1 The initlal survey for meat animal location was performed in 1990.
2 The 1980 receptor location was discontinued for 1990.
3 There was no receptor location listed for 1989.
4 The 1990 receptor location was nearer than the rect.ptor location listed in 1989.
5 The 1990 receptol location was f arther than the receptor location listed in 1989.
11
- . , ._ _ _ . ~ ~ _ _ _ _ _ _ _ __ -
m___ __ _
l I
~
RIVER BEND STATION 1 - _.RADIOLOGI_ CAL ENVIRQMJNIALMIBAIH9_BEPORT FOR 1990 2.4 Interlaboratory Comtwrison p a ram ResttLtg for 1229 The Environmental Services Group participated in the U.S. Environmental pro- i tection Agency (USEPA) Laboratory Intercomparison Ptogram during 1990 in accord-ance n th RBS Technical Specification 3/4.12.3. RBS result s (Table 3) wer e within 3
- the warning limits for the normalized range (precision) for all analyses, and within i the USEPA "known" value (accuracy) for all_ but two analyses, namely, the gross beta in water for 9/21/90 and the total potassium in milk for 4/27/90. The discrepancies
=for the gross beta in water for 9/21/90 and for potassium in milk for 4/27/90 are discussed below. The USEPA discontinued the cross-check media for " food" in 1989, and _although milk' sampling and analysis is not required of RBS at this time, the
.results for the cross-check media for " milk" are. included as a gauge for the " food" sample analyses (1.e., vegetation and fish) performed by RBS.
. 2.5' Pronram Fxecotions
. Certain samples and analyses were inadvertently omitted or unavoidably ultered I during'the 1990 operating period, out of a total effort of 1754 samples collected.
and-2339: subsequent analyses-performed. These exceptions and the reasons for the-
-omissions / alterations are delineated in Table 4 in accordance with- Technical Specification reguirements. . Corrective _ actions and impacts on program quality' are
= discussed below, t
Brief storm-related pover. outages impacted one' indic ator air sampler -( AA1) ic January, five indicator end special 11nterest air samplers ( AA1, AB1, AR1, ANS, and AP1) -in June. and one control air sampler (ALC) in >ugust. From 3 percent to
- 20 percent of each of_ the expected sample volumes was lost due to the power outages.
. A fractured (cause unknown) electrical service pole which suppot ts the weathet head
.and breaker box for the AKS air sampler necessitated disconnection of power, further
- 1mpacting L AKS _-during November and December. The time taken to replace the electricalt serviceL to AKS,--a sampling location not required by RBS Technical
~ Specifications, -resulted in the loss 'of approximatriy 83 percent - of the expected sample volume for AKS over a 5-week period _. Thes* losses are not deemed to have
, shad a aignificant impact on program quality, espe ially since the plant was shut
' down for. a refueling outage f rom October to December,1990.
Limited variety in the crops due -to a hard freeze during the winter months i
, atethe state. penitentiary (GQC) and both site gardens resulted in failure.to obtain 3 out~ of 36 required control samples and 3 out of 72 required indicator samples 'of l broadleaf vegetation during = 1990. - This did not significantly impact program
?
Equality _One.of the samples obtained from the control leestion (GQC) in June did not satisfy-the LLD requirements due to its low mass.
One USEPA cross-check' analysis for gross beta in water, dated 9/21/90, was
~
M outside the control Timits for accuracy. The sample activity reported by RBS-had been_ calculated using an .-Incorrect factor' for sait density attenuation of beta counting efficiency. When the activity-of the r,ross beta sample was recalculated i
with the. correct salt density factor, the result wau'well within the ilmits for accuracy. One'USEPA cross-check analysis for total potassium was outside the.
control limits- for accuracy. The mass for potassium reported by RBS had been converted from K-40 activity using the incorrect conversion factor (1.19 -instead of 1.133).
12 4dW, , r - , -
. _ - -, -_c., - . - - , - - - . - *- - ,-
A
RIVER llEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT FOR 1990 TABLE 3 USEPA INTERCOMPARISON (CROSS-CllEClO PROGRAM PARTICIPATION RESULTS 6 AMPLE TYPE USEPA kbS Rb5 RbS AVEkAGE kE5 ULT
_inAluin ) MfALUiut "KMOEE"._EA11E" 1Alli Edid hd @il' 1All l'at11c1Rattt3d d _._DAIL AIR FILTER 3/30/90 Beta 31.0035.50 33.67 60,92 0.354 32.1913.0%
(pCL/ filter) 3/30/90 Cm-137 10.0035.60 12.00 +0.69 0.000 11.5612.05 8/31/90 Beta 62.0015.80 69.33 e2.54 0.354 04.66 t 0,77 6/31/90 Cs-137 20.00e5.60 23.00 +1.04 0.354 22.7013.61 MittP 4/27/90 1-131 99.00111.60 100.67 e0.29 0.354 95.49tB.13 4/27/90 Cn-137 24.0015.60 24.33 60.12 0.473 24,6513.03 4/27/90 h (nat) 15!0.00190.10 (1647.00)f (+2.15) (0.409) 1545.361117.33 WM 1/26/90 Beta 12.0015.60 14.P0 .0.09 0.000 12.9112.*2 (pCA/ liter) 2/09/90 C0-60 15.0035.60 15.00 40.00 0.236 15.a.11.26 2/09/90 In-65 139.00t16.20 149.00 *1.24 (5 338 s'm.9339.60 2/09/90 Ru 106 139.00116.20 134.33 -0.56- 0.464 00114.22 2/09/90 Ba-133 74.0018.10 14.33 e0.0B 0.16' :916.21 2109/90 co-134 18.0015.50 17.67 -0.12 0.11- 17.00 2.14 2/09/90 Cs-137 18.0015 80 19.33 e0.46 0.1-
> 2.43 2/23/90 h-3 49761575 4544 -0.46 0.15' 191 . 640.99 4/17/90 Deta 52.0015.60 51.00 -0.35 0.915 t s . t.616. 39 4/17/90 Cn-134 15.0015.60 13.67 -0.46 0.11- 14.4411.77 4/17/90 Cs-137 15.0015.60 15.67 +0.12 0.1.6 16.60tl.88 5/11/90 Deta 15.0015.80 15.00 e0.00 0.23' 16.1613.65 6/05/90 co-60 24.00t 5.80 25.67 +0.55 0 .11 t. 5.12 2.69 6/08/90 Zn-65 148.00117.40 159.67 +1.35 0.11h '49.16112.30 E/08/00 Ru-106 210.00f24.30 195.00 -1.24 0.647 201.0l+17.01 6/03/90 ba-133 99.00 111.60 102 00 e0,52 0.000 96.3315.16 6/05/90 Cn 131 24.0015.80 ? 'O +0.00 0.000 23.2612.10 6/Ob/5J Cc-137 25.0015.50 4. s7 +0.53 0.116 26.2112.61 6/22/90 h-3 29331141.4 2S47.67 -0.41 0.206 2966.60 12$5.64 6/?0/90 I-131 .0016.00 36.67 -0.67 0.295 40.2614.10 te/ 1/90 Beta 10.001 5.60 (13.00)I (tl.06) (0.236) 10.9112.25 10/05/90 Co-60 20.0015.80 22.00 +0.69 0.000 20.53t2.53 10/05/90 Zn-G5 115.00113.90 126.00 e1.59 0.345 116.2519.89 10/05/90 Ru-100 L51.00117.40 147.00 -0.46 0.158 140.39tl5.33 10/05/90 Da-133 110.00112.70 111.67 +0.26 0.107 107.7319.22 10/05/90 Cs-134 12.0015.80 11.67 -0.12 0.116 11.8912.09 10/05/90 Cn-137 12.0015.50 13.67 e0.56 0.118 13.1112.17 10/10/90 H-3 7201.001833.50 1403.67 +0.4h 0. 4 ?io 7125.0St671.93 10/30/9D Deta 53.00 1 5.60 53.33 to.12 0.945 50.78 16.32 10/30/00 co.134 7.0015.60 7.00 +0.00 0.000 1,4911.11 10/30/90 Ca-137 5.0015.40 4.67 -0.12 0.118 5.94 11 55 (a) 05 EPA "known" values are listed with a range reflecting control (3 algma) limits.
(b) The normalized devlation f rom the "known" value is computed by USEPA f rom the deviation and the standard error of the mean; +2.000 in the warnin8 limit and e3.000 in the control famit.
(c) The normalized range is computed by USEPA from the mean rantle , the control and the utandard error of the range; +2,000 in the warning timtt und +3.000 tu the control limit1 lmit.
(d) The grund average of all participants' results (excluding outtlers) is listed with the e x pe r imen t al (calculated) ulema for all laboratorien.
(e) USEPA discontinued the crosa check media " food" for 1989. Although milk sampling and unalysts by RilS is not perf)rmed, the cruau-check oumples of milk tie r e unalvred, and the data ia.cluded as a gauge of the " food" sample ti.e. vegetation, flah) unalyHe9 performed by RHS. The units for the nuclides 1-131 and Os-137 ate pct / liter, und for the element K la ag/ liter.
(f) The results reported to USEPA e.nre calculated with incorr ect correction /converuton f actorn. The uppropriate values are reportsid here with the values for "normaltzed devAntAon from the known l value" and for " normalized range" calculated by RBS personnel.
13
-- . -. . . . .-.- - . = . - . - . - . . - .- . - .- - . - - - -- ,
r g .- 4 RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT POR 1990 TABLE 4 MONITORING PROGRAM EXCEPTIONS samA19_lype Petiud LO SMIC_ 'xcS R iondtegon AJr particulates and 1/02 - 1/09/00 AA1 About 20% of normal weekly sample volume Radiolodines 1/09 - 1/16/90 not collected due to power outage.
5/29 - 6/04/90 AAl, Atl*, AR1, About 8% of normal weekly sample volumen AKS*, API not collected due to power outage.
6/04 - 6/11/90 AA1, AD18, AR1, About 4% of normal weekly cample volumes-AKS*, API not collected due to power outage.
7/30 - 8/06/90 ALC About 3% of normal weekly sample volume not collected due to power fatture.
8/20 - 8/27/90 ALC About 16% of normal weekly sample volume not collected due to power failure.
11/12 - 11/19/90 AKS* About 58% of normal weekly sample volume not collected due to power outage (elec.
rio service torn loose from the step-down transformer on the utility pole).
11/19 - 12/20/00 AKS* None of normal weekly ansple volume was collected due to power outage (electric nervice had to be re-strung from the transformer),
BroadleafVegetation January CQC Only one (1) of three (3) samples ob.
tained due to limited availability caused by hard tresse.
" January C2 only two (2) of three (3) samples ob.
tained due to limited availability caused by hard freeze.
March G Q Only two (2) of three (3? samples ob.
tuined due to limited availlbility. ,
Harch C-1 Only one (1) of three (3) namples ob.
tuined due to limited availibility.
I " June CQC One (1) sample of three (3) analyzed
- i. failed the LLD requireeent.
Flah and Invertebratea Spring / summer 1990 FU - Only two (2) of three (3) samples ob.
tained due to limited availability.
l1 l Water, Cross Data -Aprl! - CWS iteaultn varied by more than 10% on a sollt sample.
I:
l 'USEPA cross-check, 9/21/90 N/A Re'aults calculated using incorrect V Grous Boto-in. Water. aalt -density factor for attenuation of bata counting efficiency; correct j; activity was obtained when correct fac-J .
tor used in calculation.
Water 10/17 - 10/24/90= CWS About 58% of hourly componite ala-quota not obtained due to power outage.
Direct Itadiation' (TLD) June- TKS* The recorded high net normalized gamma done, possibly due to severe moisture damage and corrosion observed in microecopic examination of the dost-meter's phosphor elementn.
14
, e - y- ,+#,is +--
.- . . . - . . . - -. .- . . ~ - - .. . - - - - - . - - . ~ . - - ..-.
1, .. : )
i R1VI'R BEND STATION' R@lDLOGICAL ENVIR0tidl31AL OpERAUKQ_REEQRLfQJL191(! _.
~
13.0 - LETERPJGIAUDN OP llDip REStiLTS 3.1- Summary of oneratinaaL.JERP_Real.is. I Honitoring resul'ts for the exposure pathways are itemired in Appendix A and summarized .in' Table 5. f rom which measured act ivities of the natural ty-occurring - ,
. daughters' of uranium ' and thorium. are excluded. For purposes of data summary, comparison, and discussion, the sampling locations designated "Special-Interest"
-in_ Table 1 are treated as indicator stations if they are: wit hin 16.km of RBS and -
control stations-if they are beyond 16 km.
, 3.1.1 Airborne Exenguire pathay - Mounurements of radiolodine and other gamma-emitters were all below their-respective LLDs that is, " undetectable" at
' the required analytical. sensitivities.- During the two week period f rom 5/21/90 to 6/4/90, traces of radiolodine and noble gasses were mc ured at three downwind air sample stations, due to - the presence of a small amount of failed fuel in the reactor. The releases resulting from this failed fuel were minimized by operational controls (e.g., repairing minor steam leaks), after which no further measurements
- of radiolodine and noble gasses were observed at any of the air ,ampling stations.
This fuel was t emoved during the -refueling outage in the 4th qua. cr of 1990. Gross bcLa activities averaged 0.025 pC1/m 3 at Indicatur locations and 0.0h. pol /m3-at control. locations.
-i 3 ,1. 2 ' Direct ihngJnre pathwar - The monthly averac samma < v wrer
-farlindicator and control locations were 4.20 and_4.35 mil 1Ir.s 1o. i. , W ectiv-ely. Quarter ly exposures averaged 12.39 mR total at indicator locatio..a r.ud 12.90 mR' total at control locations. >
3.1.3 Ra.t erliorne Exit 0Hte pathway - No gamma-emitters wet e' measured in surface sater;or in drinking water at levels approaching the Technical Specification LLDs The samma emitt ers Mn-54, 00-58, Pe-59, C0-60, Nb-95, 7.r-95., Cs-134 & 137, and Ba-140 were measured .1n a few monthly composite sampies f rom the discharge 1Ine LDL at concentrations between Oe9 and 56 picoeuries per liter. Gross beta activities = =!
Ja surf ace water averaged 40.4 pC1/1 in the discharge line DL and f rom 3 to 17 pCi/1 atfall other stations. ' Tritium (11-3)- activities in surface vateriaveraged -20450 :
pCl/l in Ltheidischarge .line DL and were- below detection ' limits at ' all other
- locationn. Gross beta' activities ' averaged 4.7 and 6.0 pol /l in the downgradient WD ,(indicator)L and upgradient .Wlf (control) groundwater, respectively._ Besides-natur4lly-occurring _ gamma emitters, Os-137 was measured -In Mississippi River shorelinc . sediment above (75LpC1/kliogram dry) and below (10 pCi/kg dry) the RBS l liquid discharge outfall, ' As in the case of the airborne Cs-137 uctivity,lthese-
~ slightly elevated levels (relative to baseline conditions) are probably attributnble '
to.the--1986 incident at Chernobyl,-Russla. ;
15
.u _ . . = _ _ , _ - - . _ ._ _ _ , __ .- .. . . _ . .
TABLE 5 P.ADIOLOGICAL ENVIRONMENTAL MONITOPING PROGRAM SUMMAltY (Page 1 of 4)
River Bend Station Docku: Number: 50-458 West Peliciana Palish, Louislana Reporting Peliod: 1/1/90 -12/31/90 I
Med itua ' ' Tytw and Lower Limit All Indicator Location with liighest Control Numtier of Ivthwr, Sempled Total Number of htationn, Annual Mean Locationo Nonroutine (Unit of of Analyseu Detectton1 Mean (fl' N,tunq_ . tig gn_(()2 Mean ( f 12 Regn t ed Meanurement) l'erformed (LLD) Sangu Dirt./Dir. Range Range Renults cros6 Beta 0.01 0.025 (305/312) Alt ! 0.026 (52/52) 0.020 0 AirPartlp)
(pct /m late (468) 0.018 - 0.032 0.5 km hNE 0.021 - 0.032 (L56/1566 0.006-0.028 ite- 73 NONE 0.121 (262/312) AR1 0.137 (45/522 0.111 0 (468) I;EQUliCD 0.057 - 0.244 0,8 km NNW 0.077 - 0.240 (125/150) 0.057-0.222 k-403 tion E 0.56 (309/312) Aks 0.010 (46/52) C.52 0 (465) R t 4U lit ED 0.233 - 2.270 2.6 km ssk 0.253 - 2.270 (153/156) 0.212-0.65S Ch-1N 0.05 All. <LLD ALL <l.LD 0 (106) 09 137 0.06 0.012 (4/312) AH1 0.015 (1/521 0.013 tl/52; o (468) 0.009 - 0.0l5 0.6 km NNW ningle galue single value Air Hadiolodine 1-131 0.07 0.020 (5/312) Akt 0.024 42/52) ALL <LLD 0
( pc i/r.J n (168) 0.016 - 0.031 0.6 km NNW 0.016 - 0.0:11 Direct (TLD)4 Canma 4.20 (456/456) TM2 4.96 (12/l2) 4.35t72/72) 0 (mR Total) Monthly 2.39 - 11.17 4.2 km Wsw 4.06 - 6.03 3.24 - 5.54 (456)
Gamma 12.39 (152/152) TM2 14.40( 4/l) 12.90(24/24) 0 Quarterly 7.81 - 17.37 4.2 km WSW 13.52 - 15.49 10.31-15.96 (176)
Surface Water H-3 3000 20152 Ll/6) DL 20152 (4/4) All. <LLD 0 (pC1/ liter) (12) 5705 - 35450 5705- 35450 Mn-54 15 8.05 (12/24) DL 8.05 (12/12) A t.t. <LLD 0
( 3ti ) 1.19 - 24.S 1.10 - 24.6 Co-58 15 3.63 (11/24) p l. 3.63 (11/12) All. <LLD 0 (36) 1.01 - 10.7 1.01 - 10.7 to-59 30 4.70 (6/21) DL 4.70 (6/12) ALL <l.LD 0 (36) L.77 - fL44 1,77 - 8.44 Co 60 15 19.4 (l2/21) DL 19.4 (12/12) ALL <LLD 0 (36) 2.85 - 55.5 2.85 - 55.5 Zn-65 30 All < LLD) ALL (LLD 0 (36)
Nb-95 15 3.36 (2/24) DL 3.36 (2/36) A!.L < l.LD 0 (36) 2.56 - 4.16 2.56 - 4.16 Zr-95 30 1.03 (1/24) DL 1.03 (1/12) ALL <LLD 0 (36) (single value) ningle value I-131 15 ALL (Lt.D Al.L <LLD 0 (3G)
Cn-l34 15 1416 (2/24) DL 1.16 12/12) ALL (LLD 0 (36) 0.91 - 1.41 0.91 - 1.41 Co-137 18 1. 0'l (2/28) SWU l.11 (1/12) 1.14 (1/12) 0 (36) 0.92 - 1.16 4 km ningic value single value upstream fja - 110 60 1.16 (t/24) DL 1.'6 (1/12) ALL <LLD 0 (36) (Lingle value) single value ,
16
TABLC 5 RADIOLOGICAL ENVIRONMENTAL. MONITORING PROGRAM 3DIMARY (Paga 2 of 4)
River Bend Station Docket Nutber: 50-458 West Feliciana Parish, Louisiana Reporting Period: 1/1/90 -12/31/90 Medlum or Type and Lower Llmlt All Indicator Location with Highest Control Number of Pathway sampled Total Number of Stations Annual Hoan Locations Nonroutine (Unit of of Atu11yr.es Detection I Mean (f)2 tiwge MpattiL}2 Mean (f)# H eixir t ed Mtssurement) Performed (LLD) Range Dlut./Dir- Range Range Results Surface Water La-140 15 ALL (LLD ALL <LLD 0 (pCl/ liter) (30)
(continued)
Grous beta 4 24.96(24/24) DL 40.30 112/12) 9.75 (12/12) 0 (36) 3.36 - 49.97 20.69 - 49.97 5.00 - 14.32 Croundwater H-3 3000 ALL <LLD ALL <LLD 0 (IC1/11t e r ) (6)
Hn 54 15 ALL <LLD ALL <l.LD 0 (8)
Co-58 15 ALL <LLD ALL <LI.D 0
($)
Fe-59 30 ALL <LLD A LL < LI.D 0 (8)
Co 60 15 ALL <lLD ALL <LLD 0 (8) 2n-65 30 ALL <LLD ALL <LLD 0 (S)
Nb-93 15 ALL <LLD ALL sLLD 0 (8)
Tr-95 30 ALL <LLD ALL <LLD 0 (8) 1-131 15 ALL <Ll.D ALL (LLD 0 (8)
Ca 134 15 ALL <LLD All (LLD 0 (8)
Ca-137 18i ALL <tLD ALJ. <LLD 0 (6)
Da-140 60 ALL <tLD ALL <tLD 0 (8)
La-140 15 ALL <!,LD ALL <LLD 0 (8)
Gross Heta i 4.73 (4/5) WU 6.03 (3/5) 6.03 (3/5) O L10) 3.02 - 5.73 I?D m NNE 5.25 - 0.89 5.25 - 6.89 Drinklng Water 5 H-3 3000 ALL <LLD AL <LLD 0 (pC1/ liter) (l)
Hn-54 15 ALL <LLD ALL <tLD 0 (12)
Co-58 15 ALL <LLD ALL tiLD 0 (12)
Fe-50 30 ALL <llD ALL <LLD 0 (12) i 17
e TABLE 5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
(Page 3 of 4)
River llend Station Docket Number: 50-458 West Felic.iana Palish, Louislana Regiorting Pellod: 1/1/90 -12/31/90 Medlum or type and Lower Liett All Indicator Location with Highest Control Number of Pathway Sampled Total Number of S t a t !Oftst,2 Annual Mean Locat toria, Nonroutino (Unit of of Analyticu betoctton I Mean ( f 1 .JAgn _11 NILL (1 2 Mean (f)* keported
'toanurement ) Performed (LLD) Range Dist./Dir. Hange kange Reuutta Drinking k'ater$ Co-60 15 1.60 (1/12) Donaldson- 1.60 (1/12) All < LLD 0 (pC1/11ter) (12) (olngle Salue) ville (ningle value)
(continued) 136 km Zn-65 30 A1.L <l.LD downstroom ALL <LLD 0 (L2)
Nb 9$ 15 ALL (LLD All. < Ll O O (12)
Zr-05 30 ALL RLD Alt (LLD 0 (12) 1-131 15 Al.L < l LI: ALL < LI D 0 (12)
C0-134 15 A!.L <LLD ALL <tLD 0 (12)
Cs-137 18 0.61 <!/12) SWU l.14 (1/12) 1.14 (1/12) 0 (12) (single unlue) 4 km (ringle value) alngle value upstream Ba-140 60 tLL iLLD All. <tLD 0 (12)
La-lio 15 J <tLD ALL tLLD 0 (12)
Crosa Betu 4 9.47 (12/12) SWt' 9.75 (12/12) 9.75 (12/12) )
(12) 4.53 - 14.3ti 4 km 5.00 - 11.32 5.00 - 14.32 upatrans Shoreline Bo-73 NONE SEDU 403 (1/2) 10$ (1/2) N/A Sediment 6 (4) *EQUIRED i sm (n(ngle value) single value (pC1/kg dry) upt.tream h-40 3 NONE l-(11$ (2/2) SEDD 14115 (2/2) 10567 (2/2) N/A (4) REQUIRED 13706 - 14528 4 km 13706 - 14521 477.)-16361 downstream l CH-134 150 ALL <LLD ALL <LLD 0 (4)00-137 150 LO.0 (1/2 ) SEDU 74.6 (l/2) 74.6 (1/2) 0 (4) (htsgie salue) I km (ningle value) ulngle value urntreaa 3
Flah/ h-40 NONE 3 1511 ( 8/8 ) tD 3161 <h/S) 2919 (5/5) 0 invertebratus (13) REQUIRED 2S37 - 4081 4 km 2637 - 40SL 1977 - 3508 (pCL/kg wet) downstream Mn-51 130 AlL <l.LD ALL (LLD 0 (13)
Co-55 130 ALL < LID ALL <LLD 0 (13)
Fu-59 260 Al.L <LLD ALL <tLD 0 (13)
Co-60 l 'iG AL L < LLD FU 7.49 (1/5) 7.49 (1/5) 0 (13) i km (single value) Hlngle value upss t r east Z r.- G 5 260 ALL cl.LD ALI. sLLD 0 (13) 18 .
TABLE 5-RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
(Page 4 of 4)
River Bend Station Docket Number: 50-458 West l'eliciana Pariin Louisiana Reporting Period: 1/1/90 -12/31/90 Medium or Type and Lower Limit All Indicator Location with Highest Control Number of Pothway Sampled total Number of Stations Atmua l . Hean ' . Locations Nontoutine (Unit of of Analyses Detectionl Mean (f)2 goo MeatLLL} 2 Hean (f)2 Reported
'Hoasurement) Performed (LLD) Range Dist./Dir. Range Range Results riah/- .
Ca-134 130 ALL <LLD ALL <LLD 0 Invertebraten (13)-
(pci/kg wet)
(continued) _ Co 137. 160- 7.07 (1/6) FD 7.07-(1/8) 1.67 (1/5) 0 (13) (single value) 4 km (single value) single value downstream Broadteaf- Be-73 NONE 310 (44/69) CQC 54" (21/29) 547 (21/29) N/A
. Vegetation (98) REQUIRED 71 - 2040 35 km NW 56 - 2292 56 - 2292 (pC1/kg wet)
-K-403 NONE 3503 (69/69) CQC 4374 (29/29) 4374 (29/29) N/A (98) REQUIRED 1616 - 5794 35 km NW 1926 - 8287 1926 - 8287 1-131 60 ALL (LLD ALL <LLD 0 i(98)
Ca-134 60 ALL < LDD ALL (LLD 0 (98L Ca-137 80 20.0 (5/69) CL 20.0 (5/34) 11.6 (1/29) 0 (98) 15.8 - 27.6 1 km WNW 15.8 - 27.6 single value Bu-140 NONE 47.2.(1/69) C1 47.2 (1/34) NONE O (98) REQUIRED (ulngle value) I k.m WNW (Mingle value) MEASURED EQIfdli
- 1. ' Lower Limit 'of Detection (LLO) as defined in RBS Technical $pecifications (NL' REC-il72).
2 -- Hean and range based on detectable measuremento only. Fraction of detectable measurements at spe.
cified locations is indicated in parentheseo. (f) 33, Specific activAtles!found for certain common and readily distinguished, naturally occurring nuc-lides are included to provide perspective. It should also be noted that other gamma emit ting,
!: naturally occurring nuclidea (eig4, primordial series) are of ten detected but not reported because of the complexitica and uncertainties of specific identification.
i l
i.
l l
19
- - ..:-__..- -, . ~ . . - - . n ,-c + - , , , , , - , - ~ , , , , . , , , - ,, - , . . , . , ,
4
.a,. ..
i o
RIVER BEND STATION
,_ -RADIOLOGICAL ENVIRONMENTAL. OPERATING REPORT _Ip2 1990 a
3.1.4 111gg.stion Exopsure Pathway - Specific activities for radiciodir.e pere below Lthe required LLD in the' ingestion pathway monitoring media during 1990. i
- 16. . addition to' naturally-occurring samma emitters, Cs-137 was measured in both broadleaf vegeta-tion and fish from the indicator locations, and in fish f rom the contre' location. The Cs-137 averaged 20.0 pCi/kg wet- (<LLD) in vegetation from ite garden' in Sector p (G1), a single measurement- of 7.07 pCi/kg wet was
. a' downstream fish, _ and a single measurement of 1.67 pCi/kg wet noted in _
fish._ These slightly elevated Cs-137_ activities, which are two orders of n taae below those - that would be " reportable" if due to RBS releases, are p.obably attributable to the Chernobyl incident.
3.2 Romparisonjf Operational and Baselint.BEMP Res'411g 5 Radicioolne and other gamma emitters _ in the airbort e exposure pathway were not measured at levels above the ' required 'LLDs during 1996. Gross beta activities on air particulate filters averaged 0.025 pCi/m3 at indicator and_0.020 pCi/m3 at controi locations in 1990, compared to 0.03 pC1/m3 at both indicator and control
' locations during the.preoperational phase of the REMP (Appendix B).
In the direct exposure pathway, the 1990 net average readings for monthly.and quarterly TLDs from both indicator and- control locations were slightly. lower than ,
the. corresponding values for the baseline period. Thus far, no appreciable dif fer- !
. erences .have been observed in TLD exposures between -indicator and control locations or between the same-' locations from-on_e year to the next.
In the waterborne exposure pathway,_ average activities analyzed for required gammeemitting nuclides were measured below the RBS Technical Specification LLDs i
!during ' 1990 = as ' h'ad J been the case during the preoperational phase -( Appendix B).
. Gross beta.andl tritium levels in_ water.are compared below:
WATERBORNE AYERAGE -GROSS DETA (pC1/l)
Pre-n ODatational 1936 _1M1_ JML 1939 ._1 MIL surface Water,-Upstream (4 sm) 7.80 5.76 8.93 9.30 7.79 9.75 RDS Discharge f.ine- N/A 10.10 21.76 32.38 32.05 40.39
' Surface Water, hwnstream -(4 km)-_ 8.10 5.69 8.59 8.66 7.41 9.52- i h: - -Drinking Water (Donalduony t tle) - 6.80 5.66 - 10,40 8.24 8.23 -9.47 EUpgredient Groundwater 6.00 2,25 2.22- -2.45 3,61 --6.03
. Downgradient Grosndwater 4.00 2.61 1.95 2.20 3.44 4.73 WATERBORNE AVERAGE TRIT!UM (pCi/l')
Pre-QPALLLLO.ual _lMS 1987 JML J L 1MD_ ,
Surf ace Water, Upstream (4 km) <3000 <452 <444 <586 <554 <209
- RBS Dincharge Line N/A 1023 1140 2272 3169 20452
' Surface = Water, Downstrcum (4 km)
<3000 (44 <604 <502 <554 <209 Drinking Water (Donaldsonville) (3000 <462 <$03 <586 (557 <210 Upgradient Groundwater- <3000 <446 (601 (780 <681 (211 L Downgradient Grouru.twater <3000 (446 <600 (779 4872 (207. ;
i 0
20
_._ _.._ . _ - - _ _ . _ _ _ _ _a
_ _ . . _ _ _ _ _ _ _ _ _ _ _ _ ~ _ .. ._ _ _.__.m _ _.- . - .
F j ..
RIVER BEND STATION '
? RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT-POR 1990 3.1. 4 _ hutestion Exposure Pathway -
Specific activities for radiolodine were below the required LLD in the ingestion pathway monitoring media during 1990.
InDaddition to naturally-occurring gamma emitters, Cs-137 was ' measured in both
- broadleaf vegetation. and. fish from the indicator locations, and in fish from the control location. The Cs-137 averaged 20.0 pC1/kg wet (<LLD) in vegetation from the onsite garden in Sector P~(G1), a single measurement of 7.07 pC1/kg wet was r
noted 'in a downstream fish, and a single measurement of 1.67 pCi/kg wet noted in upstream fish. These slightly elevated Os-137 activities, which are two orders of magnitude below those that- would be " reportable" if due to RBS releases, are ;
_ pro ab bly att ributable to the Chernobyl incident.
+ 3.2 G2mparison of 0.nerational and Baseline REMP Resulta
- - Radiciodine and other gamma emitters in the c.irborne exposure pathway were
-not measured at levels _ above the required LLDs during 1990. Gross beta-activities s
.on air particulate filters-averaged 0.025 pC1/m3 at indicator and 0'020-pC1/m3 atz control locations in 1990,_ compared Lo 0.03 pC1/m3 at'both indicator and control locations 'during the preoperational phase _ of the REMP ( Appendix B).
In the direct exposure pathway, the.1990 net average readings for monthly and
- quarterly TLDs: from both indicator and control locations -were slightly lower than the corresponding values for the baseline period. Thus f ar, no appreciable dif fer-erences have been observed in TLD exposures between indicator and control locations
- or between the same locations =from--one year to the next, h
- In the waterborne _ exposure pathway, average activities analyzed for required gamma-emitting nuclides 'were measured below -the RBS Technical Specification- LLDs during 1990 as had been the_ case .during the preoperational ' phase (Appendix B).
, Oross beta and tritium levels in water are compared below:
l WATEBBORNE AVERAGE GROSS BETA (pel/l)
I' Pro
- L gngIAtional 1986 1987_ _ h M,_, J M L 1990 i Surface Water, Upstream (4 km) - 7.80 5.76 8.53 4. 30 7,79- 9.75 l: : RBS Diacharge Line . N/A - 10.10 21.76 ?? , N J2.05' 40.39 Surface Water, Downstream (4 km) 8.10 5.69 8.59 5.66 7.41 9.52
- Drinking Water (Donaldsonville)' 6.80. 5 66 10.40 f> &t 8.23 '9.47 Upgradient Groundwater 6.00 2.25 2.22 3.45 3.61 6.03 Downgradient - Oroundwater. 4.00- 2.61 1.05 P.20 3.44 4.73 WATERBORNE AVERACE TRITIUH (pct /1}-
Pre.
DistAt_tund 1986. .1987 JnL 1989_ _1990 surface Water, Upstream-(4 km) (3000 <452 <444 <585 <554 <209 RBS Discharge-Line N/A -1023 1140 2272 3469 _ 20152-sucface Water, Downstream -(4 km) <3000 (45$ <604 '<502 <554 (209-
' Drinking -Water (Donaldsonville) - 43000 <462 <593 s586 <557 <210 Upgradient Groundwater (3000 <446 <601 <780 (881 <211 Downgredient Groundwater <3000 <448 <600 <779 <872 (207 20
j .
?
k y
4 E
g RIVER BEND STATION
~
R AD I 01,00 I C ALJM BQF}1{ NTAL 0 P ER ATIEUlI2QRLEQlljl90 Gross beta activities in the discharge line and surf ace water samples averaged slightly higher in 1989 and 1990 than in previous years, yet the levels remained well below reporting levels established in the RBS Technical Specifications. These activities seemingly reflect (at least in par t) a slight general increase in levels of beta-emitting materials in the Mississippi River. As observed in previous years, the annual average gross beta activity for the control location (SWU) was higher than that for the indicator location (SWD).
Tritium activities in the discharge line increased on average, reflecting the releases already noted in the 1990 Semiannual Radioactive Effluent Release Reports (see also Table 6). In the RBS boiler-t eactor, ttitium is produced by
- ternary fission of the reactor fuel ( U), although only a small f raction of that tritium would dif fuse through the fuel's cladding. Tritlum is also produced by neutron reactions with certain isotopes of boron, deutet lum and lit hium when present k in the boiler (e.g. as control rod material - boron). The observed tritium increase in the liquid discharge is attributable to the small amounts of failed fuel (i.e.
defects in a very small percentage of the f uel cladding - also responsible for the airborne radiciodine), allowing that tritium produced by ternary fission to migrate
-into the boiler water. The tritium activity observed during 1990 increased beginning in May and continued through November, tapering off with the removal of the failed fuci (see Appendix A, page A-12). Smaller increases of tritium in the liquid discharge would result f rom more ef ficient radioactive wastewater treatment and reuse (e ?, , as boiler makeup). The particulates (metals and salts) are removed in this treatment leaving the tritium behind as water (e.g. , [3H-0 1H]). When this water is reused as boiler makeup, tritium builds up in the water.
It should be noted that Discharge Line monitoring results are based on compos-iten of hourly aliquots of equal volume, rather than on flow-veighted hourly grabs.
While it may be argued that the long-term averages are fairly representative, it can be seen that the sampling requirement would be truly representative only if RBS liquid discharges were continuous and at a constant rate, which is not the case (see also the discussion of liquid ef fluents under Section 3.3 below). RBS changed to flow-weighted composite sampling of the discharge line in 1991 to accomodate NPDES permit requirements for biomonitoring. This change should have a beneficial impact on the comparisons made for predicted releases versus REMP measurements in Table 6.
In the ingestion exposure pathway, no gamma emitting nuclides were measured above LLDs during 1990, and there appear to have been no increases in radionuclide concentrations attributable to RBS operation in food / forage media over basel ine levels ( Appendix B). Slight increases in Cs-137 levels in some fish and broadleaf vegetation samples, pr esumably related to residues of the Chernobyl accident f all-out, were discussed in Section 3.1.4 (above). Naturally-occurring K-40 was measured at an average of 3503 pCi/kg in indicator vegetation and at an average of 4374 pCi/kg in control vegetation in 1990, roughly the same levels encountered prior to 21
. . . . - _- . . - . - . _ - - . - ...... - ~ . _ ~ . - . . - . . - . . _ - - - . - . _ - . . . - - . . . - . - -
'l
- n. ..
~
RIVER BEND STATION RADIOLOGICAL ENVIRQEMENTAL QPERATING REPORT POR ; )90 RDS operation . ( Appendix II) . Another nat. ural nucl ide , Be-7, averaged 310 and 547
.pcl/kg in . indicator and control vegetation samples, respectively, during 1990. .
' Al though presumably present, Be-7 was not quantifled during the preoperatlonal phase for comparison.
3.3 .
pogipati.ggingf_g)R Emil.t.FJMLSec.IAlindo.01LQls The only measurable increases in concentrations of radionuclides or levels
- of radiation, attributable:to plant operation, in the vicinity of RBS during 1990 appear to have been the expected low levels in the liquid Discharce Line. The Indicator vs.- cont rol comparisons for airborne gross beta activity (Section 3.1.1; Table 5 and Appendix A) corroborate the reports of .11mited or no releases of part-
-'iculates orJradiciodine in 1990. The 1990 TLD data (Section 3.1.2; Table 5 and
' Appendix A) showed no appreciable dif ferences in direct radiation exposures between
- Indicator and control locations. Excerpted liquid effluent data from the two Semlannual' Radioactive Ef fluent Release Reports are listed in Table 6 along with the corresponding- Discharge -Line analytical ~ data for those nuclides' which were measured by the RDIP during 1990. These nuclide activities were well below the NRC '
- reporting IcVels, but are listed here for comparison to substantiate the adequacy of source control and effluent monitoring at River Bend Station, u
F t
4 22 Mve ,-ww-,-ev-sr-.4 m , ~ + - ' -e-wr --
---'n me -- - - . - - , =
..~ , .. - . . _ . . ~ . . _ . - - _ . _ _ - _ _ - _ _ - . - . . -
RIVER DEND STATION RADIOLOGICAL. ENVIRONMENTAL OPERATING REPORT FOR 1990 TABLE 6
SUMMARY
COMPARISON OF LIQUID EFFLUENT QUANTITIES / ACTIVITIES
- AND REMP DISCHARGE LINE MONITORING RESULTS Quantitles 1st Otr. 2nd Qtr. 3rd Qtr. 4th Qtr. Total Rel eased 1990 1990 1990 1990 1990 Liters, effl.- 2.93E+06 3.65E+06 5.22E+06 4.92E+06 1.67E+07 Liters, dil. 1.14E+09 1.51E+09- 1.31E+09 1.08E+09 5.04E+09 11-3, Cur.les 4.31E+00 1.84E+01 4.01E+01 2.07E+01 8.35E+01 -
Cr-51, Cur.ies 4.76E-02 8.09E-02 1.55E-01 8.21E-02 3.66E-01 Mn-54, Curles 1.34E-02 1.39E-02 1.09E-02 8.03E-03 4.62E-02 Co-58, CuEles 9.76E-03 7.07E-03 3.97E-03 2.71E-03 -2.35E-02
-Fe-59..Curles 8.05E-03 4.50E-03 4.24E-03 3.18E-03 2.00E-02 CO-60, Curies 2.87E-02 3.01E-02 3.26E-02 2.21E-02 1.14E-01 Nb-95, Curles- 3.36E-04 3.91E-04 1,39E-03 1.10E-03 3,22E-03
- Zr-95, Curles 6.92E-05 1.69E-04 1.01E-03 7.77E-04 2.03E-03 l Ba-140,.Curles - -
- 1. 96 E-Ot. 2.87E-04 2.42E-04 1
Predicted (Extrapolated) Specific Activities (001/1)- 1990 RDtP .,
-1st Qtr. -2nd Qtr. 3rd Qtr. 4th Qtr. Mean (Range)_ '
, Measured ' Mean luglid_q_ 1990 1990 1990 1990 1990 pCUI 21156 (asts.soitoib H-3 3771 12516 30489 19080 16374 20452 (s70s.354 sono Cr-51 41.6 53.4 118 75.7 72.-2 -68. 5 (12.1 195)
Mn-54 11.1 9.18- 8.29 7.65. 9.06 8. 05 (1.1s.24.s) 00-58 8.53 4.67 3.02 2.50 4.68 3. 68 ( t.ot.io.7) i Fe- 5 9_ -- 7.04 2.97 3.22 2.93 4.04 4.70 (1,17 8,44)
Co-60' 25.1 19.9 24.8 20.4 22.6 19.4 (2.85 55.5:
- Nb-95. 0.29 0.26 1.06 1'.01 -0.66 3. 36 (2.se.4. to)
Zr-95 0.06- 0.11 0.77 0.72 0.42 1.03(ainati. value)
- Ba-140 - -
0.15 0.26 0.21 1.46(ningle value)-
- Rf fluent quantitles and nuclide activition excerptsed true the two 1990 Suetonnuat Radloactivo
- Ef fluent Release Reports already subeltted.
-b Resulta from monthly compositen. C Resulte Cros quarterly conspoaltee.
23 e
l RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT POR 1990 APPENDIX A Lis t inntn[ 1990 RDIP Rffs3 din The following tables list individual analytical results and direct measurements of radiation (TLD exposures) recorded by the Radiological Environmental Monitoring Program (REMP) during 1990. Activities measured for certain common and readily distinguished, naturally occurring nuclides are included to provide perspective. It should be noted that other gamma emittins, naturally occurring nuclides (e.g., primordial series) were often detected but are not listed because of the complexities and uncertainties of specific identifications.
A- 1
RIVER DEND STATION RADIOLOGICAL ENVJRONMENTAL MONITORINO PROGRAM Air Particulate Filter Gross ' Beta Activity (E-2 pC1/m ) -3 1990
-WEEK INDICATOR LOC' ' IONS CONTROL LOCATJONS ENDING' _ AA1 AB1 AR1 aoS AP1 AQE2 ALC 6HS AOS 01/08/90 2.19 1.89 1,79 1.81 2.08 1.96 2.08 1.87 1.68 01/15/90 2.90 -2.86 2.59 2.79 2.78 2.61 2.62 3.24 2.48 01/22/90 1,47 1.73 1.46 1.50 1.43 1.47 1.53 1.69 1.49 01/29/90 1,44 -1,73 1.71 1.47 1.70 1.68 1.54 1,82 1,64
. 02/05/90 1.77 2.00 2.00 1.90 2.04- 1.82 1.69 1.76 2.03 02/12/90 1.85 -1.94 1.84 2.17 2.14 1.93 2.01 1.74 1.83 02/20/90 1.83 2.13 1,82 2.05 2.06 1.98 2.03 1.96 1.90 02/26/90 1.42 1,68 1.42 1.61 1.54 1.75 1.64 1.33 1.69 03/05/90 2.07 1.84 2.13 2.32 1.95 2.11 1.25- 1.77 2.09 03/12/90 1.76 1.84 2.36 2.34 2,06 1.90 1.89 1.90 2.03 03/19/90 - 1.62 12.12 1.87 2.12 1.93 1.77 1.78 1.96 1.82 03/26/90 2.13- 2.80 2.52 2.64 2.33 2.10 2.38 2.29 2.29 04/02/90 1.71 2.16 2.19 2.05 1.77 1.61 1.80 1.68 1.85 04/09/90 2.00 2,26- 2.19 2.34 2.16 1.85 2.14 -1.87 2.16 04/16/90 1.73 2.37. 2.09 2.24 1.88 2.16 0.76 2.32 1.23
- 04/23/90 1.98 2.23~ 2.01 2.20 1.93 1.41 1.85 1.87 2.17 04/30/90 2.05 2.55- 2.16 2.28 2.02 1.60 1.93 1.89 2.20 05/07/90 2.18 2.29 '2.28 2,16 :2.09 1.45 2.02 2.02 2.18
- 05/14/90 2.04 2.27 2.36 1.79 1.94 1.43 1,77 1.83 1.97 05/21/90 .2.11 2.36 2.28 2.37 1.86 1.24 1.56 1.97 2.01
-05/29/90- 1.99 2.05 2.03 -1.87 1.87 1.12 1.59 1,77 1.70 06/04/90 3.06 -2.98 3.12- 2.87 2.84 2.64 2.18 2.59- 2.52 06/11/90 1.83 1.86 1.75 1,59 1.62 1.63 1.31 0.74 1.42 06/18/90 1.68 1.88 -2.11 1,91 2.02 1.84 1,40 1.41 1.66 06/25/90 2.60 2.85 2.63 2.68 0.25 2.39 2.35 0.92 2.14 07/02/90 2.88 2.77 2.78 2.95 2.45 2.69 2.24 0.55 2.15 07/09/90 2.54 2.64- 2.31 2.48 2.26 2.41 1,74 0.54 2.01 07/16/90 2.55- 2.45 2.37 2.27- 2.11 2.30 2.10 0.77 2.14 07/23/90- 2.37 2.45 2.36 2.36 1.97 2.19 1.83 -0.67 1.86 07/30/90 -3,51 3 36 3.46 3.77 3,15 3.42 2.76 0.89 3.07 08/06/90 3.28 3;70 3.'56 3.52 3.21 3.19 2.72 0.80 2.45-08/13/90 4.10 4.02' 4.19 4.16 4.00 3.79 3.60 1,05 3.27 08/20/90' 4.39 4.20 3.85 4.00 3.54 4.25 3,30 1.17 3.54 08/27/90 -3.27 3.37 3.29- 3.26 2.97 3.13 3.11 0.73 2.71 09/04/90 2.97 3.04 3.20 2.98 -2.54 2.38 2.45 10.81 2.41 09/10/90 3.94 3.90 3.91- 2.28 3.50 3.23 2.86 0.89 3.18
'09/17/90 2.18 '2.26 2.37 '2.33 1.80 1,79 0.98 1.70
-09/24/90 2.92 2.95 3.00 2.25 1.98 - 2.02' 2.66- 2.04 0.88 2.49 10/01/90- 3.63 3.26 3~34 3.15 3.37_ 2.49 2.64 0.53 3.01 10/08/90 2.88 2.56 2.46 2.71 2.42 2.14 1.90 0.35 2,20 10/15/90 2.60 2.41- 11 . 6 9 - 2.20 1.97 1.71. 1.61- 0.36 2.02 10/22/90 2.94 2.83 3'. 21 - 2 66 2.73 2.54 2.32 0.46 2.49 10/29/90 3.62 3.78- 3.13 3.70 3.39 3.04 2.94 0.59 3.61 11/05/90 3.46- 3.52 2.87 3.28 3.24 2.74 2.58 0.77 2.88 11/12/90 2.56 2.66 1.56 2.77 2-45
. 2.01 2.78 2.73 2.64-11/19/90 4.76 3.95 1.92 5.12 3.39 3.20 3.85 3.90 4.49 11/27/90- 3.11 2.91 0.90
- 2.42 2.29 2,68 2.82 2.81 12/03/90 2.78 2.54 2.86
- 2.48 2.30 2.89 2.89 2.82 12/10/90' 2.82- 2-84 . 2.94
- 2,43 2.10 2.72 2.05 -2.64 12/17/90 2.12 1.86 2.19
- 1.60 1,41 1.77 1.85 1.88 12/26/90 2.53 2.18 -2.54 2.75 2.19 2,06 2.36 2.47 2.52 01/02/91- 3.23 - 3.09 : 3.03 3.34 3.21 2.77 3.07 3.26 3.58-NOTE: Activitien shown are values actually meanuted; -' denotes that sampleu not available at location Ah5 dun to prolonged power outage.
A-2
^
- - - . _ _ _ . _ _ . _ . _ . _ - . _ . _ . _ . ~ _ ___ _ _._ _ _ _._
. Ls.
RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Air ~ Particulate Filter Beryllium-7 Activity (E-2 pC1/m 3) by Location - 1990 WEEK .
INDICATOR LOCATIONS CONTR0' LOCATIONS TEDMG . .JA1 _ R1,
,, AP1 .ES, _AP1 .JQS2 JLQ_ J[{H .30!_.
01/08/90 7.04 01/15/90 18.90 12.90 13.10 16.50 11.30 11.70 11.00 12,90 10.20
-01/22/90- 9.10 11.00 12.60 7.51 9.11 11.20 14.40 7.75
.Ct 29/90 . 16.80 9.23 11.20 8.50 8.26 11.20 11.30 02 05/90 _ 9.66 .13.50 7.95 11.10 12.50 13.90 13.10 8.29 i 02 12/90 12.30 13.50 11.60 11.30 8.40 13.90 15.20 9.29 12.50 02/20/90 5.76 14.40 11.50 15.50' 9.70 8.50 14.40 12.30 12.70-02/26/90 14.10 9.76 10.40 7.62 10.10 11.10 6.56
__03/05/90 12.80 12.30 21.30 11.90 22.10 9.51 12.40 13.90
-03/12/90 14.30 10.50 15.00 17.20 17.10- 11.80 6.64 11.20- 13.00 03/19/90 10.80 13.60 17.90 21.00 15.90 16.70 13.90 18.60 11.60 03/26/90 10,50 16.00 24.90 21.00 19.10 18.20 22.20 19.20 15.70 04/02/90 10.60 8.89 -13.70 13.20 13.10 10.00 10.20 8.02 -11.70 04/09/90 19.30 :21.501 11.60 10.80 8.92 13.60 11,10 14.70 14,70 04/16/90 13.90 13.70 12.20 15.30 14.40 13.90 6.00 16.90 8.03 04/23/90 14.10 9.64 13.20 11.10 9.81 17.08 13.00 7.58 9.71 04/30/90 12.80 20.10 16.10- 17.40 19.10 10.00 13.50 15.50 17.80 05/07/90 11.50 9.90 10. 1 12,10 8.41 5.68 6.64 _7.92 05/14/90 _10.70- 9.09' 10 t. 12.10 11.30 5,90 13.50 17.00 .16.90 05/21/90 12.90 16.20 -16.'O 13.20 10.90 5,85 16,60 9.72 15.30 J 05/29/90 -11.20 0 8.71 9,e8 9.79 7.02 7.33 6.17 10.60 8.42 06/04/90 11.20 12.80 9.40 20.00 11'.70 10.60 9.59 8.97 10.90
-06/11/90 13.00~ 11.60 12.20 11.10 5.66 11.60 6.50 . 9.63 106/18/90 13.0L 10.10 14,70 11.10 8.17 -10.90 10.40 10.10 106/25/90: 13.80 18.30 16.00- 6.92 5.97 -11i00 10.50 7.67.
'07/02/90 11.50 12.60 .9.90 1.20 14.00 11.00 10.30 8.52 07/09/90 10.20 -15.10 -11.10 12.70 9.48 17.10 -10.60 10.40 07/16/90- 12.80 10.80- 12.30 10.90 11.30 13.10 8.48 07/23/90 9.12 10.20 11.70 10.50
~
7.37 9.49 10.90
'07/30/90 12.50' 14.50' 14.30 8.'51 . 9.36 7i28- 10.10 08/06/90 11.50 12.30 10.30 9.65 12.70 14.90 12.70 7.12 l08/13/90- 16.70- 11.90 -20.50 19,70. 11.50 -18.20 14.80 16.10-
.08/20/90 15.50- 10.50 -18.70 15.10' 14.80 12.10 1.70 8.50 1 08/27/90 9.76 8.35- 8.34 8.55 L7.54 11.00 7.14
-09/04/90 16.90- 7'65- 14.00
. 9.39 9.74 '7.15- , 5.89 6.42 09/10/90 17.20 10.00 '11 80 8.76 9.32 12.40 14.60 -
'14.00 09/17/90 10.20 .9.81 6.38 6.44L 5.79 6.63
!09/24/90 11.30H 14.80 9.03 6.09 7.53 5.67 9.21 10/01/90 8 84- 12.70 14.40 15.70 ?13.20 7.93 13.20 10.30 10/08/90 18.30 12.70 -10.40. 12.10 -10.20 -11.80 9.71
- 10/15/90 14.20 -
7.71 10.50 "9.06 '6.73 7.96 110/22/90- 9.99- 16.80 13.90. 18.50; 11.40 9.65 10.40 110.70 10/29/90 8.63 11.70 10.90 -7.00: '5.42 10.00
- 11/05/90. 16.70 11.60 14.50 21;20 16.30- 17.70 10.70 11.50
-11/12/90 - 10.00 -8.53 9.07 8.69 6.39 9.72 13.-00 9.26 11/19/90 8.01 9.78 15.70 8.68 12.40 .14.10 15.40 -12.90 11/27/90 16.60 12.80 ~* 14i10 11.80 14.10 11i80 13.40 12/03/90 1 5.20 12 50 .* 13.00 10.20 11.80 17.40
'12/10/90' 11.40- 13.70 8.33 8.08 9.50 10.90 6.83 9.54 12/17/90' 111.60 12.30 110.20 * -
8.05 11,40' 11.90 11.10 8.03 12/26/90 14.90 .11.50 8.94 10.30 10.70 7.36 7.47 ' 9.95 9.44 01/02/91 11.60 6.87 J). 64 6.36 10.90 9.65 10.90 NOTRt LActivition utm u are valueu actually measurod;
- denoten that samples not ovatluble at loca-tion AKS due to. prolonged pm.dr outage.
A-3
, = ,- - - -
_ _ _ _ _ . _ ,- . . _ . .. ._ ~. _ _ __ _ _ _ _ . _ . _ _m _ -_ . . _ _
RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL HONITORING PROGRAM Air Par ticulate P11ter Cesium-134 Activity (E-2 pC1/m )3 by Location - 1990 WEEK INDICATOR LOCATION CONTROL LOCATION MDl!il AL EL JLL - AhS RL J S2 A Q_ JL 291 01/08/90 <2.59 <1.93 <1.80 <2.52 <1.67 <1.66 <1.61 <1.70 <1.68 01/05/90 <2.36 <1.69 <1.47 <1.89 <1.34 <1.44 <1.37 <1,85 <1.34 01/22/90 <1.77 <1.65 <1.39 <1.98 <1.45 <1.31 <1.25 <1.48 <1.39 01/29/90 <1.52 <1.67 <1.54 <1.78 <1.32 <1.61 <1.32 <1.46 <1.50 02/05/90 <1.85 <1.73 <1.77 <1.84 <i.53 <1.66 <1.07 <1.44 <1.28 02/12/90 <1.44 <1.65 <1.39 < 2 .' 0 7 <1.35 <1.33 <1.33 <1.54 <1.32 02/20/90 <1.48 <1.47 <1.47 <1.77 <1.36 <1.29 <1.29 <1.30 <1.43 02/26/90 <3.19 <1.78 <1.46 <2.34 <1.50 <1.77 <1.58 < 1.' 7 2 <1.79 03/05/90 <1.73 <1.67 <1.74 <1.99 <1.44 <1.55 <1.38 <l.34 <1.38 03/12/90 <1.81 ~ <1.54 <1.47 <1.42 <1.31 <0.98 <1.47 <1.52 <1.60 03/19/90. <1.73 <1.65 <1.43 <1.68 <1.40 <1.38 <1.33 <1.38 <1.48 03/26/90 <1.67_ <1.40 <1.80 <1.97 <1.31 <1.66 <1.42 <1.29 <1.42 04/02/90 <1.63 <1.52 <1.40 <1.43 <1.24 <1.12 <1.23 <1.39 <1.35 04/09/90 <1.53 -<1.70 <1.39 <1.46 <1.21 <1.33 <1.22 <1.38 <1.33 04/16/90 <1.21 <i.58 <1.56 <1.59 <1.34 <1.20 <1.12 <1.28 <1.16 04/23/90 <1.45 <1.59. <1.66 <1.57 <1.46 <1.41 <1.34 <i.12 <1.41 04/30/90 <1.43 <1.57 <1.48 <1.63 <1.29 <1,43 <1.28 <1.21 <1.47 05/07/90 <1.57 <1.46 <1.38 <1.67 <1.19 <1.28 <1.13 <1.36 <1.48 05/14/90- <1,52 <1.45- <1.52 <1.17 <1.29 <1.27 <1.08 <1.61 <1.37 05/21/90 <1.46 <1.49 <i.53 <1.41 <1.34 <1.47 <1.32 <1.51 <1.51
-05/29/90 <1.28 <1.59 <1.25 <1.54 <1.23 <1.47 <1.21 <1.21 <1.26 06/04/90 <1.95 <2.04 <2.08 <2,05 <1.61 <1.45 <1.50 <1.59 <1.43 06/11/90 <1.65 <1.85 <1.53 <1.65 <1.39 <1.39 <1.25 <1.16 <1.39 06/18/90 <1.41 <1.49 <2.04 <1.62 <1.46 <1.31 <1.20 <1.15 <1.24 06/25/90 <1.75 <1.93 <1.53 <1.62 <1.39 <1.24 <*.67 <1.23 <1.26 07/02/90 <1.59 <1.53 <1.48 <1.59 <1,34 <i 33 <1.28 <1.16 <1.40 07/09/90 <1.62 <1.88 <1.57 <1.81 <1.36 <1.64 <1.31 <1.27 <1.66 07/16/90 <1.65 <1.51 <1.54 <1.55 <1.49 <1.32 < 1.- 6 4 <1.27 <1.49 07/23/90 <1.64 <1.72 <1.78 <1.69 <1.34 <1.27 <1.53 <l.46 <1.48 07/30/90 <1.88 <1.88 <1.44 <1.82 <1.42 <1.46 <1.88 <1.49 <1.63-
.08/06/90 <1.71 <2.12 <1.61 <1.71 <1.41 <1.43 <1.36 <l.40 <1.18
-08/13/90 <1.91 <1.55 <1.26 <1.56 <1.43 <1.44 <l.53 <1.30 <1.35
- 08/20/90 <1.79 <1.52 <1.40 <1.71 <1.30 <1.48 <1.43 <1.30 <1.27
.08/27/90 <1.54 <1.77 <1.34 <1.54 <1.28 <1.41 <1.54 <1.14 <1.16 09/04/90 <1.56 <1.43 < 1 '. 3 6 <1.44 <1.15 <1.28 <1.30 <1.11 <1.09 09/10/90 <2.02 <2.04 <1.61 <1.89 <1.51 <1. 62 . <1.53 <1.42 <1.63 09/17/90 <1.65 <1.63 <1.32 <1.43 <1.28 <1.26 <1.44 < 1.' 3 2 <1.36 09/24/90 <1.46 <1.49 <1.55 <1.33 <1.27 <1.54 <1.55 <1.32 <1.02 10/01/90 ' <1.67 <1.75 <1.38 <1.48 <1.28 <1.29 <1.20 <1.22 <1.19 10/08/90 <1.66 <1.44 <1.22 <1.48 <1,09 <1.21 <1.15 <1.21 <1.28
.10/.15/90 <1.52 <1.61 <1.56 <1.41 <1.45 <1.40. <1.42 <1.28 <1.31 10/22/90 <0.94 <1.74 <1.47 <1.72. <1-10
. <1.60 <1.74 <1.46 <1.05 10/29/90 <1.22 <1.57 .<1.54 <1.43 <1.22 <1.37 <1.46 <1.31 <0.98 11/05/90 <0.85 <1.44 <1.51 <1.39 <1.31 <1.67 <1.48 <1.48 <0.96 11/12/90 <1.61 <1.55 <1.60 <1.42 <1.32 (1.48 <1.59 <1.55 <1.37 11/19/90 <1.81 <1.85 <1.55 <3.30 <1.45 <1.56 <1.59 <1.66 <1.47 11/27/90 <1.47_ <1.24 <1.12 * <1.38 <1.11- <1.11 <1.16 <0 96 12/03/90 <1.89 <2.14 <1.89 * <1.60 <1.78 <2.70 <2.50 <2.55 12/10/90 <1.56' <1.71 <1.46 * <1.67 <1.41 <1.69 <1.30 <1.55 12/17/90 <1.55 <1.92 <1.59 * <1.46 <1.49 <1.88 <1.75 <l.49 12/26/90 <1.71 <1.24 <1.79 <1.59 <0.95 <1.22 <1.20 <l.44 <1.25 01/02/91 <1.83 <1.59 <1.77 <1.68 <1.56 <1.49 <1,48 <1.66 <1.74 NOTE: Activities indicated are minimum detectablo activittes (MDAn) under the particular condi-tions of analysea (1,0., Cs-134 may or may not have been present , but if so, there cannot have been more than the amounts shown), or they are values actually measured;
- denotes that samples were not avullable at location AKS due to prolonged power outage.
A-4
. . 4 RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL, MONITORING PROGRAM Air Particulate Filter Cesium-137 Act ivity (E-2 pC1/m 3) by Location - 1990 WEEK INDICATOR LOCATION CONTROL LOCATION ENDIN(L l&L. A1_. 3R1_ JKS._ EL 20S2 JW.. lluL 30ft 01/08/90 <2.23 <1.89 <2.02 <2.42 <1.51 <1.56 <1.60 <1.73 <1.65 01/05/90 <2.05 <1.50 <1,54 <2.11 <1.25 <1.38 <1.35 <1.53 <1,53 01/22/90 <1,56 <1,65 <1.54 <2.24 <1.13 <1.52 <1,17 <1.69 <1.30 01/29/90- <1.70 <1,59 <1.58 <1.85 <1,20 <1.62 <1.32 <1.27 <1.50 02/05/90 <1.76 <1.65 <1.96 .<1.75 <1.60 <1.56 <1.27 (1.46 <t.51 02/12/90 <1.75 <1.62 <i.61 <2.33 <1.30 <1.64 ~ <1,65 <1.56 <1.54 02/20/90- <1.62 <1.44 <1,55 <1,76 <1.22 <1.22 <1,27 < 1. 4 5 <1.55 i 02/26/90- <2.30 <1.62 <1.82 <2.71 <1.90 <1.92 <1.78 <1.85 <1.60
- 03/05/90 <2.20 <1.66 <1.37 <2.08 <1.53 <1.85 <1.62 <1,38 <1.68 03/12/90 <2.04 <1.86 <1.50 <2.01 <1.56 <1.49 <1.41 <1.43 <1.51 03/19/90 <1.57 <1.95 <1.67 <1.96 <1.61 <1.81 <1.40 <1.46 <1.72 03/26/90 <1.57 <1.91 <1.20 <1,08 <1.67 <1.77 <1.57 <1.66 < 1. 5 9 '
04/02/90 <1.60 <1,86 <1.59 <1.72 <1.15 <1.61 <1,26 <1,55 <1,35 04/09/90 <1,85 <1.53 <1.21 <1.94 <1.29 <1.42 <1.49 <1.44 <1.41 04/16/90 <1.68 <1.67 <1.54 <1,80 <1.33 <l.48 <1.10 <1.49 <1.47
- 04/23/90 <1.61 <1,58 <1.64 <1.59 <1.55 <1.29 <1.51 <1.38 <1.48 04/30/90 <1.72 <1.91 <1.51 <1.82 <1.46 <1.31 <1.40 <1.45 <1.85 05/07/90 <1.59 <2.13 <1.40 <1,61 <1.36. <1.57 <1.21 <1.74 <1.79 05/14/90 <1.73 <1.57 <1.64 <1.36 .<1.60 < 1. 72 <1.08 <1.57 <1.52 05/21/90 <1.63 <1.77 <1.48 <2.17 <1.41 <1.36 <1.19 <1.52 <1.72 05/29/90 <1.46 <1,55 <1.19 <1.36 <1.15 <1.36 <1.17 <1.29 <1.49 06/04/90. <2.06 <2.56 <2.23 <1.97 <2.02 <1.54 <1.93 <1.64 <l 79 06/11/90 <1.91 <1.89 <1.61 <2.00 <1.69 <1.57 <1.43 <1.49 <1.36
, .06/18/90 <1.53 <1.83 <2.05 <1.68 <1.45- <1.41 <1.39 <1.38 <1.60 l 06/25/90 <2.06 <2.15 <1.87 <2.01 <1,24 <1.58 <1.85 <1,21 <1.40 07/02/90 <1.69 <1,46 <1.83 <1.47 <1.28 <1,50 <1.39 <1.35 <1,39
- 07/09/90 <1.81 <1.64 <1.74 <1.85 <1.38 <1.54 <1.60 <1.17 <1.68 07/16/90 <1.88 <1.50 <1.63 <1.58 <1.47 <1.61 <1.85 <1,32 <1.85 e 07/23/90 <1.98 <1.61 <1.39 <1.68 <1.64 <1.75 <1.52 <l.36 <1.63 l' 07/30/90 <1.81 <2.20 <1.92 <1.66 <1.42 <1.58 <1.59 <1.55 <1.75
, 08/06/90 <1.84 <1.90. <1.71 <1.65 <1.30 <1.72 <1.77 <1.36 <1.24 08/13/90 <2.01 <1,85 <1.68 <1.81 <1.45 <1.55 <1.66 <1.45 <1.40 t
08/20/90 <1.78 <1.77 '<1.44 <1.40 <1,73 <1.31 <1.92 <1.52 <1.24 08/27/90 <1.76 <1.99 <1.62 <1.63 <1,44 <1,21 <1.67 <1,12 <1,12 09/04/90 <1.71 <l.66 <1i39 <1.29 <1.21 <1.51 <1.58 <1.06 <1.09 09/10/90 <1.87 <2.30 <1.58 <1.83 <1.63 <1.88 <1.72 <1.47 <1.33 L
09/17/90 <1.84 <1.74 <1.43 <1.83- <1.27 <1.43 <1.39 <1.35 <1.31 09/24/90 <1.51 <1.62 .29 <1.74 <1.13 <1.34 <1.22 <1.41 <1.37
,. 10/01/90 <2.13 <1.78. .45 <1.89 <1.26 <1,49 <1.58 <1.25 <1.42 L
L 10/08/90- <1.89 <1.75 st.58 <1.58 <1.23 <1.65 <1.49 <1.30 <1.33 10/15/90 <1.85 <1.71 <l 94 <1.75 <1.69 <1.59 <l.78 <l.22 <1.60 i' 10/22/90 <1.10 <1.68 <1.68 <1.78 <1.47 <1.93 <2.00 <1.52 <1.24 l- 10/29/90: <1.24 .<1.62 <1.62 <1.38 <1.43 <1.34 <1.41 <l.60 <1.51 11/05/90 <1 15 <2.28 <1.65 <2.11 <1.29 <1.67 <1.90 <1.54 < 1.- 12 11/12/90 <1.91 <1.78 <1,70 <1.32 <1.34 <1.54 <1.65 <1,66 <1.21
-11/19/90 <1.78 <1. 93 <1.44 <3.45 <1.65 <1.88 <1.35 <1.82 <1.49 11/27/90 <1.26 <1.24 <1.26 * <1.41 <1.29 '<1.10 <1.08 <0.94 12/03/90 <1.88 <1.98 <1.69 * <1.79 <1.73 <2.90 (2i73 <2.57 12/10/90 <1.49 <1,81 <1.29 * <1.40 <1.37 <1.92 <1,39 <1.59
- 12/17/90 <1.71 <1.79 <1.54 * <1.89 <1.48 <1.61 <1.78 <1.47 12/26/90 <1.71 <1.20 <1.66 <l.82 <1.01 <1.22 <1.30 <1.45 <l.11 01/02/91 <1.93 <1.75 <1.71 <1.77 < 1. '4 2 <1.56 <1.48 <1.69 <1.53
[ NOIR Activities -indicated are minimum detect)ble activitista (tHMul under the particulur condia p~ tions of analysen (i.e.. Cn-137 may or may not have been pressent, but if no, there cannot
.have been more than the amounta 14hown), or they are values actually meaanared;
- dunotes that namples were not available ut locatton AK$ due to prolonged power outage.
A-5
L l
i RIVER BEND STATION RADIOLOGICAL. ENVIRONMENTAL MONITORING PROGRAM Char coal Cart ridge Pot uslure-40 Act ivity (E-2 pC1/m3 ) by Location - 1990 WEEK INDICATOR LOCATIONS CONTROL LOCATIONS QO1EQ lAL ._AltL EL EL AEL 20S2 R _ AWL 30fL 01/08/90 66.20 66.80 62.60 82.60 41.20 56.40 53.40 59.70 56.50 01/15/90 89,70 57.70 59.00 82.10 44.50 41.60 61.20 49.30 61.80 01/22/90 59.60 66.50 47.30 63.20 50.00 54.60 52.80 58.10 45.80 01/29/90 41.50 58.80 56.40 65.10 57.90 45.30 36.70 38.70 52.60 02/05/90 73,30 81.10 51.70 56.50 49.30 40.90 39.90 52.00 54.70 02/12/90 64.40 56.40 68.90 39.90 43.50 50.70 77.80 38.80 34.80 02/20/90 60.30 50.50 48.60 60,10 53.10 37.20 50.70 35.50 43.40 02/26/90 52.30 67.80 52.90 227.00 32.70 58.30 48.70 49.50 70.50 03/05/90 58.00 37.80 23.30 42.20 61.10 39.10 58.10 47.90 39.40 03/12/90 62.00 51.00 49.30 49.50 40.40 42.50 36.30 49.40 03/19/90 69.40 67.30 38.30 31.00 37.90 66.20 53.10 75.50 46.00 03/26/90 57.30 54.00 58.90 75.70 67.10 38.40 43.10 54.00 04/02/90 43.10 66.30 43.30 52.10 56.00 58.20 54.40 54.80 47,50 04/09/90 63.10 55.80 60.30 41.20 23.80 33.70 46.90 38.20 45.40 04/16/90 69.30 77.00 55.80 50.50 39,50 45.20 35.20 65.50 47.60 04/23/90 65.00 55.80 52.20 47.10 45.20 53.10 42.00 36.10 59.50 04/30/90 62.80 53.40 58,70 40.80 37.60 51.50 39.90 50.50 48.10 05/07/90 58.70 72.90 68.10 67.40 72.60 57.40 57.50 62.10 70.00 05/14/90 87.30 54,40 83.60 59.80 66.60 79.00 54.10 52.80 70.60 05/21/90 63.80 60.50 51.10 70.00 70.10 58.10 61.30 54.50 65.00 05/29/90 62.50 44.80 56.70 66.60 56.50 50.40 68.30 63.10 54.40 06/04/90 102.00 92.20 73.90 89.20 89.20 78.30 65.90 85.80 79.80 06/11/90 74.80 62.70 80.20 97.30 66.30 69.90 70.10 45.80 59.70 06/18/90 70.20 73.50 76.00 82.60 53.00 52.10 72.40 49.90 64.70 06/25/90 54.90 70.30 82,30 66.00 60,00 88.50 57.70 51.40 59.90 07/02/90 66.90 84.70 98.90 74.90 39.50 62.20 58.00 44.30 81.00 07/09/90 69.50 97.40 73.00 71.60 66.10 77.10 81.90 51.90 51.90 07/16/90 83.20 64.60 76.30 55.70 60.80 67.10 54.40 64.90 07/23/90 80.60 69.40 62.60 72.50 53.00 39.00 50.80 59.20 07/30/90 73.20 60.00 69.00 89.80 55.60 66,10 85.40 58.80 57.00 08/06/90 83.40 66.50 67.20 73.70 58.40 43.80 68.60 46.70 56.40 08/13/90 93.30 57.10 83.30 46.60 52,30 57.40 67.50 08/20/90 73.50 53.10 60.50 62.00 63.40 60.30 73.00 55.90 47.30 08/27/90 78.10 70.60 73.50 63.00 85.30 49,50 65.40 55.20 47.50 09/04/90 59.80 63.40 40.40 39.90 50.60 41.60 46.50 30.20 74.20 09/10/90 72.90 85.60 70.60 92.40 67.70 84.60 49.80 72.10 62.50 09/17/90 84.40 65.10 72.60 64.80 53.50 .48,10 54.80 57.10 62.90 09/24/90 65.60 73.30 67.20 99,20 46.90 61.70 $3.10 44.80 59.10 10/01/90 55.00 63.20 44.80 56.40 83.00 56.50 69.50 61.00 31.50 10/08/90 41.50 74.90 .59.30 40.80 36.30 40,60 42.80 43.50 38.00 10/15/90 32.50 41.10 28.90 29.90 40.90 36.50 59.20 21.20 10/22/90 26.00 27.90 39.60 48.10 35.20 51.90 35.30 36.00 10/29/90 41.20 44.70 47.20 37.10 48.00 42.50 23.60 43.90 24.60 11/05/90 32.20 55.90 57.80 25.30 46.80 43.90 47.40 36.80 59.80 11/12/90 46.10 49.70 44.90 41.50 29.20 38.20 44.80 32.70 42.50 11/19/90 45.90 23.60 60.30 79.30 40.00 40.60 49.80 48,30 11/27/90 31.00 43.90 49.40
- 36.70 23.90 40.20 66.80 12/03/90 47.40 46.40 44.60
- 32.70 59.70 60.00 76.20 33.40 12/10/90 38.10 36.90 41.80
- 47.60 57.00 51.70 43.70 29.00 12/17/90 49.70 81.70 65.60
- 50.40 43.20 28.10 53,30 38.20 12/26/90 43.70 44.80 32,10 48.40 29.20 30,30 36,50 33.30 50,40 01/02/91 24.70 50.00 33.50 50.40 40.50 42.10 44.80 45.50 50.40 l
NOTE: Act ivi t ion nhown are s aluun actually meanurmt;
- denotun that namples weto not available at l locatton AhS duo to prolongmi power outeHh I A-6
. . - - - - - . _ . - -~ --- . - - - - . - . . - .
I RIVER BEND STATION ItAD10 LOGICAL ENVIRONMENTAL MONITORING PRO 0i!AM Chatcoal Cat tildge Iodine-131' Activity (E-2 pC1/m 3) - 1990 WEEK INDICATOR LOCATION CONTROL LOCATION MDH9 l!L lEL. ALL .EL JI1. 3 032 31&_ JLft 20ft.
01/08/90 <2.99 <2.09 <2.04 <2.55 <1.83 <1.96 <1.88 <2.04 <2.12 01/15/90 <2.24 <1.82 <1.87 <1.96 <1.44 <1.52 <.1. 3 3 <2.22 <1.94 01/22/90 <1.86 <1.79 <1.82 <2.32 <1.85 <1.49 <1.71 <1.44 <1.82 01/29/90 <1.96 <1.42 <1.78 <1.99 <1.34 <1.75 <1.38 <1.62 <1.89 02/05/90 <1.81 <1.62 <2.00 <1.75 <1.58 <1.35 <1.26 <1.69 <1.47 02/12/90 <1.56 <1.61 <1.92 <2.05 <1.51 <1.65 <1.94 <1.62 <1.70 02/20/90 <1.79 <1.70 <1,48 <2.19 <1.31 <1.88 <1.44 <1.51 <1.77 02/26/90 <2.23 <2.25 <2.15 <2.88 <1.94 <2.17 <1.69 <2.05 <2.14 !
03/05/90 <1.84 <1.84 <1.76 <1.84 <1.65 <1.32 <1.61 <1.76 <1.83 4
-03/12/90 <1.62 <1.53 <1.69 <1.97 <1.66 (1.69 <1.60 <1.48 < 1, 58 ,
-03/19/90 <1.96 <1.76. <1.83 <1,97 <1.46 <1.74 <1.52 <1.80 <1.70 l
.03/26/90 <1.80 <1.87- <1.87 <1.87 <1.73 <1.64 <1.50 <1.85 <1.83 04/02/90 <1.87 <1.43 <1.62 <1.82 <1.38 <1.54 <1.76 <1.69 <1.74 04/09/90 <1.66 <1.61 <1.82 <1.66 <1.73 <1.57 <1.89 <1.55 <2.16 04/16/90 <1.85 - <1.64 <1.66 <1.64 <1.40 <1.61 <1.47 <1.42 <1.75 04/23/90 <1.98 <1.67 <1.76 <1.69 <1.65 <1.45 <1.56 <1.60 <i.71 04/30/90 <1.98 <1,42 <1.74 <1.73 <1.66 <1.44 <1.58 <1.40 <1.94 05/07/90 - <1.81 <1.67 <1.98 <1.70 <1.68 <1.56 <l.48 <1.48- <2.09 05/14/90 <1.92 <2.07 <2.05 <1.88 <1.48 <1.60 <1.40 <1.44 <1.67 05/21/90 <2.05 1.00 <
'1.92- <1.79 <1.47 <1.37 <1.93 <1.76 <i.60 05/29/90 <1.57 1,66 1.61 <1.64 <1.64 <1.19 <1.59 <1.21 <1.65 06/04/90 1.6! 2.41 3.09 <2.34 <2.21 <1.88 <1.97 <2.02 <2.01 06/11/90 <1.8e s2.06 <2.32 <1.99 <1.89 <1.71 <1.47 <1.50 <1.75 06/18/90 <1.72 0.96 <2.37 <1.95 <1.76 <1.74 <1.58 <1.42 <1.96 !
06/25/90 <2.08 <1.99 <2.30 <2.00 <1.67 <1.72 <1.83 <1.51 <1.77 07/02/90 < 1. 74- <1.76 (1.70 <1.93 <1.60 <1.53 <1.78 <1.74 <1.75 07/09/90 <1.91 <1.75 <2.00 <2.06' <1.70 <1.72 <1.80 <1.67 -<1.97 07/16/90 <2.22 <4.78 <1.89 <2.03 <1.44 <1.60 <1.83 <1.31 <2.15 07/23/90 <1.77 ~1.77 <2.04 <1.94- <1.54 <1.79- <1.64 <1.60 <1.79 07/30/90 _ <1.96 <1.86 <1.92 <2.03 <1.69 <1.87 <1.82 <1.69- <1.58 08/06/90 <1.69 <1.73 <1.86 <2.08 <1.71 <1.55 <1.83 <1.58 <1.59 08/13/90 <2.16 <1.97 <1.92 <2.07 <2.02 <1.61 '<1.81 <1.57 <2.07 08/20/90- <2.09 _-<1.86 <1.64 <1,66 <1.63 <1.71 <1.91- <1.48 <1.63 '
08/27/90 <1.83 <1.87 <1.53 <1.98 <1.42 <1.39 <2.02 <1,05 <1.77 L
09/04/90= <1.64 <1.39 <1.53 <1.51 <1.18 .1,30
< <1.40 <1.12- <1.10 09/10/90 <1.95 <2.24- <1.84 <1.95 <1.56 <1.77 <1.98 <1.90 <2.12 109/17/90. _ <1.69 ' <1.94 <1.83 <1.91 <1.58 <1.48 < 1.- 50 <1.68 <1.65-09/24/90- < 1. 7 7 - <1.73 <1.71 <1.65 <1.39 <1.75 <1.62 <1.51 <l.78 10/01/90- <1.48 <1.73
. <1.64 <1.61 <1-.40 <1.55 <1.70 <1.55 <1.59 10/08/90 <1.76 <1.65 ' <1.35 <1.63 <1.49 <l.68 <1.92 <1.631 <1.65
.10/15/90 < 1._ 2 7 <1.93 <1.56 <1.73- ;<1.05 - <1.35 <1.53 <1.39 <1.57 10/22/90 <1.08 <1.83 <1.56 <1.64 <1.36 <1.54 <1.71 <1.63~ <1.18-10/29/90 <1'24
. <1. 90 <1.65 <1.76 <l.44 <1.56 <1.70 <1.62 < 1.17 -
11/05/90 <1.14 <1.85 <1.59 <1.69 <1.37 <1.69 <1.28 <1.51 <1.38 11/12/90 <1.50 <1.79 <l.71 <1.61 < 1.15 - <1.50 <2.06 <1.37 <1.70 11/19/90- <1.65 <1.80 4<1.80 <2.90 <1.58 <1.60 <1.49 <l.75 <1.72 11/27/90 <1.58 <1.69 <1.85 * <1.39 <1.44 <1.35 <1.20 <1.08-
! E12/03/90- <2.33 <2.24 <2.25 * <1.89 <1.91 <3.41 <3.10 <3.53-l' 12/10/90 <1.76 <1.58 <1.76 * <1.35 <1.67 <1.93 <1.75 <1.66 12/17/90' ~<1.58- <1.83 <1.70 * <1.66 <1.43 <1.88 <2.02 <2.00-
=12/26/90 <1.29 <1.33 <1.19 <1,97 <1.13 <1.13 <1.65 <1.37 <1.24
.01/02/91' <1.69 <1.59 <1.72 <1.75 <1.40 <1.42 <1.94 <1.74 <1.63 NOTE! Activities shown are -values actually meneured, wherman thona indicated as "<" are minimum detectable activities (HDAs) under the particular conditions of unalysia) of nucliden for which
. analyses are required by itBS Technical Specifications (that to. 1-131 may or may not havo been present. but if so, thert e snnot have been more present than the amounts notodi;
- denotes that complos were not available at location AKS due to prolonged power outagw.
A-7
_ _ . _ . - _- ~ _ ~ . -,. . __._ -_ _ _ __ __ . _ . _ _
RIVER IlEND STATION RADIOLOGICAL ENVIRONMENTAL, MONITORING PROGRAM Charcoal Cartt idse Cesium-137 Act ivity (0-2 pCi/m3 ) by Location - 1990 WEEK .
INDICATOR LOCATIONS CONTROL I,0 CATIONS EMRO _ML ARL _ARL ._AKE_ _AEL __AQS2 ._ Alt 0_ _MLS- ._ AGE 01/08/90-01/15/90 01/22/90 01/29/90 02/05/90-02/12/90 02/20/90 l02/26/90 03/05/90 03/12/90
.03/19/90 03/26/90
-04/02/90
'04/09/90 04/16/90
-04/23/90 04/30/90 05/07/90 05/14/90
- 05/21/90 05/29/90 ,
- 06/04/90 06/11/90.
06/18/90-06/25/90 07/02/90:
~ 07/09/90 07/16/90
'07/23/90 1.33 07/30/90 08/06/90
-08/13/90 08/20/90
- 08/27/90- .3 09/04/90 09/10/90 09/17/90 09/24/90 1.01
-10/01/90
~10/08/90 10/15/90-iO/22/90
-10/29/901 1.31-11/05/90 11/12/90
'11/19/90 0.90 11/27/90
-12/03/90 12/10/90 12/17/90.
12/26/90 01/02/91 NOTHl Act ivit ies shown ure valtwa actually measus ed;
- deno t es t ha t o. imp laisi were riot avallublu ut ~
loca t iott AKS due to prolonge<l power outage.
A-8
,rm' y v
IITVEll BIND STATION RADIOttX11CAI. FNV11tONMlWPAL MON 1'IUltlNG IWXIllAM Norun11 zed Gzunma-Ray Npasure Sumnnry (mR)
Quarterly Thermoluminescence Dos 1 meter Hesults for 1990 INDICATOR SI6TIW lET._RW RS1RW ._DRIUZI1t 411L R W TA1 11.24 13.42 15.97 12.56 TA2 12.55 14.41 15.39 14.13 TB1 11.78 12.73 13.7G 13.44 TD2 11.71 15.10 17.37 13.93 Tcl 12.08 13.32 13.91 12 . 9 f>
TC2 9.55 11.11 13.23 11.68 TCS 10.21 10.75 12.22 10.41 TD1 11.82 14.51 14.00 13.15 TD2 11.68 11.94 13.61 11.78 TE1 11.65 12.04 14.90 12.37 TE2 10.55 10.85 11.83 9.53 TF1 10,67 12.83 14.50 12.76 TF2 11.55 15.52 14.50 13,74 TG1 12.29 13.03 16.68 15.50 702 10.81 11.84 14.10 12.88
'1111 9.53 10.45 11.83 11.00 Til2 11.01 12.1i 13.20 10.37 TJ1 10.91 11.15 13.01 11.49 TJ2 9.88 11.40 13,20 10.26 71< 1 10.74 12.53 13.61 11.49 E2 12.15 13.72 14.30 13.25 ES 10.44 11,34 12.47 10,85 TL1 10.84 13.42 14.30 12.46 TL2 9.95 10.85 11.73 10.00 TLS 11.25 14.41 13.91 13.20 TM1 9.29 10.95 11.73 10.16 TM2 13.85 13,52 15.49 15.10 TN1 11,55 13.52 14.50 12.17 TN2 9.68 10.65 12.03 10.21
'IT)1 12.46 14.31 15,98 12.95
'lT)2 10.91 13.12 15.38 12.46 TQ1 10.77 11.54 13.61 12.95 m2 10.01 12.01 13.42 10.60 NS1 11.98 14.61 15.18 13.17 TQS2 10.87 11.54 12.64 10.07 TR1 7.81 9.07 9.70 0.01 TR2 10.95 12.63 13.61 15.69 TRS 11.88 13.62 14.20 14.14 CONTROL 61WU%
TAC 12.58 12,81 14.50 13.85 TEC 11.48 12.53 15.49 12.69
'10S 11.21 12,83 14.50 13,37 T!!S 13.45 14.01 15,98 14.33 TLC 10.31 10.75 11.63 11.33 TQS3 11.51 12.01 14.79 11.72 A-9
RIVER BEND STATION RADf0 LOGICAL ENVIRONMENTAL MONITORINO PROGRAM Normalized Gamma-Ray Exposure Summary (mR)
Monthly Thermoluminescence Dosimeter Results for 1990 INDI-CATOR SIA110li .E _fEB JAB E JAY E E E SSE _9.C1 .jiEE EC TA1 3.87 3.71 3.85 3.71 3.84 4.78 4.87 4.65 4.17 5.17 5.01 4.21 TA2 4.63 4.73 4.02 3.99 3.94 4.78 4.75 5.18 5.39 5.76 5.27 4.36 TB1 4.28 4.25 4.17 3.85 3.94 4.67 4.77 5.09 4.83 5.48 4.83 4.64 TB2 4.28 4.23 4.05 4.31 4.03 5,06 4.96 5.26 4.72 5.26 4.82 3.93 TC1 4.39 4.20 4.23 3.92 3.80 4.78 4.87 4.91 5.06 5.38 4.92 4.32 TC2 3.32 3.73 3.08 3.45 3.26 3.72 4.06 4.32 4.17 4.56 3.91 3.10 TCS 3.32 3.20 3.26 3.34 3.65 3.56 4.23 3.89 3.61 3.96 3.73 3.52 TD1 4.57 3.88 3.83 3.71 4.00 5.34 4.97 5.18 4.83 5.69 5.09 4.32 TD2 3.84 3.95 3.47 3.88 3.65 4.88 4.65 4.75 4.39 6.56 5.09 3.52 TE1 4.07 3.80 3.77 3.50 3.80 4,78 4.29 4.91 5.28 4.97 4.92 4.00 TE2 4.01 3.73 3,14 3.13 3.07 4.13 4.02 4.06 3.72 4.76 3.91 3.21 TF1 3.86 3.68 3.61 3.81 3.90 4.59 4.77 4.55 4.50 5.17 4.66 4.21 TP2 4.22 3.98 4.26 4.20 3.84 4.41 5.06 4.92 5.28 5.46 5.18 4.55 TG1 4.64 4.23 3.89 4 43 3.90 4.88 5.06 5.46 4.72 5.38 4.92 4.00 TG2 4.46 4.13 3.77 3.88 3.80 4.66 4.66 5.18 4.17 5.05 4.91 3.83 Till 3.57 3.26 3.39 3.09 3.20 3.75 4.19 4.27 3.72 4.24 4.06 3.03 Til2 3.84 3.95 3.35 3.24 3.60 4.69 4.13 4,32 3.67 4,08 4.09 3.41 TJ1 3.89 3.95 3.52 3.61 3.60 3.94 4.09 4.27 4.06 4.97 4.41 3.46 TJ2 3,60 3.72 3.33 3.24 3.07 3.56 4.02 4.09 3.89 4.44 3.63 3.03 TK1 3.96 3.88 3.52 3.40 3.60 4.68 4.97 4.56 4.61 4.97 4.41 4.21 TK2 4.31 4.28 3.65 3.99 4.06 4.98 4.58 4.09 4.39 5.15 4.21 4.23 TKS 3.77 3.85 3.24 3.81 3.55 11.17 4.03 4.09 3.89 4.44 4.15 4.00 TL1 4.21 4.99 3.67 4.12 3.50 4.13 4.67 5.00 4.61 4.76 4.83 3.46 TL2 3.48 3.39 2.83 3,03 3.20 3.48 3.71 4.00 3.72 4.08 4.25 3.84 TLS 4.65 4.09 4.00 3.99 3.89 4.66 4.67 4.46 4.72 5.15 5.28 4.62 TM1 3.96 3.78 3.11 3.30 3.00 3.56 3.61 3.91 3.83 4.35 3.98 2.39 TM2 4.54 4.91 4.40 4.10 4.06 5.41 5.35 5.55 5.17 5.63 6.03 4.55 TN1 3.93 4.16 4.11 3.61 3.60 4.69 4.19 4.27 4.17 5.69 4.83 3.89 TN2 3.65 3.46 3.00 3.03 3.11 3.80 3.90 4.18 3.83 4.37 3.59 3.72 TP1 4.68 4.13 3.90 3.71 4.20 4.97 5.06 4.83 4.50 6.00 4.75 3.46 TP2 4.28 3.74 3.67 3.35 3.84 4.39 5.16 4.41 4.83 5.06 4.74 3.57 TQ1 4.21 3.95 3.47 3.61 3.30 4.13 4.48 4.55 4.50 4.76 4.06 3.35 TQ2 4.08 3.61 3.80 3.67 3.45 4.39 4.16 4.49 4.17 4.66 4.74 3.78 TQS1 4.66 3.95 3.86 3.67 3.94 4.59 4.76 5.26 4.50 5.36 4,74 4.24 TQS2 3.98 3,98 3.47 3.19 3.37 4.66 4.36 4.23 4.06 4.76 4.21 2.90 TR1 3.52 2.89 2.92 2.78 2.78 3.52 3.51 3.68 3.28 4.14 3.81 2.59 TR2 3.63 3.88 3.65 3.35 3.45 4.50 4.44 4.75 4.50 5.36 4.91 3.37 TRS 4.22 4.02 4.20 3.88 3.94 4.78 4.54 4.58 4.50 5.46 4.73 3.67 CONTROL S1hTLQ1i TAC 4.18 3.95 4.08 3.88 3.80 4.68 4.46 4.75 4.50 4.76 4.39 3.83 TEC 4.22 3.95 5.26 3.35 3.74 4.88 4.75 4.*49 4.83 5.36 4.36 3.87 TOS 4.87 4.20 4.50 3.88 4.06 4.55 4.66 4.74 4.72 5.54 5.00 4.07 THS 4.54 4.23 4.11 4.20 A 40 5.3C 4.76 5.36 4.94 5.25 5.37 4.87 TLC 3.68 3.46 3.36 3.24 3.71 4.23 4.00 4.09 3.72 3.99 4.15 3.57 TQS3 4.14 4.12 3.84 3.67 3.50 4.45 4.26 4.75 4.72 5.26 4.74 4.14 A-10
l i
RIVER llEND STATION RAD 101,001 CAL ENVIRONMENTAL MONITORING PROGRAM -
- Gross lletts Activitics (pCi/ liter) in Water Samples - 1990 IXI!LCAIOR LOCA110NS CONTRQL1GCAT10ES__.
SAMPLING PIRLQD fiED 18 DL ED S.EU EU ELAE!~-
J AN -- 8.46 6.17 35.64 10.80 <2.22 l FEB 6.02 6.06 20.69' 5.00 <2.14 ,
MAR 5.95 4.83 35.34 <2.46 5.95 <2.42 3.63 APR 6.64 8.17 .41.20 6.87 <2.06 MAY 13.73 11.78- 67.42 13.70 14.78 JtIN 12.07 12.44 49.09- 5.73 11.11 6.89 4.24 Jift 17.05 13.02 49.16 4.83 14.32 S.95 3.54 AlIO 10.13 14.36 34.00 5.36 11.08 5.25 4.07 SEP -10.11 11.21 38.09 9.63 4.46 OCT .11.08 10.50 49.97 13.57 4.78 NOV 4.66 10.55 34.32 9.08 4.94 DEC 3.36 4.53 29.77 3.02 5.90 <2.80 <2.22 NOTB; I Distilled, cetonized-woll water (laboratory reagent water).
Samples from SWD, DW,' and HWU are componites of weekly gruba; samples f rom D1.
are compositen of hourly grab i 'samplea f rom WD and WU are quarterly graba, Activitien shown are valuon ' actually. measured, whereas those indicated as "P are minista detectable activitius (MDAs) under the part icular coindit ions of anatosis (that :ia, grose beta act ivity may or siay not have been present, but. If so, there cannot have been more present than the amounta listed).
L A-11 p
~
..; s RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Tritium Activities (pC1/ liter) in Monthly Water Samples - 1990 INDICATOR L0 CATIONS CONTRE _L0fATIOnS SAMPLINO
{ PERIOD EED DH- E ED EW W E6E' JAN <175 <176 4243 <173 <176 <174 <176 FEB <178- <178 3981 <174 <181 <173 <181 MAR <178 <184 7900 <176 <181 <179 <180 APR <181 <182 5597 <181 191 n.a. <182 MAY <198 <198 10617 <198 <198 <198 <196 JUN <l70 <170 17300 <170 <170 <170 <197 JUL- -<209 <210 21008 <207 <209 <211 <210 AUG <188 <188 28884 <190 <188 <184 < 189
-SEP <191' <193 60410 <191 <193 <189 <190 OCT <187 <187 50728- <186 <187 <186 <1HO NOV -<188 <183 39626 <189 <189 <189 <188 DEC <184 <184 3575 <184 <185 <184 <184 Tritium Activities (pCi/ liter) in Quarterly Water Samples - 1990 INRICATOR LOCATIONS CONTRQL_LQff_T10fj_
SAMPLING.
EERIQD EWD DH E HD EW Hl! Efff
-QTRt <180 <180- 5705 <176 <188 <179 <179 QTR2 <205 <203 10294 <170 <205 <170 .207 QTR3 <192 <192_ 35450 <191 <194 <!89 <186
_QTR4' <179 _ <180 30360 <184 -<180 < 18 '4 -<177
. N0TE: 1Distiltro, deinntred weit water (laboratory reagent water).-
Samples from SWD, DW, and SWU are composites of weekly grabs; samples from DI. cro composites of hourly grabs; - samples f rom WD and WU are monthly graba (none obtained at Wtt in April; the license requirement for sampling la quarterly).
Activities shown are values actually measured, whereas those indicated an "<"-
are minimum detectable activities (HDAs) under the particular conditions of analysts (that Lo, tritium may or may not have been present ,-but i f no, there cannot have been more present than the amounts listed).
A-12
RIVER llEND STATION RADI01.001 CAL ENVIRONMENTAL, MONITORING PROGRAM Gamma-Emitting-Nuclide Activity (pCi/ liter) in Vatet by Location - 1990 llERVLLIUH-7 !
____ lEDICAIRR.10CAILQb'S. _CONIRQU0 fall 0M PERLOD SED W DL ED tiW EU DEC 14.90 POTASS10M-40 INDICA 19]LLQflT19NH. _fQb"IROMQGAT10M EIB100 EED DS DL HD EW W JAN 15.50 15.00 28.30 11.00 PEll 16.60 MAR 19.10 22.10 17.50 12.10 12.50
- APR 15,00 12.00 31.30 18.90 MAY 13.20 24.10 15.20
-JUN 18.10 13.80 27.00 9.27 20.00 18.40 JUL 15.00 18.40 33.30 17.50 AUG 14.70 10.30 36.40 1.70 17.90 18.00 SEP 12.80 19.10 30.80 18.20 i' OCT 26.00 NOV 19.20 17.50 23.10 19.90 DEC 13.90 13.30 33.00 12.00 13.30 L
CHROMIUM-51 INDICAI9B l0_CAIl0N$ _ _CQSISQMQfATJ.0FS EfdLQD SSD DE EL VD tiEU W JAN 23,20 PEB 24.00 MAR- 70.00-APR; 13.10 MAY- 60.40 JUN 44.80 TUL -63.10 AUG. 62,70
'SEP- 185,00
/'CT . 195.48 NOV 12.10 DEC NOTRt Activitlen shown pro values actually measured, whetrean those indicated as t" are minimum detectable . activit ies under thw particular uunditionn of analyula of nucliden for which analyses are required by HRS Technical Specificationn (that in, the huclidos may or may not have buon present, but if no, there cannot have been more present than the amountu 11n ted )
A-13
RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Gamma-Emitting Nuclide Activity (pCi/ liter) in Water by Location -1990 MANGANESE-54 1NDICATOR L0 CAT 10NS _C,QEIttQL._LQCATlQNE PERlQD SMD EM EL ED SEU EU JAN <1.81 <1.78 6.60 <1.71 FEB <2.28 <2.43 4.25 <2.12 MAR <1.73 <1.81 13.30 <2.34 <1.74 <2.17 APR <1.80 <1.63 9.84 <1.56 MAY <1.62 <1.69 24.80 <1.82 JUN <1.78 <1.72 3.02 <1.65 <1.74 <1.76 JUL <1.66 <1.59 4.43 <1.71 AUG <1.6Q <1.78 ? <1.61 <1.71 <1.76 SEP < 1. h <1.64 7 9291 <1.61 OCT <2.40 <1.72 11.61 <0.82 NOV <1.72 <1,79 6.75 <1.81 DEC <1.71 <0.95 1.19 <1.84 <0.91 <1.86 COB \LT-58 INDICATOR L90ATIO.NS _CfLNJJLOL L0gAIl0NS P_ERIOD EED DE EL ED SEU FU JAN <1.98 <2.03 1.01 <1.96 FEB <2.37 <2.34 1,74 <2.44 MAR <1.65 <1.85 0 <2.12 <1.95 <2.13 APR <1.84 <1.70 15.Q. ]a3 <1.i2 MAY
<1,8)a
<1.72 9.87 <1.98 JUN <1.9 <1.91 1.52 <1.52 <1.89 <1.79 JUL <1.88 <1.98 1.95 <2.16 AUG <1.75 <1.96 0.97 <1.98 <1.95 <2.08 SEP <1.83 <2.06 1,57 <2.02 OCT <2.65 <1.9} 3.86 <0.96 NOV <1.94 <1.9/ 1.73 <2.18 DEC <2.15 <1.22 <1.98 <2.02 <1.20 <1.96 IRON-59 LEDICATOR LOCATLQNS CONTRDLJOCATlQES PERIqD SSD DF DL Wu SEU EU JAN <3.91 <3.97 <5.01 <4.07 FEB <5.63 <5.88 (7.28 <6.10 MAR <4.22 <4.43 7.85 <3.93 <4.46 <4.12 APR <4.14 <4.30 4.52 <3.89 MAY <4.29 <4.77 8.44 <5.18 JUN <4.23 <4.02 <4.56 <3.43 <4.41 <3.55 JUL <4.76 <5.04 <5.42 <4.68 AUG <4.22 <4.60 9.51 <3.91 <4.69 <4.80 SEP <4.08 <4.78 3.08 <4.45 OCT <6.62 <4.47 1.77 <1.98 NOV <4.68 <4.40 <5.43 <4.67 DEC <4.28 <3.35 <4.54 <4.81 <3.17 <5.14 NOTf: Act iv ttler. shown are values actually measut ed, whereas those indicated as "<" are minimum detuctable activities (MDAs) under the particular conditions of analysis of nuclides for which analyses are required by RBS Technical Specifications (that is, the nuclides may or may not have been present, but if so, there cannot have been more ptesent than the amounta lis t ed) .
A-14
RIVI'.it BFND STATION RAD 101.UG1 cal. ENV1RONMLNTAL MONITORING l'ROGilAM Gainma-Etcit t ing Nuclide Ac t ivi t y (pCi/li t et ) in Water by 1.acation -1990 COBALT-60 q
__._lMLLCAT0lLIACAIl0M 19 M R01c.l E ail 0ES wi10D EVi! DE I!L MD FU UU
- f AN <1.89 <1.94 <9.;7 < ?, . 00 hb bY , 5 MAY <1.82 <1.71 55.50 <1.91 J t'N <1.93 (1.93 6.14 (1.76 < 2 . 0 's <1.84 JUL <1.83 <1.83 9.01 <1.81
<4.Z6 <'.7C 10. .:0 <1.97 S
T A'ly, <t.s6 <' .99 11.9D <1.87 <1.89 <2.49
<' .64 31.60 <0.88 OCT NOV d.79 d.04 (' .77 19.20 <1.94 DLC <1.76 <0.99 2.85 (1.71 <0.91 <1.83 ZINC-65 INJtLCAIS1LJACAILQhS ..XQNIRQLJAGAIJDfiE 11J110D SW DF DL W SFU W IAN <4. Q <4.09 <4.31 <4.13 Ptn <5.53 <5.24 <5.22 <4.85 M ' 't 78 <4.09 <. 7 . 9 0 <4.99 <3.94 <5.23
<3
<3. 84 <3.63 <4.43 <3.53
< 1. (.3 c , 61 <5.98 <3.81
<3.i4 d 5$ <4.09 <3.57 <3.67 <3.62 a <3.21 <3.83 ( 4 (11 <4.40 At <3.40 G.95 < 4 . ~t 1 (1.96 S 0l- <3.48 <4.08 < 'i . % 0 .52 <3./4 <4.15 OCT <5.46 <3.47 <5.42 <2.03 NOV <4.17 <3.83 (I. 69 <3.9; DEC <3.75 <2.16 <3.h2 <3.86 <1.92 <3.96 N10B1UM-95
_,. ._ ,._JNDICATORJA_CM10NL ..ff0!i1RQk_IACAIl0M MGPD E9 DE lil HD SEE Ef
<1 AN <2.31 <2.39 <2.43 <2.31 PER <3.39 <3.57 <3.46 <3.49 MAR <2.27 <2.39 <3.52 <2.51 </.59 <2.15 APR <2.08 <2.23 <2.13 </.04 MAY <2.31 <2.54 (2.81 JUN <2,22 <2. <
<2.23. 5 b' <1.75 <2.39 <1.91 JUI. <2.51 <2.g8s0 <2.77 <2.69 AUG <2.15 <2.49 <2.85 (2.49 <2.22 <2.47 S E.Y <2.15 <2.G4 2.56 <2.44 OCY C . 51 16 < 1.1
NOV <d".97
. Ii1 d . 68 < 3' . 0 2 <2.57 DEC <2.59 <2.09 <2.49 <3.10 <1.91 <2.77 WOTE: Act ivit ies shown are values act t.- Lly measured, whereat. t hose indica t ed na "<" are mints.um detectable ac* 1t it iet (HDAs) under the part icular condit ions of analysto of nuclides for which analysen are required by 1:!)$ Technical Specif teations (that is, the nuclides mas or may not have been present, but if so, there cannot have been more present t han the amount s listed).
A-15
RI VI'R lil>.ND STATION I;AD101.0010Al, ENVIRONMENTAL. MONIT0ltlNG l'It0 GRAM Gamm/4-Emitting Nuclide Activity (pCi/ liter) in Watei liy I.ocat ion -1940 Zl RCONil!M-9 5
. _ 1NDICA10R IOCA110NS CQNTBRidROATIOM EDILQD EED LS DL ED F.hl' h'U JAN <3.37 <3.74 <3.6i <3.55 l'EB <4.52 (4.38 <5.0 <4.67 Malt < 3 . 3' (> (3.30 <5.4 <3.37 .76 <3.44 Al'it <3.iB <3.25 < ') . 4 / <]2.90
- t. 38 5 <4.99 <3.66 MAY JUN Jt !.
< ;3 . 60
<3.61 d.1
<l.66
<3.54
<1.28
<3.63
<2.95 <3.62
<3.79
<3.18 AliG <2.97 <3.68 <3.83 <3.47 <3.44 <3.61 SEP <3.04 <3.56 <4.12 <3.39 OCT <4.77 < !) . 5 3 1.03 <4.38 NOV <3.87 <3.73 <4.38 <3.69 DEC <3.45 <2.41 <3.45 (3.94 <2.25 <3.61 10DI NI:- 131
_1EMfAIO!Uat6110D CONIRQLLOCall0ES l'ERLO.D TED DW PL ED SWU EU JAM <2,17 <4.14 <2.31 <2.36 FEB <3.97 <4.81 <3.50 <4.42 MAR 44 <3.11 <1.74 <0.75 <2.05 <0.77 APR < 1.
<1 {24 <2,66 <1.38 <1.66
<7.74 <7.19 MAY <11.10 JitN <2.03 <2.26 <2.04 <0.69 <<2.8. I')8 8 (0.68 Jt1L <4.75 <5.69 <4.78 <5.11 AliG <' 5 <3.4p <10.90 <1.97 <11.70 SEP <2 40.50 <6.)0 <2.3 <2.62 <3.01 OCT <3.94 <5.10 <6.84 <3.88 NOV <3.72 <4.08 <3.63 <4.06 DEC <4.70 (13.60 <4.54 (6,17 <14.20 <6.40 CESi tCI-134 LNILifAlqB_leCATLONS . _ _ 30KIR0klaCAT10M EDLLOD EKD DW "L WD SW11 EU JAN <1.73 <1.54 <1.70 <1,79 FEB <2.25 <2.07 (2.40 <2.13 MAR <1.65 <3.03 <2.08 <2.20
< 1. {;> 4<1. 6 APR <1.68 <
<1.1. '$ iQ (1.81 MAY 1.56 <1.54 <2.34 <1.58 JlfN <1.62 <1.h4 <1.64 <1.58 <1.60 <1.69 Jtil, <1.66 <1.67 <i.66 <1.72 AUG <1.53 <1.80 <1.86 <1.65 <1 <1.64 SEP <1.49 <1.70 <1.95 <1.6;93 OCT <2.05 <1 52 0.91 <2.30 NOV <1.74 <1./6 1.41 <1.79 DEC <1.56 <0.94 <1.58 <1.75 <0.82 <1.76 NSTE: Activitica showti are va lues act ually itseasured , wtieretir, thor *e indica t ed nai " < " are minimum detectable act ivities (MDAe) under the pat ticular conditions of analyeth of nuclides for which analyses are tsequired by RIG Technical $pecifications (that is, thw nuclides may or may not have beon present, but i f r.o . there cannot have been more than the arwunth not ed ) .
A-16
. a i
RIVI'R lil:ND STATION RADIOLOGICAL ENVIRONMl:NTAl. MONITORING Pit 0 GRAM Gamma-0mittity Nticlide Act ivit y (pCl/ liter ) in 'a'at es by Locat ion -1990 CES10M-137
.lEul0AIDR_LQCAIl0N.S _CWlROLLQCATIOM EER10D M W DL EU El' W JAN <1.85 <i.55 <1.J2 <1.84 PED <2.24 <2. 8 <2.s4 <2.26 Mall <' .8 (' O . <2.94 <2.20 <1.y4 <2.28 APR <' .4 <' .2 <1.$0 < 1. 20
- MAY <' .8 <' T <2 8 <1.84 JUN C . 3 C .di
. <i..3 <1.60 <' .82 <1.80 JUL <' .73 <' 6 <1. 9 C .79 ADO C . C 8 <. <1.62 C .2 <1.82 Sl?.P ('. <.H)J < .91 10 < 7 OCT. <2. 0.61 .92 . 1 NOV <1.8 <1.76 .16 <' 92 ,
DEC <1.78 -<0.93 <1.81 <1.89 <0.86 <1.84 t ilAltl UM- 140
_1@lCA10lLLQCAT10D ._. _f0RT10LLQ. CAT 10M EEkl@ ED W 11 ED M EU.
TAN <13.30- <18.40 <12.40 <14.50 FIl <23,80 <30,40 <23.70 <2.58 .
hk h '.Y
!ib C y.
kb0
?5 70
- kh bib
<24.50 JbN <'2 <
<?91 I; 70 . 30 <l4
< . 60 <7.21 <16.60 (7.24 JUL < l. -<?7.50 <27.80 <21.70 b lkl0 b> lf,'hh '
l
.R
-DEC 31:l8:ll:20
<19.90 <34.90
- !M8 (19.50 <27.00
&lkbM
<31.70 <23.50 s LANTilANUH-140 1Nht0AIDILLEGAT10M._. _ _C0hTROLLOCATIORS Efat0D M M RL ED M h'U JAN - <6.17 <6
<14,82 <4.88 <6.30
<1 .80 PED
. ,lg <10.20
<1{.10-A -
4' 8'
<8.'
MAY - .<6.1 < .7;2 <9.43 JUN <6.3 <5.36 45 <.1 <2.66 <6.77 <2.92 JUL <8.05 <11.00 <10.50 <9. 8 AUG <6.24 <7.14 <6.59 <6. 3 <7.39 ;
SEP, <d'80
< 86 <6.75 <7.67 :<6. 7 '
0 03 DEC' kk
<8.23 bk
<14.70 <6. O'.
74 h <11.40 N',N
<12.10 <9.93 NOTE: Activit fem shown are values actually measured, where as those indtrated an "<" are minimum detectable activities (HDAs) under the partlJular con.ittlons of arutitula of nuclides for which analysen are regtelred by RDS Technical fipconficationn (that it, the nuclides may or may r.ot have been present.. hat if so, there cannot have t>een pos e than the naounta not ed)i A'-17 h\ ,
_ , . ...... _ . .__ ._. ______._____.___.~._.._._.-.___._._.m_
RIVIR BEND STATION RAD 10 LOG 1 CAL ENV1RONMENTAL MONITORING PROGRAM Gamma-Emitting Nuclider. In Sediment (pC1/kg dry) by location - 1990 DERYLLIUM.7 PO7AS$10H.40 1.'IMDD I!QGilETM EfMELO 10tDltLM UtMMM MAY 406.00 13706.00 16301.00 AUG 14$24.00 4773.00 CESIUH+134 CESit* 137 EIMDE LWEntEA!! UnalM kQHEIRTM Lf1TE!M
-HAY (D.77 <!7.10 10.00 74.60 AtfC <!7.70 <16.B0 <21.10. <!7,10 Gamma-Emitting Nuclides in Tish (pC1/kg wet) by Location - 1990 j l
PO7AS$ltm 40 DQ.EM'MM kflIREM FIRikQ d 12 13 13 15 11 12 t) 11 11 FEB 4061 MAR 3018 JUL 2h37 3002 3405 3508 3202 Dtc 3316 3336 2446 3231 2627 1377 ttANGANES$ 54 1!QENHELM RAIUM f!MDD 11 11 AJ H 15 11, 12 0 11 ti 'l ttb <25.4 MAR ~ <l9.1 JUL <20.4 (10.0 (6.65 (4.4$ <$.17 Dtc <15.6 (34.4 <3.02 <l4.9 <32.3 <3.36
')
IRON =$9 DD.KE11 Eld Ef1ISEM IIMOD 11 12 D. H 11. Il 12 .t3 11 il 1tB <62.6 MAk' J UL. <46.6 . <47.0<40.3 <22 5 <16.1 <!?.6 Dtc <67.8 <!!8 <lf.3 <60.5 492 6 <!6.6 COBALT-58 D2MMIAEAh kfJifREM
-FEM 9D 11 42 O A4 81- 11 12 u 11 11 -
ttB <26.2 MAR <20.4 -
JUL- <20.6 (19.0 . <18.3 <5.22 c6 18 DEC < 23. 3 - <39.9 <$.38 <22.1 <36.5 <4.58
. NOTIM Activities shown are values actually measured, wherena those indicated as "<" are minimum detectable activities (MDAs) under the particular conditions .of analyela of nuclides for which analyses are required by RBS Technical $pecificationa (that to, the nuclides may or may not have been present, but if so, there cannot have been more present than the amounts list <d).
4 A-18
.a .y. -.m--[ b s , .-,, . , - - -'.v.u,,- w, $, u me m -
r,*,, w-~,-.-c.<- w ,,,,-Uwm.,..r,,,cr..m.,v...
h,.,,,, , . - , , ,
- i,~,,y,,,U-, w_-w---,,---,,,. , -,- ,
, O HIVER llEND STATION RAD 101,001 CAL ENVIRONMENTAI, MONITORING Pit 0GilAM Gamma-Emitting Nuclides in fish (pCl/kg wet) by Location - 1990 COBALT-60 .
!!OKNithEM MflibtM flR1QQ 11 12 13 f.i 15 11 12 13 11 il Fl:8 <29.8 HAR (22.3 JUL (23.9 423.0 <8.2h <$.10 <6 25 DEC (17.9 <40.6 (4.12 7.40 (32.7 <3.94
!!NC+0$
DQEMM RIMI l'fathte IIR1RD 11 . 12 83 11 11 11 13 la t_t 85 Ftb <63.4 HAH <45.2 Jill <48.8 440.9 <!8.7 (13.5 144.9 DEC (40.1 (60.1 <9.89 <36.4 <66.1 <9.26 Ctsl0H 134 I M 61ALAM ErstREMI FIRIUD 11 11 13 A.i 11 .t1 12 1) 11 .t A FLb <24.6 HAR <17.6 L J t'L (16.3 <!6.9 <5.$0 <3.02 t4.40 Dtc (15.1 <36.0 <2.64 (13.5 (25.5 <2.61 C E s i t'H.13 7 Lt0MdafEEAd L'f3IB18d RERl0D #1 12 la 11 th 11 12 14 is 33 FEB (25.1 MAR 7.07 J UI. (22.2 (18.9 <6.74 1.67 (5 04 Dtc (14.h (33.2 <2.99 (13.7 (26.1 <2 97 NOTRt Activities shown are values actually meanaured, whereuu those indicated as "<" are minlaum detectable activit tee (HDAs) under the particular conditions of analysis of nuclidea inr which analynea-are required by kas 7echnical Sleccifications (that is, the nuoliden may or may not have been present, but if nu, there cannot have been more pressent -than the amounts listed.
A-19 u._ .
- ..______--_,-_.-_____-._._____m.. ___ .---,-. ____- _._m
, e a i
IIIYl;It lil:ND STATION llAD10th01 cal, I;NVll(ONH1'.NTAI., MONIT0ltING Pi(00l(AM l
Gamma-tmitting buclide Actitity (pC1/kg wet) in titoadleat Vegetation by Imcation .1990 BiHYLLION-7 l I
. _ lhDIEAIQ1LLOC&IIDM _ 00FIROLLVIAllDR.
_.___ MLGdDILi1 MLGMDItLiL ...A&01.A.ffallIK11ARL 1
flE10D 81 42 $3 il 82 #3 #1 82 #3 ;
1 JAN til 297 470 2292 ttD. 14$ 290 196 602 2665-MAR 164 126 303 218 APR 264 164 MAT 266 44$ 126 191 377 221 JUN 115 140 230 204 165 250 JUL' 734 149 444 330 1494 !$$ 164 1060 762 AUG 257 230 IS6 297 191 2h2 56 360 436 StP 110 2040 253 206 130 369- 653 007 115 120 164 91 NOV 196 153 17 139 DFC $05 107 71 157 113 POTASSitH.40
..- .lhDICAfDLLQfAIl0M1 CONIEDil0CATIQNL MLGABEILt1 RALGAhuttLf2 JhGOLLtllil1EBilAld F1110D 41 82 #3 st 42 f3 41 42 83 JAN 4970' 4468 2691 4226 4923 4219 Felt - 4181. 4610 4756 4761 -3607 4783' 4656 2$75 MAR 4612 348$ 43$2 3635- $680 APH 4461 4218 4483 3860' 4529 3675 $427 MAY 1820 1645 1966 2937 4023 4716 5766 $150 6267 JUN 2226 2073 2l00 4948 4693 3950 3133 0632 7762 JUL' 3910 1646 3372 $229 6099 5176 4202 4674 5544 AUG 4000 2158 3292 4140 2497 3362 3778 5695 3602 SEP 2601 .2114 2112 3152 4270 $203 2750 6664 2909
. OCT 3704 1530- 1616 2782 4D28 2997 4056 3261- 3853 NOV 177$ 1854 2039 3249- 3290 5011 '1926 2474 2$43 DEC 3091- 2567 1852 2591 3435 2521 2629 3175 3375 li AR itH 140 luu1CA1Q8.AQCAT1ults COEIRQLiuCATIDR ,
RELGARDEIL11 . REGAERELR J LQL&_tKELIfEllAE L
- l'IRIOD ' #1 82 83 81 42 83 .81 #2 #3' i OCT' 47.2 NOTE Sampling requirement for vegetation in one sample of euch of three dif ferent types f rom each location per month. -Due to lack of availability, only one cont rol mample was obtained in January, March, and April, and only two cont rol camples obtained in February. Likevice, only one sample f rom Cl was obtained during March and only two samplea from C2 were takeny in January Activities shown are values actually measured.
A-20
. . _ - -. .. _ _ _ _ _ _ _ _ _ _ _ . _ _ . _ _ _ _ . - _ _ ~ . - . _ _ . _ -,
FIVPR llEND STATION RADIOLOGICAL ENVIRONMPNTAL MONITORING l'ROGRAM ;
6amma.tatt ting Nuc tido Act ivit y (pC A/kg wat ) in broadlenf Vegetation 1.y location 1990 10 DINE 131 LulCAIQLLOCAUDNa .
COEIROLLQCAUQM_
MllLGARMJLtL _. _M1.faARDIMJ 2 _AhliOLA IU111tinML E1110) #1 62 03 il 82 #3 81 42 03
- JAN <25.5 (24.6 <34.2 <28.0 <26.6 (39.5 FEB .<26.2 <29.0 <31.3 (23.8 <2J.3 (26.B <29.2 c44.3 HAH- 429.3 <23.7 <30.4 <26.2 <28.6 APR <30.4 -<32 0 <26.0 (25.6 <22 3 <27.0 <23.6 NAY (22.0 <27,6 425.8 (26.1 (25.9 <31.6 <22.6 <26.0 <25.1 JUN <26 5 424.7 (26.6 < 29 pJ <24.6 (26.0 (30.5 (25.4 (61.0 JUL (22.2 <23.3 (22.1 <28.6 <27.2 <25.3 (26.2 <33.? (20.2 AUG (27.6 <22.5 <28.6 <31.5 (20.4 <24.4 <32 1 <29.5 <31.2 StP- <!9 9 <24 6 422.6 <21.1 <26.2 (22.1 <21.2 <30.1 <28.4 OCT. (23.5 <21.1- <24.8 (23.3 431.8 <!6.2 <22.7 (26.8 <26.4 NOV (19.5 <20.5 <20.2 <th.9 -<19.6 <17.8 424.1 <26.7 426.5 Dtc (22 2 < 2 3.6 - <!9.6 <!7.6 <!'.5 (15.2 <23.6 (21.6 .<!6.9 CthiUN.134
( M1CATOR LO(ill0NS fDE U Q,Lt.DCAllDEl _
_ MLsAEML)J___ HLiAMI!Li3 ._ Akirki.A RAllM11ML l'ARIOD #1 f2 83 el #2 83 #1 #2 #3 JAN < 30. 7 - (26.9 (39.3 <34.6 (28.0 (43.5 FEB (22.6 - <30 5 <30.0 <23.9 <27.0 <28.1 <34.6 t42.6 MAR 435.6 429.6 (33.3 (26.9 <26.7 APR (29.6 .439.1.. <33.4 429.2 (27.6 (28.5 <23.0 MAY <20,6 (23 7' 426.5 <26.9 <30.5 429.1- <25.8 <27.1 <23 7 JUN. <26.3 <21.9 <24.1 <27.5 (28.3 <27.1 <29.4 (24.4 <26.6 JUL '< 23.4 422.0 <20.7 (27.8 <26.3 (23.4 <!8.9 <21.6 (9.71 .
AUC :29.6' (25.0 .<26.4 <34 1 424.2 <21.5 (21.5 <!9.1 <23.1 F SEP 420.9 423.2 (24.9 (20.4 <25.9 .<!9.2 <l9.7 (30.3 526.0 007 <22.1 (22.1 (24.0 . <21.7 <30.2 <!S.4 (22.0 426.6 <20 9 NOV (20.7 <22.4 (25.9 (20.5 <!9.8 <!7.3 <23.0 (30.3 <29.8 Utc <23.0 <28.4 <24.5 (19.4 <!b.5 <!7.5 424.6 <!$.2 <l9.4 CE81UM 137 lH.lfAIDIL10IAIIDE1_ . COETA9LLQCAT191!a_
. MLGAliML21 MA.GAMILt1 _ EltiO!.Ll'LEnnUML 21R10D #1 #2 #3 il #2 #3- #1 82 43 JAN= <34.1 <29.3 <42.1 . <31.5 <31.7 <43.3 FEb <31.6- <38.8 <33.0 <31.1 <24.5- <24.6 <35.8 <51.1
<35.4 MAR <29.5 <39.6 (33.0 <30.7 aPH ( 34.1 - < 37,7 - <32.9 <31.5- <29.6 <35.7 424.2 M*Y <32.9 .<33.4 434.3 ' <35.9 <28.1 (26.1 (28.2 <31.6' (25.7 JUN 19.4 <29.6 15.8 <29.6 <27.7 <31.4 <26.5 .26.7 <32.1 JUJ 27.6 (30.3 <24,9 <30.4 <32.9 (25.3 <25.3 434.0 <!1.8-AUG 20.7 (32.4 434.4- <33.3 (27.6 (23.2 <25.1 11.6 <24.3
'MP; <26.1 <29.0 ;<27.7 (24.2 <28.3 (25.3 <27.2 <32.2 <28.0 OCT (31.0 <24.7 16.6- <25.3 <33.4 <19.7 (25.9' s4s,9 (26.6 NOV <28.2 <24.l' 427.6 <25.1 <21.6 (21.2 (26.9 <31.0- (31.2-Dtc. <27.2 ( 27.9 <22.9 (16.4 <19.0 <!9.1 (26.2 (24.3 (22.1 N0ft Sampling requirement for vegetation la one sample of each or three dif ferent typen from each location per month. Due to lack of availab!!1ty, only one control sample was -obtained in:
January. Pfarch, and April, and only two control samples obtained in February. Likewise, only one sample f rom Gl ' was chtained during tiarch and only two samples from G2 were taken in-January.
Activjties shown are value actually measured, whereas those indicated as "<" are minimum detectable actit tllen (PtDAs) under the particular conditions of analysis of nuclides for which
- anaitaea are required by Rf18 7echnical Specifications -(that in. the nuclides may or may not have been present, but 1? so. there cannot have been more prosent than the amounta listed.
A-21
__ _ _ _ _ . _ _ __ _ _ _ _ __ __ _ _ _ . -- m_. . __
.c , .
RIVER BEND STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT POR 1990 1.
APPENDIX !!
SumatarY Of Pre 0Deration_al REr (naseline) nesul t s Table D.1 _ summarizes the results of preoperational radiological envi- <
ronmental moratoring from January,1983, through October,1985. Further detallu are available in the respective annual reports (1983,1984, and 1985). '
L
.t.
W f
1
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b w g- w w-+ew.my- w yy : ,,,,gaggyyg gyyes-upygem&y 1w s w vy-w yggwa -
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TABLE B.1 PRE 0PERAT10NAL RADIOLOGICAL ENYlRONMENTAL MONITORING PROGRAM
SUMMARY
(Page 1 of 4)
River Bend Station Doclet Numbe : 50-458 West Feliciana Parish, Louisiana Repotting Period: 1/1/83 -10/31/85 Medium or Type and 1. owe t Limit All Indicator location with Highest Control Numtier of Pathway hampled Total Numtwr of S t a t t otis, Annual Mean locationr, s Nontoutine (Unit of of Ar.alyses DetectionI Mean (ff' hamt McSh1U 2 Muan ( f )' heported Measuremer.t) l'erformed (LLD) Range Dist . /Dir. Range Range Results Air Particulate Cross tieto 0.01 0.03 (751/759) AQs2 0.03(146/156) 0.03 N/A (1086) 0.01 - 0.09 5.6 km NW 0.0 - 0.09 (320/327)
(pet /u3 ) 0.01 - 0.08 Ca-134 0.05 ALL (LI.D ALL (LLD N/A (951 ts-l37 0.06 ALL tLLD ALL (LLD N/A (95) . -
AirRadiogodine 1-131 0.07 ALL (LLD ALL (LLD N/A (pci/m ) (1066)
Direct ( T I.D ) Camma fe 8 (1015/1064) TM2 7.h (27/26) 6.71139/150) N/A Monthly J.7 - 19.3 4.2 lu WSW 3.2 - 16.2 0 - 27.6 (mR Tatul) (1214)
G aouna 19.03 (404/418) TC1 27.53 (11/11) 16.93 (5 N/A Quarterly G.6 - 32.1 1.6 km SE 12.2 - 27.6 6.6 - 2 (472)
Surface Water H3 2000 ALL <LLD ALL ' &D N/A (24)
( pC 1/11t e e )
Mr-54 16 ALI <LLD ALL (LLD N/A (GG)
Co-56 15 ALL <LLD ALL <LLD N/A (ds; fe-59 30 ALL tLLD ALL <LLD N/A (68)
Co-60 15 AL', (LLD ALL (LLD h/A
( G B 's in-65 30 ALL (LLD ALL (LLD h/A (66)
Nb 95 15 ALL tLLD ALL (LI.D N/A (68)
Zr-05 30 All (1.LD All, (LLD h/A (66) 1-131 15 ALL <tLD ALL (LLD N/A (68)
Cs-134 15 ALL (LLD ALL (LLD N/A (66)
Cs-137 16 ALL 'LLD ALL (LLD N/A (68)
Ba-140 60 ALL <LLD ALL (LLD N/A (68)
La- 14 0 15 ALL <LLD ALL <LLD N/A (68)
Cross Beta 4 6.1 (23/26) $WD 8.1 (23/26) 7.8 (24/26) N/A (52) 4- 12 4 Ks 4- 12 5 - 13 downstream B-2
. t -
l T Al'I.E B.1 l'ItE01' ERAT 10N AL RAD 101,00.lCAI. ENVill0NMENT Al. MONIT0ltl NG l'It00R AM
SUMMARY
(l' age 2 of 4 )
Rivet Bend Station !)oc ke t Nanibet ; 50-458 West l'eliciana Par ish, Lottisiana teliot t irtn Pei lod: 1/1/83 -10/31/85 Hedium or Type and Lower 1.imit All l tul t ra t o r Loc at 6on with Highent Conttul Numter of I'athway Sumpled Total Number of btattons Annual Mean totattons, Nontoutinn iL! nit of of Analyses Detectlon I Meun ( f )# .he#tt.__... _ _11e ntti Li *kun ( f I' keported Meanut eserit ) Performed ( 1.L D ) kannte Dint./Dir L.<nge kangs kenulta Groundwater 4 H-3 2000 All. < l.LD ALL <l.LD N/A (pCL/ liter) (24)
Mn-54 15 All < l.LD All <LLD N/A (22) 0o-58 15 ALL <l.LD ALL <LLD N/A (22) re 59 3D ALL (LLD All (LLD N/A (22) 00-60 15 Al.L (LLD ALL (Lt.O N/A (22)
Ka-65 30 Al,L < Lt.D Al.L <LLD N/A (22)
Nb-95 15 ALI. (LLD AL!. <LLD N/A (22)
Tr-95 30 ALL <l.LD Ali. < l.LD N/A (22) 1-131 15 All < l.LD AI.! < l.LD N/A (22)
Co-138 15 All <!LD ALL < l.LD N/A (22)
On-137 18 ALL <LLD ALL tl.l.D N/A (22)
Da-140 60 All < l.LD AlL < !.LD N/A 1221 La-140 15 ALL <t.lp All < Lt.D N/A (22)
Crohn beta 4 4 (5/12) WD 4 (5/12) 6 (2/3) N/A t15) 2-8 470 m SW 2-N 3-9 D inking Water b 11 - 3 2000 ALL < LLD ALL (LLD N/A (16)
(1<i/llter)
Mn 51 15 A L.l ( l.i.D Al.L < l.l D N/A (40)
Co-56 15 ALL <llD Al.L (LLD N/A t40)
Fe 59 30 AL.I. < LLD ALL (LLD N/A (40) 00-60 15 ALL (1.LD All. < !.LD N/A (40)
In-65 30 Al.l. < l LD All. <lLD N/A (40)
Nb-95 15 ALL <l.LD ALL cl.LD N/A (40)
B-3
s r ~.
TABLE B.1 PREOPERA*fl0NAL RADIOLOGICAL ENVIRONMENTAL HONITORING PROGRAM
SUMMARY
(Page 3 of 4)
River Bend Station Docket Numberl 50-458 West Feliciana Parish, Louit, lana Reporting Period: 1/1/83 -10/31/85 Hedium or Type and Lower Limit All Indicator Location with Highest Control Number of Pathway Sampled Total Number of $tations - Annual Mean Locations Nonroutine (Linit of of Analyses DetectionI Hean (f)2' Haptg Htan1L}2 Mean (f)2 Reported Hvasurement) Performed (LLD) Range blat./Dir. Range kange keeulta Drinking' Water $ 'tr 95 30 ALL (LLD ALL (LLD N/A (40)'
(pci/ liter) 4 131 15 ALL (LLD ALL <LLD N/A (continued) (40)
Co.134 15 ALL (LLD ALL <LLD N/A (40) i Ca.137 18 ALL (LLD ALL (LLD N/A (40)
Ba 140 60 ALL <LLD ALL (LLD N/A (40)
La.140 15- ALL <LLD ALL 4LLD N/A (40)-
Croen Beta 4 6.8 (28/26) Donaldson. 6.8 (28/28) 7.8 (24/26) N/A (54) 3 12 ville 3 12 5
- 13 138 km downstream Shorellne E 406 NONE - 13.783 (2/2) SED 13.7E3-(2/2) N07 N/A Sediment (2)- REQUIRED (11.4 15.9)t3 4 km 11.4 15.9)t3 BEQUIRSD downstress (pci/kg dry) ca.134 150' ALL <LLD ALL (LIS N/A (4)-
Co.13 7 _ 100 ALL (LLD ALL (LLD N/A Milk- K.406- NONE 1313 (6/9) HF2 1313 (6/D) 1316 (7/91 N/n (18). 1179 a 1476 6 km ESE 1179 147S 1196
- 1409-(pci/ liter)
'I 131 1 ALL <LLD ALL tLLD I N/A (81)
Co.134 15 ALL (LLP ALL (LLDI N/A (82) ca.137 18 ALL (LLD ALL (LLDI 'N/A (82)
Ba-140: 60 'ALL (LLD ALL (LLDI N/A (81).
La.140- 15 ALL (LLD ALL (LLDI N/4 (82)-
K-40 6 Fish / -NONE 9037 (2/2) FD 9037 (2/2) 7640 (4/4) N/A Invertebrates (6), REQUIRED G320 11754 4 km 6320 - 11754 4177 11438 downstream (pC1/kg vet)
Mn-54 -130 ALL (LLD ALL (LLD N/A
-(15)
B-4 u-I, . - +
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=
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TABLE li.1 PREOPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
)
(Page 4 of 4)
River Bend Station Docket Number: 50-458 West Feliciana Parish, Louisiana Reporting Period: 1/1/83 -10/31/85 Medium or Type and Lower Limit All Indirator Location with Highest Control Number of Pathway Sampled total Numbet of htatione Annual Mean Locations Nonroutine (Unit of of Analyses Detection I -Mean (f)2 hatL __.- _lltBull) Mean (f)2 hegot ted Measurement) Performed (LID) Rango Dist./Dir. Range Hange Heswl t f.
floh/ Co-58 130 ALL (LLD ALL <LLD N/A Invertebraten (15)
(continued) re-59 260 ALL <LLD S ALL <LLD6 gjg (15)
Co 60 130 ALL <LLD ALL <LLD N/A (15)
En 65 260 ALL <LLD ALL <LLD N/A (15)
Co-134 130 ALL (LLD ALL (Lt.D N/A (15) ca.137 150 ALL <LLD ALL <LLD N/A (15)
Broadleaf K-406 NONE 3369 (6/10) C2 3368 (6/10) 3768 N/A Yegetation til) REQUIRED 1396 - 5389 1.1 km NW 1398 - $389 ningle value (pci/kg wet) 1 131 60 ALL (LLD I ALL <LLD N/A (75)
Ca 134 60 ALL <LDD ALL <LLD N/A (7b)
Ca 137 60 97 (4/43) Cl 97 (4/43) ALL <LLD N/A (76) 59 - 129 1 km WNW 59 - 120 h21Idil
- 2. Mean and range based on detectable measurements orly. Fraction of detectable measurementa at speci-
-fled locations in indicated in parentheses. (f)
- 3. For each of the TLD locations in 1985, a value equal to 1/3 of its 4th Quarter gasuna done la used to almulate a " quarterly" meenuren?nt for October, 1985
- 4. Beginning in January, 19'15, groundwater was sampled f rom one upgradient (VU = control) and one down-(' gradient (FD - irw11cator) well; previously groundwater was sampled from conutruction dewatering I
wella.
- 5. The upstream surface water sampling location (swU) la used an a " control" for drinking water compara isons.
- 6. The values for K-40 were derived from the (then) inciptent fre outie analytical program 7 The values listed for the control location for milk w-re derived from the (then) incipient in-houne analytical program. Training of personnel in calibrition and analytical.siethods delayed sample pre-paration and counting. As a result, the required LLDs were not met in 2 out of 6 1-131 analynes; I out of 9 Ca-134 analyben; I out of 9 Cs-137 analysen; 2 out of 9 ba-140 analyses; and 4 out of 9 La-140 analyses. Similarly, the required L1D for 1 131 in broadleaf vegetation wun not met in ! out of 11 unalyses. (See discussion of Program Exreptions in Preoperational Radiological Environmental Monitoring Report for 1935.)
- 6. The LLD for one downstream fish sample (catfluh, analyzed in-house) was 265 pCi/kg (wet). The LLD for one upst ream fish sample (largemouth bass, analyzed in-housei van 263 pC1/kg t vet ).
B-5
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