i · procedures, can be found in sections 1101-1111(SRS EM Program) of the Savannah River Site Environmental Monitoring Section Plans and Procedures, WSRC–3Q1–2, Volume 1. Because

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DISCLAIMER

This report was prepared as an account of work sponsored

by an agency of the United States Government. Neither the

United States Government nor any agency thereof, nor any

of their employees, make any warranty, express or implied,

or assumes any legal liability “or responsibility for the

accuracy, completeness, or usefulness of any information, ‘

apparatus, product, or process disclosed, or represents that

its use would not infringe privately owned rights. Reference

herein to any specific commercial product, process, or

service by trade name, trademark, manufacturer, orotherwise does not necessarily constitute or imply its

endorsement, recommendation, or favoring by the United

States Government or any agency thereof. The views and

opinions of authors expressed herein do not necessarily

state or reflect those of the United States Government or

any agency thereof.

DISCLAIMER

Portions of this document may be illegiblein electronic image products. Images areproduced from the best available originaldocument.

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WSRC-TR-98–O0314

Savannah River Site

Environmental Data for 1998

Editors

Margaret W. ArnettAlbert R. Mamatey

Prepared for the U.S. Department of EnergyUnder Contract No. DE–AC09–96SR1 8500Westinghouse Savannah River CompanySavannah River Site, Aiken, SC 29808

I

Acknowledgments

The editors acknowledge with appreciation the efforts of the following individuals and groups:

Environmental Monitoring Section/Environmental Protection Department (for technkal expertise,review, oversighg and clerical support during the preparation of this book)

Brenda AlejoSandra BoyntonCarl CookMary DodgenLarry EldridgeDave FillerPete FleddermanLynne Geary

June HallJim Heft%er

Bob HendersonTracey HumphreyMoheb KhalilBill LittrellBob LorenzPhil MillerPriscilla PattersonStuart StinsonBrenda WalkerRobin Young

Westinghouse Savannah River Company

Timothy Jannik and Bill Carlton (for dose estimates)

John Ellinger, Karl Bergmann, Gary Fuller, and Chuck Harvel (for computer and software support)

Marvin Stewart (for formatting for the Internet)

Larry Koffman (for map production and for help with graphic and text transfer)

Bart Marcy (for authorized derivative classification)

WSRC Management Services (for customer service, illustrating, classification, printing, and qualityassurance support-Bemadette Hobbs; Eleanor Justice; Trish Baughman; Randy Collins, TomCoughenou~ Pat Dominey; Juli Heam; Sharon Lybrand; Bob Shankl% Yvonne Nixon; MichelleNorri% Greg Jansen)

Department of EnergySavannah River

Mary Langford, coordinator, and Ben Gould (for DOE-SR review)

Mina Perrin (for DOE-SR classification and approval)

Environmental Advisory Committee (for independent technkal review)

Dr. Edgar Berkey, National Environmental Technology Applications Corporation, University ofPittsburgh

Dr. Bemd Kahn, Environmental Research Center, Georgia Institute of Technology

Dr. Dennis Paustenbach, McLarenll%rt Environmental Engineering Group

Dr. Milton Russell, Energy, Environment and Research Center, University of Tennessee

Dr. Bernard Sweeney, Stroud Water Research Center, Academy of Natural Sciences

Dr. Gordon Wolman, Department of Geography and Environmental Engineering, Johns HopkinsUniversity

Preface

This document presents data from Savannah River Site routine effluent monitoring and environmental surveillanceprograms. Information in the book is summarized in the Savannah River Site Environmental Reportfor 1998(WSRC-TR-98-O0312). Information about the environmental monitoring program, including a completedescription of Environmental Protection Department/Environmental Monitoring Section sampling and analyticalprocedures, can be found in sections 1101-1111 (SRS EM Program) of the Savannah River Site EnvironmentalMonitoring Section Plans and Procedures, WSRC–3Q1–2, Volume 1.

Because of the data table columns’ space requirements, many abbreviations have been used. To assist the reader,lists of radionuclide and chemical nomenclature and sampling location abbreviations are included following thisintroduction. Units of measure, scientific notation, and conversion charts also should help the reader A collectionof maps showing radiological and nonradiological sampling locations completes this introductory section.

The first few tables include lists of the media sampled and of minimum detectable concentrations for variousanalyses/media. A table of nonradiological environmental surveillance detectionlreport limits also is included.Following these explanatory tables are data tables with radiological and nonradiological etlluent monitoringresults, radiological and nonradiological environmental surveillance results, dose estimates, and quality assurancedata.

Data tables sometimes present fewer results than would be expected according to the frequency described in thesampling and analysis schedules. There are several reasons for these discrepancies. Sample collection problems,such as loss of power to the sampling site or inaccessibility to the sampling site (because of locked gates, flooding,etc.) may have occurred. Also, results for collected samples can be rejected for such reasons as insufficient samplevolume, low chemical yield, or equipment failure. The “number of samples” columns in the tables refer to thenumber of results used to determine maximum, minimum, and average concentrations.

The following should aid the reader in interpreting the datrx

● Analytical results and their corresponding uncertainty terms generally are reported with up to three significantfigures. The last significant figure of a result is determined by the quantification of the uncertainty term. EMSattempts to report the appropriate confidence in the result with the correct number of significant figures.

“ The reported uncertainty of a single measurement reflects only the counting error-not other components ofrandom and systematic error in the measurement process—so some results may imply a greater confidencethan the determination would suggest.

● An uncertainty quoted with means represents the standard deviation of measurements about the mean value.This number is calculated from the results themselves and is not weighted by the uncertainties of theindividual results.

● All values represent the weighted average of all acceptable analyses of a sample for a particular analyte.Samples may have undergone multiple analyses for quality assurance purposes or to determine ifradionuclides are present. For certain radionuclides, quantifiable concentrations may be below the minimumdetectable activity of the analysis, in which case the actual concentration value is presented to satisfy DOEreporting guidelines.

“ The generic term “dose:’ as used in the report, refers to the committed effective dose equivalent (50-yearcommitted dose) from internal deposition of radionuclides and to the effective dose equivalent attributable tobetalgamma radiation from sources external to the body.

Copies of environmental reports maybe obtained by contacting

Bob Lorenz, Manager, Environmental Sampling and ReportingBuilding 735-16AWestinghouse Savamah River CompanyAiken, SC 29808Telephone 803-725–3556E-mail address: [email protected]

WSRGTR-98-00314SRS Environmental Data for 1998 i

Contents

Listof Figures . . . . . . . . . . . . . . . . . . . . . .

Listof Tables . . . . . . . . . . . . . . . . . . . . . . .

Radionuclide and Chemical Nomenclature

. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . v

. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . vii

. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xi

SamplingLocation and OtherAbbreviations...

. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . X111

Units of Measure, Scientific Notation, and Conversion Tables . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xv

Errata from 1997 Environmental Data . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 249

—.- .-. .

List of Figures

Figure 1

Figure 2

Figure 3

Figure 4

Figure 5

Figure 6

Figure 7

Figure 8

Figure 9

Figure 10

Radiological Sampling Locations — Air Surveillance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xvii

Radiological Sampling Locations — Surface Water (SRS Stream and Savannah River Water) . . . xviii

Radiological and Nonradiological Sampling Locations — Fish . . . . . . . . . . . . . . . . . . . . . . . . . . . . xix

Radiological Sampling Locations — Soil . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xx

Radiological Sampling Locations — Sediment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxi

Radiological Sampling Locations — Vegetation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxii

Nonradiological Sampling Locations — Liquid Effluent (NPDES)...

. . . . . . . . . . . . . . . . . . . . . . .. XXIII

Nonradiological Sampling Locations — Surface Water(SRS Stream and Savannah River Water) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxiv

Drinking Water Systems . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xxv

Nonradiological Sampling Locations — SRS Stream and Savannah River Sediment . . . . . . . . . . xxvi

WSRC-TR-98-00314SRS Environmental Data for 1998 v

. .

—-

List of Tables

Sampling

Table 1Sample Me&a Information . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1

Table 2RepresentativeMinimumDetectable Concentrations forRadiologicalAnalyses . . . . . . . . . . . . . . . . . . . . . . . . 5

Table 3NonradiologicalEnvironmentalSurveillance DetectiordReportLimits . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11

Radiological Effluent Monitoring

Table 4RadioactiveAtmosphericReleases by Source . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13

Table 5Radioactive Atmospheric Releases by Stack/Facility and Comparisonof Annual Average Concentrations to DOE Derived Concentration Guides . . . . . . . . . . . . . . . . . . . . . . . . . . . 16

Table 6Radioactive Liquid Releases by Source(Including Direct and Seepage Basin M@ationReleases) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 24

Table 7Liquid Radioactive Releases by Outfall/Facility and Comparison of AnnualAverage Radionuclide Concentrations to DOE Detivd Concentration Guides . . . . . . . . . . . . . . . . . . . . . . . . 25

Table 8Calculatti Migration of Radioactivity from Seepage Basins. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 30

Table 9Estimated Tritium Transpoti in SRSSkems and We Savannti River . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 31

Table 10Transport of Actinides in Savannah River Site Streams . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 34

Radiological Environmental Surveillance

Table 11Radioactivity inAir . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ...35

Table 12Tritium inRainwater . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 41

Table 13Radioactivity in Rain Ion Columns . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 42

Table 14ThermoluminescentDosimeter(TLD) Results-SRS &eas . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 46

Table 15Thermoluminescent Dosimeter(TLD)Results —SitePerimeterStations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ...49

Table 16Thermoluminescent Dosimeter (TLD) Results —Environmental Surveillance(AirMonitoring) Stations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 50

Table 17ThermoluminescentDosimeter(TLD) Results-PopulationCenters . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 51

Table 18Thermoluminescent Dosimeter(TLD)Results —VogtleElectricGeneratingPlant Vicinity . . . . . . . . . . . . . . 52

WSRGTR-98-00314SRSEnvkonmental Datafor1998 vjj

List of Tables

Table 19Radioactivity in Seepage Basin Water . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ...53

Table 20Radioactivity in SavannahRiverSite StreamWater . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 54

Table 21Radioactivity inSavannahRiverWater . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 62

Table 22Summary ofSavannahRiverSiteTritium Transport, 1960-1998 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 64

Table 23Radioactivity inDrinkingWater. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..65

Table 24Radioactivity inTerrestrialFoodProducts —Greens,Fruit, andBeef . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 75

Table 25Radioactivity inTerrestrialFoodProducts —Milk . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 77

Table 26Radioactivity in AquaticFoodProducts —FreshwaterFish . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 79

Table 27Radioactivity inAquaticFoodProducts —SaltwaterFish . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 98

Table 28Radioactivity inAquaticFoodProducts —Shellfish . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 99

Table 29Radioactivity inSoil . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100

Table 30Radioactivity inRiverandStream Sediment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 101

Table 31Radioactivity in GrassyVegetation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 109

Potential Radiation Doses

Table 32Meteorological Data . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 112

Table 3380-km-Radius (50-Mile)Population DistributionAroundSRS (1990Census) . . . . . . . . . . . . . . . . . . . . . . . . 119

Table 3480-km-Radius (50-Mile)Milk,Meat, and VegetationProductionAroundSRS asof1991 . . . . . . . . . . . . . . 120

Table 35AubomeReleaseLocations forMaximally ExposedIndividualDose . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 122

Table 36Parameters UsedforAdultConsumption Rates andforAtmosphericDoseCalculations . . . . . . . . . . . . . . . . 123

Table 37Site-SpecificParametersUsedwith CAP88CodeUsedforNESHAPS Calculations . . . . . . . . . . . . . . . . . . . 124

Table 38Parameters Used forAdultConsumption Rates andforLiquidDoseCalculations . . . . . . . . . . . . . . . . . . . . . 125

Table 39Site-SpecificParameters Usedin LiquidDoseCalculations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 126

Table 40CommittedDoseto theMaximallyExposed Individual fromAtmospheric Releases~~GASPCode-Uting Consmption of Cow Milk Patiway) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 127

Table 41Committed Dose to the Maximally Exposed Individual from Atmospheric Releases(MAXIGASP Code -Using Consumption of Goat Milk Pathway) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 128

Table 4280-km (50-Mile) CollectiveDosefrom AtmosphericReleases (POPGASPCode) . . . . . . . . . . . . . . . . . . . . 129

WSRGTR-98-00314...

Vlll SRSEnvironmental Data for7998–—

List of Tables

Table 43Total Site Airborne Releases and Maximally Exposed Individual Effective Dose Equivalentby Radionuclide (CAP88 Dose Calculations for 1998 NESHAP Report to EPA) . . . . . . . . . . . . . . . . . . . . . . 130

Table 44NESHAP Airborne-Dose Report Data — CAP88 Compared with MAXIGASP . . . . . . . . . . . . . . . . . . . . . . 132

Table 45NESHAP Airborne-Dose Report Data — CAP88 Comp,med with POPGASP . . . . . . . . . . . . . . . . . . . . . . . . 133

Table 46Committed Dose to Maximally Exposed Individual from Liquid Releases . . . . . . . . . . . . . . . . . . . . . . . . . . . 134

Table 47Committed Dose to Maximally Exposed Individual from Public Water Suppliesat Beaufort-Jasper Water Treatment Plant . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 135

Table 48Committed Dose to Maximally Exposed Individual from Public Water Supplies at the City of SavannahIndustrial and Domestic Water Supply Plant (near Port Wentworth, Georgia) . . . . . . . . . . . . . . . . . . . . . . . . 136

Table 49Collective Dose from Liquid Releases. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 137

Table 50Potential Doses from Irrigation Pathways . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 138

Table 51Dose from Consumption of Fish from New Savannah Bluff Lock and Dam, SRS Creek Mouths,and River Mile 120 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 139

Table 52Calculated Doses to Aquatic Biotafiom SRSReleases . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 141

Nonradiological Effluent Monitoring

Table 53Toxic Air Pollutant Emissions (1997) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 142

Table 54National Pollutant Discharge Elimination System Monitoring Data . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 146

Table 55National Pollutant Discharge Elimination System Toxicity Monitoring Data . . . . . . . . . . . . . . . . . . . . . . . . . 156

Table 56National Pollutant Discharge Elimination System Storrnwater Monitoring Data . . . . . . . . . . . . . . . . . . . . . . 157

Table 57National Pollutant Discharge Elimination System Land Application Monitoring Data . . . . . . . . . . . . . . . . . 175

Nonradiological Environmental Surveillance

Table 58Surface Water Surveillance — Inorganic Contaminants, Pesticides, and Herbicides . . . . . . . . . . . . . . . . . . . 178

Table 59Sediment Surveillance — Inorganic Contaminants, Pesticides, and Herbicides . . . . . . . . . . . . . . . . . . . . . . . 210

Table 60Fish Surveillance — Mercury . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ...212

Quality Assurance

Table 61Blind Sample Results forpHField Measurements . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ...215

Table 62Blind Sample Results for Trivium . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 216

Table 63QAPInterlaboratory Comparison of Analytical Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 217

WSRGTR-98-00314SRS Environmental Data for 1998 ix

List of Tables

Table 64QAD Interlaboratory Comparison of Analytical Results . . . . . . . . . . . . . .

Table 65Quarterly QAIQC Standards . . . . . . . . . . .

Table 66NPDES Duplicate Sample Results . . . . . .

Table 67NPDES Blind Sample Results . . . . . . . . . . . .

. . . . . . .

. . . . . . .

. . . . . . . .

. . . .

. . . .

. . . . .

. . . .

. . . .

. . . . .

. . . .

. . . . . . .

. . . . . . .

. . . . . . .

. . . . . . .

. . . .

. . . .

. . . . . . . . . . . . . . . . . . . . . . . . .

. . . . . . . . . . . . . . . . . . . . . . . . .-

. . . . . 222

. . . . . 224

. . . . . 226

. . . . . 230

Table 68SRSS~em and Savannti River Water Quali~Duplicate Sample ResulS . . . . . . . . . . . . . . . . . . . . . . . . . . 234

WSRGTR-98-00314x SRS Environmental Data for 1998

Radionuclide and ChemicalNomenclature

Nomenclature and Half-Life for Radionuclides

Radionuclide Symbol Half-Lifea!b Radionuclide Symbol Half-Lifea~b

Actinium-228

Americium-241

Americium-243

Antimony-124

Antimony-125

Barium-133

Beryllium-7

Bismuth-212

Bismuth-214

Carbon-14

Cerium-144

Cesium-134

Cesium-137

Cobalt-57

Cobalt-58

Cobalt-60

Curium-242

Curium-244

Curium-245

Europium-152

Europium-154

Europium-155

iodine-129

Iodine-131

Iodine-133

Krypton-85

Lead-212

Lead-214

Manganese-54

Neptunium-237

Neptunium-239

Nickel-59

Nickel-63

Niobium-95

AC-228

Am-241

Am-243

Sb-124

Sb-125

Ba-133

Be-7

Bi-212

Bi-214

C-14

Ce-144

CS-134

CS-137

co-57

Co-58

CO-60

Cm-242

Cm-244

Cm-245

Eu-152

Eu-154

Eu-155

I-129

1-131

I-133

Kr-85

Pb-212

Pb-214

Mn-54

Np-237

Np-239

Ni-59

Ni-63

Nb-95

6.15 h

432.7 y

7.37E3 y

60.2 d

2.758 y

10.53 y

53.28 d

2.14 m

19.9 m

5,730 y

284.6 d

2.065 y

30.17 y

271.8 d

70.88 d

5.271 y

162.8 d

18.1 y

8.5E3 y

13.48 y

8.59 y

4.71 y

1.57E7 y

8.04 d

8.040 d

10.73 y

10.64 h

27 m

312.2 d

2.14E6 y

2.35 d

7.6E4 y

looy

34.97 d

Plutonium-238

Plutonium-239

Plutonium-240

Plutonium-241

Piutonium-242

Potassium-40

Promethium-144

Promethium-147

Protactinium-231

Protactinium-234

Radium-226

Radium-228

Ruthenium-1 03

Ruthenium-106

Selenium-79

Socfium-22

Strontium-89

Strontium-90

Strontium-89,90

Technetium-99

Thallium-208

Thorium-228

Thorium-230

Thorium-232

Thorium-234

Tin-126

Tritium

Uranium-233

Uranium-234

Uranium-235

Uranium-236

Uranium-238

Zinc-65

Zirconium-95

Pu-238

Pu-239

Pu-240

Pu-241

Pu-242

K-40

Pm-144

Pm-147

Pa-231

Pa-234

Ra-226

Ra-228

Ru-103

Ru-106

Se-79

Na-22

Sr-89

Sr-90

Sr-89,90

Tc-99

TI-208

Th-228

Th-230

Th-232

Th-234

Sn-126

H-3

U-233

U-234

U-235

U-236

U-238

Zn-65

Zr-95

a h = hou~ d = da% y = yearb Reference: Chart of the Nuclides, 14th edition, revised to April 1988, GeneraI Electric Company

87.7 y

2.41 E4 y

6.56E3 y

14.4 y

3.75E5 y

1.28E09 y

360 d

2.6234 y

3.28E4 y

6.69 h

. 1.6E3 y

5.76 y

39.27 d

1.020 y

6.5E4 y

2.605 y

50.52 d

29.1 y

29.1 y

2.13E05 y

3.05 m

1.913y

7.54E4 y

1.4OE1Oy

24.10 d

lE5y

12.3 y

1.592E5 y

2.46E5 y

7.04E8 y

2.342E7 y

4.47E9 y

243.8 d

64.02 d

WSRGTR-98-00314SRS Environmental Data for 1998 xi

——

Radionuclide and Chemical Nomenclature

Nomenclature for Elements and Chemical Constituent Analyses

Constituent Symbol Constituent Symbol

Note: Some of the symbols listed in this table came from various databases used to format the data tables in thisbook and are included here to assist the reader in understanding the tables.

Aluminum.01

Ammonia

Ammonia as Nitrogen

Antimony

Arsenic

Barium

Biochemical Oxygen Demand

Benzene

Beryllium

Boron

Cadmium

Calcium

Calcium Carbonate

Carbon

Chemical Oxygen Demand

Chlorine

Chromium

Cobalt

Copper

Cyanide

Dissolved Oxygen

Fecal Coliform

Flow

Fluorine

Iron

Lead

Lithium

Magnesium

Manganese

Mercury

Nickel

Nitrogen

Nitrate as Nitrogen

Nitrite as Nitrogen

Nitrite, Nitrate

Oil and Grease

Oxygen

Ozone

Al (or AL)

NH3

NHrN (or AN)

Sb (or SB)

As (or AS)

Ba (or BA)

BOD

BEN

Be

B

Cd (or CD)

Ca

CaC03

c

COD

Cl (or CHL)

Cr (or CR)

co

Cu (or CU)

CN

DO

FEC

FLO

F

Fe (or FE)

Pb (or PB)

Li

Mg (or MG)

Mn (or MN)

Hg (or HG)

Ni (or Nl)

N

NO*N

NO.2-N

N02,N03

O&G

o

03

Particulate Matter <10 microns

Perclene

pH

Phenol

Phosphorus

Phosphate

Phosphate as Phosphorus

Polychlorinated Biphenyl

Potassium

Radium

Rhenium

Selenium

Silver

Sodium

Sulfate

Sulfur Dioxide

Temperature

Tetrachloroethylene(Perchloroethylene)

Trichloroethylene

1,1,1-Trichloroethane

Thallium

Tin

Total Dissolved Solids

Total Kjeldahl Nitrogen

Total Organic Carbon

Total Organic Halogens

Total Phosphates

Total Residual Chlorine

Total Solids

Total Suspended Solids

Total Volatile Solids

Uranium

Uranium(tested as a heavy metal)

Vanadium

Volatile Organic Compound

Zinc

PMIO

PERCL

PH

PHE

P

P04 (or P04-P)

Phosphate P

PCB

K

Ra

Re

Se (or SE)

Ag (or AG)

Na

S04 (or S04)

sop

TMP (or T orTEMP)

PERCL

TRICL

TCE

TI

SN

TDS

TKN

TOC

TOH

TP04 (or TotalPhos)

TRC

TS

TSS

TVs

u

U308

v

Voc

Zn

WSRC-TR-98-00314xii SRS Environmental Data for 1998

—

Sampling Locationand Other Abbreviations

Abbreviation Location Name/Other Applicable Information

4M

4MC

681-5G

A-1 4

AAP

ATTA

AUG L&D

ALLEN

BARN

BDC

BG

BGN

BGS

CSWTF

DARK H

E TAL

FM

FMC

GR PND

HP

IBG

IGB

JACK

L3R

LSB

LTR

PB

PAIT MR

PMR

PSB

RM

SATA

SAV 1

SAV 2

Sc

TB

TC

TCR

TNX

Four Mile

Four Mile Creek

Georgia Department of Natural Resources/Environmental Monitoring Section sampling site

Road A–14

Aiken Airport

Advanced Tactical Training Area

Augusta Lock and Dam

Allendale Gate

Barnwell Gate

Beaver Dam Creek

Burial Ground

Burial Ground North

Burial Ground South

Central Sanitary Wastewater Treatment Facility

Dark Horse

East Talatha

Four Mile

Four Mile Creek (Fourmile Branch)

Green Pond

HP (sampling location designation only; not an actual abbreviation)

Indian Burial Ground

Indian Grave Branch

Jackson

Lower Three Runs

L-Area Seepage Basin

Lower Three Runs

Pen Branch

Patterson Mill Road

Patterson Mill Road

P-Area Seepage Basin

River Mile

Small Arms Training Area (pistol range)

Savannah 1

Savannah 2

Steel Creek

Tires Branch

Tinker Creek

Tabernacle Church Road

Multipurpose Pilot Plant Campus

—.—. .. ——- ..- .—

Sampling Location and Other Abbreviations

Abbreviation Location Name/Other Applicable Information, continued

U3R Upper Three Runs

UTR Upper Three Runs

WIND Windsor Road

W JACK West Jackson

Sample Locations Known By More Than One Abbreviation

Beaver Dam Creek 400-D

Four Mile Creek+ FM-6; 4MC-6; Four Mile Creek at Leigh Road

Four Mile Creek at Road A7; FM-A7; 4M–A7

Lower Three Runs–2; L3R–2; L3R Creek and Patterson Mill

River Mile-O/8 Savannah River Mouth; Highway 17A Bridge Area; RM-O/8

River Mile 120; RM–120; River 10; R-1 O

River Mile 140; RM–140; R-6A

River Mile 160; RM-1 60; River 2; R–2

Steel Creek-4; SC-4; Steel Creek-4 at Road ~ SC and Highway 125

Tinker Creek at Kennedy Pond; TC/KP; TC–1

Upper Three Runs-4 at Road A; U3R+ U3R–Rd A

Vogtle Discharge; River 3B; R-3B

Other Abbreviations Used in This Book

Activity Median Aerodynamic Diameter

Derived Concentration Guide

Department of Energy

Duplicate

Department of Energy’s Environmental Measurements Laboratory

Effluent Treatment Facility

Georgia Power

Minimum Detectable Activity

Minimum Detectable Concentration

Minimum Detectable Limit

MNion Gallons Per Day

No Flow

Nuclear Regulatory Commission

Operations Recreation Association

“P and R“ Pond

Receiving Basin for Offsite Fuel

Replicate

Railroad Yard

Savannah River Technology Center

Standard Units

Solid Waste Disposal Facility

Toxicity Characteristic Leaching Procedure

Thermoluminescent Dosimeter

AMAD

DCG

DOE

Dup, DUP

EML

ETF

GP

MDA

MDC

MDL

MGD

NF

NRC

ORA

PAR

RBOF

Rep, REP

RR

SRTC

Su

SWDF

TCLP

TLD

WSRGTR-98-00314xiv SRS Environmental Data for 1998

.

Units of Measure, Scientific Notation,and Conversion Tables

Units of Measure Units of Measure

;ymbol Name Symbol Name

Temperature Concentration

“c degrees Centigrade ppb parts per billion

“F degrees Fahrenheit ppm parts per million

17me

d day Rate

h hour Cfs cubic feet per second

Y year gpm gallons per minute

!ength

cm centimeter Conductivity

ft foot pmho micromho

in. inch

km kilometer

m meter Radioactivity

mm millimeter Ci curie

Urn micrometer cpm counts per minute

mCi I- millicurie

Vass pci microcurie

9 gram pCi picocurie

kg kilogram Bq becquerel

mg milligram

V9 microgram Radiation Dose

mrad millirad

qrea mrem millirem

mi2 square mile Sv sievert

fi2 square foot mSv millisievert

psv microsievert

Volume R roentgen

gal gallon mR milliroentgen

L liter VR microroentgen

mL milliliter Gy gray

—

Units of Measure, Scientific Notation, and Conversion Tables

Fractions and Multiples of Units

MultipleReport

Decimal Equivalent Prefix Symbol Format106 1,000,000 mega- M E+06

103 1,000 kilo- k E+031(32 100 hecto- h E+02

10 10 deka- da E+O11()-1 0.1 deci- d E-011(3-2 0.01 centi- C E-0210-3 0.001 milli- m E-031()-6 0.000001 micro- IJ E-061()-9 0.000000001 nano- n E-091()-12 0.000000000001 pico- P E–1210-15 0.000000000000001 femto- f E-1 51o-18 r-.ormoooooooormollll-ll attcl- a E–18

I Conversion Table (Units of Radiation Measure) ICurrent System Systdme International Conversion

curie (Ci) becquerel (Bq) 1 Ci = 3.7x1 OIOBq

rad (radiation absorbed dose) gray (Gy) 1 rad = 0.01 Gy

rem (roentgen equivalent man) sievert (Sv) 1 rem= 0.01 Sv

I Conversion Table

Multiply By To Obtain

in.

ft

mi

lb

Iiq qt-U.S.ft2

mi2

ft3

dim

pcl

pCi/L (water)nCi/m3 (air)

2.54

0.305

1.61

0.4536

0.946

0.093

2.59

0.028

0.4501@

10-9

j 0-12

cm

m

km

kg

LM2

km2

M3

pCi

J.lcl

~Ci/mL (water)uCi/ml (air)

Multiply By To Obtain

cm 0.394 in.

m 3.28 ft

km 0.621 mi

kg 2.205 lb

L 1.057 Iiq qt-U.S.M2 10.764 ft2

km2 0.386 f-ni2

M3 35.31 ft3

pCi 2.22 cllm

J.lci 106 pCi

UCi/mL (water) 1(39 pCi/L (water)

UCdmL (air) 1012 pCi/m3 (air)

WSRGTR-98-00314xvi SRS Environmental Dafa for 1998

Sampling Locations

Windsor Road

Georgia

1 5 Miles-

A Radiological AirSurveillance Location

O Discontinued in1998

EPDIGISMap

Figure 1 Radiological Sampling Locations — Air Surveillance

WSRGTR-98-00314SRS Environmental Data for 1998 xvii

Sampling Locations

adiological Surface Water~mpling Location

0 EffluentA Surveillance

\

TRM-120

., 1 .

EPD/GISMap

Figure 2 Radiological Sampling Locations — Surface Water (SRS Stream and Savannah RiverWater)

WSRGTR-98-00314...Xvlli SRS Environmental Data for 1998

Sampling Locations

z

+-

+

I

m

WSRC-TR-98-00314SRS Environmental Data for 1998 xix

Sampling Locations

as

WSRGTR-98-00374xx SRS Environmental Data for 1998

Sampling Locations

+-&R

SouthCarolina

GeorgiaRM-134

1 5 Miles- 1

RM-129

N

~A Radiological Sediment Sampling Location

+US 301 Bridge

EPD/GISMap

Figure 5 Radiological Sampling Locations — Sediment

Sampling Locations

z

-+

n

3’

c0.-G50)s’Ifnc0.-%03

WSRGTR-98-00374xxii SRS Environmental Data for 1998

Sampling Locations

\r--l

/px”

coIlln

2+

I

xz1-

r-

WSRGTR-98-00314SRS Environmental Data for 1998

...XXII

Sampling Locations

‘n

Vogtle Discharge

RM-140%

Georgia ‘“b

1 6 Miles-

YRM-129

fi-

7A Nonradiological Surface Water Sampling Location RM-120

EPD/GISMap

Figure 8 Nonradiological Sampling Locations — Surface Water (SRS Stream andSavannah River Water)

wsRGTR-9&oo314xxiv SRS Environmental Data for 1998

Sampling Locations

SRS Water Systems—---- -a

● Small System

Large System

+ Elevated Storage Tank Y N

o Water Treatment Plant1 5 Miles

* Backup Water Treatment Plant-

+— Transmission Pipe I I

A-Area DrinkingWaterTreatmentFacility782-3A

A;~5e:7~duction Wells

9051125B

A-Area Perimeter Wells905-82A

7

905-112Gi’:-jqgx , .,

A

~“ ‘)

[UI-4U

905-113G. .

,..M

.(-“. ,,. ./

> ,’Jac

?

e

BstT” adeo ‘., .’701- G “-., .;

F‘B’

oad2 , , / .. ~“z-; z

I D-Area/TNX productionwetk I ~ Iw---”- m J“”””””, , ,. ”,,”

905-95K

905-3D905-136D

1 Georoia %

WSRGTR-98-00314SRS Environmental Data for 1998 xxv

EPD/GISMap

Figure 9 Drinking Water Systems

Sampling Locations

1-!!65’.’%..

Georgia

1 6 Miles~

A Nonradiological Sediment Sampling Location{+

RM-120

EPD/GISMapFigure 10 Nonradiological Sampling Locations — SRS Stream and Savannah RiverSediment

WSRC-TR-98-00314xxvi SRS Environmental Data for 1998

Sampling

Table 1Sample Media Information

Page 1 of 4

Matrix Analytical Parameter Rewesentative Aliauot a

Surveillance Air

On site Gamma

Gross alpha

Gross beta

Tritium

Strontium-89,90

Plutonium-238,239

Site perimeter

25-mile radius

Gamma

Gross alpha

Gross beta

Tritium

Strontium-89,90

Plutonium-238,239

Gamma

Gross alpha

Gross beta

Tritium

Strontium-89,90

Plutonium-238,239

100-miIeradius Gamma

Gross alpha

Gross beta

Tritium

Strontium-89,90

Plutonium-238,239

3000 m3/746 m3

746 m3

746 m3

3 m3

1500 m3 (1/2 sample)/746 m3

1500 m3 (1/2 sample)/746 m3

10000 m3/746 m3

746 m3

746 m3

3 m3

5000 m3 (1/2 sample)/746 m3

5000 m3 (1/2 sample)/746 m3

746 m3

746 m3

746 m3

3 m3

373 m3 (1/2 sample)/746 m3

373 m3 (1/2 sample)/746 m3

746 m3

746 m3

746 m3

3 m3

373 m3 (1/2 sample)/746 m3

373 m3 (1/2 sample)/746 m3

a EMS air surveillance program analytical protocols for gamma, strontium-89,90, and plutonium-238,239 were changed to746 m3 in April 1998.

Sampling

Table 1

Sample Media Information

Page 2 of 4

Matrix Analytical Parameter Representative Aliquot

Effluent Water

Gamma IL

Gross alpha lL

Gross beta lL

Tritium 5 mL

Strontium-89,90 IL

Actinides lL

Stream Water

Gamma lL

Gross alpha lL

Gross beta lL

Tritium 5 mL

Strontium-89,90 1–3 L

Actinides lL

River Water

Gamma 5L

Gross alpha lL

Gross beta lL

Tritium 5 mL

Strontium-89,90 lL

Plutonium 238,239 IL

Drinking Water

Gamma

Gross alpha

Gross beta

Tritium

Strontium-89,90

Actinides

Groundwater

Total activity

Wet/Dry Deposition (Rainwater)

Gamma

Gross alpha

lL

IL

lL

5 mL

IL

IL

5 mL

0.37 m2

0.093 m2 (1/4 sample)

WSRC-7-R-98-003742 SRS Environmental Data for 1998

Sampling


Page 3 of 4


Wet/Dry Deposition (Rainwater), cont.

Gross beta 0.093 m2 (1/4 sample)

Tritium 5 mL

Strontium-89,90 0.031 m2 (1/12 sample)

Plutonium 238,239 0.031 m2 (1/12 sample)

Soil

Gamma 650 g

Gross alpha 0.1 g

Gross beta 0.1 g

Strontium-89,90 20 g

Plutonium-238,239 log

Sediment

Gamma 650 g

Gross alpha 0.1 g

Gross beta 0.1 g



Vegetation

Gamma 200 g

Gross alpha 0.5 g

Gross beta 0.5 g

Tritium 5 mL

Strontium-89,90 5g


Actinides log

Fish

Edible Gamma 200 g

Gross alpha 1.5g

Gross beta 1.5g

Tritium 5 mL


Plutonium-238,239 200 g

WSRGTR-98-00314SRS Environmental Data for 1998 3

Sampling


Page 4 of 4


Fish, cont.

Nonedible Gamma 200 g

Gross alpha 0.5 g

Gross beta 0.5 g


Deer/Hogs

Muscle

Bone

Oysters/Crabs

Gamma 200 g

Gross alpha 1.5g

Gross beta 1.5g

Tritium 5 mL

Strontium-89,90 loog

Plutonium-238,239 Ioog

Gamma 200 g

Strontium-89,90 Ioog

Strontium-89,90 Ig

Gamma 200 g

Gross alpha 0.5 g

Gross beta 0.5 g

Strontium-89,90 Ioog

Gamma 1000 g


Tritium 5 mL

Plutonium-238,239 Ioog

Milk

Gamma lL

Tritium 5 mL

Strontium-90 500 mL

WSRGTR-98-003144 SRS Environmental Data for 1998

Sampling

Table 2Representative Minimum Detectable Concentrations for Radiological Analyses

Page 1 of 6

Note: The minimum detectable concentrations (MDCS) are calculated at the 95-percent confidence level usinginstrument background measurements and typical detector efficiencies, decay times, and countingintervals. Chemical recoveries and air filter collection efficiencies are assumed to be 100 percent, exceptfor Pu, U, Am, and Cm species for which typical chemical recoveries are used. Sample sizes are given intable 1, “Sample Media Information.” The MDCS for actual samples maybe different because of variationsin the sample preparation, size, and content, and because of variations in the chemical recoveries,counting efficiencies, reagent blanks, decay time, counting time, and instrument backgrounds.

Onsite AiF Site Perimeter Ai@ 25-Mile Radius AW Savannah AW

Nuclide pCi/m3 pCi/m3 pCi/m3 pCi/m3

4.90E+01 4.90E+01H-3

Be-7

K-40

Co-58

CO-60

Ru-103

Ru-106

I-131

CS-134

CS-137

Cc-l 41

Ce-144

Sr-89,90

Sr-90

U-234

U-235

U-238

Pu-238

Pu-239

Am-241

Cm-244

Gross alpha

Gross beta

Total activity

1.40E-02/5.63E-02

3.50E-02/l .41E-01

2.60E-03/l.05E-02

2.60 E-03/l .05E-02

2.50 E-03/l .01E-02

2.20E-02/8.85E-02

4.1OE-03/l .65E-02

2.10E-03/8.44E--03

2.00E-03/8.04E-03

2.90 E-03/l .17E-02

8.10E-03/3.26E-02

9.20 E-04/l .85E-03

1.39E-05/2.79E-05

1.40E-05/2.82E-05

1.1OE-O3

1.90E-03

4.30E-03/5.76E-02

1.00E-02/l .34E-01

7.70E-04/l .03E-02

8.00E-04/l .07E-02

7.60E-04/l .02E-02

6.50E-03/8.71 E-02

1.20E-03/l .61E-02

6.30E-0418.45E-03

6.10E-04/8.l 8E-03

8.60E-04/l.15E-02

- 2.40E-03/3.22E-02

2.80E-04/l .85E-03

4.17E-06/2.79E-05

4.20E-06/2.82E-05

1.1OE-O3

1.90E-03

4.90E+01

5.70E-02

1.40E-01

1.00E--O2

1.1OE-O2

1.00E-02

8.80E-02

1.60E-02

8.40E-03

8.20E-03

1.20E-02

3.30E-02

3.70E-03/l .85E-03

5.59 E-0512.79E-05

5.63E-05/2.82E-05

1.1OE-O3

1.90E-03

4.90E+01

5.70E-02

1.40E-01

1.00E-02

1.1OE-O2

1.00E-02

8.80E-02

1.60E-02

8.40E-C13

8.20E-03

1.20E-02

3.30E-02

3.70E-03/l .85E-C13

5.59 E-0512.79E-05

5.63 E-05/2.82E-05

1.1OE-O3

1.90E-03

a EMS air surveillance program analytical protocols for gamma, strontium-89,90, and plutonium-238,239 were changed to746 m3 in April 1998.

WSRC-TR-98-00374SRS Environmental Data for 1998 5

Sampling


Page 2 of 6

Stream/EffluentRainwate@ Water River Water

Nuclide pCiim2 pcii pcfi

H-3 1.23E+03 1.20E-I-03 4.40E+02

Be-7 1.70E+02 4.70E+01 1.1OE+O1

K-40 4.1OE+O2 1.30E+01 2.50E+01

Co-58 3.00E+O1 7.40E+O0 1.20E+O0

CO-60 3.20E+01 9.1OE+OO 1.90E+O0

Ru-103 2.80E+01 6.70E+O0 1.30E+O0

RU-106 2.80E+02 5.90E+01 1.1OE+O1

1-131 7.20E+01 1.60E+01 2.30E+O0

CS-134 2.70E+01 5.80E+O0 1.30E+O0

CS-137 2.60E+01 7.1OE+OO 1.40E+O0

Ce-141 3.60E+01 8.50E+O0 1.50E+O0

Cc-l 44 1.30E+02 2.90E+01 5.90E+O0

Sr-89,90 4.50E+01 1.40E+OOb 1.40E+O0

Sr-90

U-234 2.80E-02

U-235 1.00E-02

U-238 4.60E-02

Pu-238 6.40E-01 8.56E-03

Pu-239 6.80E-01 8.00E-03

Am-241 8.87E-03

Cm-244 7.80E-03

Gross alpha 8.60E+O0 8.00E-01

Gross beta 1.50E+01 1.40E+O0

Total activity

a Values, except for tritium, reflect wetldry deposition.b The SR-89,90value is feral-liter sample.

1.92E-02

2.1OE-O2

8.00E-01

1.40E+O0


Sampling


Page 3 of 6

Groundwater Drinking Water Soil/Sediment Vegetation

Nuclide pc”w pCilL pcilg pcdg

H-3 4.40E+02 1.80E-01

Be-7 4.70E+01 3.40E-01 4.20E-01

K-40 1.30E+01 5.50E-01 1.40E+O0

Co-58 7.40E+O0 4.40E-02 5.50E-02

CO-60 9.1OE+OO 4.70E-02 5.70E-02

Ru-103 6.70E+O0 5.00E-02 5.00E-02

RU-106 5.90E+01 3.20E-01 4.50E-01

I-131 1.60E+01 8.00E-02 8.80E-02

CS-134 5.80E+O0 3.80E-02 4.40E-02

CS-137 7.1OE+OO 4.20E-02 4.90E-02

Ce-141 8.50E+O0 7.80E-02 8.40E-02

Ce-144 2.90E+01 3.00E-01 3.40E-01

Sr-89,90 1.40E+O0 7.20E-02 1.40E-02

Sr-90

U-234 2.60E-03

U-235 1.00E-03

U-238 4.60E-03

Pu-238 4.00E-03

Pu-239 4.20E-03

Am-241 8.90E-04

Cm-244 7.80E-04

Gross alpha 1.60E+O0

Gross beta 2.90E+O0

Total activity 2.30E+03

8.00E-01

1.40E+O0

1.96E-03

1.90E-03

8.00E+OO

1.40E+01

Sampling

Table 2

Representative Minimum Detectable Concentrations for Radiological Analyses

Page 4 of 6

Highway 301 Fish River Mouth Fish Onsite Fish Panfish

Nuclide pcilg pcilg pcdg pcilg

H-3 5.72E-02 5.72E-02 5.72E-02 5.72E-02

Be-7 7.20E-01 1.50E+O0 5.00E-01

K-40 3.50E-01 9.30E-01 6.70E-01

Co-58 5.50E-02 1.1OE-O1 7.40E-02

CO-60 2.40E-02 4.60E-02 5.20E-02

Ru-103 1.40E-01 3.00E-01 1.00E-01

Ru-106 2.1OE-O1 4.20E-01 4.90E-01

1-131 6.80E+O0

CS-134 2.20E-02 3.80E-02 4.50E-02

CS-137 2.1OE-O2 4.00E-02 4.20E-02

Ce-141 3.80E41 7.1OE-O1 1.60E-01

Ce-144 1.70E-01 3.70E-01 2.30E-01

Sr-89,90 7.20E-03

Sr-90

U-234

U-235

U-238

Pu-238

Pu-239

1.00E-04

1.00E-04

1.00E-04

1.00E-04

1.00E-04

1.00E-04

2.00E-04

2.1OE-O4

Am-241

Cm-244

Gross alpha

Gross beta

Total activity

9.54E-01

1.83E-01

5.30E-01

9.5E-01

WSRC-TR-98-003148 SRS Environmental Data for 1998


Page 5 of 6

5.60E-02

1.60E+O0

2.90E+O0

Nonedible Fish Oysters/Crabs Food Products Milk

Nuclide pcilg pcdg pcijg pc~

H-3 1.80E-01 4.40E+02

Be-7 5.00E-01 2.30E-01 1.80E+01

K-40 6.70E-01 1.20E-01 4.30E+01

Co-58 7.40E-02 2.1OE-O2 2.50E+O0

CO-60 5.20E-02 7.50E-03 2.80E+O0

Ru-103 1.00E-01 5.00E-02 2.40E+O0

Ru-106 4.90E-01 7.20E-02 2.30E+01

I-131 6.80E+O0 2.90E+O0

Cs-134 4.50E-02 7.30E-03 2.40E+O0

Cs-137 4.20E-02 7.20E-03 2.70E+O0

Ce-141 1.60E-01 9.80EW2 2.80E+O0

Ce-144 2.30E-01 4.00E-02 1.20E+01

Sr-89,90 1.40E-02 7.20E-02

Sr-90 5.80E+O0

U-234

U-235

U-238

Pu-238

Pu-239

Am-241

Cm-244

Gross alpha

Gross beta

Total activity

1.60E+O0

2.90E+O0

2.00E-04

2.1OE-O4

4.40E-01

2.90E-03

WSRC-TR-98-00314SRS Envkonmental Data for 1998 9

Sampling


Page 6 of 6

Deer Muscle Deer Bone

Nuclide pcilg pcilg

H-3

Be-7

K-40

Co-58

CO-60

Ru-103

Ru-106

I-131

CS-134

CS-137

Ce-141

Cc-l 44

Sr-89,90

Sr-90

U-234

U-235

U-238

Pu-238

Pu-239

Am-241

Cm-244

Gross alpha

Gross beta

Total activity

5.00E-01

6.70E-01

7.40E-02

5.20E-02

1.00E-01

4.90EA1

6.80E+O0

4.50E-02

4.20E-02

1.60E-r)l

2.30E-01

1.40E-02 1.40E+O0

WSRGTR–98-0031410 SRS Environmental Data for 1998

--

Sampling

Table 3Nonradiological Environmental Surveillance Detection/Report Limits

Page 1 of 2

.

Report ValueParameter Units Quantitation Value Round to the nearest:

Note: ‘(NA”denotes ‘hot applicable.”

Field Measurements

Temperature “c NA 0.1

pH Su NA 0.1

Dissolved oxygen (DO) mg/L 1.0 0.1

General Water Quality Parameters

Conductivity

Chemical oxygen demand(COD)

Mercury in fish flesh

Suspended solids (TSS)

Nitrogen-Nitrate (N03-N)

Nitrogen-Nitrite (N02-N)

Ortho-Phosphate-P (0-P04-P)

Total organic carbon(TOC)

Metals

Aluminum (Al)

Cadmium (Cd)

Calcium (Ca)

Chromium (Cr)

Copper (Cu)

Iron (Fe)

Lead (Pb)

Magnesium (Mg)

Manganese (Mn)

Mercury (Hg)

Nickel (Ni)

Silver (Ag)

Sodium (Na)

Zinc (Zn)

Pesticides

Aldrin

Alpha-BHC

Beta-BHC

Umhos/cm

mg/L

pglg

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

pglL

pglL

pg/L

NA

20

0.33

3

0.05

0.02

0.01

1.0

0.05

0.002

0.05

0.005

0.005

0.02

0.003

0.03

0.01

0.0001

0.01

0.005

0.09

0.005

0.05

0.05

0.05

1

1

0.01

1

0.01

0.01

0.001

0.1

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.0001

0.001

0.001

0.001

0.001

0.001

0.001

0.001


..

Sampling

Table 3Nonradiological Environmental Surveillance Detection/Report Limits

Page 2 of 2

Report ValueParameter Units Quantitation Value Round to the nearest:

Pesticides (cont.)

Delta-BHC

Lindane (gamma-BHC)

Chlordane

4,4-DDD

4,4-DDE

4,4-DDT

Dieldnn

Endosulfan 1

Endosulfan II

Endosulfan sulfate

Endrin

Endrin aldehyde

Heptachlor

Heptachlor epoxide

Methoxyclor

Toxaphene

Herbicides

2,4-D

2,4,5-TP (Silvex)

Volatile Organic Compounds

Tetrachloroethene

111-Trichloroethane

Trichloroethene

Vinyl Chloride

1,2-cis-Dichloroethylene

pgL

pg/L

pglL

pgIL

pg/L

pglL

pg/L

pglL

pglL

pg/L

pg/L

pglL

pg/L

pglL

pg/L

pglL

pg/L

pglL

pglL

pglL

pglL

pglL

pglL

0.05

0.05

0.5

0.05

0.05

0.05

0.05

0.05

0.05

0.05

0.05

0.05

0.05

0.05

0.20

2.50

0.10

0.10

2.0

2.0

2.0

2.0

2.0

0.001

0.001

0.10

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.001

0.01

0.10

0.01

0.01

0.1

0.1

0.1

0.1

0.1


—. .—


Table 4

Radioactive Atmospheric Releases by Source

Page 1 of 3

Curiesa

Radio- y::$- Reactor Heavy Diffuse andnuciide Reactors “ Materials Water SRTCC Fugitived Total

Note: Blank spaces indicate no quantifiable activity

GASES AND VAPORS

H-3(oxide) 2.28E+04 3.45E+04 4.04E+02 9.31 E+02

H-3(elem.) 2.41 E+04

H–3 Total

c-1 4

Kr-85

Xc-l 35

I-129

l–l 31

1-133

Na-22

Cr-51

Fe-55

co-57

Co-58

CO-60

Ni-59

Ni-63

Zn-65

S*79

2.28E+04 5.86E+04 4.04E+02

7.01 E-02

1.70E+04

4.95E-02

1.25E-02

5.92E-05 8.29E-06

1.59E-04

PARTICUiATES

2.65E-07

9.31 E+02

9.68E-05

1.29E-05

7.76E-11

1.21E-04

3.90E-04

9.40E–11

1.27E-04

1.38E-04

8.33E-13

8.21 E-06

2.23E-05

1.85E-11

Sr-89,90ejf 1.62E-03 3.22E-04 5.05E-04 2.61 E-04 2.66E-05 2.58E-02

Zr-95 1.71E-05

Nb-95 1.13E-04

Tc-99 2.82E-05

Ru-103 2.26E-05

Ru-106 2.26E-05

Sri-l 26 1.29E-13

1.08E-05

a One curie equals 3.7 E+IO Becquerels.b Includes separations, waste management, and tritium facilitiesc Savannah River Technology Centerd Estimated releases from minor unmonitored diffuse and fugitive sources

Includes unidentified beta emissions; Includes Sr-89

5.86E+04

2.41E+04

8.27E+04

7.02E-02

1.70E+04

4.95E-02

1.25E-02

6.75E-05

1.59E-04

7.76E-11

1.21E-04

3.90E-04

9.40E-11

1.27E-04

1.38E-04

8.33E–13

8.21E-06

2.23E-05

1.85E-11

2.85E-02

1.71E-05

1.13E-04

2.82E-05

2.26E-05

3.34E-05

1.29E–13


..-


Table 4

Radioactive Atmospheric Releases by Source

Page 2 of 3

Curiesa

Radio- Separa- Reactor Heavy Diffuse andnuclide Reactors tionsb Materials Water SRTCC Fugitived Total

St)-l 25 5.27E-05.---.-

Cs-134

Cs-137

Cc-l 41

C*144

Pm-l 47

Eu-152

Eu-154

Eu-155

Ra–226

Ra–228

Th–228

Th–230

Th–232

Pa–231

U–232

U–233

U–234

U-235

U–236

U–238

Np-237

Pu-238

Pu-239e

Pu-240

Pu-241

Pu-242

ANI-241

AM-243

CM-242

1.79E-07

2.32E-07

3.50E-05 3.77E-04

2.62E-05

1.57E-06

6.92E-05

1.15E-04

2.19E-04 1.12E-04

3.31 E-05

1.20E-06

3.39E-05

6.21E-06

6.32E-05

4.76E-08

5.09E-05

2.17E-08

1.31E-04

2.30E-06 4.89E-03

4.16E-05

1.45E-04

9.79E–10

4.19E-08

5.74E-06

1.1OE-O6

8.64E-06

2.13E-05

9.44E-06

1.02E-05

7.51 E-07

1.00E-09

2.35E-06

1.83E-05

2.1OE-O6

2.39E-09

5.12E-05

1.01E-09

3.28E-04

2.98E-05 6.71E-06 1.41E-03

1.12E-06

6.02E-05

1.59E-07

5.75E-06

a One curie equals 3.7 E+1OBecquerels.b Includes separations, waste management, and tritium facilitiesc Savannah River Technology Centerd Estimated releases from minor unmonitored diffuse and fugitive sourcese Includes unidentified alpha emissions

1.89E-05

1.58E-07

5.zYt-u51

1.31E-04

5.30E-03

4.16E-05

1.45E-04

9.79E–10

4.19E-08

5.74E-06

1.1OE-O6

8.64E-06

2.13E-05

9.44E-06

1.02E-05

7.51E-07

1.00E-09

1.20E-06

2.35E-06

7.84E-05

9.88E-06

2.39E-09

1.84E-04

1.01E-09

4.43E-04

1.83E-03

1.12E-06

6.02E-05

1.59E-07

3.89E-05

1.89E-05

1.58E-07


——


Table 4Radioactive Atmospheric Releases by Source

Page 3 of 3

Curiesa

Radio- se::$- Reactor Heavy Diffuse andnuclide Reactors “ Materials Water SRTCC Fuaitived Total

Cm-244 3.67E-06 4.90E+9 1.30E-04 1.34E-04

Cm-245 2.08E–13 2.08E-13

Cm-246 9.37E-07 9.37E-07

cf-249 5.27E–16 5.27E-16

cf-251 2.17E-14 2.17E–14

a One curie equals 3.7 E+1OBecquerels.b Includes separations, waste management, and tritium facilitiesc Savannah River Technology Centerd Estimated releases from minor unmonitored diffuse and fugitive sources


.


Table 5Radioactive Atmospheric Releases by Stack/Facility and Comparisonof Annual Average Concentrations to DOE Derived Concentration Guides

Page 1 of 8

AverageQuantity EffluentReleased Atmospheric Concentration

During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (vCi) Volume (mL) (pCtimL) (pCf/mL)


A-Area (Savannah River Technology Center)

735-A

773-A B

773-A C

773-A Sandfilter CO-60 2.65E-01 9.32E+14 2.84E–16 8.OE–11Discharge

I–131 8.17E+O0 9.32E+14 8.77E–15 4.OE–1O

[–133 1.59E+02 9.32E+14 1.71E–13 2.OE-09

776-A Stack [–131 1.17E-01 1.75E+14 6.69E–16 4.OE–10

Cs-137 2.30E+O0 1.75E+14 1.31E–14 4.OE–1O

C-Area (C-Reactor)

728-N

105-C Crane Maint. Cs–137 5.36E-02 1.81E+13 2.96E-15 4.OE-1 ODec Exhaust

105-C Stack DeconExhaustNo ‘AG

Port. C02 Blast. DeconExhaustNo ‘AG

C-Area Main Stack H–3(oxide) 3.56E+08 9.02E+14 3.95E-07b 1.OE-07(148ft)

D-Area (Heavy Water Rework)

420-D Stack H–3(oxide) 3.47E+08 2.37E+14 1.47E-06b 1.OE-07

421–2D Stack H–3(oxide) 1.33E+07 1.57E+14 8.49E-08 1.OE-07

772–D Stack H–3(oxide) 4.37E+07 2.70E+14 1.62E-07b 1.OE-07

F-Area (Separations and Waste Management)

235-F Sandfilter U–234 5.47E-01 5.53E+14 9.89E–16 9.OE–14Discharge

U-235 2.77E-02 5.53E+14 5.OIE–17 1.OE–13

U–238 5.62E-01 5.53E+14 1.02E-1 5 1.OE-13

a Source DOE Order 5400.5. In cases where different chemical forms have different DCGS,the lowest DCG for theracfionuclide is given. These DCGSare defined as the air concentration of that radionuclide that will give a 50-year committedeffective dose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values onlyand are not considered release limits or standards.

b Exceeds DCG

WSRGTR-98-O031416 SRS Environmental Data for 1998



Page 2 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (WCi) Volume (mL) (pCf/mL) (pCUmL)

1.08E~2 5.53E+14 1.95E-17 2.OE-14

241-F MiscellaneousExhaust

241-F Purge Exhaust

241-F Tank AnnulusExhaust

291-F Stackb

6.1D

6.4D

772-1 F

772-4F

Pu-239

Am–241

Cm-244

Cs-137

Cs–137

Cs-137

Sr-89,90

1-131

X*1 35

Cs–137

U-234

U-235

U-238

Pu–238

Pu-239

Am-241

Cm-244

Ru–106

Cs-137

Arn-241

RU-106

SIJ-125

Cs-137

Am-241

U–234

1.87E-02

1.21E-02

4.99E-01

1.69E+01

5.52E+O0

3.78E+01

9.27E+O0

4.95E+04

4.04E+01

1.04E+01

1.28E+O0

2.97E+01

3.54E+O0

5.18E+01

5.02E+O0

1.79E+O0

5.08E-01

6.79E+O0

3.13E-01

1.03E+01

1.79E-01

1.26E+O0

2.05E+01

4.38E-02

5.53E+14

5.53E+14

2.38E+13

4.53E+13

2.06E+14

3.31E+15

3.31E+l 5

3.31E+l 5

3.31 E+l 5

3.31 E+15

3.31E+15

3.31 E+l 5

3.31E+15

3.31E+15

3.31E+l 5

3.31 E+l 5

8.20E+12

8.20E+12

8.20E+12

2.25E+12

2.25E+12

2.25E+12

2.25E+12

2.23E+15

3.38E–17

2.19E-17

2.1OE-14

3.73E–13

2.68E-14

1.14E-14

2.80E–15

1.50E-11

1.22E–14

3.13E-15

3.87E-16

8.96E–15

1.07E-1 5

1.56E-14

1.51E-15

5.39E-16

6.20E-14

8.28E–13

3.82E-14C

4.58E-12

7.96E-14

5.60E-13

9.11E–12C

1.96E-17

2.OE-14

4.OE-14

4.OE-1 O

4.OE-1 O

4.00E-1 O

9.OE-12

4.OE-1 O

8.OE-08

4.OE-1 O

9.OE–14

1.OE–13

1.OE-13

3.OE–14

2.OE-14

2.OE–14

4.OE–14

3.OE–11

4.OE-1 O

2.OE-14

3.OE-11

1.OE-09

4.OE-1 O

2.OE-14

9.OE–14

a Source DOE Order 5400.5. In cases where different chemical forms have different DCGS,the lowest DCG for theradionuclide is ciiven.These DCGSare defined as the air concentration of that radionuclide that will give a 50-year committedeffective dose ~quivalent of 100 mrem under conditions of continuous exposure for one year. DCGsare reference values onlyand are not considered release limits or standards.

b Includes data from both isokinetic and charcoal sampling systemsc Exceeds DCG




Page 3 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (pci) Volume (mL) (pCi/mL) (~Ci/mL)

U–238 8.08E-02 2.23E+15 3.62E–17 1.OE-13

Pu–238 2.25E-03 2.23E+I 5 1.OIE-18 3.OE–14

Pu–239 9.82E-03 2.23E+15 4.40E–18 2. OE–14

Am–241 6.19E-03 2.23E+15 2.78E–18 2.OE-14

800 Cell Stack Exhaust Sr-89,90 2.00E+OO 8.92E+13 2.24E-14(21l-F)

9.OE–12

Cs–137 3.12E+O0 8.92E+13 3.49E-14 4.OE–1O

A–Line F Stack U–234 1.31E+OO 3.56E+13 3.68E–14 9.OE–14(221-1 F)

U–235 8.29E-02 3.56E+13 2.33E-15 1.OE–13

U-238 1.86E+O0 3.56E+13 5.22E–14 1.OE–13

Pu–238 5.14E-02 3.56E+13 1.44E-1 5 3.OE–14

Pu–239 3.46E-01 3.56E+13 9.70E–15 2.OE-14

Am–241 6.13E-02 3.56E+13 1.72E–15 2.OE–14

Cm–244 1.45E-01 3.56E+13 4.08E-15 4.OE-14

H-Area (Separations and Waste Management)

241-84H (ETF Lab)

241-81 H (ETF Process)

232–H Line 1&2 Stack H–3(el) 1.71E+1O 1.33E+15(200ft)

1.29E-05 2.OE-02

H-3(oxide) 9.13E+09 1.33E+15 6.85E-06b 1.OE-07

232–H Line 3 Stack H-3(el) 2.68E+08 2.46E+14 1.09E-06(200ft)

2.OE-02

H-3(oxide) 4.30E+09 2.46E+14 1.75E-05b 1.OE-07

233-H H-3(el) 2.1OE+O8 1.06E+15 1.98E-07 2.OE-02

H-3(oxide) 3.77E+08 1.06E+15 3.56E-07b 1.OE-07

234-H H-3(el) 3.77E+09 1.77E+15 2.13E-06 2.OE-02

H-3(oxide) 2.O3E+1O 1.77E+15 1.15E-05b 1.OE-07

238-H H-3(el) 2.72E+09 4.46E+14 6.09E-06 2.OE-02

a Source: DOE Order 5400.5. In cases where different chemical forms have different DCGS,the lowest DCG for theradionuclide is given. These DCGSare defined as the air concentration of that radionuclide that will give a 50-year committedeffective dose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values onlyand are not considered release limits or standards.

b Exceeds DCG




Page 4 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (uCi) Volume (mL) (vCi/mL) (~CtimL).. - . . ..

241-H Miscellaneous Cs–137Exhaust

241–H Purge Exhaust

241-H Tank AnnulusExhaust

244-H Vessel VentExhaust

261-H (Off Gas)

291-H Stackc

299-H (Building &HPHood)

Cs-134

Cs-137

Cs-137

Cs–137

Cs–137

U-234

U-235

U-238

Pu-238

Pu-239

Am-241

Cm–244

Sr-89j90

I-131

Cs-137

U-234

U–235

U–238

Pu–238

Pu–239

Am–241

Cm–244

1.90E+01

2.32E-01

2.1 OE+O2

2.96E+01

1.30E+O0

3.18E+01

6.30E-01

8.00E-02

7.56E-01

9.68E+O0

3.76E+O0

1.60E+O0

8.70E-03

8.79E+O0

4.99E+01

1.06E+01

4.16E-02

1.04E-02

1.16E-01

9.68E+01

1.08E+01

1.1OE+OO

1.35E+O0

3.58E+14

1.08E+14

1.08E+14

7.22E+14

6.43E+12

1.21E+14

1.21E+14

1.21 E+14

1.21 E+14

1.21 E+14

1.21 E+14

1.21 E+14

1.21E+14

3.99E+15

3.99E+15

3.99E+15

3.99E+15

3.99E+15

3.99E+15

3.99E+15

3.99E+15

3.99E+15

3.99E+15

5.32E–14

2.15E-15

1.94E–12

4.11E-14

2.02E-13

2.63E-13

5.21E-15

6.61 E-16

6.25E-15

8.00E-14b

3.11E-14b

1.32E-14

7.19E–17

2.20E-15

1.25E-14

2.65E-15

1.04E-17

2.59E-18

2.90E-17

2.42E-14

2.71 E–15

2.77E-16

3.39E-16

4.OE-1 O

2.OE-10

4.OE-1 O

4.OE-1 O

4.OE-1 O

4.OE-1 O

9.OE-14

1.OE-13

1.OE-13

3.OE-14

2.OE-14

2.OE-14

4.OE-14

9.OE-12

4.OE-10

4.OE-1 O

9.OE-14

1.OE-13

1.OE-13

3.OE-14

2.OE-14

2.OE-14

4.OE-14

a Source:DOE Order5400.5. In caseswhere different chemical forms have different DCGS, the lowest DCG for theradionuclide is given. These DCGSare defined as the air concentration of that radionuclide that will give a 50-year committedeffective dose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values onlyand are not considered release limits or standards.

b Exceeds DCGc Includes data from both isoldnetic and charcoal sampling systems


Radiological Effluent Monitotfng


Page 5 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (f.lci) Volume (mL) (pCi/mL) (pCi/mL)

K-Area (K-Reactor)

K-Area Disassembly Cs–137 3.44E+01 1.88E+15 1.83E–14 4.OE–1O

K–Area Main Stack H–3(oxide) 1.12E+09 2.62E+15 4.27E-07b 1.OE-07(148ft)

L-Area (L-Reactor)

L-Area Disassembly Cs–137 3.27E-01 1.20E+15 2.73E–16 4.OE–1O

L–Area Main Stack H–3(oxide) 6.40E+08 1.74E+1 5 3.68 E-07b 1.OE-07(148ft)

Cs–137 2.23E-01 1.74E+15 1.28E-1 6 4.OE-1 O

M-Area (Reactor Materials)

313-M Stacks U–234 4.31 E-04 4.53E+12 9.52E–17 9.OE–14

U–238 4.34E-04 4.53E+12 9.58E–17 1.OE–13

321–M Machining Room U–234 1.66E+01 5.34E+13 3.11E-1 3b 9.OE-14Stack

U–235 3.46E+O0 5.34E+13 6.48E-14 1.OE-13

U–238 4.02E-01 5.34E+13 7.53E-15 1.OE-13

Pu–238 5.82E-03 5.34E+13 1.09E–16 3.OE-14

Am-241 1.06E-02 5.34E+13 1.99E–16 2.OE-14

Cm-244 2.66E-03 5.34E+13 4.98E-17 4.OE-14

U–234 3.12E+O0 5.33E+14 5.85E-15 9.OE-14321–M Stacks

M-Area VTF

U–235

U-238

Pu–238

Pu–239

Am-241

U-232

U-234

U–235

5.13E-01

8.03E-01

2.92E-02

4.90E-03

6.71E-03

1.20E+O0

1.42E+01

2.24E+O0

5.33E+14

5.33E+14

5.33E+14

5.33E+14

5.33E+14

4.58E+13

4.58E+13

4.58E+13

9.63E–16

1.51E–15

5.48E–17

9.21 E–18

1.26E–17

2.62E–14b

3.1OE–13b

4.89E-14

1.OE–13

1.OE–13

3.OE-14

2.OE-14

2.OE-14

2.OE-14

9.OE–14

1.OE-13


b Exceeds DCG

20WSRGTR-98-00314

SRS Environmental Data for 1998—



Page 6 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (pCi) Volume (mL) (pCi/mL) (pCdmL)

U-238 6.20E+01 4.58E+13 1.35E–1 2b 1.OE-13

Pu-238 1.26E-02 4.58E+13 2.75E-16 3.OE-14

Pu-239 7.1OE-O3 4.58E+13 1.55E–16 2.OE-14

Am–241 4.36E-03 4.58E+13 9.52E-17 2.OE-14

Cm-244 2.24E-03 4.58E+13 4.89E-17 4.OE-14

P-Area (P-Reactor )

P-Area Main Stack H–3(oxide) 2.07E+1 O 2.1OE+l 5 9.86E-06 1.OE-07(148ft)

S-Area (Defense Waste Processing Facility). . .

221-S Personnel Area U-234 3.80E-01(Zone 2)

250-S Glass WasteBldg #1488

250-S Glass WasteBldg #1509

U–235

U-238

Pu–238

Pu–239

Am-241

Cm-244

U-234

U–235

U-238

Pu-238

Pu–239

Am-241

Sr-89,90

U–234

U-235

U–238

7.50E-03

1.23E+O0

2.80E-01

8.12E-03

6.18E-02

6.30E-02

4.32E+O0

3.06E-03

1.56E+01

1.49E-02

1.21E-02

3.36E+O0

7.96E-01

5.22E+O0

1.09E-05

1.37E+01

8.64E+14

8.64E+14

8.64E+14

8.64E+14

8.64E+14

8.64E+14

8.64E+14

9.35E+14

9.35E+14

9.35E+14

9.35E+14

9.35E+14

9.35E+14

9.01E+14

9.01E+14

9.01E+14

9.01E+14

2.20E–17 9.OE-14

8.68E–18

1.42E–15

3.24E–16

9.40E–18

7.15E–17

7.29E-17

2.31 E-16

3.27E–18

1.67E–14

1.59E–17

1.29E–17

3.59E-15

8.83E-16

5.79E–15

1.21E-20

1.52E–14

1.OE-13

1.OE-13

3.OE-14

2.OE-14

2.OE-14

4.OE-14

9.OE–14

1.OE-13

1.OE-13

3.OE-14

2.OE-14

2.OE-14

9.OE-12

9.OE-14

1.OE–13

1.OE-13

a Source DOE Order 5400.5. In cases where different chemical forms have different DCGS,the lowest DCG for theradionuclide is given. These DCGSare defined as the air concentration of that radionuclide that will give a 50-year mmmittedeffective dose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values onlyand are not Conidered release limits or standards.

b Exceeds DCG




Page 7 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (uCi) Volume [mL) (uCi/mL) (uCi/mLl

Pu–239

Arn-241

Cm–244

250-S Glass Waste U–234Bldg #3928

U–238

Pu–238

Pu-239

Am-241

250-S Glass Waste U–234Bldg #3940

U-235

U–238

Pu–238

Pu–239

Am–241

Cm-244

291-S Vit. Process U–234(Zone 1)

U–235

U–238

Pu–238

Pu–239

Am-241

Cm–244

511–S Low Pt. Pump Pit U–234

U–235

U–238

2.36E+O0

1.09E-02

3.20E-02

1.65E-02

4.34E-01

2.98E+O0

5.74E-01

1.35E-02

8.32E-01

4.02E-01

8.46E-03

1.89E-01

1.28E-02

9.38E-04

2.72E-03

1.92E-03

2.22E+O0

5.84E-02

2.16E+O0

1.46E+O0

4.84E-02

1.56E-01

2.76E-01

2.08E-01

6.68E-03

2.24E-01

9.01E+14

9.01E+14

9.01E+14

9.01E+14

2.36E+14

2.36E+14

2.36E+14

2.36E+14

2.36E+14

8.41E+13

8.41E+l 3

8.41E+13

8.41E+13

8.41E+13

8.41E+l 3

8.41E+l 3

1.63E+15

1.63E+15

1.63E+15

1.63E+15

1.63E+15

1.63E+15

1.63E+15

2.47E+14

2.47E+14

2.47E+14

2.62E-15

1.21E–17

3.55E–17

1.83E–1 7

1.83E-15

1.26E–14

2.43E–15

5.72E–17

3.53E–15

4.78E-15

1.01E–16

2.25E–15

1.52E-16

1.12E–17

3.32E–17

2.28E–17

1.36E-15

3.58E-17

1.33E–15

8.96E–16

2.97E–17

9.57E-17

1.69E–16

8.42E–16

2.70E–17

9.07E–16

3.OE-14

2.OE-14

2.OE-14

4.OE–14

9.OE-14

1.OE–13

3.OE–14

2.OE-14

2.OE-14

9.OE–14

1.OE–13

1.OE–13

3.OE-14

2.OE–14

2.OE–14

4.OE–14

9.OE-14

1.OE-13

1.OE–13

3.OE–14

2.OE–14

2.OE-14

4.OE–14

9.OE–14

1.OE–13

1.OE-13

a Source DOE Order 5400.5. In cases where different chemical forms have different DCGS,the lowest DCGfor theradionuclide is given. These DCGSare defined as the air concentration of that radionuclide that will give a 50-year committedeffective dose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values onlyand are not considered release limits or standards.

WSRGTR-9SO031422 SRS Environmental Data for 1998



Page 8 of 8


During 1998 Release During 1998 DOE DCGsaStack/Facility Radionuclide (pCi) Volume (mL) (pCi/mL) (pCi/mL)

Pu–238 5.04E-02 2.47E+14 2.04E–16 3.OE-14

Am-241 3.92E-02 2.47E+14 1.59E-1 6 2.OE-14

Cm–244 5.94E-03 2.47E+14 2.40E-17 4.OE–14

Z-Area (Saltstone)

21o-z

704-Z




Table 6Radioactive Liquid Releases by Source(Including Direct and Seepage Basin Migration Releases)

Page 1 of 1

Curiesa

SavannahRiver

Radio- Reactor Heavy Technologynuclide Reactors Separations Materials Water~NX Center Total


H-3 (oxide)

Sr-89,90c

1-129

CS-134

Cs-137

U-234

U-235

U-238

Pu-238

Pu-239f

Am-241

Cm-244

3.44E+03

2.21 E-2

1.16E-02

6.70E-03

7.16E-05

5.09E-03

4.90E-04

1.36E-03

6.75E+03

2.78E-01

7.82E-02

1.01E-04

1.82E-01

3.99E-02

1.70E-03

4.78E-02

9.80E-04

2.78E-02

3.93E-06

2.36E-06

3.25E-03

7.02E-06

4.17E-06

5.38E-05

3.19E-06

2.38E-03

1.34E-05

3.98E+02 1.52E+O0 1.06E+04

3.22E-03 4.24E-03 3.11E-01

7.82E-02d

1.01E-04

1.93E-01 e

9.20E-06 8.48E-05 4.67E-02

4.30E-07 2.83E-06 1.78E-03

2.39E-05 7.83E-05 5.30E-02

2.59E-06 1.47E-05 1.49E-03

1.70E-03 4.41 E-03 3.76E-02

1.73E-05

2.36E-06

a One curie equals 3.7E+1O Becquerels.b Includes separations, waste management, and tritium facilitiesc Includes unidentified beta emissionsd Measured iodine-129 results were not available for 1997 and 1998 from the Savannah River Technology Laboratory. This

value was measured in 1996.e For conservatism, the higher release number (2.24E41) calculated from River Mile 120 fish concentrations was used for

dose calculations (chapter 7, “Potential Radiation Doses; SRS ErrvirorrrnentalReportfor 1998 (WSRC-TR-98-O0312).f Includes unidentified alpha emissions



ITable 7Liquid Radioactive Releases by Outfall/Facility and Comparison of AnnualAverage Radionuclide Concentrations to DOE Derived Concentration Guides

Page 1 of 5

IQuantity of Average

Radionuclides EffluentReleased Concentration

Outfall or During 1998 During 1998 DOE DCGsa Fraction ofFacility Radionuclide (Ci) (pCtimL) (~Ci/mL) DOE DCG

Note: “MDL” denotes “minimum detectable level.”

A-Area (Savannah River Technology Center)

TB-2 Outfall at Road 1A H–3 1.52E+O0 1.98E-06 2.00E-03 9.91E-04

Cs-137 Below MDL 3.46E-10 3.00E-06 1.15E-04

U-234 8.48E-05 1.24E-10 6.00E-07 2.06E-04

U-235 2.83E-06 6.00E-12 6.00E-07 1.00E-05

U-238 7.83E-05 1.18E–10 6.00E-07 1.96E-04

Pu–238 1.47E-05 1.06E–11 4.00E-08 2.66E-04

Pu–239 8.79E-07 1.65E–12 3.00E-08 5.50E-05

Sum of Fractions — 1.84E-03

D-Area (Heavy Water Rework)

400-D Effluent H-3 3.98E+02 3.97E-05 2.00E-03 1.99E-02Discharge

Sr-69,90 Below MDL -5.70E-12 1.00E-06 0.00E+OO

Cs-137 Below MDL 6.26E-1 O 3.00E-06 2.09E-04

Sum of Fractions — 2.01 E-02

F-Area (Separations and Waste Management)

F-ill H-3 1.07E-01 2.90E-07 2.00E-03 1.45E-04

Sr-89,90 Below MDL –1 .77E-1 O 1.00E-06 0.00E+OO

Cs-137 Below MDL –7.75E-11 3.00E-06 0.00E+OO


F-012 281-8F H–3 5.87E-01 9.53E-06 2.00E-03 4.76E-03Retention Basin

Sr-89,90 2.16E-04 3.82E-09 1.00E-06 3.82E-03

Cs-137 1.00E-02 9.48E-08 3.00E-06 3.16E-02


F-01 3 200-F Cooling H-3 3.09E-02 –2.28E+7 2.00E-03 0.00E+OOBasin

Sr-89,90 1.1OE-O3 1.12E-08 1.00E-06 1.12E-02

a Source: DOE Order 5400.5. In cases where different chemioal forms have different DCGS,the lowest DCG for the radionuclideis given. DCGSare defined as the concentration of that radionuclide that will give a 50-year committed effective dose equivalentof 100 mrem under renditions of continuous exposure for one year. DCGSare reference values only and are not consideredrelease limits or standards.

‘I


I


Table 7Liquid Radioactive Releases by Outfall/Facility and Comparison of AnnualAverage Radionuclide Concentrations to DOE Derived Concentration Guides

Page 2 of 5

Quantity of AverageRadionuclides Effluent

Released ConcentrationOutfall or During 1998 During 1998 DOE DCGsaFacility

Fraction ofRadionuclide (a) (~Ci/mL) (pCi/mL) DOE DCG

Cs–137 2.20E-03 2.84E-08 3.00E-06 9.46E-03

FM–3 F–Area Effluent

U3R–2 F Storm Sewer

U3RF-3 Naval FuelsEffluent

H-3

Sr-89,90

Cs–137

H-3

Sr-69,90

Cs–137

U–234

U–235

U–238

Pu–238

Pu–239

Am–241

Crrt-244

H–3

Sr-89,90

Cs–137

U–234

U-235

U-238

Pu–238

Pu–239

Am–241

1.19E+O0

3.19E-03

5.61E-03

2.17E-01

Below MDL

Below MDL

4.29E-05

3.88E-06

1.35E-04

7.02E-06

3.92E-06

3.68E-06

2.31 E-06

1.56E-01

Below MDL

Below MDL

1.29E-05

3.56E-07

3.96E-06

1.99E-07

1.01E-07

2.46E-07

7.12E-07

1.85E-09

4.15E-09

1.14E-06

2.39 E-1 O

2.07E–1 O

2.1OE-10

1.92E-11

5.59E–1 O

4.37E–11

2.78E–11

2.25E–11

9.69E–12

3.03E-06

1.95E–10

3.86E–1 O

3.92E-1 O

1.50E–11

1.O7E–10

8.97E–12

7.21E-12

7.90E–12


2.00E-03 3.56E-04

1.00E-06 1.85E-03

3.00E-06 1.38E-03


2.00E-03 5.71E-04

1.00E-06 2.39E-04

3.00E-06 6.90E-05

6.00E-07 3.51E-04

6.00E-07 3.20E-05

6.00E-07 9.32E-04

4.00E-08 1.09E-03

3.00E-08 9.25E-04

3.00E-08 7.50E-04

6.00E48 1.62E-04


2.00E-03 1.52E-03

1.00E-06 1.95E-04

3.00E-06 1.29E-04

6.00E-07 6.53E-04

6.00E-07 2.51 E-05

6.00E-07 1.78E-04

4.00E-08 2.24E-04

3.00E-08 2.40E-04

3.00E-08 2.63E-04

a Source DOE Order 5400.5. in cases where different chemical forms have different DCGS,the lowest DCGfor theradionuclide is given. DCGSare defined as the concentration of that radionuclide that will give a 50-year committed effectivedose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values only and arenot mnsidered release limits or standards.




Page 3 of 5


Released ConcentrationOutfall or During 1998 During 1998 DOE DCGsa Fraction ofFacility Radionuclide (Ci) (~CtimL) (pCi/mL) DOE DCG

Cm-244 5.09E-08 1.68E-12 6.00E-08 2.80E-05


H-Area (Separations and Waste Management)

FM-1 C H-Area Effluent H–3 4.74E+O0 9.57E-06 2.00E-03 4.79E-03

Sr–89,90

Cs-137

H-004 H-3

Sr-89,90

Cs–137

U-234

U-235

U–238

Pu-238

Pu-239

H-017 281-8H H-3Retention Basin

Sr-89,90

Cs-134

Cs-137

H-018 200-H Cooling H-3Basin

Sr-89,90

Cs-134

Cs-137

2.55E-04

1.36E-02

3.12E-01

Below MDL

Below MDL

3.27E-06

1.95E-07

1.28E-06

7.36E-07

1.40E-07

4.16E-01

1.16E-03

7.96E-05

2.01 E-02

7.37E-01

2.61 E-03

2.09E-05

2.54E-02

1.04E-09

1.28E-08

1.37E-05

2.22E-10

3.93E-10

9.08E–11

7.40E–12

3.44E-11

1.28E–11

4.02E–12

1.46E-05

1.64E-08

7.53E-09

3.52E-07

1.12E-05

3.27E-08

1.26E-08

5.16E-07

1.00E-06 1.04E-03

3.00E-06 4.26E-03


2.00E-03 6.86E-03

1.00E-06 2.22E-04

3.00E-06 1.31E-04

6.00E-07 1.51E-04

6.00E+7 1.23E-05

6.00E-07 5.74E-05

4.00E-08 3.21E-04

3.00E-08 1.34E-04


2.00E-03 7.32E-03

1.00E-06 1.64E-02

2.00E-06 3.76E-03

3.00E-06 1.17E-01


2.00E-03 5.58E-03

1.00E-06 3.27E-02

2.00E-06 6.30E-03

3.00E-06 1.72E-01


a Source: DOE Order 5400.5. In cases where different chemical forms have different DCGS.the lowest DCG for theradionuclide is given. DCGSare defined as the concentration of that radionuclide that will tive a 50-year committed effectivedose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values only and arenot considered release limits or standards.



Page 4 of 5


Released ConcentrationOutfall or During 1998 During 1998 DOE DCGsa Fraction ofFacility Radionuclide (Ci) (pCi/mL) (pCdmL) DOE DCG

HP-1 5 Tritium Facility H-3 5.44E-01 1.64E-05 2.00E-03 8.19E-03Outfall

Sr-89,90 4.64E-07 1.26E–1 O 1.00E-06 1.26E-04

Cs–137 Below MDL 2.52E–10 3.00E-06 8.40E-05


HP–52 H–Area Tank H–3 2.51 E+OO 2.51 E-06 2.00E-03 1.26E-03Farm

Sr-89,90 Below MDL 3.27E-10 1.00E-06 3.27E-04

Cs–137 2.67E-04 2.61 E-09 3.00E-06 8.70E-04

U3R–2A ETF Outfall at H-3 5.67E+02 6.49E-03 2.00E-03 3.25E+O0Road C

Sr-89,90 Below MDL 2.78E-09 1.00E-06 2.78E-03

Cs–137 4.95E-02 5.24E-07 3.00E-06 1.75E-01

Sum of Fractions — 3.42E+O@

K-Area (K-Reactor)

K Canal H-3 7.02E-01 1.43E-06 2.00E-03 7.13E-04

Sr-89,90 Below MDL 1.33E–1O 1.00E-06 1.33E-04

Cs-137 Below MDL 4.53E–10 3.00E-06 1.51E-04


L-Area (L-Reactor)

L-07 H-3 3.34E+O0 4.88E-07 2.00E-03 2.44E-04

Sr-89,90 Below MDL 1.34E-1 O 1.00E-06 1.34E-04

Cs–137 Below MDL 1.32E–1O 3.00E-06 4.39E-05


M-Area (Reactor Materials)

TB-3 M-Area Effluent Cs–137 Below MDL 6.13E–10 3.00E-06 2.04E-04at Road D

U–234 7.02E-06 -1 .42E-11 6.00E-07 O.OOE+OO

a Source DOE Order 5400.5. In cases where different chemical forms have different DCGS,the lowest DCG for theradionuclide is given. DCGSare defined as the concentration of that radionuclide that will give a 50-year committed effectivedose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values only and arenot considered release limits or standards.

b Sum of fractions is greater than 1. For more detail, refer to chapter 5, page 75, of the SRS Errviromnenta/Reporffor 7998(WSRC-TR-98+0312).

wsRGTR-9&oo31428 SRS Environmental Data for 1998

.—



Page 5 of 5


Released ConcentrationOutfall or During 1998 During 1998 DOE DCGsa Fraction ofFacility Radionuclide (Ci) (pCi/mL) (pCi/mL) DOE DCG

U-235 4.17E-06 7.38E-12 6.00E-07 1.23E-05

U-238 5.38E-05 2.59E-11 6.00E-07 4.32E-05

Pu–238 3.19E-06 -4.66E-12 4.00E-08 0.00E+OO

Am-241 1.34E-05 8.1OE-12 3.00E-08 2.70E-04


P-Area (P-Reactor)

105-R Sumps H-3 1.96E+O0 3.57E-04 2.00E-03 1.78E-01

Sr-89,90 4.09E-05 5.40E-08 1.00E-06 5.40E-02

Cs-137 7.48E-04 1.86E-07 3.00E-06 6.21E-02


S-Area (DWPF)

S-004 H-3 6.82E-01 1.82E-05 2.00E-03 9.1OE-O3

Sr-89,90 Below MDL 4.77E-11 1.00E-06 4.77E-05

C*137 Below MDL 5.23E-10 3.00E-06 1.74E-04

U-234 5.32E-07 2.82E-11 6.00E-07 4.70E-05

U-235 2.79E-08 6.60E-13 6.00E-07 1.1OE-O6

U-238 5.88E-07 2.62E-11 6.00E-7 4.36E-05

Pu-238 1.30E-06 3.33E-11 4.00E-08 8.33E-04


TNX Area

TNX-008 H-3 2.62E-01 6.89E-07 2.00E-03 3.45E-04

Cs-137 Below MDL -2.14E-1O 3.00E-06 0.00E+OO

U–234 9.20E-06 1.92E-11 6.00E-07 3.20E-05

U-235 4.30E-07 1.01E-12 6.00E-07 1.68E-06

U-238 2.39E-05 4.32E–11 6.00E-07 7.20E-05

Pu-238 2.59E-06 6.93E-12 4.00E-08 1.73E-04


a Source:DOEOrder 5400.5. In cases where different chemical forms have different DCGS,the lowest DCG for theradionuclide is given. DCGSare defined as the concentration of that radionuclide that will give a 50-year committed effectiiedose equivalent of 100 mrem under conditions of continuous exposure for one year. DCGSare reference values only and arenot considered release limits or standards.



Table 8Calculated Migration of Radioactivity from Seepage Basins

Page 1 of 1

Location Source Description 1994 1995 1996 1997 1998

FMA7-(FM3A+FM2B)

FM2B-(FM1C+H017+HOI8+HP52)

FM3A-(FM3+F012+F013)

(U3R-4)-(Direct)

PB-3-K Canal

SC2A

FMA7--(FM3A+FM2B)

FM2~FMlC+HO17+HO18+HP52)

FM3A-(FM3+F012+FO13)

FMA7-(FM3A+FM2B)

FM2B-(FM1C+HO17+HO18+HP52)

FM3A-(FM3+F012+FO13)

FMA7

200-F seepage basins toFour Mile Creek

200-H seepage basins toFour Mile Creek

200-H seepage basin 4and Solid Waste DisposalFacility to Four Mile Creek

SWDF to Upper ThreeRuns

K-Area retention basin toIndian Grave Branch

100-P seepage basin toSteel Creeka







Tritium (Curies)

2880 2,370 1,620 1,000 1,477

739 528 505 400 515

3090 4,010 3,200 2,960 3,488

344 326 164 267 386

878 1,650 1,290 2,150 3,089

386 355 320 393 507

Total Strontium (Millicuries)

78 111 68.2 105 84.3

35 40 31.3 0.4 45.2

0.77

Cesium-137 (Millicuries)

3 b 29.8 b 55.5

b b 17.4 11.4 b

b

Iodine-1 29 (Millicuries)

200-F and 200-H seeDaae 74 10 78.2 78.2C 78.2Cbasins and Solid Waste -Disposal Facility to FourMile Creek

a Includes some secondary effluent releases from P-Area when water is diverted from PAR Pondb Not detectedc Measured iodine-129 results were not available for 1997 and 1998 from the Savannah River Technology Laboratory. This value

was measured in 1996.


.


Table 9Estimated Tritium Transport in SRS Streams and the Savannah River

Page 1 of 3

Direct Releases (Curies)

Area Release Point 1994 1995 1996 1997 1998

Reactor

100-P PAR Pond overflow to Lower 59 56 47 46 110

1OO-L

100-K

1Oo-c

Three Runs Creek (L3R2)

L-Lake overflow to Steel Creek 473 472 376 715 (243)a(SC4)

●Process sewer to L Lake

●Reactor heat exchanger cool-ing water to L Lake

●Combined in 1992 (LO07) (19)’ (11)’ (10)’ (6)a (3)a

(K-Canal) 15 11 12 2 1

Process Sewer to Four Mile 1 3 2 1 b

Creek (C-Canal)

Subtotal 548 542 437 764 111

Separations

200-F Effluentto Four Mile Creek 13 2 1 1 1

Effluent to Upper Three Runs 1 1 2 1 2

200-H Effluent to Four Mile Creek 10 9 7 9 8

Effluent to Upper Three Runs 13 14 11 15 2

Effluent Treatment Facility 389 142 308 382 567

Subtotal 426 168 329 408 580

D-Area and TNX

400-D Process sewer to Beaver Dam 235 628 183 402 398Creek (400-D)

TNX TNX-008 1

Subtotal 235 628 183 402 399

A-Area

700-A Effluentto Tires Branch (T.B-2) 2

Subtotal 2

Total Direct Releasesc 1,210 1,340 949 1,570 1092

a Not used in totals because release was counted elsewhereb Discontinued in 1998c Because of rounding, sums of individual columns might not equal totals.




Page 2 of 3

Migration (Curies)

Area Release Point 1994 1995 1996 1997 1998

2oo-F&H

2oo-F&H

100-K

100-P

Solid Waste Disposal Facilityand General Separations Areato Upper Three Runs

Solid Waste Disposal Facility(FM3A-FM3) and H-Area seep-age basin to Four Mile Creek

200-F seepage basin to FourMile Creek

200-H seepage basin to FourMile Creek

904-88G to Indian GraveBranch and Pen Branch

Seepage basin to Steel Creek

Subtotal

Total Direct Releasesand Migrational

(344)’ (326)a (164)’ 267 386

3090 4,010 3,200 2,960 3,488

2880 2,370 1,620 1,000 1,477

739 528 505 400 515

878 1,650b 1,290b 2,150 3,090

(386)C (355)C (320)’ (393)C 507

7,500 8,560 6,610 6,780 9,463

8,800 9,900 7,560 8,350 10,555

Stream Transport (Curies)

1994 1995 1996 1997 1998Release PointArea

F&H Upper Three Runs at Road A 747 483 485 665 957(U3R4)

400-D Beaver Dam Creek at swamp 235 628 183 402 398

F&H Four Mile Creek at Road Al 3 6,980 7,350 4,620 4,570 5,790(FM6)

100-K Pen Branch at Road A (PB3) 1,890 2,440 2,310 2,150 3,090

100-L Steel Creek at Road A (SC4) 473 472 376 715 243

100-P Lower Three Runs at Road B 59 56 47 46 110(L3R2)

Totald 10,400 11,430 8,020 8,550 10,588

a Not used in totals because migration release was counted as part of transport totalb Beginning in 1995, this value was determined from K018-K Canal. The KO18location was discontinued in 1997. The value is

now (P8-3) – (K-Canal).c Not used in totals because release was counted as part of direct released Because of rounding, sums of individual columns might not equal totals.




Page 3 of 3

River Transport (Curies)

1994 1995 1996 1997 1998

Tritium measured in the Savannah River 12,100 12,600 10,090 9,030 10,600below SRS (RM 120)

Tritium measured in the Savannah River 1,170 1,940 1,140 1,330 1,180above SRS (RM 160)

Tritium measured in the Savannah River 10,900 10,660 8,950 7,700 9,420below SRS (downriver minus upriver)a

a Because of rounding, sums of individual columns might not equal totals.

WSRGTR-98-O0314SRS Environmental Data for 1998 33


Table 10Transport of Actinides in Savannah River Site Streams

Page 1 of 1

Location Source Description 1996 1997 1998

FM-6

U3R-4

P13-3

L3R–2

SC-4

FM-6

U3R-4

PB-3

L3R–2

SC-4

FM-6

U3R-4

PB-3

L3R–2

SC-4

FM-6

U3R4

PB-3

L3R–2

SC-4

FM-6

U3R-4

PB-3

L3R–2

SW

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transporl

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

stream transport

Uranium-234 (Curies)

6.08E-04 4.35E-03 1.62E--O2

6.38E-03 1.88E-02 2.38E-02

5.47E-04 2.94E-03 1.74E-03

6.45E-04 1.51E-03 4.96E-03a a a


5.47E-06 1.63E-04 1.07E-03

2.04E-04 5.63E-04 6.37E-04

5.31E-06 2.24E-05 4.60E-05

1.28E-05 2.67E-05 2.56E-05a a a


8.09E-04 5.27E-03 2.00E-02

8.89E-03 2.06E-02 2.79E-02

4.66E-04 2.76E-03 1.32E-03

3.55E-04 1.07E-03 3.77E-03a a a

PIutonium-238 (Curies)

1.38E-04 l.ll E-04 1.99E-04

2.53E-03 8.48E-04 7.99E-04

5.29E-05 1.74E-05 4.00E-05

8.30E-05 2.50E-05 4.50E-04a a a

Plutonium-239 (Curies)b b 1.15E-05

b b 6.71E-05b b 2.96E-05b b 1.28E-05a a a

a Not analyzedb Below minimum detectable concentration (1.OE–llKCVmL)

WSRGTR–98-0031434 SRS Environmental Data for 1998


Table 11Radioactivity in Air

Page 1 of 6

No. ofLocation Samples Arithmetic Mean ~ a Maximum * a Minimum * u

H-3, pCi/cu m

Onsite

A-Area

Burial Ground North

Burial Ground South

F-Area

H-Area

Site Perimeter

Allendale Gate

BarnwellGate

D-Area

Darkhorse @ WillistonGate

East Talatha

Green Pond

Highway 125 @ RoadA-1 4

Highway 21/167

Highway 39 @Williston Gate

Jackson

Patterson Mill Road

Talatha Gate

West Jackson

Windsor Road

25-Mile-Radius

Aiken Airport

Augusta Lock and Dam614

Highway 301 @ state line

6

24

7

6

7

25

25

25

25

23

25

5

24

3

24

24

24

24

24

25

25

16

(2.92 A 4.35)E+01

(1.47 t 0.85)E+02

(9.77 t 3.60)E+01

(2.96 * 1.62)E+01

(1.84 t 1.35)E+02

(7.85 ~ 6.82)E+O0

(1.52 ~ 0.95)E+01

(1.81A 1.51)E+01

(1.59A 1.09)E+01

(1.12 t 0.82)E+01

(9.96 ~ 7.32)E+O0

(7.16 * 2.85)E+O0

(1.05A 0.64)E+01

(1.02* 0.76)E+01

(9.27 y 6.12)E+O0

(9.17 t 5.28)E+O0

(1.20A 0.85)E+01

(1.08 t 0.76)E+01

(1.13+ 0.70)E+01

(0.83 A 1.09)E+01

(5.08 t 3.59)E+O0

(6.74 t 4.55)E+O0

(1.18 ~ 0.03)E+02

(3.92 * 0.14)E+02

(1.44 t 0.02)E+02

(4.31 * 0.33)E+01

(4.64 t 0.08)E+02

(3.36 t 0.35)E+01

(4.35 ~ 0.52)E+01

(7.96 + 0.53)E+01

(4.74 ~ 0.45)E+01

(2.88 k 0.43)E+01

(3.10 * 0.63)E+01

(9.94 t 2.49)E+O0

(3.15 ~ 0.50)E+01

(1.88 t 0.29)E+01

(2.61 f 0.68)E+01

(2.13 ~ 0.62)E+01

(4.13 t 0.34)E+01

(2.81 ~ 0.37)E+01

(2.92 ~ 0.41)E+01

(5.37 A 1.78)E+01

(1.34* 0.66)E+01

(1.44 ~ 0.54)E+01

(7.82 t 2.09)E+O0

(3.31 ~ 0.21)E+01

(5.77 * 0.43)E+01

(6.95 ~ 1.04)E+O0

(9.51 * 0.33)E+01

(1.28 ~ 3.48)E+O0

(3.88 k 2.74)E+O0

(6.78 A 0.74)E+1

(3.90 ~ 1.98)E+O0

(0.33 t 7.48)E+O0

(4.31 ~ 7.74)E+O0

(3.63 ~ 2.35)E+O0

(1.66 k 2.62)E+O0

(4.54 t 3.00)E+OO

(2.57 ~ 2.59)E+O0

(2.67 ~ 2.06)E+O0

(2.99 k 3.02)E+O0

(-1.15 ~ 5.35)E+O0

(1.42 k 0.61)E-01

(-0.76 k 1.51)E-01

(1.58 k 1.02)E-01

(-2.29 t 5.90)E+O0

CO-60, pCi/cu m

Onsite

A-Area 3 (-0.17 k 1.23)E-03 (0.24 k 1.88)E-03 (-7.85 * 7.77)E-04

Burial Ground North 39 (1.92 A 3.41)E-03 (9.39 A4.18)E+3 (-7.75 ~ 3.77)E-03

Burial Ground North 3 (4.69 ~ 3.40)E-04 (6.39 ~ 3.39)E-04 (3.68 * 3.56)E-04

Burial Ground South 1 (1.18 ~ 3.46)E-03


.—



Page 2 of 6

No. ofLocation Samoles Arithmetic Mean k c Maximum t u Minimum * o.

Burial Ground South

F-Area

F-Area

H-Area

H-Area

She Perimeter

Site perimeter composite

Allendale Gate

Bamwell Gate

D-Area

Darkhorse @ Williston Gate

East Talatha

Green Pond

Highway 21/167

Jackson

Patterson Mill Road

Talatha Gate

West Jackson

Windsor Road

25-Mila-Radius

25 mile radius

Aiken Airport


3

1

3

1

3

13

39

52

39

39

39

39

52

39

39

39

38

39

12

39

38

34

(-0.32 f 7.08)E414

(1.10 t 0.48)E-02

(-0.54 A 1.04)E-03

(-2.03 ~ 2.86)E-03

(2.80 t 5.87)E-04

(0.40 * 2.35)E-04

(1.23 t 3.32)E-03

(1.45 A 3.55)E-03

(1.49 i 3.76)E-03

(0.92 t 3.88)E-03

(1.41 ~ 3.34)E-03

(1.03 + 4.18)E-03

(1.57* 3.22)E-03

(1.97 * 4.22)E-03

(1.51 t 3.39)E-03

(2.29 k 4.23)E-03

(0.87 + 3.66)E-03

(1.47 f 3.51)E-03

(-0.08 A 1.54)E-03

(1.37 f 3.53)E-03

(1.58+ 3.53)E-03

(2.98 t 3.56)E-03

(6.88 ~ 9.65)E-04

(8.93 k 7.61)E-04

(4.81 * 3.40)E-04

(3.70 t 1.84)E-04

(7.59 t 3.26)E-03

(1.23 t 0.44)E+2

(9.48 k 3.14)E-03

(2.08 A 9.57)E-02

(1.30 t 0.44)E-02

(1.48 ~ 0.50) E-412

(1.06 t 0.41)E+2

(1.09 t 0.38)E-02

(7.27 t 3.07)E-03

(1.50 t 0.62)E+2

(1.07+ 0.48)E-03

(8.78 + 3.69)E-03

(2.12 ~ 1.64)E-03

(1.07 f 0.45)E-02

(1.13+ 0.50)E-02

(8.47 * 3.77)E-03

(-6.56 ~ 6.03)E-04

(-1 .92 i- 1.42)E-03

(1.33 ~ 3.08)E-04

(-3.21 ~ 3.61)E-04

(-5.56 A 3.31)E-03

(-5.68 ~ 3.05)E-03

(-7.08 ~ 4.88)E-03

(-6.26 A3.19)E-03

(-7.80 t 3.57)E-03

(-1 .10 t 0.96)E42

(-7.60 ~ 3.62)E-03

(-9.43 ~ 5.13)E-03

(-7.48 * 2.64)E43

(-6.61 t 4.32)E-03

(-7.14 t 4.05)E-03

(-7.50 t 4.26)E-03

(-2.00 ~ 1.64)E-03

(-9.30 ~ 4.73)E-03

(-8.98 ~ 4.69)E-03

(-3.75 ~ 3.90)E-03Highway 301 @ state line

Cs-137, pCi/cu m

Onsite

A-Area 3 (0.54 * 1.07)E-03 (2.00 ~ 1.61)E-03 (-7.31 t 5.93)E-04

Burial Ground North 39 (0.65 13.16)E-03 (7.27 t 3.63)E-03 (-5.77 k 3.24)E-03

Burial Ground North 3 (1.87 i 3.69)E-04 (5.10 t 4.53)E-04 (-1 .11 + 3.19)E-04

Burial Ground South 1 (-1 .20 * 3.53)E-03

Burial Ground South 3 (-3.41 k 7.52)E-04 (-2.59 + 7.ll)E-04 (-4.74 f 0.82)E-03

F-Area 1 (-0.52 t 4.17)E-03

F-Area 3 (-2.43 * 9.72)E-04 (1.55 ~ 1.17)E-03 (-1 .35 ~ 0.85)E-03

WSRGTR-9SO037436 SRS Environmental Data for 1998



Page 3 of 6

No. ofLocation Sam~les Arithmetic Mean ~ c Maximum * cr Minimum * c

H-Area

H-Area

Site Perimeter

Site perimeter composite

Allendale Gate

Barnwell Gate

D-Area


East Talatha

Green Pond

Highway 21/167

Jackson

Patterson Mill Road

Talatha Gate

West Jackson

Windsor Road

25-Mile-Radius

25 mile radius

Aiken Airport



Pu-238, pCticu m

1

3

13

39

52

39

39

39

39

52

39

39

39

38

39

12

39

39

34

(1.77 t3.00)E-03

(-1 .16 * 4.89)E-04

(-0.08 f2.ll)E-04

(-0.22 * 2.98)E-03

(-0.15 * 3.14)E-03

(0.27 t 3.39)E-03

(0.64 * 3.61)E-03

(-0.39 t 3.00)E-03

(0.47 t 3.85)E-03

(-0.51 f 2.99)E-03

(0.60 t 3.76)E-03

(-0.42 A 3.03)E-03

(0.18 t 3.85)E-03

(1.19* 3.32)E-03

(-0.09 * 3.13)E-03

(0.59 t 1.51)E-03

(-0.18 A 3.20)E-03

(0.28 t 3.17)E-03

(0.25 k 3.18)E-03

(3.29 t 3.00)E-04

(3.41 t 1.88)E-04

(5.97* 3.31)E-03

(8.90 t 3.35)E-03

(7.13 * 3.49)E-03

(6.51 * 3.18)E-03

(6.73 A 3.15) E-4)3

(1.09 t 0.64)E-02

(1.06* 0.39)E-02

(1.02 t 0.39)E-02

(4.42 t 3.O1)E-03

(9.03 t 3.66)E+3

(9.08 f 4.02)E-03

(5.10 A 3.50)E-03

(2.69 f 1.67)E-03

(7.91 t 2.62)E-03

(6.79 t 3.00)E-03

(7.34 t 3.08)E-03

(-3.51 k 7.34)E-04

(-3.02 * 1.89)E-04

(-6.41 *3.O1)E-03

(-7.98 * 3.65)E-03

(-9.96 &4.44)E+3

(-6.28 * 2.94)E-03

<-7.39 ~ 3.48)E-03

(-2.94 ~ 0.97)E-02

{-8.79 +4.14)E-03

(-6.27 *4.51 )E-03

(-5.88 * 3.27)E-03

(-8.80 *4.39)E-03

(-3.46 t 5.14)E-03

(-8.04 * 3.68)E~3

(-0.55 ~ 1.86)E43

(-8.20 ~ 4.54)E-03

(-8.45 k 3.81)E+3

(-4.09 * 3.28)E-03

Onsite

A-Area 3 (&3.42 * 2.28)E-06 (-1 .12 * 4.99)E-06 (-5.68 & 3.33)E-06

BurialGround North 3 (-0.91 t 2.41)E-06 (1.05 &2.71)E+6 (-3.61 t 1.52)E-06

Burial Ground South 3 (–1.07 A 1.96)E-06 (0.16 A2.07)E-06 (-3.33 * 1.91)E-06

F-Area 3 (1.44 k 5.33)E-06 (5.76 t 5.88)E-06 (-4.51 * 2.22)E-06

H-Area 3 (-3.31 A 8.49)E+7 (0.60 A4.I1)E-06 (-1 .07 ~ 2.03)E-06

Site Perimeter

Site perimetercomposite 13 (0.07 * 1.38)E-06 (4.06 * 1.69)E-06 (-1 .55 A 0.50)E-06

25-Mile-Radius

25 mile radius 13 (-1.42 * 4.96)E-06 (8.63 * 5.24)E-06 (-8.40 *4.73)E-06


.



Page 4 of 6

No. ofLocation Samples Arithmetic Mean ~ o Maximum ~ a Minimum * o

Pu-239, pCticu m

Onsite

A-Area 3 (-3.31 * 1.26)E-06 (-2.05 t 4.68)E46 (-4.58 * 0.98)E-06

BurialGround North 3 (-3.91 * 4.72)E-06 (-0.14 f 1.66)E-06 (-9.20 A 3.81)E-06

Burial Ground South 3 (0.02 * 4.33)E-06 (4.38 t 3.27)E-06 (-4.27 + 1.72)E-06

F-Area 3 (-2.32 A 2.75)E-06 (0.57 t 3.13)E-06 (4.91 Y 3.26)E-06

H-Area 3 (-2.10 + 2.95)E-06 (0.19 k 2.80)E-06 (-5.43 t 2.62)E-06

Site Perimeter

Site perimetercomposite 13 (-2.23 f 6.74)E-07 (0.74 * 1.05)E-06 (-1 .44 ~ 0.57)E-06

25-Mile-Radius

25 mile radius 13 (-5.69 t 4.61)E-06 (2.86 i- 9.61)E-06 (-1 .39 ~ 0.45)E-05

Sr-89,90, pCi/cu m

Onsite

A-Area 3 (-1 .06 i- 4.ll)E-04 (3.61 * 4.09)E-04 (4.11 ~ 4.78)E-04

BurialGround North 3 (1.28 t 1.75)E-04 (3.08 t 2.30)E-04 (-0.42 f 2.20)E-04

Burial Ground South 3 (-1 .12 t 2.73)E-04 (1.86 t 4.78)E-04 (-3.49 t 4.95)E-04

F-Area 3 (-1 .74 f 1.53)E-04 (-0.05 * 3.20)E-04 (-3.03 12.76)E-04

H-Area 3 (1.94 t 2.76)E-04 (4.45 f 2.43)E-04 (-1 .01 ~ 2.ll)E-04

Site Perimeter

Site perimeter composite 13 (1.10 t 4.80)E-05 (1.09* 0.84)EW4 (-6.72 ~ 7.16)E-05

25-Mile-Radius

25 mile radius 13 (-3.02 * 5.08)E-04 (5.11 ~ 9.93)E-04 (-1 .22 * 0.61)E-03

Gross Beta, pCi/cu m

Onsite

A-Area 13 (1.37* 0.41)E-02 (2.29 t 0.19)E-02 (7.50 ~ 1.33)E-03

BurialGround North 50 (1.90 t 0.59)E42 (3.40 t 0.16)E-02 (9.43 ~ 0.93)E-03

Burial Ground South 13 (1.44 t 0.38)E-02 (2.17 f 0.14)E~2 (7.25 f 0.88)E43

F-Area 14 (1.21 t 0.39)E-02 (1.81 A 0.15)E-02 (3.67 t 0.57)E-03

H-Area 13 (1.27* 0.36)E-02 (2.14 ~ 0.13)E-02 (7.84 ~ 0.83)E-03

Site Perimeter

Allendale Gate 50 (1.86+ 0.62)E-02 (3.50 ~ 0.17)E-02 (7.84 ~ 0.83)E-03

Barnwell Gate 51 (1.88 t 0.64)E-02 (3.51 30.18)E-02 (8.01 t 0.82)E-03

D-Area 51 (1.58* 0.56)E-02 (3.18 ~ 0.18)E+2 (6.97 f 0.87)E-03

Darkhorse @ Williston Gate 52 (1.88+ 0.85)E42 (6.11 * 0.21)E-02 (1.35 t 0.39)E43


—



Page 5 of 6

No. ofLocation Sam~les Arithmetic Mean* a Maximum * a Minimum + c.

East Talatha 51 (1.89 t 0.64)E-02

Green Pond 51 (1.89 * 0.67)E-02

Highway 125 @ Road 13 (1.37 t 0.25)E-02A-1 4

Highway 21/167 51 (1.87 i- 0.67)E-02

Highway 39 @ 10 (1.33 t 0.27)E-02Williston Gate

Jackson 51 (1.68* 0.59)E-02

Patterson Mill Road 51 (1.81 t 0.61)E-02

Talatha Gate 51 (1.68 k 0.54)E-02

West Jackson 50 (1.90 t 0.71)E-02

Windsor Road 52 (1.82 * 0.61)E4J2

25-MiIe-Radius

Aiken Airport 51 (1.81 i- 0.57)E-02

Augusta Lock and Dam 50 (1.84* 0.53)E-02614

Highway 301 @ state line 34 (2.16 t 0.59)E+2

Gross Alpha, pCi/cu m

(3.41 * 0.16)E-02

(3.67 ~ 0.24)E-02

(1.87 * 0.13)E-02

(4.61 t 0.22)E-02

(1.72 k 0.08)E-02

(3.19 A 0.17)E-02

(3.47 ~ 0.18)E-02

(3.05 t 0.20)E-02

(3.50 t 0.19)E-02

(3.69 t 0.18)E-02

(3.34 t 0.22)E-02

(3.00 t 0.15)E-02

(3.37 A 0.19)E-02

(9.54 t 0.91)E-03

(8.40 A 0.91)E-03

(1.06 * O.1O)E-O2

(8.23 t 0.82)E-03

(7.84 t 0.83)E+3

(8.35 A 1.O1)E-03

(8.27 * 0.82)E-03

(8.81 * 0.91)E-03

(6.36 * 0.80)E-03

(8.56 k 0.84)E43

(7.75 A 0.76)E43

(9.24 + 0.83)E-03

(1.11 f O.1O)E-O2

Onsite

A-Area

Burial Ground North

Burial Ground South

F-Area

H-Area

Site Perimeter

Allendale Gate

Bamwell Gate

D-Area


East Talatha

Green Pond

Highway 125 @Road A-1 4

Highway 21/167

Highway 39 @ WillistonGate

13

50

13

14

13

51

51

51

52

50

51

13

51

10

(5.76 k 5.39)E-04

(1.46 k 0.69)E-03

(6.84 t 3,64)E-04

(9.60 * 5.43)E-04

(6.96 f2.41)E-04

(1.45 t 0.84)E+3

(1.46 AO.94)E-03

(1.19 t 0.68)E-03

(1.49 * 0.91)E-03

(1.54 t 0.95)E-03

(1.65 k 0.90)E-03

(6.52 f 4.35)E-04

(1.49* 0.84)E-03

(7.76 + 2.08)E+4

(1.72 ~ 0.64)E-03

(3.67 * 0.67)E-03

(1.45 ~ 0.47)E-03

(1.73A 0.46)E-03

(1.05 ~ 0.36)E-03

(3.95 ~ 0.70)E-03

(5.21 t 0.87)E43

(3.34 t 0.68)E-03

(4.58 k 0.80)E-03

(3.98 t 0.74)E-03

(4.20 t 0.72)E-03

(1.84 t 0.46)E-03

(4.40 t 0.92)E-03

(1.11 ~ 0.26)E-03

(-1 .21 t 3.05)E-04

(4.95 A 2.98)E-04

(2.56 * 2.53)E-04

(0.62 k2.61)E-04

(2.72 * 2.40)E-04

(1.47 t 2.24)E-04

(1.13* 2.03)E-04

(0.69 k 2.32)E-04

(-1 .91 * 1.39)E-04

(3.41 * 2.68)E-04

(3.02 A 2.73)E-04

(2.51 t 2.37)E-04

(1.94 t 2.18)E414

(5.04 * 1.99)E-04




Page 6 of 6

No. ofLocation Samples Arithmetic Mean t a Maximum * a Minimum t a

Jackson 51 (1.34 k 0.95)E-03 (5.39 t 0.85)E-03 (0.44t 2.16)E-04

Patterson Mill Road 51 (1.45 t 0.85)E-03 (4.34 A 0.81)E+3 (2.01 * 2.35)E-04

Talatha Gate 50 (1.39* 0.84)E+3 (3.24 A 0.71)E-03 (0.44 * 2.14)E-04

West Jackson 50 (1.64 f 1.05)E-03 (5.91 t 0.93)E-03 (0.70 t 2.23)E-04

Windsor Road 52 (1.45+ 0.78)E-03 (3.99 + 0.78)E-03 (2.34 + 2.21)E-04

25-Mile-Radius

Aiken Airport 50 (1.45* 0.74)E+3 (3.13 + 0.63)E-03 (3.56 ~ 2.80)E-04

Augusta Lock and Dam 50 (1.49* 0.65)E-03 (2.93 t 0.63)E-03 (4.20 k 2.91)E-04614

Highway 301 @ state line 34 (1.64 k 0.74)E-03 (3.62 ~ 0.66)E-03 (3.53 t 2.57)E-04

WSRGTR-98-0031440 SRS Environmental f3ata for 1998


Table 12Tritium in Rainwater

Page 1 of 1

No. ofLocation Samples Arithmetic Mean ~ a Maximum k cs Minimum ~ c

H-3, pCi/L

Onsite

A-Area

BurialGround North

Burial Ground South

F-Area

H-Area

Site Perimeter

Allendale Gate

Barnwell Gate

D-Area


East Talatha

Green Pond

Highway 125 @ RoadA-1 4

Highway 21/167

Highway 39 @Williston Gate

Jackson

Patterson Mill Road

Talatha Gate

West Jackson

Windsor Road

25-Mile-Radius

Aiken Airport



100-Mila-Radius

Savannah, Ga.

6

24

6

6

6

23

23

23

24

24

24

6

23

4

24

24

23

23

25

23

25

14

25

(4.85 t 5.20)E+02

(5.25 t 3.33)E+03

(1.94 t 1.39)E+04

(4.67 * 4.44)E+03

(2.76 * 1.95)E+04

(1.43* 4.36)E+02

(3.92 t 3.27)E+02

(9.94 A 9.81)E+02

(3.92 i 5.75)E+02

(3.82 t 5.47)E+02

(4.01 A 4.73)E+02

(4.65 t 5.93)E+02

(1.75A 3.08)E+02

(1.89 t 4.78)E+02

(2.85 A 5.08)E+02

(3.02 t 4.19)E+02

(5.93 A 5.64)E+02

(0.76 t 1.30)E+03

(4.21 A 5.73)E+02

(3.20 A 3.32)E+02

(2.63 t 5.57)E+02

(0.08 t 2.96)E+02

(0.58 t 2.51)E+02

(9.48 A 2.14)E+02

(1.57 t 0.05)E+04

(3.68 * 0.09)E+04

(1.16 * 0.02)E+04

(6.29 A 0.09)E+04

(1.65 f 0.35)E+03

(1.37 * 0.27)E+03

(4.30 t 0.39)E+03

(2.23 t 0.41)E+03

(1.86* 0.42)E+03

(1.57 k 0.38)E+03

(1.29 * 0.31)E+03

(9.25 * 3.90)E+02

(6.89 t 3.39)E+02

(1.59 * 0.38)E+03

(1.46* 0.17)E+03

(2.21 * 0.40)E+03

(6.07 t 0.42)E+03

(2.46 t 0.43)E+03

(9.88 A2.65)E+02

(1.87* 0.35)E+03

(5.29 & 3.62)E+02

(4.91 * 3.72)E+02

(-3.83 k 3.67)E+02

(1.64* 0.40)E+03

(4.12 t 0.31)E+03

(1.05 t 0.35)E+03

(8.60 i- 0.51)E+03

(-3.66 A 3.75)E+02

(-0.92 f 3.18)E+02

(0.59 A 3.29)E+02

(-5.29 * 3.70)E+02

(-3.55 A 3.75)E+02

(-2.79 k 3.64)E+02

(-2.37 t 2.43)E+02

(-5.12 t 3.76)E+02

(-2.46 A 3.45)E+02

(-5.84 f 3.92)E+02

(-5.20 * 3.94)E+02

(-3.27 t 3.73)E+02

(-3.47 t 3.69)E+02

(-2.81 A 3.79)E+02

(-1.89 t2.81)E+02

(-5.12 t 3.22)E+02

(-4.87 * 3.90)E+02

(-3.86 f 3.43)E+02



Table 13Radioactivity in Rain Ion Columns

Page 1 of 4

No. ofLocation Samples Arithmetic Mean k a Maximum k c Minimum t c

CO-60, pCi/sq m .

Onsite

Burial Ground North 8 (5.46 t 5.72)E+O0 (1.50 t 0.82)E+01 (-3.08 * 9.43)E+O0

H-Area 3 (-5.22 t 4.00)E+OO (-0.82 t 8.62)E+O0 (-8.63 + 9.28)E+O0

Site Perimeter

Site Perimeter

BarnwellGate 4 (9.97 * 9.1O)E+OO (2.1O* 1.07)E+OI (0.08 * 1.00)E+O1

D-Area 12 (1.51 f 7.89)E+O0 (1.44* 0.92)E+01 (-1 .32 * 0.96)E+01

Darkhorse @ Williston Gate 12 (1.70* 7.54)E+O0 (1.32+ 0.94)E+01 (-1 .19 A 0.67)E+01

Green Pond 12 (2.97 * 6.19)E+O0 (1.03* 0.88)E+01 (-6.63 + 9.74)E+O0

Patterson Mill Road 12 (3.41 * 8.58)E+O0 (2.42 * 0.93)E+01 (-0.67 + 1.23)E+01

25-MiIe-Radius

Aiken Airport 3 (0.97 t 1.15)E+01 (2.25 * 1.15)E+01 (0.33 f 9.52)E+O0

Augusta Lock and Dam 3 (2.63 f 5.62)E+O0 (0.86 t 1.09)E+01 (-2.62 * 9.57)E+O0614

Highway 301 @ State Line 7 (4.05 i 5.93)E+O0 (1.02A 0.72)E+01 (-0.45 t 1.19)E+01

100-Mile-Radius

Savannah, Ga. 13 (1.38 ~ 9.80)E+O0 (2.33 + 1.16)E+01 (-1 .54 * 1.06)E+01

Cs-137, pCi/sq m

Onsite

Burial Ground North

H-Area

Site Perimeter

Barnwell Gate

D-Area

Darkhorse @rWilliston Gate

Green Pond

Patterson Mill Road

25-Mile-Radius

Aiken Airport


Highway 301 @ State Line

100-MiIe-Radius

Savannah, Ga.

8

3

4

12

12

12

12

3

3

7

13

(2.25 t 4.19)E+O0

(2.90 t 3.40)E+O0

(-1 .82 t 7.05)E+O0

(4.51 t 6.91)E+O0

(-1 .02 ~ 7.90)E+O0

(2.71 * 9.27)E+O0

(-0.48 A 7.18)E+O0

(4.66 f 2.96)E+O0

(-0.66 t 6.93)E+O0

(0.06 t 1.06)E+01

(0.33 + 9.35)E+O0

(6.80 * 8.95)E+O0

(6.64 t 8.85)E+O0

(7.86 * 7.94)E+O0

(1.73* 0.80)E+01

(1.20 t 0.86)E+01

(1.80 t 0.94)E+01

(1.09 t 0.74)E+01

(6.97 t 8.61)E+O0

(0.67 * 1.06)E+01

(1.52 k 1.02)E+01

(1.46 + 0.87)E+01

(-0.70 * 1.O1)E+O1

(-0.01 t 8.73)E+O0

(-7.79 f 9.21)E+O0

(-9.83 * 9.49)E+O0

(-1 .86 + 0.89)E+01

(-1 .15 * 0.66)E+01

(-9.32 k 9.18)E+O0

(0.13 * 1.09)E+01

(-7.05 * 8.80)E+O0

(-1 .03 * 0.84)E+01

(-2.06 t 0.95)E+01


.-



Page 2 of 4

No. ofLocation Samples Arithmetic Mean * a Maximum A a Minimum *IS

Pu-238, pCdsq m

Onsite

H-Area 1 (-5.09 * 4.66)E-02

Site Perimeter

Barnwell Gate 1 (-7.06 t 3.71)E-02

D-Area 1 (-1.55 A 0.37)E-01

Darkhorse @ Williston Gate 1 (-4.04 * 6.03)E-02

Green Pond 1 (-8.89 * 3.46)E-02

Patterson Mill Road 1 (-6.33 A 5.08)E-02

25-Mile-Radius

Aiken Airport 1 (-1.04 * 0.61)E-01

Augusta Lock and Dam 1 (-1 .07 ~ 0.23)E-01614

100-Mile-Radius

Savannah, Ga. 1 (-1.15 * 0.22)E-01

Pu-239, pCdsq m

Onsite

H-Area

Site Perimeter

Barnwell Gate

D-Area


Green Pond

Patterson Mill Road

25-Mile-Radius

Aiken Airport


100-Mile-Radius

Savannah, Ga.

1

1

1

1

1

1

1

1

1

(-2.47 t 3.28)E-02

(-4.47 * 1.12)E-02

(-1.02 t 8.11)E+2

(-1.12 A 0.59)E+1

(-6.18 k 1.66)E-02

(-1 .72 k 2.69)E42

(-7.04~ 8.18)E-f)2

(-8.45 k 2.60)E-02

(-7.67 ~ 2.02)E-02

Sr-89,90, pCdsq m

Onsite

H-Area 1 (-5.11 t 3.82)E+O0

Site Perimeter

BarnwellGate 1 (-2.76 * 4.19)E+O0




Page 3 of 4

No. ofLocation Samples Arithmetic Mean ~ a Maximum + a Minimum * o

D-Area 1 (-3.91 + 4.17)E+O0

Darkhorse @ Williston Gate 1 (-1 .12 t 4.31)E+O0

Green Pond 1 (-2.95 A 3.90)E+O0

Patterson Mill Road 1 (-1 .34 A 4.32)E+O0

25-Mile-Radius

Aiken Airport 1 (-2.98 * 3.05)E+O0

Augusta Lock and Dam 1 (0.53 + 4.53)E+O0614

100-MiIe-Radius

Savannah, Ga. 1 (1.23 t 4.43)E+O0

Gross Beta, pCi/sq m

Onsite

BurialGround North

H-Area

Site Perimeter

Bamwell Gate

D-Area

Darkhorse @ WillistonGate

Green Pond

Patterson Mill Road

25-Mile-Radius

Aiken Airport


Highway 301 @ State Line

100-Mile-Radius

Savannah, Ga.

8

3

4

12

12

12

12

3

3

7

12

(1.27 k 0.95)E+02

(1.04 t 0.20)E+02

(1.63A 1.01)E+02

(1.00+ 0.93)E+02

(1.24 t 1.08)E+02

(9.01 + 7.89)E+01

(6.22 * 7.75)E+01

(8.08 * 4.15)E+01

(6.95 * 5.92)E+01

(1.25 t 1.27)E+02

(1.93+ 2.05)E+02

(2.66 t 0.13)E+02

(1.26* 0.09)E+02

(2.58 t 0.13)E+02

(3.42 t 0.15)E+02

(3.99 * 0.16)E+02

(2.72 A 0.13)E+02

(2.35 A 0.14)E+02

(1.05 t 0.06)E+02

(1.37 ~ O.1O)E+O2

(3.74 k 0.19)E+02

(7.1O+ 0.26)E+02

(1.32 t 0.48)E+01

(8.57 k 0.79)E+01

(3.29 * 0.55)E+01

(1.40* 0.48)E+01

(1.92+ 0.44)E+01

(2.26 f 3.27)E+O0

(0.20 * 3.88)E+O0

(3.29 ~ 0.40)E+01

(2.74 A 0.61)E+01

(2.88 t 0.51)E+01

(1.39+ 0.45)E+01

Gross Alpha, pCtisq m

Onsite

BurialGround North 8 (3.54 t 4.78)E+O0 (1.49 A 0.70)E+01 (-0.29 t2.52)E+O0

H-Area 3 (4.98 k 2.41)E+OO (7.41 t 3.78)E+O0 (2.60 t 2.56)E+O0

Site Perimeter

BarnwellGate 4 (0.09 * 1.51)E+OO (2.04 + 5.16)E+O0 (-1 .12 * 1.55)E+O0

D-Area 12 (3.20 f 4.48)E+O0 (1.10 f 0.43)E+01 (-3.36 * 2.98)E+O0

Darkhorse @ WillistonGate 12 (2.93 + 2.12)E+O0 (6.91 * 3.75)E+O0 (0.68 * 2.14)E+O0



ITable 13Radioactivity in Rain [on Columns

Page 4 of 4 II

No. ofLocation Samples Arithmetic Mean * a Maximum * a Minimum + a

Green Pond 12 (1.37 f 2.98)E+O0 (8.23 * 4.07)E+O0 (-1 .87 k 1.60)E+O0

Patterson Mill Road 12 (1.13* 3.62)E+O0 (1.18A 0,37)E+01 (-2.28 ~ 1.31)E+O0

25-Mile-Radius

Aiken Airport 3 (2.77 A 2.23)E+O0 (4.94 * 3.13)E+O0 (0.49 t 1.67)E+O0

Augusta Lock and Dam 3 (1.20A 2.63)E+O0 (4.12 k 2.88)E+O0 (-0.99 t 2.33)E+O0614

Highway 301 @ State Line 7 (2.51 k 3.71)E+O0 (8.84 A 4.13)E+O0 (-2.26 A 2.62)E+O0

100-Mile-Radius

Savannah, Ga. 12 (2.97 * 4.45)E+O0 (8.84 * 5.48)E+O0 (-4.47 * 2.04)E+O0.



Table 14Thermoluminescent Dosimeter (TLD) Results —SRS Areas

Page 1 of 3

Quarterly Exposure in mR/DayYearly Exposure in mFUYear

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mFi/Year

Notes: 1. mR = milliRoentgen, exposure unit for gamma radiation. One mR is approximately equal to 1 mrem.Although the TLD is an integrating device, the derived unit mWday is used to facilitate data comparisonbetween locations or through time at a single location.2. An 18% uncertainty is associated with each result.3. Blank spaces indicate missing TLD results. Computer data transfer problems resulted in loss of all datafor the 3rd and 4th quarters.4. Program changes instituted in mid-1998 eliminated monitoring at all area boundary locations. Annualexposures are not presented for these locations.

643-26E 1

643-26E 2

643-7G 1

643-7G 2

643-7G 3

643-7G 4

643-G 1

643-G 2

643-G 3

643-G 4

Al

A2

A3

A4

A5

A6

A7

A8

F1

F2

F3

F4

F5

F6

H1

0.30

0.24

0.32

0.27

0.30

0.42

0.25

0.31

0.39

0.32

0.24

0.32

0.26

0.30

0.24

0.26

0.29

0.23

0.23

0.26

0.23

0.27

0.39

0.27

0.31

0.29

0.31

0.42

0.26

0.31

0.41

0.32

0.31

0.28

0.30

0.25

0.26

0.30

0.21

0.25

0.28

0.28

0.40

0.28



Table 14Thermoluminescent Dosimeter (TLD) Results —SRS Areas

Page 2 of 3

Quarterly Exposure in mR/DayYearly Exposure in mFt/Year

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mIUYear

H2 0.30 0.30

H3

H4

H5

H6

H7

H8

K1

K2

K3

K4

L1

L2

L3

L4

N1

N2

N3

N4

N5

P1

P2

P3

P4

R1

R2

R3

R4

R5

R6

R7

RR 1

0.27

0.40

0.40

0.27

0.29

0.31

0.20

0.18

0.24

0.21

0.21

0.20

0.20

0.26

0.25

0.27

0.34

0.33

0.54

0.23

0.19

0.20

0.22

0.20

0.21

0.18

0.22

0.21

0.19

0.20

0.26

0.29

0.42

0.40

0.28

0.29

0.32

0.23

0.21

0.28

0.23

0.24

0.23

0.23

0.28

0.30

0.38

0.37

0.51

0.26

0.21

0.24

0.25

0.22

0.25

0.21

0.25

0.24

0.22

0.23

0.27



Table 14Thermoluminescent DosimeterSRS Areas

(TLD) Results —

Page 3 of 3

Quarterly Exposure in mR/DayYearly Exposure in mR/Year

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mFf/Year

RR 2 0.27 0.27

S1 0.28 0.29

S2 0.32 0.33

S3 0.33 0.35

S4 0.33 0.32

Z1 0.22 0.23

Z2 0.21 0.22

Z3 0.22 0.22

Z4 0.26 0.25



Table 15Thermoluminescent Dosimeter (TLD) Results —Site Perimeter Stations

Page 1 of 1

Quarterly Exposure in mRfDayYearly Exposure in mR/Year

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mFi/Year

Notes: 1. mR = milliRoentgen, exposure unit for gamma radiation. One mR is approximately equal to 1 mrem.Although the TLD is an integrating device, the derived unit mR/day is used to facilitate data comparisonbetween locations or through time at a single location.2, An 18% uncertainty is associated with each result.3. Blank spaces indicate missing TLD results. Computer data transferproblems resulted in loss of-all datafor the 3rd and 4th quarters.

PP15 0.19 0.18 66

PP 42 0.20 0.19 71

PP 48 0.18 0.17 63

PP 51 0.18 0.17 63

PP 57D 0.17 0.16 60

PP 61B 0.18 0.17 63

PP 65D 0.21 0.20 76

PP 72B 0.18 0.17 64

PP 75D 0.15 0.15 55



Table 16Thermoluminescent Dosimeter (TLD) Results —Environmental Surveillance (Air Monitoring) Stations

Page 1 of 1

Quarterly Exposure in mlUDayYearly Exposure in mR/Year

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mR/Year

Notes: 1. mR = milliRoentgen, exposure unit for gamma radiation. One mR is approximately equal to 1 mrem.Although the TLD is an integrating device, the derived unit mEYdayis used to facilitate data comparisonbetween locations or through time at a singie location.2. An 18% uncertainty is associated with each result.3. Blank spaces indicate missing TLD results. Computer data transfer problems resulted in loss of all datafor the 3rd and 4th quarters.

A Areaa 0.24

BGN

BGSa

F Area’

H Areaa

A–14’

Aiken

Allendale

Bamwell

D Area

Dark Horse

East Talatha

Green Pond

Hwy21/167

Hwy 39’

Jackson

Patt Mill Rd

West Jackson 0.24

Windsor Rd 0.14

0.19

0.16

0.22

0.15

0.20

0.15

0.19

0.18

0.18

0.17

0.17

0.13

0.26 0.38 115

0.23

0.29

0.29

0.18

0.21

0.16

0.20

0.19

0.19

0.17

0.18

0.25

0.19

0.20

0.17

Aiken Airport 0.18

Augusta Lock and Dam 0.25

Hwy301b

Savannah 1 0.16

Savannah 2 0.16

a Program changes instituted in mid-1998 eliminated monitoring at this location. An annual exposure is not presented for thislocation.

b High Savannah River levels prevented monitoring for the first 2 quarters of 1998.


_—.-


Table 17ThermoluminescentPopulation Centers

Dosimeter (TLD) Results —

Page 1 of 1

Quarterly Exposure in mR/DayYearly Exposure in mlUYear

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mFf/Year

Notes: 1. mR = miIliRoentgen, exposure unit for gamma radiation. One mR is approximately equal to 1 mrem.Although the TLD is an integrating device, the derived unit mR/day is used to facilitate data comparisonbetween locations or through time at a single location.2. An 18% uncertainty is associated with each result.3. Blank spaces indicate missing TLD results. Computer data transferproblems resulted in loss of all datafor the 3rd and 4th quarters.

Barnwell 0.20 0.22 76

Beech Island 0.25 0.30 100

Girard 0.30 110

Jackson 0.21 0.25 83

Martin 0.15 0.18 60

McBean 0.27 98

New Ellenton 0.24 0.28 95

Williston 0.26 0.29 99

Windsor 0.11 39


Table 18Thermoluminescent Dosimeter (TLD) Results —Vogtle Electric Generating Plant Vicinity

Page 1 of 1

Quarterly Exposure in mR/DayYearly Exposure in mR/Year

Location Quarter 1 Quarter 2 Quarter 3 Quarter 4 mR/Year

Notes: 1. mR = milliRoentgen, exposure unit for gamma radiation. One mR is approximately equal to 1 mrem.Although the TLD is an integrating device, the derived unit mR/day is used to facilitate data comparisonbetween locations or through time at a single location.2. An 18% uncertainty is associated with each result.3. Computer data transfer problems resulted in loss of all data for the 3rd and 4th quarters.

GAP 1H 0.16 0.15 57

GAP 1L 0.16 0.15 57

GAP 2H 0.16 0.17 61

GAP 2L 0.17 0.17 62

GAP 3H 0.17 0.18 64

GAP 3L 0.17 0.17 62

GAP 4H 0.18 0.18 66

GAP 4L 0.18 0.18 65

GAP 5H 0.16 0.16 58

GAP 5L 0.12 0.14 47

NRC 1 0.17 0.14 55

NRC 2 0.10 0.10 37

NRC 3 0.13 0.10 42

NRC 4 0.16 0.12 50

NRC 5 0.20 0.16 64

NRC 6 0.15 0.12 48

NRC 7 0.14 0.11 46

NRC 8 0.10 0.10 37



Table 19Radioactivity in Seepage Basin Water

Page 1 of 1

No. ofLocation Samples Arithmetic Mean * a Maximum * c Minimum t a

H-3, pCi/L

EAV Basin North (E-004) 12 (7.14 t 2.00)E+03 (1.23A 0.05)E+04 (4.54A 0.31)E+03

SWDF Basin North 12 (1.16 * 0.69)E+04 (2.60 * 0.06)E+04 (4.55 * 0.32)E+03(E402)

SWDF Basin South 12 (1.08 t 0.66)E+04 (2.61 t 0.06)E+04 (3.94 f 0.21)E+03(E-001)

CO-60, pcfi

EAV Basin North (E-004) 12 (1.16A 2.69)E+O0 (5.39 * 1.99)E+O0 (-2.77 i- 2.64)E+O0

CS-137, pci/L

EAV Basin North (E-004) 12 (-0.1 9A 1.69)E+O0 (2.79 * 2.05)E+O0 (-2.17 ~2.06)E+O0

Gross Beta, pCi/L

EAV Basin Nort (E-004) 12 (2.66 t 1.29)E+O0 (5.08 * 1.04)E+O0 (8.13 t 6.16)E-01

SWDF Basin North 12 (3.52 ~ 1.08)E+O0 (5.59 t 0.79)E+O0 (1.78 ~ 1.ll)E+OO(E-002)

SWDF Basin South 12 (3.38 t 1.33)E+O0 (6.97 A 1.34)E+O0 (2.08 A 0.82)E+O0(E-001)

Gross Alpha, pCi/L

EAV Basin North (E-004) 12 (1.16 + 1.25)E+O0 (3.28 t 1.18)E+O0 (-0.89 A 2.30)E-01

SWDF Basin North 12 (1.64* 0.97)E+O0 (3.07 t 0.77)E+O0 (3.22 t 3.94)E-01(E-002)

SWDF Basin South 12 (2.04 ~ 2.80)E+O0 (8.18 k 1.93)E+O0 (4.45 k 4.07)E-01(E-001)



Table 20

Radioactivity in Savannah River Site Stream Water

Page 1 of 8

No. ofLocation Samples Arithmetic Mean + c Maximum * a Minimum * o

H-3, p~i

Tires Branch

TB-5 near Road C

Upper Three Runs

McQueen Branchat Road F

Crouch Branch at Road 4

U3R–1A Treadway BridgeRoad 8-1

U3R–3 at Road C

U3R4 at Road A

Four Mile Creek

C-Canal

Caster Creek—southeastof C-Area

FM–2 at Road 4

FM–2B above F-Areaeffluent

FM-3A below F-Areaeffluent

FM-6 at Road A–12.2

FM–A7 at Road A–7

H-008 Outfall

HP–50 Tritium FacilityOutfall

Twin Lakes-westof C-Area

Pen Branch

IGB-21 800 feet southof Road 6-1

K-01 1 Outfall at B Road

PB-3 at Road A–13.2

Steel Creek

SC-2A 1 mile aboveRoad B

SC-4 Steel Creekat Road A

26

26

26

52

26

26

27

26

26

26

26

26

26

26

26

26

26

26

27

26

26

(8.15 t 3.33)E+02

(8.87 A 1.18)E+03

(1.34* 0.28)E+04

(5.12 t 3.52)E+02

(4.23 f 4.06)E+03

(4.26 * 3.36)E+03

(2.31 * 0.43)E+03

(2.83 * 0.49)E+03

(1.58* 0.89)E+04

(4.87 + 1.59)E+04

(1.31 t 0.42)E+06

(1.90A 0.47)E+05

(3.20 t 1.06)E+05

(3.39 * 3.93)E+03

(1.61 t 1.50)E+04

(1.23 t 0.33)E+04

(5.71 f 1.22)E+05

(3.38 10.58)E+05

(1.17* 0.28)E+05

(1.94 t 0.71)E+05

(5.24 A 1.19)E+03

(1.47 t 0.26)E+03

(1.12* 0.03)E+04

(2.09 t 0.04)E+04

(2.46 ~ 0.34)E+03

(1.59A 0.06)E+04

(1.35* 0.06)E+04

(3.26 t 0.29)E+03

(4.44 t 0.32)E+03

(4.44 f 0.09)E+04

(8.52 f 0.48)E+04

(2.86 + 0.03)E+06

(2.39 + 0.02)E+05

(4.78 f 0.09)E+05

(1.98* 0.03)E+04

(6.50 t 0.08)E+04

(1.99 t 0.05)E+04

(7.96 t 0.09)E+05

(4.38 * 0.05)E+05

(1.74 ~ 0.01)E+05

(2.75 * 0.02)E+05

(7.96 f 0.37)E+03

(1.19 t 2.33)E+02

(6.71 t 0.25)E+03

(6.61 k 0.35)E+03

(-0.18 A 2.28)E+02

(-2.56 * 0.14)E+03

(1.20* 0.38)E+03

(1.53A 0.27)E+03

(1.70 t 0.36)E+03

(3.60 k 0.30)E+03

(2.51 + 0.29)E+04

(8.70 * 0.14)E+05

(1.06* 0.01)E+05

(1.40* 0.04)E+05

(4.28 * 3.81)E+02

(2.54 + 0.28)E+03

(3.05 * 0.30)E+03

(3.30 * 0.08)E+05

(2.06 t 0.03)E+05

(6.17 t0.ll)E+04

(8.66 + 0.13)E+04

(3.24 t 0.39)E+03



Table 20Radioactivity in Savannah River Site Stream Water

Page 2 of 8

No. ofLocation Samples Arithmetic Mean ~ a Maximum f c Minimum t a

Lower Three Runs Creek

L3R–1A at Road B 26 (1.10 * 1.27)E+03 (7.21 * 0.26)E+03 (4.71 * 2.41)E+02

L3R–2 Patterson Mill Road 26 (1.58A 0.58)E+03 (2.73 t 0.28)E+03 (6.62 A 3.69)E+02

L3R-3 at Highway 125 12 (7.97 * 4.59)E+02 (1.39 k 0.26)E+03 (-0.24 * 3.63)E+02

R-Area downstream of R–1 26 (3.84 A 2.13)E+03 (9.80 * 0.50)E+03 (1.27 t 0.38)E+03

CO-60, pCi/L

Upper Three Runs



U3R-3 at Road C

U3R-4 at Road A

Four Mile Creek

C-Canal

FM–2 at Road 4

FM-2B above F-Areaeffluent

FM–3A below F-Areaeffluent

FM-6 at Road A-12.2

FM-A7 at Road A–7

H-008 Outfall

HP-50 Tritium FacilityOutfall

Pen Branch

K-01 1 Outfall at B Road

PB-3 at Road A-13.2

Steel Creek




L3R-2 Patterson Mill Road

L3R-3 at Highway 125

R-Area downstream of R-1

26

26

26

26

27

26

26

26

26

26

26

26

26

27

26

26

26

12

26

(0.25 t 2.42)E+O0

(-0.42 * 2.00)E+OO

(0.68 * 3.30)E+O0

(0.50 * 2.74)E+O0

(0.09 f 2.04)E+O0

(0.82 * 2.48)E+O0

(0.74 * 2.31)E+O0

(0.74 * 2.84)E+O0

(0.99 t 2.97)E+O0

(1.25* 1.96)E+O0

(1.26* 2.48)E+O0

(0.48 * 3.46)E+O0

(0.76 * 2.29)E+O0

(0.54 * 5.44)E+O0

(0.39 * 3.18)E+O0

(1.37+ 4.55)E+O0

(0.42 * 2.37)E+O0

(1.05 ~ 2.35)E+O0

(0.22 + 2.76)E+O0

(5.27 * 2.77)E+O0

(4.30 ~ 1.92)E+O0

(5.55 t 3.ll)E+OO

(5.05 t 2.80)E+O0

(5.99 t 2.44)E+O0

(4.62 A 2.77)E+O0

(4.92 * 2.25)E+O0

(5.72 A 2.21)E+O0

(1.08 k 0.47)E+01

(4.80 *2.21 )E+O0

(5.78 A 2.50)E+O0

(5.73 k 2.56)E+O0

(4.96 f 2.14)E+O0

(1.17 t 0.47)E+01

(9.60 A2.65)E+O0

(1.17A 0.73)E+01

(4.04 * 2.39)E+O0

(5.58 k 2.12)E+O0

(4.23 & 2.49)E+O0

(-3.74 * 2.78)E+O0

(-3.18 A 2.84)E+O0

(-7.49 t 2.89)E+O0

(-3.86 A 2.82)E+O0

(-3.86 A 2.53)E+O0

(-5.53 ~ 2.80)E+O0

(-4.21 t 2.53)E+O0

(-5.40 A 2.74)E+O0

(-3.48 A 2.28)E+O0

(-2.64 * 2.82)E+O0

(-3.49 t 2.87)E+O0

(-6.91 k 2.83)E+O0

(4.64 t 1.87)E+O0

(-1.84 t 1.02)E+01

(-4.81 A2.12)E+O0

(-1 .18 A 0.30)E+01

(-6.41 A 2.81)E+O0

(-1 .86 * 2.68)E+O0

(-6.39 * 2.80)E+O0




Page 3 of 8

No. ofLocation Samples Arithmetic Mean k o Maximum * u Minimum t c

CS-137, pci/L

Upper Three Runs



U3R-3 at Road C

U3R-4 at Road A

Four Mile Creek

C-Canal

FM–2 at Road 4





H-008 Outfall


Pen Branch

K-011 Outfall at B Road

PB-3 at Road A–13.2

Steel Creek




L3R–2 Patterson Mill Road

L3R–3 at Highway 125


26

26

26

26

27

26

26

26

26

26

26

26

26

27

26

26

26

12

26

(0.67 f 1.87)E+O0

(0.23 ~ 2.12)E+O0

(0.38 A 2.35)E+O0

(-0.43 t 2.17)E+O0

(0.53 * 1.45)E+O0

(1.81A 1.74)E+01

(6.10 * 5.29)E+O0

(6.20 + 4.31)E+O0

(4.74 t 4.77)E+O0

(7.68 f 3.46)E+O0

(4.67 * 3.14)E+O0

(0.84 + 2.65)E+O0

(1.60 ~ 2.40)E+O0

(1.06 ~ 3.77)E+O0

(5.29 + 3.81)E+OO

(1.84 t 3.88)E+O0

(1.92 t 1.97)E+O0

(1.17 t 2.62)E+O0

(1.17* 0.89)E+01

(4.17 * 1.89)E+O0

(3.81 * 2.02)E+O0

(4.19 + 2.32)E+O0

(4.54 * 2.44)E+O0

(3.38 k 2.15)E+O0

(7.90 * 0.63)E+01

(1.73A 0.36)E+01

(1.89+ 0.38)E+01

(1.80 ~ 0.38)E+01

(1.44 * 0.32)E+01

(1.06A 0.35)E+01

(5.87 ~ 2.1O)E+OO

(8.39 * 2.94)E+O0

(1.04+ 1.04)E+01

(1.61A 0.28)E+01

(9.95 * 9.16)E+O0

(5.98 k 2.00)E+OO

(3.92 + 1.35)E+O0

(3.63 + 0.52)E+01

(-2.95 * 2.19)E+O0

(-6.49 i- 2.63)E+O0

(-4.41 k 2.20)E+O0

(-3.38 * 2.17)E+O0

(-2.39 t 2.30)E+O0

(-2.87 t 2,28)E+O0

(-0.34 t 2.56)E+O0

(-1 .04 A 1.85)E+O0

(-2.98 t 2.51)E+O0

(-1 .60 t 2.50)E+O0

(-0.56 t 1.96)E+O0

(-5.65 * 2.38)E+O0

(-3.20 i- 2.18)E+O0

(-1 .03 t 0.46)E+01

(-0.43 A 2.57)E+O0

(-1 .05 t 0.85)E+01

(-3.49 t 2.33)E+O0

(-5.41 * 2.29)E+O0

(3.06 + 2.73)E+O0

U-234, pc”ti

Upper Three Runs

U3R-4 at Road A 26 (9.26 A 6.23)E-02 (2.97 A 0.26)E-01 (3.24 t 0.84)E42

Four Mile Creek

FM-6 at Road A-12.2 26 (6.88 t 8.13)E+1 (3.01 * 0.22)E+O0 (5.65 ~ 1.20)E-02


—



Page 4 of 8

No. ofLocation Samples Arithmetic Mean * a Maximum * cs Minimum f cr

Pen Branch

PB-3 at Road A-13.2 27 (5.52 + 4.66)E-02 (2.08 * 0.25)E-01 (-0.67 A 5.65)E-03


L3R-2 (Weekly Grab) 26 (1.38 t 0.71)E-02 (2.51 A 0.61)E-02 (-3.10 t 3.83)E-03

L3R-2 Patterson Mill Road 26 (8.57 * 7.28)E-02 (3.06 A 0.31)E-01 (1.12* 0.80)E-02

U-235, pCi/L

Upper Three Runs

U3R-4 at Road A 26 (0.46 k 1.02)E-f)2 (4.62 A 0.81)E-02 (-7.14 A 1.91)E-03

Four Mile Creek

FM-6 at Road A-12.2 26 (5.29 A 7.12)E-02 (3.13 * 0.37)E-01 (1.98 A2.16)E413

Pen Branch

PB-3 at Road A-13.2 27 (3.17 A 4.72)E-03 (1.45 A 0.81)E-02 (-5.27 *2.61 )E-03


L3R-2 (Weekly Grab) 26 (-1 .71 * 3.17)E-03 (3.27 * 1.83)E43 (-9.06 k 1.14)E-03

L3R-2 Patterson Mill Road 26 (2.39 t 5.09)E+3 (1.33 A 0.57)E-02 (-7.02 * 2.41)E-03

U-238, pCi/L

Upper Three Runs

U3R-4 at Road A 26 (1.10 t 0.78)E-01 (4.14 t 0.30)E-01 (4.02 f 0.88)E-02

Four Mile Creek

FM-6 at Road A-12.2 26 (8.37 * 9.94)E-01 (3.85 k 0.27)E+O0 (7.61 * 1.13)E-02

Pen Branch

PB-3 at Road A-13.2 27 (4.82 +4.ll)E-02 (1.62 A 0.22)E-01 (0.33 + 1.07)E-02


L3R-2 (Weekly Grab) 26 (0.79 t 1.34)E-02 (2.44 * 0.66) E-2 (-3.82 A 0.66)E-02

L3R-2 Patterson Mill Road 26 (6.64 t 5.30)E-02 (2.22 t 0.25)E-01 (-4.25 t 7.65)E-03

Pu-238, pCi/L

Upper Three Runs

U3R-4 at Road A 26 (-0.78 * 7.03)E-02 (4.44 * 0.97)E-02 (-3.49 + 0.24)E-01

Four Mile Creek

FM-6 at Road A–12.2 26 (0.29 * 2.52)E-02 (4.19 * 0.96)E-02 (-9.50 + 2.79)E-02

Pen Branch

PB-3 at Road A-13.2 27 (-0.08 * 1.30)E-02 (3.57 * 0.95)E-02 (-5.29 * 0.61)E-02


—



Page 5 of 8

No. ofLocation Samples Arithmetic Mean * u Maximum f a Minimum + IS


L3R–2 (Weekly Grab) 26 (-0.16 * 1.22)E-02 (1.89 t 0.45)E-02 (-5.36 * 0.41)E-02

L3R–2 Patterson Mill Road 26 (0.73 * 1.03)E-02 (3.29 i 0.86)E-02 (-7.09 ~ 2.32)E-03

Pu-239, pCi/L

Upper Three Runs

U3R-4 at Road A 26 (0.46 * 3.09)E-03 (8.69 ~ 4.25)E-03 (-5.24 * 0.97)E-03

Four Mile Creek

FM-6 at Road A-12.2 26 (1.28 t 4.48)E-03 (1.57 t 0.56)E-02 (-5.73 A 1.19)E-03

Pen Branch

PB-3 at Road A–13.2 27 (1.46 ~ 3.20)E-03 (8.71 t 4.26)E-03 (-3.59 + 1.30)E-03


L3R–2 (Weekly Grab) 26 (0.04 ~ 2.51)E-03 (5.55 * 2.59)E-03 (-4.83 + 0.93)E-03

L3R–2 Patterson Mill Road 26 (0.87 t 2.70)E-03 (8.69 * 4.24)E-03 (-3.33 f 0.16)E-03

Sr-89,90, pCi/L

Upper Three Runs


U3R–3 at Road C

Four Mile Creek

FM–2 at Road 4


FM–3 F-Area effluent




H-008 Outfall

Pen Branch



PB-3 at Road A-13.2

12

12

12

12

12

12

12

12

12

4

12

14

(0.42 t 4.26)E-01

(0.61 f 3.58)E-01

(3.24 + 1.90)E+O0

(4.29 * 1.35)E+O0

(1.85A 2.41)E+O0

(2.10 t 2.O1)E+OO

(6.79 t 4.99)E+O0

(6.88 + 2.23)E+O0

(3.81 t 4.32)E-01

(3.73 f 2.07)E-01

(0.25 + 5.74)E-01

(2.73 * 2.14)E-01

(7.36 A 4.54)E-01

(7.24 * 4.85)E-01

(6.23 + 0.49)E+O0

(6.47 A 0.68)E+O0

(7.96 ~ 1.44)E+O0

(6.93 + 0.73)E+O0

(2.07 + 0.06)E+01

(1.10 * 0.08)E+01

(1.17 t 0.48)E+O0

(5.87 A 4.16)E-01

(1.06A 0.43)E+O0

(6.62 * 1.68)E-01

(-7.44 * 4.21 )E-01

(-6.56 * 3.77)E-01

(8.11 ~ 2.69)E-01

(1 .99* 0.44)E+O0

(-4.93 A 7.68)E-01

(0.02 + 3.05)E-01

(2.88 i- 0.25)E+O0

(4.04 * 0.53)E+O0

(-1 .59 ~ 3.43)E-01

(1 .60 t 4.37)E-01

(-6.89 k 3.38)E-01

(-0.20 * 1.19)E-01




Page 6 of 8

No. ofLocation Samples Arithmetic Mean * o Maximum A ts Minimum k cr

Steel Creek

SC-2A 1 mile above 12 (0.70 + 4.28)E-01 (6.75 *4.40)E-01 (-7.30 * 3.82)E-01Road B

SC-4 Steel Creek 12 (1.03 Y 0.87)E-01 (3.23 A 1.45)E-01 (0.25 ~ 1.35)E-01at Road A


L3R-1 A at Road B 12 (1.50 A 3.33)E-01 (6.29 * 4.28)E~l (-3.31 ~ 4.26)E-01

L3R-2 Patterson Mill Road 12 (1.45 *0.61)E41 (2.32 * 0.96)E-01 (6.50 k 9.17)E-02

L3R–3 at Highway 125 12 (0.30 * 2.06)E-01 (4.55 * 3.14)E-01 (-2.34 ~ 3.04)E-01

Gross Beta, pCi/L .

Tires Branch

TB-5 near Road C

Upper Three Runs



U3R-lA Treadway BridgeRoad 8-1

U3R-3 at Road C

U3R-4 at Road A

Four Mile Creek

C-Canal

FM-2 at Road 4


FM-3A below F-Areaeffluent

FM-6 at Road A-12.2

FM-A7 at Road A-7

H-008 Outfall

HP–50 Tntium FacilityOutfall

Pen Branch



PB-3 at Road A-13.2

26

26

26

51

26

26

27

25

26

26

26

26

27

26

4

26

27

(2.39 t 1.52)E+O0

(9.15 * 5.51)E-01

(1.74t 0.68)E+O0

(1.75 t 0.87)E+O0

(2.27 t 3.15)E+O0

(1.43 k 0.91)E+O0

(7.75 t 5.ll)E-01

(2.06 A 1.58)E+01

(1.64 t 0.82)E+01

(9.01 A 5.64)E+O0

(1.60 t 0.94)E+01

(2.43 + 1.02)E+01

(8.09 k 3.58)E+O0

(5.42 t 3.52)E+O0

(1.38 t 0.91)E+O0

(1.29 t 0.41)E+O0

(9.52 * 6.94)E-01

(7.24 + 0.87)E+O0

(2.19 * 0.60)E+O0

(3.82 A 0.65)E+O0

(4.82 A 0.74)E+O0

(1.60A 0.07)E+01

(4.80 k 0.63)E+O0

(1.86 t 0.48)E+O0

(5.51 A 0.21)E+01

(3.52 t 0.18)E+01

(2.30 ~ O.1O)E+O1

(3.94 * 0.17)E+01

(4.33 t 0.19)E+01

(1.54* 0.13)E+01

(1.78 + 0.09)E+01

(2.63 t 0.64)E+O0

(2.58 t 0.45)E+O0

(1.95 k 2.30)E+O0

(7.03 ~ 3.87)E+1

(-4.07 ~ 3.21)E-01

(6.36 ~ 4.37)E-01

(4.46 A 4.15)E-01

(2.53* 3.91)E-01

(3.30 A 3.61)E-01

(-1 .70 A 4.83)E-01

(3.08 * 0.62)E+O0

(5.69 k 0.65)E+O0

(1.94 ~ 0.51)E+O0

(2.83 ~ 4.31)E-01

(1.06 ~ 0.09)E+01

(1.91 ~ 0.33)E+O0

(7.72 t 4.60)E-01

(4.40 t 5.17)E-01

(1.89 ~ 3.63)E-01

(-2.60 A 7.49)E+1




Page 7 of 8

No. ofLocation Samples Arithmetic Mean * c Maximum k c Minimum * o

Steel Creek

SC-2A 1 mile above 26 (4.93 * 3.24)E+O0 (1.73* 0.27)E+01 (2.01 * 0.47)E+O0Road B

SC-4 Steel Creek 26 (1.43* 0.88)E+O0 (4.46 A 1.27)E+O0 (3.30 + 3.68)E-01at Road A


L3R-1 A at Road B 26 (2.09 * 0.91)E+O0 (4.26 + 0.70)E+O0 (7.46 * 4.07)E-01

L3R-2 Patterson Mill Road 26 (2.02 + 0.71)E+O0 (3.64 t 0.64)E+O0 (7.47 * 4.ll)E-01

L3R-3 at Highway 125 12 (1.58* 0.51)E+O0 (2.57 A 0.59)E+O0 (9.81 & 4.66)E-01

R-Area downstream of R-1 26 (9.46 f 6.56)E+O0 (2.94 + 0.14)E+01 (4.37 * 0.68)E+O0

Gross Alpha, pCVL

Tires Branch

TB-5 near Road C

Upper Three Runs



U3R-1 A Treadway BridgeRoad 6-1

U3R-3 at Road C

U3R-4 at Road A

Four Mile Creek

C-Canal

FM–2 at Road 4



FM-6 at Road A-12.2

FM-A7 at Road A–7

H-008 Outfall


26

26

26

51

26

26

27

25

26

26

26

26

27

26

(4.08 * 3.27)E+O0

(2.02 A 2.69)E-01

(1.29 t 1.O1)E+OO

(3.81 t 1.58)E+O0

(4.44 * 6.76)E+O0

(2.48 i- 1.37)E+O0

(7.86 * 4.38)E-01

(3.84 * 2.89)E+O0

(1.19 t 0.76)E+O0

(2.68 t 1.33)E+O0

(4.33 * 4.83)E+O0

(3.49 * 3.07)E+O0

(4.36 * 1.64)E+O0

(4.76 + 3.20)E+O0

(1.18 A 0.13)E+01

(1.02+ 0.42)E+O0

(4.89 A 0.76)E+O0

(8.99 t 1.00)E+OO

(2.99 * 0.14)E+01

(6.82 * 0.87)E+O0

(2.00 * 0.53)E+O0

(1.09A 0.12)E+01

(3.44 A 0.79)E+O0

(6.43 + 1.13)E+O0

(2.00 k 0.20)E+01

(1.21+ O.1O)E+O1

(8.16 + 1.15)E+O0

(1.58 k 0.12)E+01

(7.03 t 3.03)E-01

(-1 .72 ~ 1.35)E-01

(2.91 * 2.90)E+1

(1.08* 0.36)E+O0

(6.81 f 2.95)E-01

(6.42 k 2.80)E-01

(1.26 k 1.85)E-01

(1.07 f 9.27)E-01

(0.62 * 4.15)E-01

(7.89 * 3,78)E+1

(0.69 ~ 2.93)E-01

(8.92 ~ 7.19)E-01

(1.20 ~ 0.48)E+O0

(2.14 * 3.26)E-01

WSRC-TR-9FO031460 SRS Environmental Data for 1998

.



Page 8 of 8

No. ofLocation Samples Arithmetic Mean k u Maximum * o Minimum * a

Pen Branch

IGB-21 800 feet south 4 (6.08 A 5.98)E-01 (1.42 t 0.53)E+O0 (0.45 * 2.39)E-01of Road 6-1

K-011 Outfall at B Road 26 (4.38 A 6.70)E-01 (2.53 * 0.49)E+O0 (-2.57 * 1.61)E-01

PB-3 at Road A-13.2 27 (5.64 k 5.23)E-01 (2.02 * 0.53)E+O0 (-2.08 * 1.65)E-01

Steel Creek

SC-2A 1 mile above 26 (2.46 A 3.16)E+O0 (1.62 t 0.32)E+01 (3.11 *2.51 )E-01Road B

SC-4 Steel Creek 26 (0.98 k 1.14)E+O0 (5.37 * 1.24)E+O0 (-3.78 * 2.97)E-01at Road A


L3R-lA at Road B 26 (3.34 ~ 6.45)E-01 . (2.76* 0.73)E+O0 (-1 .85 ~ 1.26)E-01

L3R-2 Patterson Mill Road 26 (1.07A 0.72)E+O0 (2.41 * 0.59)E+O0 (0.33 * 2.ll)E-01

L3R-3 at Highway 125 12 (6.63 A 4.54)E-01 (1.62 A 0.52)E+O0 (-0.27 A 3.12)E-01

R-Area downstream of R-1 26 (2.90 A 3.45)E-01 (1.29 * 0.51)E+O0 (-2.39 t 1.21)E-01


t

Table 21Radioactivity in Savannah River Water

Page 1 of 2

No. ofLocation Samples Arithmetic Mean f IS Maximum t IS Minimum f cs

H-3, p~i

RNer Mile 120 52 (9.48 t 4.63)E+02 (2.54 + 0.06)E+03 (2.59 * 0.89)E+02

River Mile 140 52 (9.15 ~ 6.14)E+02 (2.43 t 0.11)E+03 (0.24 t 1.28)E+02

River Mile 150 52 (1.06 t 0.81)E+03 (2.71 ~ 0.13)E+03 (-0.39 * 1.36)E+02

River Mile 160 52 (0.92 + 1.36)E+02 (6.25 A 1.38)E+02 (-1 .14 + 1.30)E+02

Vogtle Discharge 51 (0.38 * 1.27)E+04 (7.22 + 0.07)E+04 (0.09 f 1.36)E+02

CO-60, pCi/L

Savannah River

River Mile 120 52 (1.42 f 4.61)E-01 (1.71+ 0.65)E+O0 (-8.41 A 4.87)E-01

River Mile 140 52 (1.44 * 8.06)E-01 (2.86 + 1.17)E+O0 (-1.38 i- 1.41)E+O0

River Mile 150 52 (0.41 t 4.55)E-01 (1.08A 0.32)E+O0 (-9.17 i- 5.92)E-01

River Mile 160 52 (0.58 + 4.97)E-01 (2,13+ 1,26)E+O0 (-1 .44 A 1.53)E+O0

Vogtle Discharge 52 (2.24 ~ 5.16)E-01 (2.25 + 1.08)E+O0 (-1 .38 * 0.75)E+O0

CS-137, pcti

River Mile 120 52 (1.00A 3.76)E-01 (1.17 fl.15)E+O0 (-9.33 k 5.59)E-01

River Mile 140 52 (1.17 A9.ll)E-01 (2.72 t 1.19)E+O0 (-3.73 * 1.25)E+O0

River Mile 150 52 (0.60 + 3.45)E-01 (9.30 f 5.02)E-01 (-9.00 t 6.07)E-01

River Mile 160 52 (0.01 i- 3.61)E-01 (8.70 f 3.83)E411 (-1 .14 t 0.55)E+O0

Vogtle Discharge 52 (0.31 ~ 3.87)E-01 (1.10 t 0.92)E+O0 (-9.20 + 8.00)E+l

Pu-238, pCiiL

River Mile 120 1 (-2.61 t 1.ll)E-03

River Mile 140 1 (-1 .58 t 1.28)E-03

River Mile 150 1 (-3.29 + 0.19)E-03

River Mile 160 1 (-2.74 ~ 1.16)E-03

Vogtle Discharge 1 (-1 .58 i 1.98)E-03

Pu-239, pCi/L

River Mile 120 1 (1.63 ~ 2.28)E-03

River Mile 140 1 (1.24 ~ 1.19)E-03

River Mile 150 1 (5.52 t 8.96)E-04

River Mile 160 1 (1.73+ 1.42)E-03

Vogtle Discharge 1 (-0.78 ~ 1.34)E-03

Sr-89,90

River Mile 120 1 (2.16 f 6.62)E+2

River Mile 140 1 (4.66 k 9.45)E-Q2



Table 21Radioactivity in Savannah River Water

Page 2 of 2

No. ofLocation Samples Arithmetic Mean ~ a Maximum ~ u Minimum ~ u

River Mile 150 1 (1.79* 1.09)E-01

River Mile 160 1 (2.85* 1.ll)E-01

Vogtle Discharge 1 (1.16 f 0.97)E-01

Gross Beta, pCi/L

River Mile 120 52 (1.60 t 0.49)E+O0 (3.02 k 0.35)E+O0 (4.48 t 5.16)E-01

River Mile 140 52 (1.78A 0.55)E+O0 (2.94 ~ 0.68)E+O0 (7.96 t 3.63)E-01

River Mile 150 52 (1.58 k 0.49)E+O0 (2.75 * 0.63)E+O0 (5.72 *4.61 )E-01

River Mile 160 52 (1.72 ~ 0.49)E+O0 (3.08 t 0.64)E+O0 (7.72 * 4.79)E-01

Vogtle Discharge 52 (1.82 t 0.89)E+O0 (5.91 t 0.47)E+O0 (-3.73 A 4.75)E-01

Gross Alpha, pCtiL

River Mile 120 52 (1.55 t 2.20)E-01 (8.95 t4.33)E-01 (-2.50 A2.09)E-01

River M]le140 52 (2.19 + 2.74)E-01 (9.75 t 4.23)E-01 (-1 .85 ~ 3.37)E-01

River Mile 150 52 (1.90 A2.38)E+1 (8.37 ~ 3.71)E-01 (-2.16 * 1.53)E-01

River Mile 160 52 (1.29 t2.67)E-01 (7.08 * 3.89)E-01 (-4.63 A 2.44)E4M

Vogtle Discharge 52 (2.31 * 3.13)E-01 (1.14 ~0.51)E+O0 (-2.54 *1 .80)E--O1



Table 22Summary of Savannah River Site Tritium Transport, 1960-1998

Page 1 of 1

Estimated Tritium Transport (Ci)

Based on Point-of-Release Based on Stream Based on Savannah River

Concentrations Concentrations and Concentrations andYear and Flow Ratesa Flow Rates Flow Rates

196019611962196319641965196619671968196919701971197219731974197519761977197819791980198119821983198419851986198719881989199019911992199319941995199619971998

64,000b69,000b58,000b97,000b

lll,ooob108,40084,90070,60063,80064,60036,90038,20046,80071,10059,90055,60059,60043,80037,60029,40024,90023,90032,20034,20032,80025,00027,80022,70019,30017,30016,10027,40013,80011,3008,8009,9007,5608,350

10,555

69,60083,00064,00096,900

131,600109,20097,80077,00067,20064,00043,20044,70047,30062,80054,60050,00047,40039,70035,30027,10028,80022,10031,30033,00032,60022,30022,30020,50018,30017,80015,60026,60013,10012,70010,40011,4008,0208,550

10,588

73,70077,00063,000

122,800143,000100,20078,30068,50061,80058,10031,80039,10045,30061,10046,00049,50051,10042,50036,60030,60030,70025,10030,60033,00033,20024,10022,10026,20014,60015,60014,50026,30013,80012,20010,90010,7008,9507,7009,420

a Includes direct releases to streams and migration from seepage basins and the Solid Waste Disposal Facility to streamsb Includes heat exchanger cooling water released from P-Area (of PAR Pond origin) to Steel Creek



Table 23Radioactivity in Drinking Water

Page 1 of 10

No. ofLocation Samples Arithmetic Mean * a Maximum k o Minimum t o

H-3, pCi/L

Onsite

105-C C-Area domesticwaterfaucet

105-K K-Area domesticwater faucet

105-L L-Area domesticwater faucet

221-F F-Area domesticwater faucet

221-H H-Area domesticwater faucet

241-24H H-Area domesticwater faucet

617-G Wackenhut TrainingFacility

616-G Class. yardlunchroom

661-G Firing Range(pumphouse)

679-T TNX domesticwater faucet

681-3G domesticwater faucet

701-12G Patrol Gate 7

701-1 3G Patrol Gate 6

701-1 F F-Area domesticwater faucet

701-1 H H-Area domesticwater faucet

701-3G Barnwell Gate

701-4G Williston Gate

701-5G Talatha Gate

701-6G Jackson Gate


703-A EOC (kitchen)



7

8

8

7

7

3

1

1

1

1

1

1

1

1

1

1

1

1

1

1

1

3

3

(0.74 t 1.03)E+02

(1.83 * 6.61)E+01

(0.18 t 9.60)E+01

(8.20 t 8.85)E+01

(-0.06 A 1.08)E+02

(-1 .00 t 1.09)E+02

(2.85 t 1.01)E+02

(-2.31 t 1.31)E+02

(1.01 t 0.15)E+03

(0.32 t 1.33)E+02

(0.48 + 1.42)E+02

(2.88 t 1.34)E+02

(2.43 k 0.15)E+03

(0.99 * 1.43)E+02

(1.80 A 1.33)E+02

(1.06A 1.43)E+02

(3.21 t 1.44)E+02

(6.26 t 1.46)E+02

(-2.62 * 1.30)E+02

(1.32 A 0.14)E+03

(1.81* 1.44)E+02

(5.24 * 7.84)E+01

(1.27A 1.74)E+02

(2.47 ~ 1.42)E+02

(1.01* 0.87)E+02

(1.84A 1.35)E+02

(1.71 A 1.31)E+02

(1.43 ~ 1.31)E+02

(0.24 k 1.26)E+02

(1.38 t 1.36)E+02

(2.37 k 1.31)E+02

(-4.18 * 6.07)E+01

(-0.69 t 1.31)E+02

(-1.51 * 1.31)E+02

(-0.90 f 1.40)E+02

(-1 .83 t 1.29)E+02

(-1 .74 A 1.28)E+02

(-0.17 * 1.26)E+02

(-7.42 k 8.83)E+01



.


Page 2 of 10

No. ofLocation Samples Arithmetic Mean t o Maximum t o Minimum t a

704-S S-Area domestic 1water faucet

706-N lunchroom 1

708-A A-Area cafeteria 1(restroom)

730-4B lunchroom 3

735-7G PAR Pond lab 1

760-G Forestry Building 1

772-D lunchroom 7

772-F F-Area domestic 3water faucet

Z-Area Building 704-Z 1

Treatment Plants—Raw

Beaufort Public Water 12Works

N. Augusta Public Water 12Works

Savannah Public Water 12Works

EMS Sampler

BeaufortPublicWater 25Works

Treatment Plants—Finished

BeaufortPublicWater 12Works

N. Augusta Public Water 12Works

Savannah Public Water 12Works

CO-60, pC”fi

Onsite

105-C C-Area domestic 7 (-0.21 * 2.68)E+O0 (2.51 + 2.08)E+O0 (-5.21 t 2.52)E+O0water faucet

105-K K-Area domestic 8 (1.10 i 3.43)E+O0 (4.90 A 2.58)E+O0 (+.79 * 2.75)E+O0water faucet

105-L L-Area domestic 8 (0.42 t 2.28)E+O0 (5.15 t 2.25)E+O0 (-2.05 + 2.25)E+O0water faucet

221-F F-Area domestic 7 (-1 .11 t 2.99)E+O0 (4.58 + 2.63)E+O0 (-5.23 + 2.48)E+O0water faucet

(0.16 + 1.32)E+02

(2.98 f 1.44)E+02

(-0.17 + 1.32)E+02

(-7.47 * 7.94)E+01

(-2.14 * 1.31)E+02

(0.76 t 1.42)E+02

(-1 .82 + 7.50)E+01

(-8.52 * 6.25)E+01

(-1 .89 * 0.92)E+02

(7.38 * 0.34)E+02

(1 .03+ 1.28)E+02

(8.99 * 3.78)E+02

(7.27 t 0.22)E+02

(7.28 * 2.67)E+02

(1 .32* 1.11)E+02

(8.29 t 2.95)E+02

(1.67A 8.60)E+01

(0.69 * 1.37)E+02

(-0.17 * 1.26)E+02

(1.06* 0.09)E+03

(2.88 * 0.88)E+02

(1.58* 0.12)E+03

(1.60* 0.12)E+03

(1.14 * 0.14)E+03

(2.97 f 1.33)E+02

(1.22+ 0.13)E+03

(-1 .26 t 1.28)E+02

(-1 .25 * 1.31)E+02

(-1 .40 t 1.30)E+02

(3.15 * 0.97)E+02

(-1.15 * 1.19)E+02

(4.26 ~ 1.28)E+02

(1.64+ 1.27)E+02

(3.35 11 .36)E+02

(-0.37 * 1.34)E+02

(4.30 t 1.28)E+02




Page 3 of 10

No. ofLocation Samples Arithmetic Mean ~ IS Maximum t c Minimum * c







681-3G domesticwater faucet




701–1 H H-Area domesticwater faucet



701-5G Talatha Gate

701-6G Jackson Gate


703-A EOC (kitchen)



704-S S-Area domesticwater faucet

706-N lunchroom

708-A A-Area cafeteria(restroom)

730-4B lunchroom

735-7G PAR Pond lab

760-G Forestry Building

772–D lunchroom

7

3

1

1

1

1

1

1

1

1

1

1

1

1

“1

1

1

3

3

1

1

1

3

1

1

7

(0.47 k 1.98)E+O0

(2.27 * 3.03)E+O0

(-1 .62 + 1.81)E+O0

(-2.23 * 2.55)E+O0

(3.81 t 1.98)E+O0

(1.72 ~ 2.43)E+O0

(-0.33 * 2.49)E+O0

(-6.39 t 2.58)E+O0

(1.18 t 2.32)E+O0

(-0.70 t 2.69)E+O0

(-0.56 * 2.14)E+O0

(3.41 * 1.86)E+O0

(3.57 + 2.08)E+O0

(1.02 t 2.28)E+O0

(-0.08 k 1.43)E+O0

(2.47 ~ 2.46)E+O0

(2.18 ~ 1.40)E+O0

(0.22 * 3.16)E+O0

(1.20 t 1.17)E+O0

(1.93 t 2.46)E+O0

(-0.53 * 1.93)E+O0

(-2.68 * 2.57)E+O0

(0.40 * 2.74)E+O0

(3.52 * 2.07)E+O0

(0.55 t 1.53)E+O0

(0.73 * 2.1O)E+OO

(3.81 * 2.81)E+O0

(5.33 A 2.68)E+O0

(3.46 A 2.60)E+O0

(2.38 A 2.07)E+O0

(3.03 + 1.50)E+O0

(3.17 * 1.80)E+O0

(-1 .65 t 2.71)E+O0

(-0.73 k 2.53)E+O0

(-2.84 * 2.70)E+O0

(0.05 * 1.30)E+O0

(-2.43 ~ 2.26)E+O0

(4.12 + 2.94)E+O0



Page 4 of 10

No. ofLocation Samples Arithmetic Mean + u Maximum * o Minimum * o

772-F F-Area domestic 3 (-0.36 t 3.52)E+O0 (2.53 + 2.36)E+O0water faucet

(-4.28 t 2.59)E+O0

Z-Area Building 704-Z


Beaufort Public WaterWorks

N. Augusta Public WaterWorks

Savannah Public WaterWorks

EMS Sampler






1 (-2.47 * 2.72)E+O0

12 (3.83 t 6.12)E-01

12 (-0.48 ~ 2.49)E+O0

12 (0.64 ~ 1.53)E+O0

25 (1.23A 0.44)E+O0

12 (-1.14 ~ 2.18)E+O0

12 (0.49 t 2.27)E+O0

12 (0.97 t 2.54)E+O0

(5.02 + 2.39)E+O0

(2.86 k 2.93)E+O0

(3.00 t 2.41)E+OO

(5.65 * 2.63)E+O0

(2.88 t 2.70)E+O0

(3.98 * 2.16)E+O0

(4.62 A 2.ll)E+OO

(-2.66 * 2.80)E+O0

(-5.46 + 2.85)E+O0

(-1 .70 t 2.58)E+O0

(-3.48 k 2.46)E+O0

(-4.16 A 2.86)E+O0

(-3.88 * 2.37)E+O0

(-3.01 + 2.27)E+O0

CS-137, pcfi

Onsite

105-C C-Area domestic 7 (-0.22 t 2.75)E+O0 (5.57 + 2.02)E+O0 (-2.49 * 2.30)E+O0water faucet

105-K K-Area domestic 8 (1.05+ 2.55)E+O0 (4.27 t 1.92)E+O0 (-2.38 A 2.50)E+O0water faucet

105-L L-Area domestic 8 (1.53 ~ 8.20)E-01 (1.32 f 2.15)E+O0 (-0.72 k 2.19)E+O0water faucet

221-F F-Area domestic 7 (-0.74 * 4.ll)E+OO (5.03 A 2.13)E+O0 (-7.63 * 2.26)E+O0water faucet

221-H H-Area domestic 7 (0.27 t 1.69)E+O0 (2.68 t 2.37)E+O0 (-1 .61 t 2.53)E+O0water faucet

241–24H H-Area domestic 3 (7.59 * 2.06)E-01 (0.95 * 2.34)E+O0 (0.54 t 2.09)E+O0water faucet

617-G Wackenhut Training 1 (-2.97 A 1.51)E+O0Facility

618-G Class. yard 1 (-2.70 * 2.30)E+O0lunchroom

661-G Firing Range 1 (1.52 t 1.92)E+O0(pumphouse)




Page 5 of 10

No. ofLocation Samples Arithmetic Mean ~ c Maximum i-c Minimum ~ a


681-3G faucet







701-5G Talatha Gate

701-6G Jackson Gate


703-A EOC (kitchen)




706-N lunchroom


730-4B lunchroom

735-7G PAR Pond lab


772-D lunchroom







1

1

1

1

1

1

1

1

1

1

1

1

3

3

1

1

1

3

1

1

7

3

1

12

12

12

(-1 .24 t 2.47)E+O0

(0.15 k 1.99)E+O0

(2.08 * 2.25)E+O0

(-2.21 t 2.35)E+O0

(-1 .25 * 2.34)E+O0

(3.38 * 2.29)E+O0

(2.38 * 1.89)E+O0

(-1 .04 t 2.07)E+O0

(-0.59 + 2.04)E+O0

(1.31+ 1.43)E+O0

(1.46+ 2.41)E+O0

(-2.82 A 1.51)E+O0

(-0.42 * 1.35)E+O0

(-1.77 A 2.38)E+O0

(0.45 t 2.26)E+O0

(-4.57 t 2.43)E+O0

(1.01 * 2.26)E+O0

(-0.06 & 1.21)E+O0

(-0.34 A 2.ll)E+OO

(1.23* 1.17)E+O0

(1.27 * 1.1O)E+OO

(1.27* 1.79)E+O0

(3.00 A 2.09)E+O0

(8.70 t 58.8)E42

(1.24 t 1.76)E+O0

(-1 .38 t 2.52)E+O0

(0.68 * 2.39)E+O0

(0.77 k 1.15)E+O0

(1.09*1 .88)E+O0

(2.76 A 2.34)E+O0

(3.33 * 2.31)E+O0

(3.33 f 2.20)E+O0

(3.49 * 2.23)E+O0

(3.23 k 2.16)E+O0

(-1 .92 * 2.18)E+O0

(-3.95 t 2.21)E+O0

(-1 .33 + 1.41)E+O0

(-0.15 * 2.21)E+O0

(0.08 t 2.37)E+O0

(-1 .99 A 2.31)E+O0

(-1 .88 t 2.18)E+O0

(-4.68 k 2.51)E+O0




Page 6 of 10

No. ofLocation Samples Arithmetic Mean + a Maximum t c Minimum * o

EMS Sampler

Beauforl PublicWater 25 (-0.1 Ot 0.41)E+OO (4.22 ~ 2.21)E+O0 (-3.84 * 2.33)E+O0Works


BeaufortPublicWater 12 (-0.36 ~ 1.80)E+O0 (1.50+ 2.18)E+O0 (-3.84 f 2.23)E+O0Works

N. Augusta PublicWater 12 (0.34 + 1.63)E+O0 (2.76 * 2.33)E+O0 (-2.25 * 1.64)E+O0Works

Savannah Public Water 12 (0.85 t 1.86)E+O0 (3.66 * 2.1 O)E+OO (-3.17 + 2.13)E+O0Works

Sr-89,90, pCi/L

Onsite

105-(2 C-Area domesticwater faucet



221–F F-Area domesticwater faucet

221–H H-Area domesticwater faucet

241–24H H-Area domesticwater faucet





701–12G Patrol Gate 7


701–1 F F-Area domesticwater faucet




1

1

1

1

1

1

1

1

1

1

1

1

1

1

1

1

(2.73 * 3.15)E-01

(0.22 + 3.93)E41

(-1.90 * 4.09)E-01

(-1 .29 t 3.71 )E-01

(-1 .42 * 3.81)E+1

(-1 .94 * 3.78)E-01

(-3.67 * 3.41 )E-01

(4.72 * 4.39)E-01

(-2.14 * 4.00)E41

(1.23 ~ 3.91 )E-01

(-3.84 * 3.31 )E-01

(-0.68 f 3.80)E+1

(0.70 * 3.97)E-01

(2.52 f 3.85)E41

(-0.01 t 2.65)E-01

(-1 .15 * 3.46)E-01


——.



Page 7 of 10

No. ofLocation Samples Arithmetic Mean * u Maximum A a Minimum * o

701–5G Talatha Gate 1 (-0.71 * 3.49)E41

701-6G Jackson Gate 1 (-2.22 * 3.70)E-01

701-8G Patrol Gate 8 1 (0.10 * 3.57)E-01

703-A EOC (kitchen) 1 (5.42 * 3.09)E41

704-F F-Area domestic 1 (-1 .86 ~ 3.64)E411water faucet

704-H H-Area domestic 1 (-1 .58 * 3.78)E-01water faucet

704-S S-Area domestic 1 (5.62 * 4.20)E-01water faucet

708-A A-Area cafeteria 1 (-2.59 + 3.63)E-01(restroom)

730-4B lunchroom 1 (1.12 * 4.13)E-01

735-7G PAR Pond lab 1 (1.17 i- 3.70)E-01

760-G Forestry Building 1 (0.62 * 4.33)E-01

772-D lunchroom 1 (1.11* 4.08)E-01

772-F F-Area domestic 1 (2.99 t 5.08)E-01water faucet

Z-Area Building 704-Z 1 (0.24 A 4.24)E-01

Gross Beta, pCi/L

Onsite

105-C C-Area domesticwater faucet









7

8

8

7

7

3

1

1

1

(6.76 * 7.28)E41

(1.42 t 0.46)E+O0

(1.28* 0.39)E+O0

(4.76 t 4.30)E-01

(4.11 A 3.09)E41

(2.23 A 0.58)E+O0

(6.75 A 4.95)E-01

(1.38* 0.56)E+O0

(2.18 t 0.57)E+O0

(1 .73* 0.54)E+O0 (-1 .16 * 4.20)E-01

(2.03 t 0.60)E+O0 (4.60 * 4.94)EW1

(2.09 k 0.59)E+O0 (9.50 * 4.84)E411

(1.04* 0.46)E+O0 (-0.56 A 4.42)E+1

(7.83 + 5.00)E-01 (-0.08 A 4.89)E-01

(2.85 * 0.65)E+O0 (1.69* 0.66)E+O0



Page 8 of 10

No. ofLocation Samples Arithmetic Mean * a Maximum *IS Minimum t a

1

1

1

1

1

1

1

1

1

1

1

1

3

3

1

1

1

3

1

1

7

3

1

12

12

12

679-T TNX domestic (3.85 + 0.73)E+O0water faucet

681–3G faucet



701–1 F F-Area domesticwater faucet

701–1 H H-Area domesticwater faucet

701-3G Bamwell Gate


701-5G Talatha Gate

701-6G Jackson Gate


703-A EOC (kitchen)




706-N lunchroom


730-4B lunchroom

735-7G PAR Pond lab

760-G Forestfy Building

772-D lunchroom


Z-Area Building704-Z





(3.37 t 0.64)E+O0

(1.04 t 0.58)E+O0

(3.26 A 5.13)E-01

(3.99 ~ 5.04)E-01

(1.1of 0.60)E+O0

(0.49 + 4.45)E-01

(-0.43 * 4.34)E-01

(2.48 + 0.61)E+OO

(1.30 t 0.57)E+O0

(-4.14 * 4.68)E+1

(0.77 + 5.46)E+1

(0.12 t 2.07)E-01

(1.21A 0.55)E+O0

(7.40 t 5.85)E411

(2.63 * 5.54)E-01

(-1 .86 f 5.21)E-01

(7.44 + 8.25)E-01

(2.15 t 0.60)E+O0

(1.14 t 0.54)E+O0

(2.65 t 0.22)E+O0

(1.28+ 0.31)E+O0

(6.22 * 5.77)E-01

(1.69 t 0.14)E+O0

(1.48 t 0.49)E+O0

(1.43 t 0.29)E+O0

(1.48* 4.99)E-01

(1.57* 0.59)E+O0

(1.70* 0.60)E+O0

(2.97 + 0.64)E+O0

(1.58* 0.50)E+O0

(2.50 t 0.44)E+O0

(2.33 + 0.54)E+O0

(1.97* 0.59)E+O0

(-2.26 * 4.24)E-01

(5.70 t 3.16)E-01

(2.46 ~ 4.55)E-01

(2.33 t 0.61)E+O0

(9.67 * 6.05)E-01

(1.10 A 0.54)E+O0

(6.87 t 5.06)E-01

(1.08* 0.52)E+O0




Page 9 of 10

No. ofLocation Samples Arithmetic Mean * c Maximum A a Minimum * G

EMS Sampler

Beaufort PublicWater 25 (1.30 * 0.18)E+O0 (2.68 * 0.65)E+O0 (0.10 * 1.1O)E+OOWorks


Beaufort PublicWater 12 (1.54 * 0.47)E+O0 (2.47 f 0.60)E+O0 (9.68 t 4.09)E-01Works

N. Augusta PublicWater 12 (9.66 A 2.70)E-01 (1.37 * 0.57)E+O0 (3.75 * 4.31)E-01Works

Savannah PublicWater 12 (1.47 f 0.59)E+O0 (2.84 * 0.62)E+O0 (5.65 * 4.79)E-01Works

Gross Alpha, pCf/L

Onsite

105-C C:Area domesticwater faucet










681-3G faucet





701-3G Bamwell Gate

7

8

8

7

7

3

1

1

1

1

1

1

1

1

1

1

(4.58 f 5.90)E+1

(1.03 t 3.78)E41

(5.17 A 2.37)E+1

(9.82 k 4.58)E+1

(1.39 t 0.79)E+O0

(1.50 * 1.06)E+O0

(4.91 f 3.63)E-01

(2.09 t 0.70)E+O0

(3.99 t 0.73)E+O0

(0.71 ~ 3.38)E-01

(2.98 t 0.70)E+O0

(2.28 t 3.50)E-01

(8.88 * 3.86)E+1

(2.02 t 0.71)E+O0

(6.22 * 4.59)E-01

(3.07 k 2.88)E41

(1.65 t 0.62)E+O0 (-1.00 ~ 2.76)E-01

(9.53 A 5.22)E-01 (-2.36 A 1.76)E-01

(7.97 t 4.33)E-01 (2.13 f 3.32)E-01

(1.76 k 0.62)E+O0 (5.76 t 4.28)E-01

(2.55 A 0.73)E+O0 (7.43 * 3.55)E-01

(2.57 A 0.82)E+O0 (4.54 A 4.60)E-01


— —. —..~,.-,



Page 10 of 10

No. ofLocation Samples Arithmetic Mean * ci Maximum * a Minimum + a

701-4G Williston Gate 1

701–5G Talatha Gate

701-6G Jackson Gate


703-A EOC (kitchen)




706-N lunchroom


730-4B lunchroom

735-7G PAR Pond lab


772-D lunchroom







EMS Sampler






1

1

1

1

3

3

1

1

1

3

1

1

7

3

1

12

12

12

25

12

12

12

(0.64 t 2.23)E-01

(1.01 ~ O.ll)E+O1

(1.66+ 0.50)E+O0

(4.14 f 2.96)E-01

(9.77 t 5.38)E-01

(8.50 k 8.09)E+1

(9.72 A 6.61)E-01

(6.51 t 4.86)E-01

(9.77 t 5.38)E41

(2.43 t 3.74)E-01

(1.02 t 0.23)E+O0

(4.29 * 4.45)E-01

(9.51 + 5.04)E-01

(4.17 t 2.75)E-01

(8.76 A 3.64)E41

(4.44 + 4.49)E41

(2.20 * 0.85)E-01

(1.73 f 3.62)E-01

(0.27 * 1.51)E-01

(3.54 t 1.05)E-01

(-0.31 + 2.53)E-01

(-0.09 + 1.17)E-01

(0.18 A 2.84)E41

(1.77 ~ 0.58)E+O0

(1.48* 0.60)E+O0

(1.27 ~ 0.61)E+O0

(6.97 * 4.39)E-01

(1 .20* 0.49)E+O0

(6.44 k 4.ll)E-01

(1.05A 0.46)E+O0

(3.07 ~ 2.93)E-01

(9.53 t 4.98)E-01

(2.57 f 3.89)E-01

(2.14 ~ 3.25)E-01

(6.34 + 4.69)E-01

(2.35 t 3.31)E-01

(2.26 t 3.54)E-01

(8.31 A 5.03)E-01

(-1 .20 * 2.43)E-01

(4.84 f 4.68)E-01

(-1 .57 * 2.69)E-01

(-2.29 + 1.41)E-01

(-1 .79 A 3.54)E-01

(-3.42 * 2.84)E-01

(-6.24 + 3.21)E-01

(-1 .52 k 3.05)E-01

(-2.64 * 1.91)E-01


+


Cu

‘5Y

0mA!

+1



c.-

+1

H

?3.0<

+1w.

+1 +1mmul~

+1 +1

WSRC-TR-98-00314

76 SRS Environmental Data for 1998————..-


Table 25Radioactivity in Terrestrial Food Products — Milk

Page 1 of 2

No. ofLocation Samples Arithmetic Mean k cr Maximum f IS Minimum ~ IS

Communities Around SRS

Dairy (Major Distributor) 12 (3.82 * 7.17)E+01 (1.83* 0.62)E+02 (-0.93 * 1.36)E+02

Denmark, S.C., dairy 12 (1.58 * 1.15)E+02 (2.89 * 1.31)E+02 (-6.76 * 9.65)E+01

Girard, Ga., dairy 12 (1.53 t 0.79)E+02 (2.75 * 1.26)E+02 (0.30 * 1.32)E+02

Gracewood, Ga., dairy 11 (1.40 t 0.89)E+02 (3.05 * 0.88)E+02 (0.38 t 1.30)E+02

Jackson, S.C., dairy 11 (5.38 A 0.97)E+02 (6.83 t 1.29)E+02 (4.02 Y 1.30)E+02

Waynesboro, Ga., dairy 12 (0.50 A 1.36)E+03 (4.81 k 0.08)E+03 (–1.25 t 1.32)E+02

CO-60, pCi/L


Dairy (Major Distributor) 12 (-0.26 * 1.75)E+O0 (2.18 * 1.19)E+O0 (-2.97 + 2.60)E+O0

Denmark, S.C., dairy 12 (1.02* 1.91)E+O0 (5.22 * 1.27)E+O0 (-1 .89 * 1.60)E+O0

Girard, Ga., dairy 12 (0.38 * 2.O1)E+OO (3.65 * 1.20)E+O0 (-2.97 * 1.82)E+O0

Gracewood, Ga., dairy 12 (0.28 A 1.48)E+O0 (2.87 * 1.06)E+O0 (-2.73 A 1.35)E+O0

Jackson, S.C., dairy 10 (0.60 * 1.44)E+O0 (2.34 * 1.18)E+O0 (-2.31 t 1.71)E+O0

Waynesboro, Ga., dairy 12 (0.48 *2.15)E+O0 (4.00 * 1.18)E+O0 (-2.43 * 1.42)E+O0

CS-137, pci/L


Dairy (Major Distributor) 12 (2.18 *2.06)E+O0 (7.39 A 1.98)E+O0 (-1 .39 t 2.16)E+O0

Denmark, S.C., dairy 12 (3.68 * 1.69)E+O0 (7.87 * 2.26)E+O0 (1.43* 1.03)E+O0

Girard, Ga., dairy 12 (1.38 k 1.53)E+O0 (4.38 * 1.ll)E+OO (-0.93 * 1.24)E+O0

Gracewood, Ga., dairy 12 (1.31* 0.94)E+O0 (3.43 + 0.97)E+O0 (-0.18 * 1.07)E+O0

Jackson, S.C., dairy 10 (7.65 *6.85)E-01 (1.78* 1.00)E+OO (-0.30 f 1.28)E+O0

Waynesboro, Ga., dairy 12 (1.67* 1.05)E+O0 (3.59 * 1.O1)E+OO (0.06 t 1.50)E+O0

Sr-90, pCi/L


Dairy (Major Distributor) 2 (0.45 * 1.12)E+O0 (1.24 * 0.96)E+O0 (+.38 * 9.67)E-01

Denmark, S.C., dairy 2 (5.36 * 3.39)E-01 (7.76 * 9.73)E-01 (2.97A 9.67)E41

Girard, Ga., dairy 2 (-0.95 * 5.48)E-01 (2.92 * 9.48)E-01 (-4.82 * 8.84)E41

Gracewood, Ga., dairy 2 (2.47 t 1.38)E+O0 (3.45 t 1.23)E+O0 (1.50* 1.O1)E+OO

Jackson, S.C., dairy 2 (0.89 A 1.26)E+O0 (1.78A 0.96)E+O0 (0.00* 8.60)E-01

Waynesboro, Ga., dairy 2 (0.35 * 1.06)E+O0 (1.10 t 1.00)E+OO (-3.98 + 8.97)E-01


Table 25Radioactivity in Terrestrial Food Products — Milk

Page 2 of 2

No. ofLocation Samples Arithmetic Mean * m Maximum *IS Minimum * cr

Sr-89,90, pCi/L

Communities around SRS

Dairy (Major Distributor) 1 (1.36+ 0.90)E+O0

Denmark, S.C., dairy 1 (1.47+ 0.74)E+O0

Girard, Ga., dairy 1 (7.84 * 8.75)E-01

Gracewood, Ga., dairy 1 (1.08* 0.88)E+O0

Jackson, S.C., dairy 1 (7.81 ~ 8.71)E411

Waynesboro, Ga., dairy 1 (1.95 t 8.45)E-01



Table 26Radioactivity in Aquatic Food Products — Freshwater Fish

Page 1 of 19

No. ofLocation Samples Arithmetic Mean ~ c Maximum * a Minimum * a

Note: Not enough fish could be collected for composite samples from the FM-6 at RoadA-12.2 and the P8-3 atRoad A-13.2 locations. Therefore, there are no data from these locations.

H-3, pCUg

Offsite (Edible)

New Savannah Bluff Lock and Dam (formerly Augusta Lock and Dam)

Bass

Bowfin

Bream

Freshwater Catfish

Sucker

Beaver Dam Creek River Mouth

Bass

Bream

Freshwater Catfish

Four Mile Creek River Mouth

Bass

Bowfin

Bream

Freshwater Catfish

Sucker

HwY-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker

L3R Creek River Mouth

Bass

Bream

FreshwaterCatfish

Steel Creek River Mouth

Bass

Bowfin

Bream

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(6.11 * 6.42)E-02

(4.23 ~ 2.73)E-02

(7.68 * 2.25)E-02

(1.04* 0.79)E+1

(1.12 i- 0.48)E+1

(6.88 t 1.31)E-02

(4.73 * 2.23)E-02

(5.75 * 8.26)E-02

(3.92 * 5.77)E+O0

(8.95 ~ 5.71)E-01

(3.37 ~ 2.80)E-01

(7.72 + 1.35)E-01

(6.13 * 5.83)E-01

(4.02 t O.ll)E-01

(5.47 * 3.23)E-01

(4.14 t 1.02)E-01

(1.95 * 0.35)E-01

(1.20 f 0.23)E-01

(5.65 A 3.70)E-01

(5.62 ~2.48)E+l

(6.45 ~ 0.95)E-01

(8.97 *4.72)E-01

(4.79 * 1.03)E-01

(7.07 *3.75)E-01

(1.27* 1.26)E-01

(6.10 *2.89)E-02

(9.55 *5.87)E-02

(1.91 t 1.00)E-01

(1.50 * 0.33)E-01

(8.08 * 3.97)E-02

(7.21 k 2.69)E-02

(1.53 A 0.56)E-01

(1.06 ~ O.O1)E+O1

(1.45* 0.03)E+O0

(5.84 * 0.54)E-01

(9.23 ~ 0.41)E+1

(1.29 ~ 0.04)E+O0

(4.10 ~ 0.53)E-01

(9.19 t 0.59)E-01

(4.91 * 0.53)E-01

(2.27 * 0.52)E-01

(1.46 k 0.27)E-01

(9.92A 0.86)E-01

(8.46 A 0.69)E41

(7.14* 1.42)E-01

(1.44 * 0.06)E+O0

(5.90 * 0.57)E-01

(1.07* 0.06)E+O0

(-0.08 * 9.60)E-02

(1.10 * 3.26)E-02

(5.18 +4.17)E-02

(0.34 * 1.03)E-01

(5.71 *2.90)E-02

(5.48 * 5.51)E-02

(2.88 k2.55)E-02

(0.45 k 5.55)E-02

(3.13 * 0.67)E-01

(3.12 *0.21)E41

(3.25 * 4.95)E-02

(6.62 + 0.49)E-01

(2.74 * 0.21)E-01

(3.89 k 0.53)E-01

(3.38 & 0.60)E-01

(2.99 * 0.47)E41

(1.57* 0.38)E-01

(1.04 * 0.31)E-01

(3.35 * 0.30)E-01

(3.89 + 0.31)E-01

(5.37 * 1.38)E-01

(5.78 k 0.48)E-01

(3.86 * 0.60)E-01

(3.23 * 0.42)E-01




Page 2 of 19

No. ofLocation Samples Arithmetic Mean ~ o Maximum * cr Minimum * a

Freshwater Catfish 3 (6.20 * 0.31)E-01 (6.50 t 0.42)E411 (5.88 * 0.59)E+1

Sucker 3 (6.93 * 1.32)E-01 (8.24 * 0.30)E411 (5.61 * 0.28)E+1

U3R Creek River Mouth

Bass 3 (4.17 ~ 5.27)E-01 (1.02 i- 0.05)E+O0 (5.81 * 4.21)E-02

Bream 3 (5.37 ~ 4.67)E-01 (1 .07 f 0.04)E+O0 (1 .83+ 0.31)E-01

Freshwater Catfish 3 (5.03 k 5.29)E-02 (0.93 * 1.16)E-01 (-0.09 *1 .08)E-01

CO-60, pCilg

Offsite (Edible)


Bass

Bowfirr

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

HwY-17 Bridge Area

Bass

Bream

Freshwater Catfish

HwY-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(-0.48 * 1.30)E-02

(-0.45 t 2.17)E-02

(0.82 f 1.14)E-02

(-0.13 * 1.70)E-02

(-0.11 A 1.64)E-02

(1.58 ~ 1.12)E-02

(-0.74 + 1.50)E-02

(0.09 * 1.98)E-02

(1.53+ 0.29)E+2

(-0.27 t 1.27)E-02

(1.23& 0.42)E-02

(1.07+ 0.68)E-02

(-0.21 * 1.56)E-02

(0.85 t 2.32)E-02

(-0.47 A 2.93)E-02

(2.29 k 6.51)E-03

(1.47* 0.85)E+2

(8.36 ~ 6.1O)E-O3

(1.38 ~ 0.22)E-02

(4.43 + 6.18)E-03

(0.68 * 1.04)E-02

(1.01 * 1.48)E42

(1.48 A 1.50)E-02

(2.09 f 1.68)E42

(1.82 t 1.49)E-02

(1.62 t 1.63)E-02

(2.23 t 1.31)E-02

(0.73 t 1.54)E-02

(1.94 k 1.50)E-02

(1.87 * 1.25)E-02

(0.78 + 1.54)E-02

(1.56 t 1.41)E-02

(1.54 t 0.76)E-02

(1.23 t 1.55)E-02

(3.00 t 0.92)E-02

(1.51* 1.28)E-02

(0.62 t 1.72)E-02

(2.35 t 0.68)E-02

(1.53 t 0.59)E42

(1.58* 0.65)E-02

(1.12 t 0.69)E-02

(1.72 k 1.45)E-02

(-1 .32 t 1.54)E-02

(-2.80 t 1.65)E-02

(-0.08 t 1.40)E-02

(-1 .26 t 1.50)E-02

(-1 .66 * 1.67)E-02

(0.29 11.26)E-02

(-2.26 t 1.29)E-02

(-2.00 t 1.35)E-02

(1.36 t 1.55)E-02

(-1 .67 t 1.48)E-02

(0.76 * 1.57)E-02

(0.29 * 1.74)E-02

(-1 .86 t 1.63)E-02

(-1 .61 t 1.58)E-02

(-3.84 t 1.70)E-02

(-0.52 A 1.51)E-02

(6.51 f 5.89)E-03

(4.01 * 6.70)E-03

(1.16* 0.43)E-02

(-0.86 A 7.16)E-03

(-0.36 * 1.57)E-02


———



Page 3 of 19

No. ofLocation Samples Arithmetic Mean ~ c Maximum & o Minimum ~ a


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

Stokes Bluff Landing

Bass

Bream

Freshwater Catfish


Bass

Bream

Freshwater Catfish

Onsite (Edible)

❑eaver Dam Creek (400-D)

Bream

L-Lake

Bass

Bream

Freshwater Catfish

L3R-2 Patterson Mill Rd

Bass

Bream

PAR Pond

Bass

Bream

Pond B

Bass

Bream

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(1.67* 0.79)E-02

(9.11 t 1.60)E-03

(2.20 * 1.78)E-02

(2.57 A 1.31)E-02

(1.01 * 1.37)E-02

(4.00 t 1.71)E-02

(1.10 A 0.99)E-02

(0.73 A 1.25)E-02

(0.44 * 1.38)E-02

(2.18 * 2.39)E-02

(-1.21 * 0.41)E-02

(8.84 t 6.38)E-03

(0.04 t 2.25)E-02

(-0.69 * 1.59)E-02

(4.93 * 1.42)E-02

(-0.76 t 1.77)E~2

(1.41 A 0.73)E-02

(2.28 A 1.56)E-02

(1.14* 1.48)E-02

(0.54* 1.25)E-02

(-1 .58 * 1.60)E-02

(0.17 k 1.20)E-02

(-2.23 * 1.37)E-02

(-1.68+ 1.58)E-02

(1.33 t 1.55)E-02

(-0.58 * 3.85)E-03

(0.42 A 2.58)E-02

(2.32 * 2.16)E-02

(0.18 t 1.94)E-02

(2.14 + 1.99)E-02

(-0.45 t 1.50)E-02

(-0.50 t 1.94)E-02

(-2.54 + 2.1O)E-O2

(1.47A 0.28)E-02

(3.85 t 1.93)E-03

(1.57 t 0.49)E-02

(1.79 k 1.26)E-02

(0.57 A 1.34)E-02

(2.07 21.39)E-02

(1.31A 1.33)E-02

(0.18 t 1.25)E-02

(1.09 * 1.38)E-02

(1.81 * 1.73)E-02 (3.75 * 1.79)E-02 (0.44 * 1.50)E-02

(-7.35 A 6.63)E43

(-1.10 A 1.84)E-02

(0.32 A 1.70)E-02

(-0.32 * 1.37)E-02

(0.92 * 1.15)E-02

(2.29 t 1.67)E-02

(-1 .50 + 1.67)E-02

(-2.67 * 2.15)E-02

(-0.67 * 1.61)E-02

(0.80 + 2.21)E-02

(1.23 A2.61)E-02

(3.31 t 1.33)E-02

(4.19 t 2.14)E-02

(-0.83 A 1.22)E-02

(-0.74 + 2.15)E-02

(0.05 * 1.ll)E-02

(1.37 k 0.64)E-02

(1.33 * 1.74)E-02

(2.10 k 1.81)E-02

(-0.59 t 1.86)E-02

(0.89 k 1.82)E-02

(-2.79 A 7.80)E-03

(1.82* 0.71)E-02

(0.52 f 1.12)E-02

(2.64 k 1.86)E-02

(-1 .03 A 1.21)E-02

(1.38* 1.61)E-02




Page 4of19

No. ofLocation Samples Arithmetic Mean t a Maximum * a Minimum * a

SC4 Steel Creek at Road A

Bass 3 (1.45* 0.58)E-02 (1.85* 2.13)E-02

Bream 3 (-2.50 * 5.03)E-03 (0.30 * 1.89)E-02

FreshwaterCatfish 1 (1.26+ 1.70)E-02

U3R-4 at Road A

Bass 2 (-1 .18 * 1.77)E-02 (0.07 * 1.15)E-02

Bream 3 (-0.62 * 1.88)E-02 (1.53 tl.16)E-02

Freshwater Catfish 2 (-0.77 * 2.23)E-02 (0.81 * 1.99)E-02

Offsite (Nonedible)


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

HwY-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(8.90 k 6.81)E-03

(-0.85 f 1.32)E-02

(1.24 f 0.95)E42

(1.77 t 1.20)E-02

(-0.49 + 1.39)E-02

(1.30 12.00)E-02

(0.36 t 1.O1)E-02

(2.81 t 8.05)E+3

(1.03 k 1.96)E-02

(-1 .20 t 0.75)E-02

(1.09 t 1.79)E-02

(-1 .56 f 1.40)E-02

(-1.02 * 8.36)E-03

(1.33 t 0.79)E-02

(1.47 i- 6.48)E+3

(1.45A 0.97)E-02

(1.10 t 1.74)E-02

(-0.42 A 1.71)E-02

(1.60 ~ 1.69)E-02

(0.33 ~ 1.55)E-02

(2.12 t 1.32)E-02

(3.08 + 1.44)E-02

(0.86 + 1.45)E-02

(3.59 * 1.67)E-02

(1.23 t 1.64)E-02

(1.20+ 1.20)E-02

(2.62 ~ 1.37)E-02

(-0.61 + 1.55)E-02

(2.30 f 1.28)E-02

(-0.33 f 1.41)E-02

(0,54 * 1.09)E-02

(1.82 t 0.87)E-02

(7.94 t 5.43)E-03

(2.56 + 0.82)E-02

(2.14 ~ 0.89)E-02

(1.51 ~ 0.64)E-02

(0.79 ~ 1.98)E-02

(-0.68 ~ 1.97)E-02

(-2.43 + 1,93)E-02

(-1 .93 + 1.68)E-02

(-2.35 + 2.61)E-02

(0.25 t 1.20)E-02

(-2.28 + 1.53)E-02

(0.24 * 1.30)E-02

(0.73 ~ 1.17)E-02

(-1 .91 ~ 1.47)E-02

(-0.05 t 1.26)E-02

(-0.74 ~ 1.30)E-02

(-0.30 ~ 1.45)E-02

(-1 .16 ~ 2.02)E-02

(-2.04 k 1.31)E-02

(-0.97 t 1.35)E-02

(-3.08 * 1.25)E-02

(-1.05 f 1.71)E-02

(4.17 t 6.45)E-03

(-0.50 t 1.00)E-02

(8.00 k 6.40)E43

(-9.06 + 6.63)E-03

(-1 .78 f 1.58)E-02




Page 5 of 19

LocationNo. of

Samples Arithmetic Mean *IS Maximum * a Minimum * a


Bass

Bream

FreshwaterCatfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish

3

3

3

3

2

3

3

3

3

3

3

(5.02 ~ 4.07)E-03

(1.16A 0.44)E-02

(1.49 t 0.97)E-412

(1.89 * 0.92)E42

(-3.42 ~ 0.73)E-02

(2.27 * 1.31)E-02

(0.65 * 1.60)E-02

(1 .37* 1.12)E-02

(1.92 t 0.46)E-02

(-7.41 t 6.50)E413

(0.22 * 1.03)E-02

(9.25 * 7.70)E-03

(1.41* 1.32)E-02

(2.07 t 1.28)E-02

(2.96 A 1.15)E-02

(-2.90 t 1.48)E-02

(3.55 t 1.54)E-02

(2.04 A 1.23)E-02

(2.24 A 1.33)E-02

(2.39 A 1.40)E-02

(-0.26 + 1.66)E-02

(1.35 t 1.36)E-02

(0.11 * 1.07)E-02

(0.65 t 1.31)E-02

(0.38 * 1.27)E-02

(1.34 t 0.82)E-02

(-3.94 * 1.65)E-02

(0.92 * 1.29)E-02

(-1 .10 A 1.30)E-02

(0.10 * 1.60)E-02

(1.47 t 1.40)E-02

(-1 .48 * 1.33)E-02

(-0.66 & 1.52)E-02

Cs-137, pCi/g

Offsite (Edible)


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

3

3

3

3

3

3

3

3

3

3

3

3

3

(3.36 * 3.86)E-02

(1.15 t 0.39)E-01

(2.13 * 1.91)E-02

(9.48 t 4.30)E-03

(1.91 t 0.95)E-02

(3.88 t 2.14)E-01

(2.62 + 2.64)E-02

(4.23 t 3.20)E-02

(3.63 * 1.30)E-01

(2.84 t 0.40)E-01

(4.57 ~ 5.45)E-02

(1.13 t 0.51)E-01

(5.27 + 3.69)E+2

(7.28 * 2.05)E-02

(1.58 t 0.22)E-01

(3.75 k 1.41)E-02

(1.44* 1.35)E-02

(2.97 t 1.35)E-02

(6.25 A 0.46)E-01

(4.76 A 1.54)E-02

(6.56 k 1.84)E-02

(4.74 k 0.40)E-01

(3.11 ~ 0.36)E-01

(1.07 ~ 0.24)E-01

(1.50 t 0.30)E-01

(7.69 k 1.50)E-02

(-0.44 t 1.46)E-02

(8.34 A 2.54)E-02

(0.02 + 1.19)E-02

(0.63 k 1.31)E-02

(1.14 A 1.35)E-02

(2.08 + 0.27)E-01

(-0.34 + 1.15)E-02

(0.58 t 1.41)E-02

(2.21 t 0.19)E-01

(2.38 t 0.29)E+1

(0.33 t 1.53)E-02

(5.52 ~ 1.92)E-02

(1.02+ 1.34)E-02




Page 6 of 19

No. ofLocation Samples Arithmetic Mean k a Maximum ~ o Minimum ~ a

HwY-17 Bridge Area

Bass

Bream

Freshwater Catfish

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

FreshwaterCatfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bream

Freshwater Catfish

Onsite (Edible)

Beaver Dam Creek (400-D)

Bream

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(5.09 * 1.65)E-02

(8.40 * 8.02)E42

(3.57 t 0.12)E-02

(9.51 * 5.44)E-02

(8.08 * 2.21 )E-02

(2.94 A 0.78)E-02

(5.59 * 0.49)E-02

(6.48 t 5.37)E-02

(1 .89* 0.86)E-01

(1 .31* 0.81 )E-01

(2.14 * 1.68)E+1

(1 .65* 0.84)E+O0

(3.84 * 0.82)E4M

(9.70 f 6.23)E-02

(8.87 + 2.ll)E-02

(2.59 + 0.79)E-01

(6.49 * 2.55)E-02

(7.60 * 0.77)E-02

(5.63 * 0.16)E+2

(9.73 * 4.99)E-02

(3.25 * 2.96)E-02

(5.52 * 4.25)E-02

(6.55 * 1.24)E-02

(1 .76* 0.35)E-01

(3.68 * 2.1 O)E-O2

(1.57 * 0.13)E-01

(1 .06 f 0.12)E-01

(3.83 * 1.18)E-02

(5.87 * 1.07)E-02

(1 .27* 0.23)E-01

(2.75 * 0.21 )E-01

(2.10 * 0.28)E-01

(3.86 * 0.37)E-01

(2.52 t 0.13)E+O0

(4.38 * 0.41)E-01

(1.62 t 0.15)E-01

(1.12* 0.21)E-01

(3.25 t 0.37)E-01

(8.68 * 2.98)E42

(8.28 * 1.99)EW2

(5.78 + 2.05)E-02

(1.49 t 0.23)E-01

(5.99 * 1.82)E-02

(1.04 t 0.17)E-01

(3.31 t 1.13)E-02

(2.97 * 1.56)E-02

(3.44 t 1.37)E-02

(5.76 * 1.05)E-02

(6.28 i- 1.ll)E-02

(2.38 t 0.82)E412

(5.02 * 0.94)E-02

(3.32 f 1.67)E-02

(1.02* 0.20)E-01

(4.89 + 1.28)E-02

(5.02 f 2.66)E-02

(8.47 k 0.54)E-01

(2.89 A 0.35)E-01

(3.76 A 1.79)E-02

(7.21 ~ 1.23)E-02

(1.72 i- 0.23)E-01

(3.70 t 2.08)E42

(6.77 t 2.62)E-02

(5.47 t 2.77)E-02

(4.93 A 1.98)E-02

(0.12 t 1.34)E-02

(2.76 t 1.34)E-02

(5.55 t 4.O1)E-02 (8.66 * 1.57)E-02 (1.02 t 1.37)E-02




Page 7 of 19

No. ofLocation Samples Arithmetic Mean * o Maximum k o Minimum & u

L-Lake

Bass

Bream

Freshwater Catfish


Bass

Bream

PAR Pond

Bass

Bream

Pond B

Bass

Bream

SC-4 Steel Creek at Road A

Bass

Bream

Freshwater Catfish

U3R-4 at Road A

Bass

Bream

Freshwater Catfish

Offsite (Nonedible)

3

3

3

3

3

3

3

3

3

3

3

1

2

3

2

(6.90 10.59)E-01

(2.38 i 0.34)E-01

(3.65 f 0.38)E-01

(6.18 * 0.73)E+O0

(1.75+ 0.44)E+O0

(8.87 + 1.01)E+OO

(3.01 t 0.50)E+O0

(1.00A 0.11)E+02

(2.95 t 0.08)E+01

(1.85 t 0.60)E+O0

(8.22 * 1.70)E-01

(5.64 * 0.55)E-01

(7.09 f 0.66)E-02

(1.03 f 0.41)E-01

(1.26* 0.65)E41

(7.35 A 0.57)E-01

(2.77 t 0.40)E-01

(3.99 * 0.43)E-01

(7.02 f 0.36)E+O0

(2.08 & 0.12)E+O0

(9.56 * 0.48)E+O0

(3.56 ~ 0.20)E+O0

(1.13* 0.04)E+02

(3.05 10.15)E+01

(2.25 + 0.13)E+O0

(1.01 + 0.07)E+O0

(7.56 t 1.40)E-02

(1.35* 0.27)E-01

(1.73 k 0.36)E-01


Bass 3

Bowfin 3

Bream 3

Freshwater Catfish 3

Sucker 3


Bass 3

Bream 3


(2.24 f 0.53)E-02

(8.30 t 5.22)E-02

(2.04 & 0.73)E-02

(0.49 * 2.31)E-02

(1.96 Y 0.85)E-02

(3.16 +1.61 )E-01

(2.04 * 0.50)E-02

(3.47 t 2.53)E-02

(2.69 * 1.32)E-02

(1.43 k 0.21)E-01

(2.81 + 1.17)E-02

(2.99 i 1.30)E-02

(2.79 t 1.20)E-02

(5.01 * 0.38)E-01

(2.60 & 1.52)E-02

(6.14 k 1.51)E-02

(6.22 f 0.50)E-01

(2.15 k 0.24)E-01

(3.24 * 0.22)E-01

(5.67 + 0.20)E+O0

(1.26 k 0.08)E+O0

(7.71 i 0.39)E+O0

(2.59 * 0.15)E+O0

(9.1 1 * 0.30)E+01

(2.88 * 0.14)E+01

(1 .16+ 0.09)E+O0

(6.96 * 0.39)E-01

(6.62 * 3.29)E-02

(5.68 i 1.57)E-02

(8.03 A2.36)E-02

(1 .66* 1.44)E-02

(4.95 &2.33)E-02

(1.36+ 1.31)E-02

(-1 .55 t 1.18)E-02

(1.10* 1.35)E-02

(2.11 + 0.29)E-01

(1.65 k 1.29)E-02

(1.10 A 1.29)E-02

WSRGTR-98-00314SRS Errk+zmrrental Data for 1998 85



Page 8 of 19

No. ofLocation Samples Arithmetic Mean i CT Maximum & o Minimum i u


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish

3

3

3

3

3

3

3

3

3

3

3

3

3

3

2

3

3

3

3

3

3

(1.88+ 0.36)E-01

(3.54 t 0.86)E-01

(6.01 ~ 2.26)E-02

(7.99 ~ 2.47)E-02

(1.43 t 2.42)E-02

(6.37 t 3.19)E-02

(7.39 t 3.88)E-02

(2.36 ~ 0.29)E-02

(7.30 ~ 5.69)E-02

(3.88 + 0.21)E-02

(9.88 + 5.84)E+2

(7.26 15.83)E-02

(9.33 i8.18)E-02

(8.49 * 3.21)E-01

(2.09 f 0.23)E-01

(5.74 * 4.22)E-02

(5.25 11 .98)E-02

(1.87 t 0.55)E-01

(4.62 + 3.23)E-02

(2.52 ~ 1.00)E-02

(4.76 ~ 2.32)E-02

(2.29 ~ 0.26)E-01

(4.34 t 0.38)E-01

(7.84 & 2.29)E-02

(1.01 ~ 0.27)E-01

(3.62 ~ 1.31)E-02

(1.00 *0.12)E-01

(1.18 t0.12)E-01

(2.57 + 0.85)E-02

(1.39 +0.14)E-01

(4.10 ~ 1.74)E-02

(1.66* 0.18)E-01

(1.20* 0.22)E-01

(1.87 kO.31)E-01

(1.20 10.05)E+O0

(2.25 f 0.30)E-01

(9.52 * 1.95)E-02

(7.36 ~ 3.1O)E-O2

(2.23 A 0.32)E-01

(6.97 + 1.86)E-02

(3.59 t 1.29)E-02

(6.27 t 1.79)E-02

(1.66+ 0.40)E-01

(2.63 + 0.29)E-01

(3.48 i 1.25)E-02

(5.26 ~ 2.39)E-02

(-1 .1811 .30)E-02

(4.00 + 0.99)E-02

(4.47 t 0.85)E-02

(2.02 + 0.70)E-02

(3.90 A 0.91)E-02

(3.68 k 1.05)E-02

(6.45 11 .29)E-02

(0.77 A 1.22)E-02

(3.51 12.O1)E-02

(5.63 ~ 0.43)E411

(1.92+ 0.32)E-01

(1.19 t 1.33)E-02

(3.42 * 1.39)E-02

(1.24 f 0.19)E-01

(0.94 ~ 1.31)E-02

(1.61 f 1.17)E-02

(2.09 * 1.22)E-02

Pu-238, pCi/g

Offsite (Edible)


Bass 3 (-0.41 & 1.84)E-05 (0.74 t 1.90)E-05 (-2.53 t 3.95)E-05

Bovdh 3 (-0.74 t 2.37)E-05 (1.86 t 2.37)E-05 (-2.78 + 1.46)E-05

Bream 3 (-1 .56 ~ 2.46)E+5 (0.52 * 4.68)E-05 (-4.27 & 3.05)E-05

Freshwater Catfish 3 (-6.08 ~ 8.22)E-06 (-0.09 + 1.71)E-05 (-1 .70 ~ 0.84)E-05

Sucker 3 (1.97+ 3.63)E-05 (6.16 14.52)E-05 (-.25 f 2.15)E-05

—-




Page 9 of 19

No. ofLocation Samples Arithmetic Mean + u Maximum * o Minimum * c


Bass

Bream

Freshwater Catfish


Bass

Bream

Freshwater Catfish

Sucker

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish

3

3

3

3

3

3

1

3

3

3

3

3

3

3

3

3

3

3

3

1

3

3

3

(-1 .32 * 0.64)E45

(-4.35 i 6.62)E-05

(-1 ,11 f 0.39)E-05

(-1 .06 t 2.1O)E-05

(-4.86 12.64)E-05

(0.12 * 1.48)E-05

(-4.39 ~ 1.35)E-05

(-1 .22 + 6.42)E-05

(-2.14 f 1.98)E-05

(1.23 i 7.32)E-05

(-2,05 t 0.58)E-05

(0.80 + 1.24)E-05

(0.20 i 1.97)E-05

(-5.90 A 6.40)E-05

(-2.19 ~ 1.02)E-05

(-4.87 + i .56)E-06

(-1 .90 * 9.62)E-06

(-1 .49 & 9.27)E-05

(2.35 ~ 4.27)E-05

(1.91 + 1.78)E-05

(0.65 * 2.54)E-05

(5.76 i 4.19)E45

(4.98 t 9.06)E-05

(-0.71 * 1.21)E-05

(1.75 * 6.39)E-05

(-0.85 k 1.47)E-05

(0.25 * 2.24)E-05

(-1 .89 f 5.24)E-05

(1 .79 i 1.68)E-05

(3.40 * 3.24)E-05

(-0.75 i 1.30)E-05

(9.57 + 8.96)E-05

(-1 .54 & 1.88)E45

(2.21 + 1.47)E-05

(2.44 * 4.45)E-05

(-1 .65 + 3.64)E-05

(-1 .03 t 1.17)E-05

(-0.39 * 1.55)E-05

(0.64 * 1.05)E-05

(8.80 t 9.69)E-05

(7.1 5 ~ 4.21 )E-05

(2.22 * 2.52)E-05

(0.97 f 1.13)E-04

(1 .47& 0.60)E-04

(-1 .99 + 0.82)E-05

(-1 .14 * 0.68)E-04

(-1 .56 t 1.ll)E-05

(-3.48 * 5.45)E-05

(-6.95 A 6.64)E-05

(-1 .02 Y 1.24)E-05

(-8.55 A 5.08)E-05

(-4.40 + 2.66)E-05

(-4.10 + 1.70)E-05

(-2.67 * 2.02)E-05

(-0.13 f 2.03)E-05

(-1 .31 * 2.36)E-05

(-1 .33 A 0.46)E-04

(-2.97 t 2.02)E-05

(-6.67 t 4.73)E-06

(-1 .24 t 0.96)E-05

(-9.19 A 7.25)E-05

(-1 .00 t 2.76)E-05

(-2.28 & 1.74)E-05

(1.35* 3.48)E-05

(-3.32 + 1.67)E-05

Pu-239, pCi/g

Offsite (Edible)


Bass 3 (1.06* 2.13)E-05 (3.52 k 3.ll)E-05 (-0.28 * 4.54)E-05

Bowfin 3 (1.51 f 2.30)E-05 (4.12 k 3.04)E-05 (-0.19 * 1.77)E-05

WSRGTR-98-00314SRS Envlironmenral Dafa for 1998 87

I

I

Radioloairal Fnvimnmental .~lmmillanrw


Table 26

Radioactivity in Aquatic Food Products — Freshwater Fish

Page 10 of 19

No. ofLocation Samples Arithmetic Mean * o Maximum *IS Minimum * o

3

3

3

3

3

3

3

3

1

3

3

3

3

3

3

3

3

3

3

3

3

1

3

3

3

Bream 3

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bream

Freshwater Catfish

Sucker

HwY-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish

(-3.63 * 9.99)E+5

(-0.07 t 1.64)E-05

(-2.70 k 3.37)E-05

(0.85 + 1.09)E-05

(-1 .24 * 1.03)E-04

(7.87 t 9.64)E-06

(-2.99 A 0.91)E-05

(-2.42 t 8.55)E-05

(2.30 + 2.25)E-05

(4.39 * 3.17)E-05

(-4.12 * 1.81)E-05

(0.74 t 1.06)E-05

(2.22 * 4.23)E-05

(-0.97 k 1.23)E-05

(-0.66 t 1.60)E-05

(1.85 ~ 4.30)E-05

(-3.80 * 1.14)E-05

(0.70 * 5.ll)E-05

(1.01* 2.76)E-05

(-1 .23 k 0.44)E+5

(-9.71 t 4.06)E-05

(0.84 * 3.94)E-05

(-0.38 f 1.87)E-05

(-0.36 t 2.16)E-05

(1.82* 7.75)E-05

(-3.33 t 3.31)E-05

(7.71 k 4.31 )E-05

(1.66 * 1.93)E-05

(1 .18 ~ 1.92)E-05

(1.74 k 1.97)E-05

(-2.48 i- 5.05)E-05

(1.81 t 1.70)E-05

(-1 .96 t 1.90)E-05

(4.29 + 4.94)E-05

(4.33 A 2.12)E-05

(-2.95 k 4.61)E+5

(1.70 t 2.72)E-05

(7.1Ot 5.78)E-05

(0.19 * 2.44)E-05

(0.27 t 2.41)E-05

(5.12 t 4.82)E-05

(-3.13 * 3.48)EW5

(5.96 * 7.07)E-05

(3.49 * 1.95)E-05

(-9.28 i- 6.58)E-06

(-5.37 + 4.41 )E-05

(5.33 t 3.77)E-05

(1.41 t2.57)E+5

(1.08 A 0.78)E-04

(0.08 t 2.37)E-05

(-1 .11 t 0.31)E-04

(-1 .60 * 1.94)E-05

(-4.91 t 3.31)E-05

(-0.37 ~ 1.16)E-05

(-2.30 * 0.41)E-04

(-O.1Ot 1.91)E-05

(-3.63 * 1.77)E-05

(-1 .20 + 0.86)E-04

(-0.12 t 1.90)E-05

(-6.20 t 4.17)E-05

(-0.40 f 1.24)E-05

(-0.25 ~ 3.97)E-05

(-2.26 * 1.94)E-05

(-2.50 t 0.66)E-05

(-3.02 t 0.79)E+5

(-5.12 A 6.00)E-05

(-4.24 * 1.14)E-05

(-1 .95 ~ 1.34)E-05

(-1 .73 t 0.74)E-05

(-1 .34 & 0.69)E-04

(-2.05 * 1.62)E-05

(-2.77 + 1.35)E-05

(-0.28 t 1.23)E-04

(-6.52 ~ 0.97)E-05




Page 11 of 19

No. ofLocation Samples Arithmetic Mean * ts Maximum t c Minimum * a

Sr-89,90, pCilg

Offsite (Edible)


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catish

Sucker

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(8.37 f 3.79)E-03

(1.86 i- 2.35)E-03

(4.05 k 3.51)E-03

(5.70 * 6.51)E-03

(8.07 * 1.32)E-03

(8.21 * 3.61)E-03

(1.59 * 0.61)E-02

(2.86 * 2.19)E-03

(1.48 * 0.12)E-02

(3.39 * 1.12)E-03

(2.44 A 1.38)E-02

(7.27 * 1.08)E-03

(1.34 t 0.58)E+2

(4.48 * 3.61)E-03

(3.16 * 3.20)E-03

(7.32 t 0.64)E-03

(1.53 f 0.97)E-03

(1.25 * 0.60)E-02

(5.76 * 2.44)E-03

(6.16 t 3.12)E-03

(1.56 * 1.23)E-03

(1.50* 0.32)E-02

(1.87* 2.78)E-03

(4.58 * 7.29)E-03

(8.89 * 5.72)E-03

(1.45* 1.08)E-02

(1.24 * 0.37)E-02

(3.79 t 3.18)E-03

(8.06 * 5.31)E-03

(1.31 A 0.51)E-02

(9.51 * 4.47)E-03

(1.16 t 0.45)E-02

(2.23 * 0.92)E-02

(5.13 & 4.65)E-03

(1.61 k 0.50)E-02

(4.12 * 4.O1)E-03

(3.51 * 1.33)E-02

(8.51 t 3.96)E-03

(1.94 * 0.49)E-02

(8.39 * 4.84)E-03

(5.22 * 4.22)E-03

(7.90 t 8.62)E~3

(2.15 k 3.88)E-03

(1.93 * 0.50)E-02

(8.00 +4.17)E-03

(9.76 * 6.78)E-03

(2.41 * 2.70)E-03

(1.86 A 0.50)E-02

(4.89 * 3.49)E-03

(1.13 * 1.18)E+2

(1.55 * 0.48)E-02

(2.69 * 0.38)E-02

(4.87 t 3.27)E-03

(-0.76 t 2.05)E-03

(1.55 *7.48)E-03

(0.91 * 4.39)E-03

(6.93 & 3.34)E-03

(4.42 * 3.72)E-03

(1.02 t 0.80)E42

(0.75 k 3.80)E-03

(1.39* 0.45)E+2

(2.11 * 2.75)E-03

(8.81 * 7.41)E-03

(6.59 * 3.84)E-03

(7.86 * 3.27)E-03

(1.27* 3.03)E-03

(-0.53 * 3.13)E-03

(6.64 * 8.55)E-03

(0.41 * 3.79)E-03

(8.11 * 3.91)E-03

(3.15 * 3.17)E-03

(4.36 * 6.42)E-03

(0.14* 3.08)E+3

(1.22 t 0.39)E-02

(-0.60 *2.91 )E-03

(-0.32 * 1.09)E-02

(5.33 * 4.24)E-03

(6.84 *4.19)E-03




Page 12 of 19

No. ofLocation Samples Arithmetic Mean + c Maximum t a Minimum ~ a

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(1.76 t 0.79)E-01

(1.04* 0.60)E-01

(2.90 t 0.44)E411

(9.13 + 5.70)E-02

(2.00 f 0.48)E-01

(2.90 t 0.32)E-01

(2.34 t 0.09)E-01

(1.52 t 0.86)E+1

(1.59+ 0.54)E+O0

(2.80 + 1.25)E-01

(3.82 A 3.1O)E-O1

(1.90 f 0.27)E-01

(2.88 * 0.65)E-01

(2.84 * 0.97)E-01

(1.40+ 0.85)E-01

(2.63 t 1.19)E-01

(2.00 f 0.14)E-01

(2.17 f 1.00)E-01

(2.06 * 0.38)E-01

(2.15 k 0.12)E-01

(1.52* 0.23)E-01

(3.13 t 0.19)E-01

(2.63 t 0.43)E-01

(2.24 * 0.39)E411

(1.72 t 0.44)E-01

(3.38 * 0.52)E-01

(1.28A 0.35)E-01

(2.55 A 0.48)Egl

(3.25 t 0.47)E-01

(2.43 t 0.39)E-01

(2.51 * 0.43)E-01

(2.20 + 0.07)E+O0

(4.14 f 0.36)E-01

(7.39 * 0.91)E-01

(2.1OA 0.33)E-01

(3.53 t 0.54)EW1

(3.52 k 0.53)E-01

(2.33 t 0.46)E-01

(3.72 ~ 0.53)E-01

(2.16* 0.46)E-01

(3.08 t 0.52)E-01

(2.34 t 0.39)E-01

(2.28 * 0.43)E-01

(1.77 t 0.36)E4M

(3.35 t 0.51)E-01

(2.90 * 0.49)E-01

(1.56+ 3.84)E-03

(4.34 + 6.63)E-03

(3.47 A 3.88)E-03


Bass 3 (2.40 * 1.00)E-03 (3.51 + 4.27)E-03

Bream 3 (8.38 + 3.62)E-03 (1.13 t 0.88)E-02

Freshwater Catfish 3 (6.84 + 5.52)E-03 (1.32 ~ 0.51)E-02

Offsite (Nonedible)


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

(8.47 + 3.24)E-02

(5.87 + 3.70)E-02

(2.53 ~ 0.48)E-01

(2.57 A 2.90)E-02

(1.70 t 0.44)E41

(2.63 t 0.34)E-01

(2.24 + 0.39)E-01

(9.38 + 1.94)E-02

(1.22+ O.1O)E+OO

(1.67* 0.45)E-01

(1.92* 0.46)E-01

(1.60+ 0.31)E-01

(2.24 + 0.48)E-01

(1.72* 0.44)E-01

(6.52 + 2.64)E-02

(1.37& 0.38)E-01

(1.88* 0.32)E-01

(1.09A 0.42)E-01

(1.63 t 0.36)E4M

(2.04 * 0.42)E-01

(1.31 t 0.24)E4M

(3.00 * 0.50)E-01 .

(2.14 * 0.45)E-01




Page 13 of 19

No. ofLocation Samples Arithmetic Mean k u Maximum ~ u Minimum * c

Bream 3 (3.40 * 0.18)E-01 (3.53 k 0.73)E-01 (3.20 t 0.72)E-01

FreshwaterCatfish 3 (1.40 * 0.29)E-01 (1.73 * 0.44)E-01 (1.21* 0.41)E41

Sucker 3 (5.56 * 5.67)E-01 (1.20 * 0.08)E+O0 (1.46* 0.43)E-01


Bass 3 (5.06 t4.98)E-Ql (1.08 A 0.07)E+O0 (1.65 t 0.39)E-01

Bream 3 (2.28 * 0.82)E-01 (3.20 A 0.47)E-01 (1.61 t 0.40)E-01

Freshwater Catfish 3 (1.65 k 0.69)E-01 (2.37 t 0.31)E-01 (9.96 A 2.36)E-02

Gross Beta, pCi/g

Offsite (Edible)


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

HwY-17 Bridge Area

Bass

Bream

Freshwater Catfish

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(1.93A 0.25)E+O0

(2.53 A 0.31)E+O0

(1.98 i- 0.74)E+O0

(1.93 t 0.19)E+O0

(2.30 A 0.55)E+O0

(2.05 * 0.81)E+O0

(2.86 + 0.28)E+O0

(1.70+ 0.42)E+O0

(2.21 t 0.35)E+O0

(2.09 k 0.29)E+O0

(2.13 k 0.70)E+O0

(3.46 * 0.50)E+O0

(2.11 * 0.85)E+O0

(2.91 A 0.41)E+O0

(2.71 + 0.51)E+O0

(3.09 t O.1O)E+OO

(2.15 A 0.36)E+O0

(2.71 ~ 0.41)E+O0

(2.83 t 0.43)E+O0

(2.15 * 0.35)E+O0

(2.71 A 0.41)E+O0

(2.66 t 0.51)E+O0

(3.17 k 0.45)E+O0

(2.18 t 0.39)E+O0

(2.49 A 0.47)E+O0

(2.42 k 0.43)E+O0

(2.92 * 0.43)E+O0

(3.85 * 0.46)E+O0

(3.02 + 0.46)E+O0

(3.39 * 0.43)E+O0

(3.17 * 0.45)E+O0

(3.21 t 0.43)E+O0

(1.65 t 0.34)E+O0

(2.16 A 0.38)E+O0

(1.45A 0.37)E+O0

(1.82A 0.35)E+O0

(1.68 k 0.36)E+O0

(1.13A 0.23)E+O0

(2.61 * 0.43)E+O0

(1.42* 0.34)E+O0

(1.82A 0.34)E+O0

(1.87& 0.40)E+O0

(1.57+ 0.33)E+O0

(2.90 A 0.30)E+O0

(1.33 + 0.38)E+O0

(2.68 + 0.41)E+O0

(2.16 f 0.26)E+O0

(3.03 t 0.41)E+O0




Page 140f 19

No. ofLocation Samples Arithmetic Mean * c Maximum *CT Minimum * a

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bream

Freshwater Catfish

Onsite (Edible)

Beaver Dam Creek (40&D)

Bream

L-Lake

Bass

Bream

Freshwater Catfish


Bass

Bream

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(1.98* 0.44)E+O0

(2.75 * 0.68)E+O0

(2.73 * 0.40)E+O0

(1.33 t 0.39)E+O0

(2.30 k 0.12)E+O0

(2.94 ~ 0.23)E+O0

(2.07 + 0.65)E+O0

(2.25 * 0.35)E+O0

(2.25 * 0.62)E+O0

(2.78 * O.1O)E+OO

(2.33 * 0.52)E+O0

(2.01 + 0.45)E+O0

(2.62 t 0.35)E+O0

(3.25 * 0.21)E+O0

(2.39 * 0.19)E+O0

(2.93 * 0.63)E+O0

(9.26 ~ 3.47)E-01

(3.05 t 0.43)E+O0

(1.48+ 0.56)E+O0

(2.76 * 0.37)E+O0

(2.94 + 0.44)E+O0

(3.51 * 0.74)E+O0

(2.88 * 0.41)E+O0

(6.83 ~ 1.56)E+O0

(4.24 f 0.77)E+O0

(2.48 f 0.37)E+O0

(3.50 + 0.42)E+O0

(3.11 * 0.43)E+O0

(1.76 t 0.36)E+O0

(2.38 * 0.41)E+OO

(3.20 & 0.45)E+O0

(2.80 * 0.31)E+OO

(2.60 * 0.39)E+O0

(2.77 * 0.40)E+O0

(2.84 & 0.39)E+O0

(2.88 ~ 0.42)E+O0

(2.43 + 0.38)E+O0

(2.82 + 0.45)E+O0

(3.42 * 0.47)E+O0

(2.59 * 0.31)E+O0

(3.66 * 0.45)E+O0

(1.25* 0.33)E+O0

(3.54 * 0.46)E+O0

(2.08 * 0.37)E+O0

(3.00 + 0.40)E+O0

(3.36 ~ 0.45)E+O0

(4.10 * 0.46)E+O0

(3.36 * 0.45)E+O0

(7.94 * 0.60)E+O0

(4.74 * 0.50)E+O0

(1.64* 0.33)E+O0

(2.17 * 0.36)E+O0

(2.31 k 0.37)E+O0

(1.00* 0.34)E+O0

(2.16 t 0.38)E+O0

(2.80 k 0.44)E+O0

(1.55* 0.37)E+O0

(1.91* 0.36)E+O0

(1.56* 0.34)E+O0

(2.67 * 0.38)E+O0

(1.84* 0.37)E+O0

(1.52+ 0.34)E+O0

(2.21 ~ 0.42)E+O0

(3.02 * 0.46)E+O0

(2.21 * 0.42)E+O0

(2.56 A 0.41)E+O0

(5.63 * 2.98)E-01

(2.80 * 0.44)E+O0

(9.64 * 1.82)E-01

(2.34 t 0.37)E+O0

(2.47 * 0.42)E+O0

(2.68 & 0.40)E+O0

(2.65 t 0.30)E+O0

(5.05 * 0.50)E+O0

(3.35 * 0.44)E+O0




Page 150f 19

No. ofLocation Samples Arithmetic Mean * a Maximum t cs Minimum * a

PAR Pond

Bass 3

Bream 3

Pond B

Bass 3

Bream 3


Bass 3

Bream 3


U3R-4 at Road A

Bass 2

Bream 3


Offsite (Nonedible)

(6.36 A 3.68)E+O0

(3.25 A2.18)E+O0

(6.93 A 0.28)E+01

(1.28* 0.90)E+01

(3.78 * 0.28)E+O0

(3.36 * 0.38)E+O0

(2.80 * 0.39)E+O0

(2.76 t 0.80)E+O0

(2.18 t 0.12)E+O0

(2.78 A O.O1)E+OO

(9.19 * 0.61)E+O0

(4.60 f 0.48)E+O0

(7.17 *0.16)E+01

(1.84 A 0.08)E+01

(4.03 * 0.46)E+O0

(3.66 A 0.46)E+O0

(3.32 A 0.31)E+O0

(2.32 k 0.38)E+O0

(2.79 + 0.42)E+O0


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

Hwy-301 Bridge Area

Bass

Bowfin

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(1.59 t 0.75)E+O0

(2.03 * 1.88)E+O0

(1.39 * 0.61)E+O0

(9.74 * 5.75)E-01

(2.55 * 0.33)E+O0

(2.11 * 0.31)E+O0

(1.08* 1.18)E+O0

(1.38* 0.94)E+O0

(4.27 * 1.88)E+O0

(1.83* 0.86)E+O0

(1.80* 0.42)E+O0

(1.42* 0.44)E+O0

(1.51* 0.66)E+O0

(2.04 * 0.45)E+O0

(1.80* 0.70)E+O0

(2.44 * 1.02)E+O0

(4.02 k 1.1O)E+OO

(2.09 * 1.03)E+O0

(1.33* 0.93)E+O0

(2.79 * 1.O1)E+OO

(2.46 * 0.88)E+O0

(2.35 * 1.06)E+O0

(2.32 * 0.84)E+O0

(5.53 + 1.34)E+O0

(2.44* 1.O1)E+OO

(2.07 * 0.85)E+O0

(1.84* 0.54)E+O0

(2.24* 0.82)E+O0

(2.56 * 0.92)E+O0

(2.45 * 0.73)E+O0

(2.20 ~ 0.30)E+O0

(7.35 ~ 3.39)E-01

(6.62 ~ 0.15)E+01

(2.39 ~ 0.40)E+O0

(3.48 t 0.40)E+O0

(2.93 * 0.43)E+O0

(2.19 k 0.39)E+O0

(2.09 * 0.35)E+O0

(2.77 * 0.42)E+O0

(1.06* 0.95)E+O0

(2.84 k 8.46)E-01

(1.02 ~ 0.93)E+O0

(3.11 * 8.61)E-01

(2.18 * 1.00)E+OO

(1.93* 0.84)E+O0

(0.19 * 8.46)E-01

(4.30 t 7.32)E-01

(2.11 * 0.83)E+O0

(8.46 * 8.28)E-01

(1.32* 0.76)E+O0

(9.63 * 8.96)E+1

(9.40 * 7.87)E-01

(1.72* 1.04)E+O0

(1.06 * 0.90)E+O0



Page 160f 19

No. ofLocation Samples Arithmetic Mean * cr Maximum * a Minimum * u

Bream 3 (1.43 k 0.64)E+O0

Freshwater Catfish 3 (0.33 t 1.ll)E+OO

Sucker 3 (2.09 t 1.77)E+O0


Bass 3 (1.66+ 0.19)E+O0

Bream 3 (1.30* 0.14)E+O0

Freshwater Catfish 3 (2.81 * 0.58)E+O0


Bass 3 (2.43 t 0.60)E+O0

Bowfin 3 (2.16+ 0.85)E+O0

Bream 3 (1.29 t 0.87)E+O0

Freshwater Catfish 3 (1.56 t 0.63)E+O0

Sucker 3 (2.21 * 1.80)E+O0


Bass 3 (1.56+ 0.50)E+O0

Bream 3 (1.16 t 0.63)E+O0

Freshwater Catfish 3 (1.46 t 0.74)E+O0

Gross Alpha, pCi/g

Offsite (Edible)

(1.89 t 0.81)E+O0

(1.61 ~ 0.93)E+O0

(4.13 t 0.97)E+O0

(1.88 ~ 0.93)E+O0

(1.45+ 0.93)E+O0

(3.39 A 1.1O)E+OO

(3.09 * 0.92)E+O0

(3.07 f 1.04)E+O0

(2.12 f 0.93)E+O0

(2.17 + 0.84)E+O0

(4.22 ~ 0.95)E+O0

(2.07 t 0.66)E+O0

(1.88 i- 0.67)E+O0

(2.28 * 0.98)E+O0

(6.96 t 8.96)E-01

(-3.48 t 8.12)E41

(1.04 t 0.65)E+O0

(1.54*1 .06)E+O0

(1.18 t 0.84)E+O0

(2.22 t 0.98)E+O0

(1.93 t 0.84)E+O0

(1.39+ 1.41)E+O0

(3.82 + 7.09)E-01

(9.17 k 7.63)E-01

(7.47 t 7.09)E-01

(1.06 t 0.93)E+O0

(7.52 * 8.28)E-01

(8.33 t 8.61)E-01


Bass 3 (0.50 * 2.14)E-01 (2.64 + 2.28)E-01 (-1 .64 + 1.37)E-01

Bowfin 3 (-0.63 t 1.23)E-01 (0.40 * 2.06)E-01 (-1 .98 t 1.53)E-01

Bream 3 (-0.21 t 1.15)E-01 (1.04 * 1.60)E-01 (-1 .22 t 0.97)E+1

Freshwater Catfish 3 (-2.48 f 7.03)E-02 (0.46 A 1.81)E-01 (-0.94 t 1.53)E-01

Sucker 3 (-0.58 * 1.74)E-01 (1.37 * 2.21)E-01 (-1 .98 ~ 1.51)E-01

Beever Dam Creek River Mouth

Bass 3 (-5.21 * 1.54)E-02 (-0.36 t 2.54)E-01 (-0.67 t 1.19)E-01

Bream 3 (-0.93 * 1.25)E-01 (0.41 A 1.75)E-01 (-2.05 f 1.04)E-01

Freshwater Cattish 3 (-1.08 f 0.46)E4N (-0.54 * 1.15)E-01 (-1 .40 f 0.89)E-01


_. —-—



Page 17 of 19

No. ofLocation Samples Arithmetic Mean ~ ci Maximum * a Minimum k a


Bass

Bowfin

Bream

Freshwater Catfish

Sucker

HwY-17 Bridge Area

Bass

Bream

Freshwater Catfish

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bream

Freshwater Catfish

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(-6.20 * 6.03)E-02

(-3.09 A 8.06)E-02

(-1.68 * 0.24)E-01

(-1.05 *1 .18)E-01

(-0.58 t 1.14)E-01

(-0.39 * 1.56)E-01

(1.04 t4.66)E-02

(-0.42 * 1.34)E-01

(-5.01 * 8.65)E-02

(2.53 * 0.88)E-01

(-0.94 t 1.76)E-01

(-5.53 * 7.21)E-02

(-5.63 * 9.00)E-02

(-9.43 A 4.25)E-02

(2.11 t 9.22)E-02

(-0.09 *1 .60)E-01

(-2.95 + 7.85)E-02

(0.27 t 2.09)E-01

(-1.80 * 0.04)E-01

(7.22 * 8.66)E-02

(-1.54 t 0.59)E-01

(-0.55 t 1.45)E-01

(0.41 k 1.76)E-01

(-1 .46 + 1.22)E-01

(-2.48 t 8.87)E-02

(-9.89 Y 9.22)E-02

(-0.60 t 2.91)E-02

(-0.23 k 1.65)E-01

(0.50 * 1.68)E41

(-1.45 * 1.12)E-01

(0.26 A 2.09)EW1

(0.72 t 2.30)E-01

(1.16 * 2.ll)E-01

(0.39 A 1.72)E-01

(1.12 + 2.ll)E-01

(0.50 * 1.81)E-01

(3.43 t 2.88)EW1

(1.09 t 1.96)E-01

(0.15 * 1.33)E-01

(0.48 k 2.17)E-01

(-0.45 A 1.51)E-01

(1.27 t 1.85)E-01

(1.14 + 1.98)E-01

(0.43 t 1.98)E+1

(2.34 *2.18)E-01

(-1 .76 * 0.99)E-01

(1.26 A 2.05)E-01

(-1 .15 + 1.91)E-01

(1.12 * 2.17)E-01

(2.42 t 2.70)E-01

(-0.33 * 1.92)E-01

(0.29 * 1.36)E-01

(-0.41 t 1.54)E-01

(2.71 + 9.52)E-02

(-1.32 f2.14)E-01

(-1.11 * 1.86)E-01

(-1 .93 + 1.02)E-01

(-2.02 *1 .08)E-01

(-1 .33 * 1.99)E-01

(-1 .96 t 1.48)E-01

(-0.43 A 1.26)E-01

(-1 .21 t 1.66)E-01

(-1 .04 A 1.55)E-01

(1.67 k2.18)E-01

(-2.01 f 1.59)E-01

(-1.29 k 0.91)E-01

(-1.10 t 1.71)E-01

(-1.19 t 1.29)E-01

(-0.43 ~ 1.15)E-01

(-1 .91 t 1.43)E-01

(-1 .13 t 1.65)E-01

(-1 .84* 1.38)E-01

(-1 .85 k 0.99)E-01

(-0.28 * 1.82)E-01

(-2.21 * 1.71)E-01

(-1 .39 A 1.98)E-01

(-0.88 * 1.47)E-01

(-2.75 A 1.32)E-01

(-1 .27 A 0.87)E-01

(-2.05 t 1.06)E-01

(-0.28 k 1.73)E-01




Page 180f 19

No. ofLocation Samples Arithmetic Mean k a Maximum * a Minimum + a

Onsite (Edible)

Beaver Dam Creek (40&D)

Bream

L-Lake

Bass

Bream

Freshwater Catfish


Bass

Bream

PAR Pond

Bass

Bream

Pond B

Bass

Bream


Bass

Bream

Freshwater Catfish

U3R4 at Road A

Bass

Bream

Freshwater Catfish

3

3

3

3

3

3

3

3

3

3

3

3

1

2

3

2

(0.13 f 1.88)E-01

(0.03 t 1.55)E-01

(0.31 t2.67)E-01

(-1 .05 t 0.27)E-01

(0.04 * 1.80)E41

(0.50 t 3.46)E42

(-0.29 f 2.07)E-01

(0.36 + 1.43)E-01

(6.56 t 7.09)E-01

(0.99 t 2.34)E-01

(-7.66 t 3.63)E-02

(8.79 t 5.25)E-02

(0.42 * 1.48)E-01

(-4.83 t 6.65)E-02

(-1.12 * 0.73)E-01

(-0.65 k 1.65)E-01

(1 .84* 2.24)E-01

(1.77 * 1.76)E-01

(3.39 * 2.52)E-01

(-7.38 * 7.91 )E-02

(2.01 * 2.46)E-01

(0.26 11 .79)E-01

(1 .54+ 2.O1)E-01

(1.84 * 2.1 O)E-O1

(1 .45+ 0.49)E+O0

(3.49 * 2.73)E-01

(-0.55 + 1.92)E-01

(1 .23+ 2.32)E-01

(-0.01 * 1.15)E-01

(-0.29 * 1.78)E-01

(0.51 * 1.65)E-01

Offsite (Nonedible)


Bass 3 (-2.46 t 8.ll)E-01 (6.11 A 8.78)E-01

Bowfin 3 (-2.93 t 2.73)E-01 (0.07 A 5.85)E41

Bream 3 (-2.84 f 3.63)E-01 (-0.10 t 4.85)E-01

Freshwater Catfish 3 (-3.41 * 1.15)E-01 (-2.61 t 5.83)E-01

Sucker 3 (-3.96 + 1.41)E-01 (-2.96 + 5.85)E-01

(-1 .88 ~ 1.02)E-01

(-1 .22 ~ 0.97)E-01

(-1 .34 * 1.68)E41

(-1 .22 * 0.97)E-01

(-1 .52 * 1.70)E-01

(-0.35 A 1.49)E-01

(-2.53 + 1.68)E-01

(-1 .01 + 2.25)E-01

(0.94 + 3.68)E-01

(-1 .14 t 1.56)E-01

(-1 .19 t 1.50)E-01

(0.27 * 2.09)E+1

(-0.95 * 1.26)E-01

(-1 .61 t 1.35)E-01

(-1 .82 f 0.98)E-01

(-1 .00 A 0.53)E+O0

(-5.24 k 4.96)E-01

(-6.96 t 4.41)E-01

(-4.72 * 4.48)E-01

(-5.58 ~ 5.20)E-01




Page 19 of 19

No. ofLocation Samples Arithmetic Mean * c Maximum * c Minimum ~ a


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

FreshwaterCatfish

Sucker

Hwy-301 Bridge Area

Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish


Bass

Bowfin

Bream

Freshwater Catfish

Sucker


Bass

Bream

Freshwater Catfish

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

3

(1.27* 3.39)E-01

(-4.44 * 3.98)E-01

(-2.66 * 2.94)E-01

(-0.98 * 5.29)E-01

(-0.36 *4.41 )E-01

(-3.10 A 3.19)E-01

(-0.05 *4.O1)E-01

(0.28 * 3.27)E-01

(-6.53 * 1.29)E-01

(-1 .90 * 3.09)E-01

(-0.18 * 2.64)E-01

(-0.78 * 4.83)E-01

(-1.06 k 3.39)E-01

(-1 .48 * 3.24)E-01

(-3.51 k 1.46)E-01

(-2.14 * 2.96)E-01

(-3.37 k 3.51)E-01

(-0.33 * 1.02)E+O0

(1.43 t 2.95)E-01

(-3.52 & 1.05)E-01

(-1 .66 * 4.76)E4M

(-5.84* 1.00)E-01

(-1.50 * 3.21)E-01

(-6.54 * 3.60)E-01

(4.05 t 5.91)E-01

(0.06 t4.76)E-01

(0.03 f4.78)E-01

(0.39 A 1.33)E+O0

(4.72 t 6.04)E-01

(-0.33 A 5.56)E-01

(2.62 t 3.77)E-01

(3.76 A 4.65)E41

(-0.51 f 1.05)E+O0

(-0.05 * 6.ll)E-01

(2.46 t 5.35)E-01

(4.66 * 5.35)E-01

(1.74 k4.73)E-01

(2.25 ~ 5.27)E-01

(-2.46 k 3.78)E+1

(-0.33 * 6.33)E-01

(-0.40 A 5.71)E-01

(7.81 A 8.27)E-01

(4.83 * 6.37)E-01

(-2.32 t 4.55)E-01

(2.07 A 5.90)E-01

(-4.73 A 4.42)E-01

(0.77 t 3.28)E-01

(-2.39 * 5.15)E-01

(-2.51 * 4.83)E-01

(-7.49 * 4.67)E-01

(-5.79 * 3.20)E-01

(-6.58 * 3.70)E-01

(-3.25 * 4.84)E-01

(-6.59 *5.90)E-01

(-4.66 * 3.03)E-01

(-2.72 * 5.20)E-01

(-7.43 * 4.26)E-01

(-5.47 * 4.56)E+1

(-2.81 * 5.56)E-01

(-4.55 t 3.07)E-01

(-4.83 * 8.57)E-01

(-3.62 + 5.56)E-01

(-5.17 k 3.29)E-01

(-5.56 + 5.36)E-01

(-7.24 * 3.95)E-01

(-1.22 * 0.69)E+O0

(-0.35 * 5.56)E-01

(-4.20 * 4.O1)E-01

(-7.03 * 6.06)E41

(-6.68 k 3.62)E-01

(-5.17 * 3.45)E-01

(-8.89 * 5.03)E-01


—

./ . .


Table 27Radioactivity in Aquatic Food Products — Saltwater Fish

Page 1 of 1

No. ofLocation Samples Arithmetic Mean ~ a Maximum * a Minimum * cs

Note: Only edible portions were analyzed.

CO-60, pCtig

RM-O/8 Savannah River Mouth (HwY-17A Bridge Area)

Marine Catfish 3 (-8.43 k 8.20)E-03 (0.05 * 1.46)E-02 (-1 .56 * 1.45)E-02

Marine Mullet 3 (-1 .75 + 1.64)E-02 (-0.63 * 1.57)E-02 (-3.63 * 1.57)E-02

Red Fish (drum) 3 (-9.15 A 9.87)E-03 (0.22 t 1.36)E-02 (-1 .53 t 1.22)E-02

CS-137, pcdg

RM-O/8 Savannah River Mouth (Hwy-17A Bridge Area)

Marine Catfish 3 (0.15 A 1.17)E-02 (1.17 + 1.52)E-02 (-1 .12 + 1.47)E-02

Marine Mullet 3 (4.27 k 1.56)E-02 (6.04 f 1.81)E-02 (3.07 * 1.91)E-02

Red Fish (drum) 3 (2.48 * 1.15)E-02 (3.46 * 1.34)E-02 (1.22+ 1.47)E-02

Gross Beta, pCi/g

RM-O/8 Savannah River Mouth (HvJY-17A Bridge Area)

Marine Catfish 3 (2.77 * 0.16)E+O0 (2.96 ~ 0.30)E+O0 (2.68 * 0.40)E+O0

Marine Mullet 3 (2.43 t 0.08)E+O0 (2.47 * 0.42)E+O0 (2.33 t 0.37)E+O0

Red Fish (drum) 3 (2.52 * 0.48)E+O0 (3.07 * 0.43)E+O0 (2.16 t 0.39)E+O0

Gross Alpha, pCdg

RM-O/8 Savannah River Mouth (HvvY-17A Bridge Area)

Marine Catfish 3 (-0.68 k 5.01)E-02 (0.51 * 1.46)E-01 (-0.36 t 1.78)E-01

Marine Mullet 3 (-2.24 t 4.23)E-02 (0.26 f 1.27)E-01 (-0.48 t 1.30)E-01

Red Fish (drum) 3 (-1.16 ~ 0.69)E-01 (-0.43 A 1.98)E-01 (-1 .80 * 1.56)E-01



Table 28Radioactivity in Aquatic Food Products — Shellfish

Page 1 of 1

No. ofLocation Samples Arithmetic Mean * a Maximum * c Minimum * o

CO-60, pCi/g

RM-O/8 Savannah River 2 (0.66 * 1.17)E-02 (1.48 t 1.12)E-02 (-0.16 ~ 1.12)E-02Mouth (Savannah Shellfish)

CS-137, pCi/g

RM-O/8 Savannah River 2 (6.27 A 5.75)E-03 (1.03 t 1.1O)E-O2 (0.22 t 1.22)E-02Mouth (Savannah Shellfish)

Sr-89,90, pCi/g

RM-O/8 Savannah River 2 (-1 .22 * 1.22)E-03 (-0.04 k 1.06)E-02 (-0.21 ~ 1.03)E-02Mouth (Savannah Shellfish)

Gross Beta, pCi/g

RM-O/8 Savannah River 2 (1.44 A 0.51)E+O0 (1.80 * 0.24)E+O0 (1.08 ~ 0.27)E+O0Mouth (Savannah Shellfish)

Gross Alpha, pCi/g

RM-O/8 Savannah River 2 (1.09 t 1.12)E+O0 (1.88 * 0.41)E+O0 (2.96 ~ 2.02)E-01Mouth (Savannah Shellfish)



F

‘51-

almIf

c.-


Table 30Radioactivity in River and Stream Sediment

Page 1 of 8

Location River Mile 1994 1995 1996 1997 1998

Note: Blankspacesindicateactivitywasbe/owthelowerlimitof detection.

CO-60, pCi/g (dry weight)

Savannah River

Beaver Dam Creek river mouth

Highway 301

Lower Three Runs mouth

Above Lower Three Runs

Below Little Hell Landing

Above Little Hell Landing

Steel Creek-Pen Branch mouth

Below Four Mile Creek

R-3A above Vogtle

Upper Three Runs mouth

Demiere’s Landing (control)

SRS Streams

Four Mile 2 at Road 4

118.7

129.0

129.5

134.0

136.6

141.0

150.2

151.0

157.2

160.5

Four Mile 3A below F-Area effluent

Four Mile A-7A (in a beaver pond)

Four Mile discharge at swamp

Four Mile at Road A-7

Lower Three Runs 1A at Road B

Pen Branch discharge at swamp


Steel Creek discharge at swamp

(1.17* 0.06)E+O0

(6.27 t 1.13)E-02

(2.49 t 0.15)E-01

(0.22 k 2.16)E-02

(0.01 t 2.53)E-02

(4.46 t 2.76)E-02

(7.01 A 2.24)E-02

(1.07 k 2.21 )E-02

(2.82 A 0.69)E-02

(-1 .09 * 2.72)E-02

(-0.74 * 1.26)E-02

(4.37 A 2.50)E-02

(1.92 t 0.12)E-01

(2.11 t 1.07)E-02

(1.57 A 0.80)E-02

(8.43 * 3.51 )E-02

(3.17 t 0.26)E-01 (2.1OAO.12)E4I (9.12 & 0.89)E-02

(-0.79 * 1.08)E-02

(9.31 t 2.94)E-02

(1.90 t 1.41)E-02

(-0.28 A 1.ll)E-02

(0.05 k 6.60)E-03

(-2.11 * 2.32)E-02

(-1 .09 k 1.28)E-02

(-1 .93 t 1.12)E-02

(1.10 t 0.62)E-02

(-1 .26 k 1.77)E-02

(1.35 t 0.13)E-01

(1.05* 0.09)E-01

(5.66 t 0.73)E-02

(0.86 A 1.06)E-02

(-4.69 t 3.23)E-02

(1.65A 0.63)E-02

(-0.51 t 1.78)E-02

(4.95 t 1.26)E-02

(-1.34 t 1.63)E-02

(1 .38* 1.66)E-02

(-0.94 * 1.51)E-02

(-1 .43 A 1.51)E-02

(00.00 * 4.31)E-02

(-0.88 * 1.75)E-02

(8.67 * 1.13)E-02

(0.84 k 1.08)E-02

(9.14 A 1.72)E-02

(7.77 t 0.90)E-02

(-8.07 * 9.78)E-03

(-1 .89 t 0.96)E-02

(5.85 A 3.48)EW2

(1.55 k 0.14)E-01


s.-

.i-

.+1d-

~

6mm.—1%

+1 +1 +1 +1 +1 +1 +1 +1

+1 +1 +1 +1 +1 +1 +1

n)

aVI



z“J.J’ii7ii7Oq00

@aa)u)If H+l+l i-1+1

tmmmo:CQo. 1-w.r -NW.----

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00

litg0+1Fq1-

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Y

E

—



Page 4 of 8


R-3A above Vogtle 151.0

Upper Three Runs mouth 157.2

Demiere’s Landing (control) 160.5

SRS Streams



Four Mile A-7A (in a beaver pond)


Four Mile at Road A–7



R-Area downstream of R–1

Steel Creek discharge at swamp

Steel Creek 4 at Road A

Steel Creek at Road B(SC-2A, 1 mile above Road B)

Tires Branch 4A (1.42 ~ 0.07)E+O0 (2.53 * 0.12)E+O0

Tires Branch 4B

Tires Branch 5 near Road C

Tinker Creek 1

Upper Three Runs 1A, Treadway Bridge,Road 8-1

Pu-238, pCi/g (dry weight)

Savannah River

Beaver Dam Creek river mouth (0.06 + 3.21)E-04 (1.14 *0.58)E-03

Highway 301 118.7 (1.11 t 0.26)E-03 (1.30* 0.52)E-03 (1.16 t 0.53)E-03 (-4.53 t 1.93)E-03 (2.21 + 1.13)E-03


a‘a10a)mIf

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WSRGTR-98-O0314SRSEnvironmental Datafor1998 705


Page 6 of 8


Tinker Creek 1 (-0.06 t 1,22)E-03 (7.11 * 8.05)E-04

lJ~~r~~e Runs 1A, Treadway Bridge, (0.21 t 1.08)E-03 (5.74 k 7.14)E-04

Pu-239, pCi/g (dry weight)

Beaver Dam Creek river mouth

Highway 301 118.7

Lower Three Runs mouth 129.0

Above Lower Three Runs 129.5

Below Little Hell Landing

Above Little Hell Landing

Steel Creek-Pen Branch mouth

Below Four Mile Creek

R–3A above Vogtle

34.0

36.5

41.0

50.2

51.0

Upper Three Runs mouth 157.2

Demiere’s Landing 160.5

SRS Streams



Four Mile A–7A (in a beaver pond)


Four Mile at Road A-7




(3.88 ~ 1.67)E-04

(4.04 k 0.78)E-03

(2,48 f 0.43)E-03

(1.00 * 0.20)E-03

(5.28 t 1.84)E-04

(4.10 * 1.79)E-04

(1,25 f 0.36)E-03

(2.69 k 0.31)E-03

(2.03 t 0.44)E-03

(5.25 * 0.12)E-01

(4.11 ~ 0.46)E413

(8.72 t 0.31)E-02

(1.43 t 0.09)E-02

(8.23 A 1.09)E-03

(1.92 t 0.34)E-03

(2.17 t 0.41)E-03

(5.86 t 0.55)E-03

(2.34 A 0.44)E-03

(5.24 t 0.76)E-03

(2.89 k 0.77)E-03

(5.05 A 0.62)E-03

(1.26 f 0.29)E-03

(1.30 t 0.59)E-03

(1.81 t 0.37)E-03

(-7.78 * 6.19)E-04

(1.41 t 0.ll)E-02

(9.51 A 5.40)E-04

(2.27 * 1.68)E-03

(3.75 k 4,27)E-04

(3.88 A 5.ll)E-04

(2.71 k 3.ll)E-04

(-1.55 ~ 4.83)E-04

(3.46 k 1.31)E-03

(2.31 ~ 5.94)E44

(0.33 * 4.62)E-04

(7.18 * 0.56)E-02

(5.57 t 6.41)E-04

(5.29 * 1.14)E-03

(1.97 t 0.27)E-02

(7,28 A 3.59)E-04

(2.36 ~ 2.48)E-03

(-3.85 A 9.78)E-04

(1.07* 0.93)E-03

(-2.76 * 7,25)E-04

(1.03* 1.18)E-03

(3.97 t 1.95)E-03

(-0.47 t 1.05)E-03

(3.13 t2.ll)E-03

(1.50A 0.33)E-02

(1.24 t0.15)E-01

(4.95 * 1.48)E-03

(5.58 t 0.75)E-02

(-1 .98 + 0,96)E-03

(2.35 A 0.44)E-02

(1.08* 0.55)E-03

(-2.03 k 3.51)E-04

(1.36 t 1.08)E-03

(2.22 t 1.19)E-03

(0.52 * 1.27)E-03

(1.84 t 0.93)E-03

(-3.94 t 7.06)E-04

(3.33 A 0.51)E-02

(-4.62 t 5.61)E-04

(3.03 & 0.37)E-02

(5.09 k 1.72)E-03

(7.03 t 0.90)E-02

(6.81 * 1.81)E-03

(6.63 ~ 1.66)E-03

(-4.54 t 5.51)E-04

(3,22 t 0.35)E-02

(8.56 + 0.87)E-02


+1 +1

+1+ 1-H-1+-H

1-

-H.-iicoqu

a

is&>.=

o-0(6i? a-

m

WSRGTR-98-00314SRSEnvironmental Datafor 1998 107


co

4 +1-H-H-H-H

.+H

.

.6

l-l +1 -HCoolo-C6ti--

m

UJcz UY



m%1-

00)2

WSRGTR-98-f0314SRS Environmet?tal Dat~ for 1998 109


m

N

c.-

-i-l +1 +1 +1 +1 +1

-u(0L?



C9

C9a)UIx

s.-

++

-H

-H

WSRC-TR-98-O0314SRS Environmental Data for 1998 111


Table 32Meteorological Data

Page 1 of 7

USNRC Computer Code-XOQDOQ, Version 2.0 Run Date: 98.077 (SRL 6/29/83 VERSION)43848 Wind Stats H-Area 60 minute 62M 92-96 Stability from Sigma A

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class AExtremely Unstable Conditions

(M/S) NUMAX NNE NE ENE E ESE SE SSE

2.00 0.445 0.420 0.449 0.436 0.440 0.379 0.331 0.376

4.00 0.997 0.791 0.983 1.163 1.106 0.805 0.620 0.504

6.00 0.787 0.465 0.292 0.244 0.160 0.132 0.146 0.096

8.00 0.112 0.137 0.009 0.011 0.002 0.011 0.014 0.002

12.00 0.011 0.007 0.000 0.000 0.000 0.002 0.000 0.000

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 2.352 1.820 1.733 1.854 1.708 1.329 1.111 0.978

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class AExtremelv Unstable Conditions

(M/S) S -UMAX Ssw Sw Wsw w WNW NW NNW TOTAL

2.00 0.376 0.369 0.497 0.536 0.399 0.406 0.301 0.381 6.541

4.00 0.689 0.862 1.090 1.473 1.305 0.844 0.509 0.579 14.320

6.00 0.192 0.221 0.324 0.335 0.367 0.308 0.141 0.267 4.477

8.00 0.011 0.027 0.036 0.075 0.046 0.068 0.016 0.064 0.643

12.00 0.000 0.002 0.002 0.009 0.021 0.023 0.000 0.009 0.087

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 1.268 1.481 1.949 2.428 2.138 1.649 0.967 1.300 26.068


_.—



Page 2 of 7


Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class BModerately Unstable Conditions


2.00 0.046 0.082 0.082 0.073 0.050 0.034 0.030 0.059

4.00 0.312 0.504 0.602 0.682 0.461 0.342 0.219 0.223

6.00 0.123 0.440 0.481 0.422 0.180 0.137 0.109 0.151

8.00 0.002 0.116 0.048 0.023 0.018 0.018 0.025 0.025

12.00 0.000 0.014 0.000 0.000 0.000 0.000 0.000 0.002

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.483 1.156 1.213 1.200 0.709 0.531 0.383 0.460

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class BModerately Unstable Conditions

(M/S) SUMAX Ssw Sw Wsw w WNW NW NNW TOTAL

2.00 0.048 0.071 0.068 0.089 0.032 0.062 0.064 0.052 0.942

4.00 0.342 0.303 0.461 0.584 0.395 0.344 0.176 0.208 6.158

6.00 0.205 0.265 0.395 0.639 0.477 0.315 0.123 0.123 4.584

8.00 0.014 0.046 0.132 0.189 0.353 0.246 0.043 0.009 1.309

12.00 0.000 0.002 0.018 0.055 0.105 0.096 0.025 0.005 0.322

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.609 0.687 1.074 1.556 1.362 1.063 0.431 0.397 13.315




Page 3 of 7


Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class CSlightly Unstable Conditions

(MIS)UMAk N NNE NE ENE E ESE SE SSE

2.00 0.039 0.046 0.052 0.046 0.027 0.043 0.057 0.071

4.00 0.198 0.600 1.234 0.842 0.618 0.360 0.342 0.388

6.00 0.084 0.579 1.070 0.607 0.426 0.326 0.315 0.360

8.00 0.000 0.091 0.287 0.114 0.064 0.052 0.114 0.155

12.00 0.000 0.009 0.007 0.011 0.007 0.007 0.014 0.048

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.321 1.325 2.650 1.620 1.142 0.788 0.842 1.022

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class CSlightly Unstable Conditions

(MIS)UMAX s Ssw Sw Wsw w WNW NW NNW TOTAL

2.00 0.055 0.046 0.041 0.036 0.034 0.034 0.052 0.039 0.718

4.00 0.486 0.556 0.618 0.725 0.543 0.422 0.251 0.239 8.422

6.00 0.411 0.447 0.607 0.627 0.666 0.598 0.230 0.064 7.417

8.00 0.107 0.217 0.281 0.347 0.536 0.426 0.082 0.007 2.880

12.00 0.041 0.062 0.062 0.105 0.210 0.148 0.021 0.002 0.753

14.10 0.000 0.000 0.000 0.002 0.005 0.000 0.000 0.000 0.007

TOTAL 1.100 1.328 1.609 1.842 1.994 1.628 0.636 0.351 20.197




Page 4 of 7

USNRC Computer Code-XOQDOQj Version 2.0 Run Date: 98.077 (SRL 6/29/83 VERSION)43848 Wind Stats H-Area 60 minute 62M 92-96 Stability from Sigma A

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class DNeutral Conditions

$& NNNE NE ENE E ESE SE SSE

2.00 0.009 0.032 0.027 0.032 0.036 0.034 0.036 0.048

4.00 0.109 0.392 1.168 0.728 0.529 0.440 0.541 0.639

6.00 0.073 0.445 1.122 0.618 0.559 0.534 0.661 1.008

8.00 0.000 0.034 0.080 0.034 0.023 0.025 0.039 0.296

12.00 0.002 0.000 0.005 0.002 0.000 0.000 0.005 0.039

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.193 0.903 2.402 1.414 1.147 1.033 1.282 2.030

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class DNeutral Conditions

$& sSsw Sw Wsw w WNW NW NNW TOTAL

2.00 0.016 0.048 0.050 0.039 0.014 0.011 0.039 0.027 0.499

4.00 0.759 0.789 0.716 0.730 0.600 0.483 0.381 0.294 9.298

6.00 1.259 0.737 0.949 0.917 0.741 0.705 0.358 0.103 10.787

8.00 0.242 0.148 0.135 0.068 0.052 0.039 0.030 0.002 1.247

12.00 0.032 0.023 0.018 0.002 0.027 0.005 0.000 0.000 0.160

“ 14.10 0.000 0.000 0.000 0.000 0.023 0.005 0.000 0.000 0.027

TOTAL 2.308 1.745 1.868 1.756 1.457 1.248 0.808 0.426 22.018




Page 5 of 7


Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class ESlightly Stable Conditions


2.00 0.000 0.005 0.014 0.002 0.005 0.014 0.014 0.021

4.00 0.034 0.244 0.643 0.246 0.217 0.315 0.369 0.477

6.00 0.036 0.591 0.750 0.762 0.509 0.513 0.625 0.755

8.00 0.000 0.011 0.023 0.025 0.021 0.014 0.009 0.027

12.00 0.000 0.000 0.000 0.002 0.000 0.000 0.000 0.000

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.070 0.851 1.430 1.037 0.752 0.856 1.017 1.280

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class ESlightly Stable Conditions

(M/S) sUMAX Ssw Sw Wsw w WNW NW NNW TOTAL

2.00 0.032 0.021 0.007 0.007 0.009 0.007 0.011 0.007 0.173

4.00 0.529 0.543 0.452 0.525 0.353 0.278 0.267 0.249 5.740

6.00 0.953 0.876 0.889 0.855 0.392 0.338 0.242 0.125 9.211

8.00 0.041 0.030 0.055 0.009 0.009 0.007 0.002 0.000 0.283

12.00 0.000 0.000 0.000 0.005 0.014 0.002 0.000 0.000 0.023

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 1.555 1.470 1.403 1.401 0.777 0.632 0.522 0.381 15.430




Page 6 of 7

USNRC Computer Code-XOQDOQ, Version 2.0 Run Dat= 98.077 (SRL 6/29/83 VERSION)43848 Wind Stats H-Area 60 minute 62M 92-96 Stability from Sigma A

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class FModerately Stable Conditions

gl! NNNE NE ENE E ESE SE SSE

2.00 0.002 0.002 0.000 0.000 0.000 0.000 0.002 0.002

4.00 0.007 0.064 0.084 0.018 0.016 0.036 0.057 0.050

6.00 0.016 0.212 0.130 0.100 0.096 0.178 0.155 0.155

8.00 0.000 0.014 0.002 0.000 0.002 0.005 0.002 0.005

12.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.025 0.292 0.216 0.118 0.114 0.219 0.216 0.212

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class FModerately Stable Conditions

JL#3& sSsw Sw Wsw w WNW NW NNW TOTAL

2.00 0.002 0.000 0.002 0.009 0.000 0.000 0.000 0.000 0.023

4.00 0.087 0.071 0.062 0.103 0.021 0.027 0.041 0.068 0.812

6.00 0.171 0.135 0.182 0.235 0.059 0.048 0.023 0.030 1.925

8.00 0.002 0.002 0.005 0.009 0.000 0.000 0.005 0.000 0.052

12.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.262 0.208 0.251 0.356 0.080 0.075 0.069 0.098 2.812


I



Page 7 of 7


Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class GExtremely Stable Conditions

(MIS)UMAk N NNE NE ENE E ESE SE SSE

2.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

4.00 0.000 0.007 0.002 0.000 0.000 0.002 0.000 0.000

6.00 0.002 0.014 0.009 0.002 0.002 0.014 0.014 0.011

8.00 0.000 0.000 0.000 0.000 0.000 0.000 0.002 0.000

12.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.002 0.021 0.011 0.002 0.002 0.016 0.016 0.011

Joint Frequency Distribution of Wind Speed and Direction: Atmospheric Stability Class GExtremely Stable Conditions

(MIS)UMAX s Ssw Sw Wsw w WNW NW NNW TOTAL

2.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

4.00 0.007 0.002 0.002 0.002 0.002 0.002 0.000 0.005 0.034

6.00 0.011 0.014 0.007 0.016 0.002 0.000 0.002 0.002 0.123

8.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.002

12.00 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

14.10 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000

TOTAL 0.018 0.016 0.009 0.018 0.004 0.002 0.002 0.007 0.159


-—


Table 3380-km-Radius (50-Mile) Population Distribution Around SRS (1990 Census)

Page 1 of 1

Dir (Miles)a 5-1o 10-20 20-30 30-40 40-50 Total

N’- 2.600E+01

NNE 6.000E+OO

NE 1.000E+OO

ENE 2.700E+01

E 1.550E+02

ESE 3.600E+01

SE 2.600E+01

SSE 4.000E+O1

s 1.000E+OO

Ssw 2.000E+OO

Sw 1.700E+01

Wsw 6.000E+O1

w 5.500E+01

WNW 4.490E+02

NW 2.710E+02

NNW 3.63E+02

Total 1.535E+03

5.321 E+03

1.320E+03

2.945E+03

3.126E+03

6.743E+03

1.556E+03

5.470E+02

3.91 OE+O2

5.580E+02

8.970E+02

9.440E+02

1.103E+O3

3.314E+03

3.342E+03

5.899E+03

1.803E+04

5.603E+04

1.002E+04

2.066E+03

2.928E+03

4.483E+03

5.305E+03

1.931E-I-03

6.511E+03

7.690E+02

1.332E+03

2.008E+03

2.240E+03

7.112E+03

7.941E+03

1.069E+05

8.793E+04

2.716E+04

2.766E+05

5.067E+03

4.445E+03

5.269E+03

5.337E+03

8.812E+03

2.711E+03

6.685E+03

1.356E+03

7.251E+03

4.181E+03

2.606E+03

2.285E+03

7.994E+03

5.031E+04

2.657E+04

6.665E+03

1.475E+05

1.221E+04

1.437E+04

1.020E+04

4.077E+04

4.334E+03

3.253E+03

8.577E+03

2.539E+03

3.335E+03

2.944E+03

2.660E+03

5.818E+03

6.780E+03

1.155E+04

3.025E+03

6.079E+03

1.384E+05

3.264E+04

2.220E+04

2.134E+04

5.375E+04

2.535E+04

9.487E+03

2.235E+04

5.095E+03

1.248E+04

1.003E+04

8.467E+03

1.638E+04

2.608E+04

1.725E+05

1.237E+05

5.830E+04

6.201E+05

a No one lives within 5 milesof thecenterof SRS beoause all areaswithinthis distanceare inside the site boundaty.



Table 3480-km-Radius (50-Mile) Milk, Meat, and Vegetation Production Around SRSas of 1991

Page 1 of 2

Site Annual Milk Production (L)

Dir (miles) O-5 5-10 10-20 20-30 30-40 40-50 Total

N 0.0 0.0

NNE 0.0 0.0

NE 0.0 0.0

ENE 0.0 0.0

E 0.0 0.0

ESE 0.0 0.0

SE 0.0 0.0

SSE 0.0 0.0

s 0.0 0.0

Ssw 0.0 0.0

Sw 0.0 0.0

Wsw 0.0 0.0

w 0.0 0.0

WNW 0.0 0.0

NW 0.0 0.0

NNW 0.0 0.0

Total 0.0 0.0

Site Annual Meat Production (kg)

Dir (miles) O-5 5-10

N 0.0 0.0 5.300E+04 8.800E+04 2.500E+05 9.800E+05 1.371 E+08

NNE 0.0 0.0 5.300E+04 8.800E+04 2.000E+05 4.100E+05 7.51OE+O5

NE 0.0 0.0 7.1OOE+O4 1.700E+05 3.500E+05 4.500E+05 1.041E+06

ENE 0.0 0.0 8.300E+04 2.000E+05 4.600E+05 5.700E+05 1.313E+06

E 0.0 0.0 8.300E+04 1.900E+05 3.400E+05 5.1OOE+O5 1.123E+06

ESE 0.0 0.0 8.300E+04 1.900E+05 2.200E+05 2.500E+05 7.430E+05

SE 0.0 0.0 1.200E+05 2.1OOE+O5 2.600E+05 3.000E+05 8.900E+05

SSE 0.0 0.0 1.1OOE+O5 1.900E+05 2.600E+05 2.900E+05 8.500E+05

s 0.0 0.0 9.400E+04 1.500E+05 2.000E+05 2.700E+05 7.140E+05

Ssw 0.0 0.0 9.500E+04 1.800E+05 2.900E+05 3.900E+05 9.550E+05

Sw 0.0 0.0 9.500E+04 1.700E+05 2.700E+05 3.200E+05 8.550E+05

4.200E+04

4.200E+04

3.200E+04

2.500E+04

2.500E+04

2.500E+04

2.500E+03

4.800E+05

1.000E+06

9.900E+05

9.900E+05

9.900E+05

6.700E+05

2.300E+05

4.200E+04

4.200E+04

5.62E+06

10-20

6.900E+04

6.900E+04

1.000E+06

1.200E+06

1.400E+06

5.600E+05

0.000E+OO

8.600E+05

2.1OOE+O6

3.800E+06

2.200E+06

1.700E+06

1.300E+06

1.1OOE+O6

3.800E+05

6.000E+04

1.781E+07

20-30

1.000E+06

2.1OOE+O5

2.700E+06

4.400E+06

3.900E+06

3.000E+04

0.000E+OO

1.200E+06

3.000E+06

7.400E+06

5.800E+06

2.400E+06

2.200E+06

1.200E+06

1.400E+06

1.700E+06

3.954E+07

30-40

5.300E+06

5.000E+05

2.000E+06

5.200E+06

4.900E+06

4.900E+05

0.000E+OO

1.200E+06

3.500E+06

7.600E+06

4.800E+06

3.500E+06

3.600E+06

2.000E+06

1.000E+06

3.400E+06

4.899E+07

40-50

6.411E+06

8.21OE+O5

5.732E+06

1.083E+07

1.023E+07

1.105E+O6

2.500E+03

3.740E+06

9.600E+06

1.979E+07

1.379E+07

8.590E+06

7.770E+06

4.530E+06

2.822E+06

5.211E+06

1.11OE+O8

Total

WSRGTR-98-00374120 SRSEnvironmental Datafor1998


Table 3480-km-Radius (50-Mile) Milk, Meat, and Vegetation Production Around SRSas of 1991

Page 2 of 2

Site Annual Meat Production (kg), Cent’d.

Dir (miles) O-5 5-10 10-20 20-30 30-40 40-50 Total

Wsw 0.0 0.0 9.500E+04 1.600E+05 2.300E+05 4.000E+05 8.850E+05

w 0.0 0.0 5.800E+04 1.000E+05 2.100E+05 4.1OOE+O5 7.780E+05

WNW 0.0 0.0 4.800E+04 6.200E+04 1.300E+05 2.900E+05 5.300E+05

NW 0.0 0.0 5.800E+04 8.000E+04 2.800E+05 2.700E+05 6.830E+05

NNW 0.0 0.0 5.300E+04 8.800E+04 3.300E+05 6.200E+05 1.091E+06

Total 0.0 0.0 1.247E+06 2.316E+06 4.280E+06 6.730E+06 1.457E+07

Site Annual Vegetation Production (kg)

Dir (miles) O-5 6-10 10-20 20-30 30-40 40-50 Total

N

NNE

NE

ENE

E

ESE

SE

SSE

s

Ssw

Sw

Wsw

w

WNW

NW

NNW

Total

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

3.600E+05

3.600E+05

3.600E+05

3.600E+05

3.600E+05

3.600E+05

2.500E+06

1.700E+06

7.200E+04

3.500E+02

3.500E+02

3.500E+02

4.500E+04

2.600E+05

3.600E+05

3.600E+05

7.458E+06

6.000E+05

6.000E+05

6.900E+05

6.600E+05

5.900E+05

2.200E+06

4.500E+06

2.900E+06

5.400E+05

1.200E+05

7.800E+02

5.800E+02

2.300E+04

3.800E+04

4.300E+05

6.000E+05

1.449E+07

8.400E+05

5.1OOE+O5

1.000E+06

1.200E+06

8.500E+05

1.900E+06

3.000E+06

3.600E+06

8.400E+05

2.500E+05

2.200E+03

7.900E+03

1.700E+04

6.200E+04

8.400E+05

8.400E+05

1.614E+07

8.700E+05

6.300E+03

5.000E+05

1.500E+06

1.400E+06

1.1 OOE+O6

1.1OOE+O6

1.1 OOE+O6

9.700E+05

1.1 OOE+O5

3.1 OOE+O5

2.900E+03

5.200E+04

1.1 OOE+O6

1.1OOE+O6

1.1 OOE+O6

1.232E+07

2.670E+06

1.476E+06

2.550E+06

3.270E+06

3.200E+06

5.560E+06

1.11OE+O7

9.300E+06

2.422E+06

4.804E+05

3.133E+05

1.173E+04

1.370E+05

1.848E+06

2.730E+06

2.900E+06

5.041E+07



Table 35Airborne Release Locations for Maximally Exposed Individual Dose

Page 1 of 1

Release Source AreaSavannah River

F,H,P,K,C M D Technology Center Diffuse & Fugitive

Release height, m 61 0 16 ’31 0

Release locationSite coordinate

East 58000 50041 20938 51863 58000

North 62000 104828 65284 106670 62000


—


Table 36Parameters Used for Adult Consumption Ratesand for Atmospheric Dose Calculations

Page 1 of 1

Pathway Maximally Exposed Individual Population

Note: Values were determined by the Savannah River Technology Center for SRS.

Fruits, vegetables, and grains (kg/yr) 276 163

Leafy vegetables (kg/yr) 43 21

Cow milk (Uyr) 230 120

Goat milk (L/yr) 230 rda

Meat (beef) (kg/yr) 81 43

Inhalation (m3/yr) 8,000 8,000

Fraction of external dose received after taking 0.7 0.5structural shielding into account



Table 37Site-Specific Parameters Used with CAP88 Code Used for NESHAPSCalculations

Page 1 of 1

Particle size, AMADa

H-3, C-1 4, Kr-85

All other

Meteorological data

Plume rise

Number of stacks

Stack heights, m

Height of lid, m

Rainfall, crn/yr

Average air temperature, C

Surface roughness length, m

Height of wind measurements, m

Average wind speed, M/s

Population size

Food supply fractions (fraction from local sources)

Vegetable

Meat

Milk

o

1

1992–96; H-Area

None

2

0 and 61

1000

122.4

17.8

0.4

61

3.92

620,100

0.70

0.44

0.40

a Activity Median Aerodynamic Diameter


-. -m- ;


Table 38Parameters Used for Adult Consumption Ratesand for Liquid Dose Calculations

Page 1 of 1

Pathway Maximally Exposed Individual Population

Note: Values were determined by the Savannah River Technology Center for SRS.

Water consumption (L/yr) 730 370

Fish consumption (kg/yr) 19 9

Marine invertebrates (kg/yr) Not applicable 2

Boatinga 21 1,100,000

Swimminga 8.9 160,000

Shoreline recreation 23 960,000

Water treatment plantsb

Water consumption (L/yr) 730 370

a Maximum individual values are in units of hourslyear. Population values are in units of peraon-hours/year and are applicable tothe 80-kilometer population of 620,100.

b The drinking water pathway dose is calculated for the maximally exposed individual and for the population served by thedownriver Beaufort-Jasper Water Treatment Plant (60,000 people) near Beaufort, S.C., and the City of Savannah Industrial andDomestic Water Supply Plant (10,000 people) at Port Wentworth, Ga.



Table 39Site-Specific Parameters Used in Liquid Dose Calculations

Page 1 of 1

River flow rate at Highway 301 for 1998 (CUft/sec)a

River dilution in estuary

Transit time from process areas to river (hr)

Transit time from SRS to water treatment plants (hr)

Water treatment time (hr)

Edible aquatic food harvest (kg/yr)

Fish – SpOlt

Fish - commercial

Invertebrates - salt water

Irrigation (acres devoted to each of thefour major food types)

Shore width factor

Fish bioaccumulation factor for cesium

12,521

3

24

72

24

35,000b

2,700b

390,000b1,ooobJc

0.2

3,000

a The effeti”ve river flow rate was based on tritium measurements. The measured river flow rate was 16,329 cfs.b Values determined by SRTC for SRS [Hamby, 1991]. The LADTAP II dose madel prorates the aquatic food harvest amongej

the 80-kilometer population of 620,100.c Inigation is considered a “special case” scenario. The food produced on each 1,000-acre parcel is assumed to be eaten by

the 80-kilometer population of 620,100.


—..


Table 40Committed Dose to the Maximally Exposed Individual(MAXIGASP Code – Using Consumption of Cow Milk

from Atmospheric ReleasesPathway)

Page 1 of 1

Pathway Maximally Exposed Individual Dose (mrem)a Percent of Total Dose

Plume 4.49E-05 0.07

Ground 7.78E-04 1.1

Inhalation 2.92E-02 42.6

Vegetation 2.86E-02 41.8

Cow milk 7.09E-03 10.4

Meat 2.72E-03 4.0

Total 6.85E-02

Radionuclide Maximally Exposed Individual Dose (mrem)a Percent of Total Doseb

Gases and Vapors

H-3 4.58E-02 66.8

C-14 1.67E-05 0.02

Kr-85 4.49E-05 0.07

I-129 7.05E-03 10.3

Particulate

CO-60

Sr-90

Cs-134

Cs-137

Ra-228

Th-228

Th-230

U-234

U-238

Pu-238

Pu-239

Am-241

Am-243

Cm-244

Total

2.1OE-O5

2.35E-03

1.04E-05

8.44E44

1.63E-05

1.39E-05

1.63E-05

2.83E-05

6.62E-05

1.46E-03

1.03E-02

1.14E-04

8.01E-05

2.88E44

6.85E-02

a Committed effective dose equivalentb Radionuclides contributing 0,01?’. or more of the total dose

0.03

3.4

0.02

1.2

0.02

0.02

0.02

0.04

0.1

2.1

15.0

0.2

0.1

0.4



Table 41Committed Dose to the Maximally Exposed Individual from AtmosphericReleases (MAXIGASP Code — Using Consumption of Goat Milk Pathway)

Page 1 of 1

Pathway Maximally Exposed individual Dose (mrem)a Percent of Total Dose

Plume 4.49E-05 0.06

Ground 7.78E-04 1.0

Inhalation 2.92E-02 38.0


Goat Milk 1.54E-02 20.1

Meat 2.72E-03 3.5

Total 7.68E-02

Radionuclide Maximally Exposed Individual Dose (mrem)a Percent of Total Doseb

Gases and Vapors

H-3

C-14

Kr-85

1-129

Particulate

CO-60

Sr-90

CS-137

Ra-228

Th-228

Th-230

U-234

U-238

Pu-238

Pu-239

Am-241

Am-243

Cm-244

Total

5.38E-02

1.73E-05

4.49E-05

7.23E-03

2.1 OE-O5

2.40E-03

9.22E-04

1.44E-05

1.39E-05

1.63E-05

2.82E-05

6.60E-05

1.46E-03

1.03E-02

1.1 4E-04

8.01 E-05

2.88E-04

7.68E42

a Committed effective dose equivalentb Radionuclides contributing 0.01%’. or more of the total dose

70.0

0.02

0.06

9.4

0.03

3.1

1.2

0.02

0.02

0.02

0.04

0.1

1.9

13.4

0.1

0.1

0.4



Table 4280-km (50-Mile) Collective Dose from Atmospheric Releases (POPGASP Code)

Page 1 of 1

IPathway Population Dose (person-rem)a Percent of Total Dose

Plume 4.33E-03 0.1

Ground 6.70E-02 1.9

Inhalation 2.40E+O0 69.2


Cow Milk 2.75E-01 7.9

Meat 6.03E-02 1.7

Total 3.47E+O0

Radionuclide Population Dose (person-rem)a Percent of Total Doseb

Gases and Vapors

H-3 2.68E+O0 77.2

C-14 6.55E-04 0.02

Kr-85 4.33E-03 0.1

I-129 2.32E-01 6.7

Particulate

CO-60

Sr-90

CS-134

Cs-137

Ra-228

Th-228

Th-230

Th-232

U-234

U-235

U-238

Pu-238

Pu-239

Am-241

Am-243

Cm-244

1.1OE-03

5.06E-02

3.97E-04

5.71E-02

3.67E-04

8.74E-04

9.94E-04

3.67E-04

3.14E-03

4.41 E-04

6.78E4J3

7.37E-02

3.39E-01

7.43E-03

3.64E-03

1.32E-02

0.03

1.5

0.01

1.6

0.01

0.03

0.03

0.01

0.1

0.01

0.2

2.1

9.8

0.2

0.1

0.4

Total 3.47E+O0

a Committed effective dose equivalentb Radionuclides contributing 0.1% or moreof the total dose



Table 43Total Site Airborne Releases and Maximally Exposed IndividualEffective Dose Equivalent by Radionuclide(CAP88 Dose Calculations for 1998 NESHAP Report to EPA)

Page 1 of 2

Radionuclide Releases (curies) Maximally Exposed Individual EDE (mrem) Percent of Dose. .H-3 (oxide)

Pu-239a

I-129

Pu-238

Sr-89,90b

Cs-137

Cm-244

Kr-85

U-238

Am-241

Am-243

U-234

Th-230

Th-228

CO-60

C-14

U-235

Ra-228

CS-134

U-232

Cm-246

Pu-240

H-3 (elemental)

Pu-241

U-233

Th-232

RU-106

Ra-226

Ce-144

Sb-125

Eu-154

5.86E+04

1.83E-03

1.25E-02

4.43E-04

2.85E-02

5.30E-03

1.34E-04

1.70E+04

1.84E-04

3.89E-05

1.89E-05

7.84E-05

1.02E-05

9.44E-06

1.38E-04

7.02E-02

9.88E-06

2.13E-05

1.31E-04

1.20E-06

9.37E-07

1.12E-06

2.41 E+04

6.02E+5

2.35E46

7.51 E-07

3.34E-05

8.64E-06

1.45E-04

5.29E-05

5.74E~6

7.54E-02

2.13E-03

8.14E-04

4.74E-04

4.02E-04

2.94E-04

1.27E-04

9.99E-05

6.85E-05

6.29E-05

3.42E-05

3.31E-05

8.75E-06

7.44E-06

6.99E-06

4.33E-06

4.1OE-O6

2.40E-06

2.30E-06

1.88E+6

1.73E-06

1.33E-06

1.24E-06

1.14E-06

1.05E-06

9.22E-07

6.83E-07

6.68E47

6.58E-07

2.90E-07

2.31 E-07

94.3

2.7

1.0

0.6

0.5

0.4

0.2

0.1

0.09

0.08

0.04

0.04

0.01

0.009

0.009

0.005

0.005

0.003

0.003

0.002

0.002

0.002

0.002

0.001

0.001

0.001

0.0009

0.0008

0.0008

0.0004

0.0003

a Includes unidentified alpha emissionsb Includes unidentified beta emissions



Table 43Total Site Airborne Releases and Maximally Exposed IndividualEffective Dose Equivalent by Radionuclide(CAP88 Dose Calculations for 1998 NESHAP Report to EPA)

Page 2 of 2

Radionuclide

Pu-242

Co-58

1-131

Zn-65

Nb-95

Tc-99

Zr-95

Xc-l 35

Fe-55

Cm-242

Ru-103

Ce-141

1-133

Eu-152

Cr-51

Eu-155

Np-237

Pa-231

U-236

Ni-63

Na-22

Cm-245

Pm-147

co-57

Sn-126

Ni-59

Releases (curies)

1.59E-07

1.27E-04

6.75E-05

2.23E-05

1.13E-04

2.82E-05

1.71E-05

4.95E-02

3.90E-04

1.58E-07

2.26E-05

4.16E-05

1.59E-04

4.19E-08

1.21E-04

1.1OE+6

1.01E-09

1.00E-09

2.39E-09

8.21E-06

7.76E-11

2.08E–13

9.79E-10

9.40E–11

1.29E-13

8.33E-13

Maximally Exposed Individual EDE (mrem)

1.80E-07

1.32E-07

8.00E-08

6.08E-08

5.50E-08

4.17E-08

2.63E-08

2.00E-08

1.17E-08

9.19E-09

7.95E-09

5.21E-09

2.60E-09

2.04E-09

1.94E-09

1.76E-09

1.66E-09

1.66E-09

9.95E–1 O

3.12E-1 O

1.91E-12

3.93E-13

1.54E–13

5.16E-14

8.43E-16

4.25E-17

Total 8.00E-02

Percent of Dose

0.0002

0.0002

0.0001

0.00008

0.00007

0.00005

0.00003

0.00003

0.00001

0.00001

0.00001

0.000007

0.000003

0.000003

0.000002

0.000002

0.000002

0.000002

0.000001

0.0000004

0.000000002

0.0000000005

0.0000000002

0.00000000006

0.000000000001

0.00000000000005



Table 44NESHAP Airborne-Dose Report Data — CAP88 Compared with MAXIGASP

Page 1 of 1

Maximally Exposed Individual Dose Commitment at Site Boundaryfrom Atmospheric Releases

CAP88 Code MAXIGASP Code

Millirema Percent of Dose Millirema Percent of Dose

By Pathway

Plume

Ground

Inhalation

Foodb

Total

By Radionuclide

Gases and Vapors

H.3c

G14

Kr-85

I-129

Particles

CO-60

Sr-90

CS-134

CS-137

Ra-228

Th-228

Th-230

U-234

U-238

Pu-238

Pu-239

Am-241

Am-243

Cm-244

Total

6.73E-05

3.74E-04

2.42E-02

5.56E-02

8.00E-02

7.54E-02

4.33E-06

9.95E-06

8.14E-04

6.99E-06

4.02E-04

2.30E-06

2.94E-04

2.40E-06

7.44E-06

8.75E-06

3.31 E-05

6.85E-05

4.74E-04

2.13E-03

6.29E-05

3.42E-05

1.27E-04

8.00E42

0.08 4.49E-05 0.07

0.5 7.78E-04 1.1

30.3 2.92E-02 42.6

69.5 3.84E412 56.1

6.85E-02

94.3

0.005

0.01

1.0

0.009

0.5

0.003

0.4

0.003

0.01

0.01

0.04

0.09

0.6

2.7

0.08

0.04

0.2

4.58E-02

1.67E-05

4.49E-05

7.05E-03

2.1OE-O5

2.35E-03

1.04E-05

8.44E44

1.63E-05

1.39E+5

1.63E-05

2.83E-05

6.62E+5

1.46E-03

1.03E-02

1.14E-04

8.01 E-05

2.88E-04

6.85E42

a Committed effective dose equivalentb Meat, milk, and vegetablesc Dose from tritium in foods calculated with absolute humidity of 11.4 g water/cubic meter of air

66.8

0.02

0.07

10.3

0.03

3.4

0.02

1.2

0.02

0.02

0.02

0.04

0.1

2.1

15.0

0.2

0.12

0.4



Table 45NESHAP Airborne-Dose Report Data — CAP88 Compared with POPGASP

Page 1 of 1

Collective Committed Dose from Atmo.$mhericReleases

CAP88 Code POPGASP Code

Person-rema Percent of Dose Person-rema Percent of Dose

By Pathway

Plume

Ground

Inhalation

Foodb

Total

By Radionuclide

Gases and Vapors

H.3C

C-14

Kr-85

1-129

Particulate

CO-60

Sr-90

Cs-134

Cs-137

Ra-228

Th-228

Th-230

Th-232

U-234

U-235

U-238

Pu-238

Pu-239

Am-241

Am-243

Cm-244

Total

8.24E-03 0.1 4.33E-03 0.1

3.91 E-02 0.5 6.70E-02 1.9

2.89E+O0 35.5 2.40E+O0 69.2

5.20E+O0 63.9 1.OIE-00 29.0

8.13E+O0 3.47E+O0

7.72E+O0

4.19E-04

1.22E-03

3.66E-02

8.04E-04

3.18E-02

2.52E-04

3.37E-02

2.53E-04

7.86E-04

9.03E-04

9.71E-05

3.41E-03

4.24E-04

7.06E-03

4.82E-02

2.16E-01

6.52E-03

3.52E-03

1.31E-02

8.13E+O0

95.0

0.005

0.2

0.5

0.01

0.4

0.003

0.4

0.003

0.01

0.01

0.001

0.04

0.005

0.09

0.6

2.7

0.08

0.04

0.2

2.68E+O0

6.55E-04

4.33E-03

2.32E-01

1.1OE-O3

5.06E-02

3.97E-04

5.71 E-02

3.67E-04

8.74E-04

9.94E-04

3.67E-04

3.14E-03

4.41 E-04

6.78E-03

7.37E-02

3.39E-01

7.43E-03

3.64E-03

1.32E-02

3.47E+O0

a Committed effective dose equivalentb Meat, milk, and vegetablesc Dose from tritium in foods calculated with absolute humidity of 11.4 g water/cubic meter of air

77.2

0.02

0.1

6.7

0.03

1.5

0.01

1.6

0.01

0.03

0.03

0.01

0.1

0.01

0.2

2.1

9.8

0.2

0.1

0.4



Table 46Committed Dose to Maximally Exposed Individual from Liquid Releases

Page 1 of 1

By Pathway

Pathway Individual Dose (mrem)a Percent of Total Dose

Fish 6.18E-02 50.3

Water 6.09E-02 49.6

Shoreline 1.95E-04 0,2

Swimming 1.28E-07 0.0001

Boating 1.51 E-07 0,0001

Total 1.23E-01

By Radionuclide

Radionuclide Individual Dose (mrem)a Percent of Total Dose

H-3 (oxide) 4.46E-02 36.3

Sr-90 4.69E-03 3.8

I-129 1.99E-03 1.6

CS-134 3.85E-05 0.03

CS-137 5.80E-02 47.2

U-234 8.33E-04 0.7

U-235 3.11E-05 0.03

U-238 8.39E-04 0,7

Pu-238 4.03E-04 0.3

Pu-239 1.15E-02 9.4

Am-241 8.39E-06 0.007

Cm-244 5.84E417 0.0005

Total 1.23E-01

a Committed effective dose equivalent


.


Table 47Committed Dose to Maximally Exposed Individual from Public Water Suppliesat Beaufort-Jasper Water Treatment Plant

Page 1 of 1

Radionr.rclide Individual Dose, mrema Percent of Total Dose

H-3 (oxide) 3.34E-02 71.5

Sr-90 2.02E-03 4.3

I-129 1.1OE-03 2.4

Cs-134 3.73E-07 0.0008

Cs-137 5.60E-04 1.2

U-234 6.07E-04 1.3

U-235 2.23E-05 0.05

U-238 6.12E-04 1.3

Pu-238 2.83E-04 0.6

Pu-239 8.08E-03 17.3

Am-241 3.89E-06 0.008

Cm-244 2.71 E-07 0.0006

Total 4.67E-02




Table 48

Committed Dose to Maximally Exposed Individual from Public Water Supplies

at the City of Savannah !ndustrial and Domestic Water Supply Plant(near Port Wentworth, Georgia)

Page 1 of 1

Radionuclide Individual Dose, mrema Percent of Total Dose

H-3 (oxide) 3.80E-02 71.5

Sr-90 2.29E-03 4.3

I-129 1.28E-03 2.4

CS-134 4.26E-07 0.0008

Cs-137 6.38E-04 1.2

U-234 6.92E-04 1.3

U-235 2.66E-05 0.05

U-238 6.92E-04 1.3

Pu-238 3.19E-04 0.6

Pu-239 9.20E-03 17.3

Am-241 4.26E-06 0.008

Cm-244 3.19E-07 0.0006

Total 5.32E-02




Table 49Collective Dose from Liquid Releases

Page 1 of 1

By Pathway

Pathway Collective Dose (person-rem)a Percent of Total Dose

sport fish 1.12E-01 6.2

Commercial fish 1.09E-03 0.1

Beaufort-Jasper 1.42E+O0 78.4

Port Wentworth 2.70E-01 14.9

Saltwater invertebrates 6.70E-04 0.04

Recreation - river 8.16E-03 0.5

Total 1.81E+OO

By Radionuclide

Radionuclide Collective Dose (person-rem)a Percent of Total Dose

H-3 1.21E+OO 66.8

Sr-90 7.70E-02 4.3

I-129 4.09E-02 2.3

CS-134 8.49E-05 0.005

CS-137 1.33E-01 7.3

U-234 2.21 E-02 1.2

U-235 8.31E-04 0.05

U-238 2.22E-02 1.2

Pu-238 1.03E-02 0.6

Pu-239 2.95E-01 16.3

Am-241 1.48E-04 0.008

Cm-244

Total


.03E-05 0.0006

.81 E+OO



Table 50Potential Doses from Irrigation Pathways

Page 1 of 1

Food Types Maximally Exposed Individual (mrem)b Population (person-rem)b

Vegetation 6.12E-02 3.83E+O0

Leafy vegetable 9.53E-03 2.46E-01

Milk 1.63E-02 2.22E+O0

Meat 5.20E-03 2.78E-01

Total 9.22E-02 6.57E+O0

a Irrigated acreage for each food type assumed to be 1,000 acresb Committed effective dose equivalent

wsRGTR-9t&oo314138 SRS Environmental Data for 1998


Table 51Dose from Consumption of Fish from New Savannah Bluff Lock and Dam,SRS Creek Mouths, and River Mile 120

Page 1 of 2

Average Concentration in Composites, pCi/ga

Location Species H-3 Sr-90 Cs-137 Pu-238 Pu-239

NSB L&Db BassBreamCatfish

U3R Mouth BassBreamCatfish

BDC Mouth BassBreamCatfish

FMC Mouth BassBreamCatfish

SC Mouth BassBreamCatfish

L3R Mouth BassBreamCatfish

RM 120 BassBreamCatfish

6.11E-027.68E-021.04E-014.17E-015.37E-015.03E-026.88E-024.73E-025.75E-023.92E+O03.37E-017.72E-018.97E+17.07E-016.20E-015.65E-015.62E-016.45E-014.02E-014.14E-011.95E-01

8.37E-03

4.05E-03

5.70E-03

2.40E-03

8.38E-03

6.84E-03

8.21 E-03

1.59E-02

2.86E-03

1.48E-02

2.44E-02

7.27E-031.50E-02

4.58E-03

8.89E-035.76E-03

6.1 6E-031.56E-03

4.48E-03

7.32E-03

1.53E-03

Dose from Consumption of 19 kg/year (42 Ibs), mremc

Location Species H-3 Sr-90

3.36E-022.13E-029.48E-039.73E-023.25E-025.52E-023.38E-012.62E-024.23E-023.63E-014.57E-021.31E-011.65E+O09.70E-02

8.87E-02

1.89E-011.31 E-012.14E-019.51E-022.94E-025.59E-02

CS-137

-4.1 OE-O6–1 .56E-05-8.08E-066.50E-065.76E-054.98E-05

–1 .32E-05-4.35E-05–l.ll E-05–1 .06E-05-4.86E-051.20E-06

4.87E-06–1 .49E-052.35E-052.00E-06

-5.90E-05–2.19E-05-1 .22E--O51.23E-05

–2.05E-05

Pu-238

1.06E-05-3.63E-05-7.00E-07-3.60E-061.82E-05

–3.33E-058.50E-06

–1 .24E-047.87E-06

-2.99E-05-2.42E-052.30E-051.01E-05

-9.71 E-058.40E-061.85E-05

-3.80E457.00E-06

4.12E-052.22E-05

–9.70E-06

Pu-239

NSB L&Db Bass 7.31E-05 2.07E-02 3.19E-02 \ d ~ 8.66E-04 5.35E-02Bream 9.19E-05 1.00E-02 2.02E-02 ~

~-—_

73.03E-02

Catfish 1.24E-04 1.41E-02 9.01E-03 ! 2.32E-02U3R Mouth Bass 4.99E-04 5.93E-03 9.24E-02 ~ ~ 9.93E-02

4.16E-03 1.49E-03 5.79E-02BreamCatfish

BDC Mouth BassBreamCatfish

FMC Mouth BassBreamCatfish

6.43E-046.02E-058.24E-055.66E-056.88E4154.69E-034.03E-049.24E-04

2.07E-021.69E-022.03E-023.93E-027.06E-033.66E-026.03E-021.80E-02

3.09E-025.24E-023.21 E-012.49E-024.02E-023.45E-014.34E-021.24E-01

3.60E-03 ~—~ 7.30E-02- 6.94E-04 3.42E-01

d 6.42E-02

- =~8.66E-05 1.88E-03 1:45E-01

a Each composite included five fish; three composites of each species type were collected at each sampling location.b New Savannah Bluff Lock and Dam (formerly Augusta Lock and Dam)c Dose was based on maximum consumption of 19 kg/yea~ to obtain dose from average consumption of fish (9 kg/year),

multiply doses in table by 0.474.d Dose based on negative concentration of individual radionuclides in fish was not calculated (shaded areas) and was not used

in total dose column.



Table 51Dose from Consumption of Fish from New Savannah Bluff Lock and Dam,SRS Creek Mouths, and River Mile 120

Page 2 of 2

Dose from Consumption of 19 kg/year (42 Ibs), mrema (cont.)

Location Species H-3 Sr-90 CS-137 Pu-238 Pu-239 Total

Sc Mouth Bass 1.07E-03 3.71k-02 1.57E+O0 ! !-Et%Bream 8.46E-04 1.13E-02 9.22E-02 ~Catfish 7.42E-04 2.20E-02 8.43E-02 1.70E-03 6.86E-04

L3R Mouth Bass 6.76E-04 1.42E-02 1.80E-01 1.44E-04 1.51E-03Bream 6.73E-04 1.52E-02 1.24E-01 ~ bCatfish 7.72E-04 3.85E-03 2.03E-01 ;

RM 120 Bass 4.81 E-04 l.ll E-02 9.03E-02 [ +Bream

—...—. .———4.4.96E-04 1.81E-02 2.79E-02 8.88E-04 1.81E-03

Catfish 2.33E-04 3.78E-03 5.31E-02 -- T—.. .— ...- . ...—

1.61 E+OO1.04E-011.09E-01

1.96E-011.40E-012.08E-011.02E-014.92E-025.71E-02

a Dose was based on maximum consumption of 19 kg/yeac to obtain dose from average consumption of fish (9 kglyear),multiply doses in fable by 0.474.

b Dose based on negative concentration of individual radionuclides in fish was not calculated (shaded areas) and was not usedin total dose column.



Table 52Calculated Doses to Aquatic Biota from SRS Releases

Page 1 of 1

Dose to Biota, rad/da,b

Stream Location Flow, cfs Fish Invertebrate Algae

Upper Three Runs U3R-4

Beaver Dam Creek 400-D

Four Mile Creek FM3 above Road E

Pen Branch K-018

Steel Creek Steel Creek 2A above Road B

Lower Three Runs L3R1A above Road B

Stream Location

290

12

7

28

4

49

Flow, cfs

1.85E-05 2.16E-05

1.04E-05 1.32E-05

2.29E-03 2.82E-03

3.37E-05 3.56E-05

3.04E-04 3.56E-04

2.27E-06 2.77E-06

Dose to Biota, rad/da,b

Raccoon Duck

Upper Three Runs U3R4 290 8.06E-06 8.36E45

Beaver Dam Creek 400-D 12 8.33E-06 1.81E-04

Four Mile Creek FM3 above Road E 7 1.57E-03 2.90E-02

Pen Branch K-018 28 1.05E-05 1.88E-04

Steel Creek Steel Creek 2A above Road B 4 1.64E-04 2.55E-03

Lower Three Runs L3R1A above Road B 49 1.1OE-O6 1.36E-05

a Calculated with CRITR methodology incorporated in the LADTAPIIcomputerprogramb The DOE limit is 1 ract/d.

6.82E-06

2.30E-05

2.1OE-O3

4.41 E-05

1.79E-04

1.89E-06



Table 53Toxic Air Pollutant Emissions (1997)

Page 1 of 4

Chemical Abstract Actual EmissionsPollutant Number (CAS) (Tons/Year)

Note: Emissions are calculated each year as part of an annual emissions inventoty In 1998, operating data werecompiled and emissions calculated for 1997 operations for all site air emission sources. Because thisprocess, which begins in January requires up to 6 months to complete, this report provides 1997emissions only Actual emissions for 1998 will be compiled and reported in depth in the SRSEnvironmental Report for 1999 and in SRS Environmental Data for 1999.

ACETALDEHYDE

ACETIC ANHYDRIDE

ACETONITRILE

ACROLEIN

AMMONIUM CHLORIDE

ANILINE

ANTIMONY COMPOUNDS

ARSENIC

BENZENE

BERYLLIUM

BIPHENYL

BIS-(2-ETHYLHEXYL) PHTHALATE

BROMOFORM

BUTADIENE (1, 3-)

CADMIUM

CARBON DISULFIDE

CARBON TETRACHLORIDE

CHLORDANE

CHLORINE

CHLOROBENZENE

CHLOROFORM

CHROMIUM (+6) COMPOUNDS

COBALT COMPOUNDS

CRESOL

CUMENE

CYANIDE

CYANIDE COMPOUNDS

DIBUTYL PHTHALATE

DICHLOROBENZENE (P–)

75-7-o

108-24-7

75-5-6

107-2-8

12125-2-9

62–53-3a

7440-38-2

71-43-2

7440-41-7

92-52-4

117-81-7

75-25-2

108-99-0

7440-43-9

75-15-0

56-23-5

57–74-9

7782–5&5

108-90-7

67-88-3a

a

1319-77-3

96-82-8

57–1 2–5

a

84-74-2

106-46-7

2.489E-01

1.140E-06

7.930E411

1.066E-02

3.373E-04

8.790E-03

2.446E-03

7.921 E-03

1.336E+01

1.330E-03

1.334E-02

2.798E-04

3.443E+O0

6.833E-02

4.577E-03

1.524E-03

6.515E-03

1.609E-03

1.231 E-f)l

1.529E-03

1.371E+O1

6.286E-05

1.328E-03

1.311E-03

1.565E-02

1.239E-03

9.313E-03

4.350E-04

1.389E-06

a No CAS number




Page 2 of 4

Chemical Abstract Actual EmissionsPollutant Number (CAS) (Tons/Year)

DIMETHYLFORMAMIDE 68-12-2 4.974E-05

DINITROPHENOL (2, 4-)

DINITROTOLUENE (2, 4-)

DIOXANE (1,4-)

DIPHENYL MERCURY

ETHANOLAMINE

ETHYL BENZENE

ETHYLENE DIBROMIDE

ETHYLENE DICHLORIDE

ETHYLENE GLYCOL

ETHYLIDENE DICHLORIDE

FORMALDEHYDE

FORMIC ACID

HEPTACHLOR

HEXACHLOROBENZENE

HEXACHLOROBUTADIENE

HEXACHLOROCYLOPENTADIENE

HEXACHLOROETHANE

HEXAMETHYLENE (1, 6-) DIISOCYANATE

HEXANE

HYDRAZINE

HYDROCHLORIC ACID

HYDROGEN SULFIDE

HYDROQUINONE

ISOPHORONE

MAIATHION

MANGANESE COMPOUNDS

MERCURY

METHOXYCHLOR

METHANOL

METHYL ETHYL KETONE (2-BUTONE)

METHYL ISOBUTYL KETONE

METHYL METHACRYIATE

51-28-5

121-14-2

123-91-1

587-85-9

141-43-5

100-41-4

108-93-4

107-&-2

107-21–1

75-34-3

50-O-O

64-18-6

76-44-8

118-74-1

87-68-3

77-47-4

67–72-1

822-6-O

110-54-3

302-1-2

7647-1-o

7783-6-4

123-31-9

78-59-1

121-75-5a

7439-97-8

72-43-5

67-56-1

78-93-3

108-1&l

80-62-8

2.977E-07

1.200E-03

1.200E-03

2.708E-03

1.663E--O2

6.561 E-01

3.569E-06

2.254E-07

2.679E-01

1.296E-03

1.560E+O0

3.114E+O0

1.784E-05

6.333E-05

8.670E-09

6.194E-04

5.360E-05

4.460E-05

1.259E+O0

1.285E-03

4.214E+01

1.204E+01

6.508E-02

6.950E-03

4.530E-04

5.145E-01

3.874E-02

3.111E-02

7.301E-01

1.938E-01

6.711E-01

2.438E-03

a No CAS number


----


Table 53

Toxic Air Pollutant Emissions (1997)

Page 3 of 4

Chemical AbstractPollutant Number (CAS)

Actual Emissions(Tons/Year)

METHYL TERT–BUTYL ETHER

METHYLENE CHLORIDE

NAPHTHALENE

NICKEL OXIDE

NICKEL

NITRIC ACID

NITROBENZENE

NITROPHENOL (P–)

NITROPROPANE (2–)

NITROSOPHENOL (P-)

OXALIC ACID

PHENOL

PHOSPHORIC ACID

PHOSPHORUS

POLYCHLORINATED BIPHENYLS (PCB)

POLYCYCLIC ORGANIC MA_iTER

PROPOXUR

PROPYLENE OXIDE (1, 2–)

SELENIUM COMPOUNDS

SODIUM HYDROXIDE

STYRENE

SULFURIC ACID

TETRACHLOROETHANE (1,1,2, 2-)

TETRACHLOROETHYLENE (PERCHLOROETHYLENE)

TOLUENE

TOLUENE–2,4-DI ISOCYNANATE

TOXAPHENE

TRICHLOROBENZENE (1,2, 4-)

METHYL CHLOROFORM

TRICHLOROETHANE (1,1, 2-)

TRICHLOROETHYLENE (TCE)

TRIETHYLAMINE

TRIMETHYLPENTANE (2,2, 4-)

1634-4-4

75-9-2

91–20-3

1313-99-1

7440-2-0

7697–37–2

98-95-3

100-2-7

79-46-9

104-91-6

1M2–7

108-95-2

7664-38-2

7723-14-0

a

a

114-26-1

75-56-9

a

1310-73-2

100-42-5

7664-93-9

79–34-5

127-18-4

106-86-3

584-84-9

8001–3+2

120-62-1

71-55-6

79-o-5

79-1-6

121-44-8

540-84-1

7.737E-01

1.330E-01

1.003E-02

1.284E-06

8.980E-02

1.599E+01

1.723E-03

1.452E-05

9.140E-08

1.452E-04

6.133E-03

9.240E-02

2.030E-01

6.748E-29

1.609E-03

2.183E-02

2.000E-05

4.500E-07

2.697E-03

1.331E+OO

1.844E-02

6.698E+O0

1.233E-03

1.449E+01

2.070E+O0

5.230E-06

9.338E-02

6.740E-05

5.085E-02

5.684E-03

9.476E-01

2.000E-05

5.137E-02

a No CAS number

wsRc-TR-9&oo374144 SRS Environmental Data for 1998

—..



Page 4 of 4

Chemical Abstract Actual EmissionsPollutant Number (CAS) (’Tons/Year)

VINYL ACETATE 108-5-4 1.392E-03

VINYL CHLORIDE 75-1-4 1.293E-03

VINYLIDENE CHLORIDE 75-35-4 2.668E-09

XYLENE (MIXED ISOMERS) 1330-2&7 5.499E+O0

XYLENE (M-) 108-38-3 2.040E-01

XYLENE (O-) 95-47-6 5.674E-01

XYLENE (P-) 106-42-3 2.620E41



Table 54National Pollutant Discharge Elimination System Monitoring Data

Page 1 of 10

Permit SCOOO0175

Note: Penrrit /eve/s can be found in WSRC NPDES Environmental Monitoring Program (ESH-EMS-910110) orin the permit itself. The permit is available from the South Carolina Depatiment of Health andEnvironmental Control.

No. of No. inMeasurement Units Samples Maximum Minimum Average Average

Outfall A-01Ef7/uentconsists of the fo//owing types of wastewater noncontact coo/ing water steam condensate,/aboratory drain wate~ coo/ing tower overflow steam-c/caning-rack wastewateL well f/ush watergroundwater air stripper effluent from outfall A–1A, and stormwatec

BOD mg/L 12 8.50E+O0 0.00E+OO 12 7.08E411

CHL mg/L 12 0.00E+OO 0.00E+OO 12 0.00E+OO

Cu mg/L 57 2.77E-01 0.00E+OO 57 1.74E-02

FLO MGD 12 1.44E+O0 2.88E411 12 8.88E-01

HG mg/L 53 7.00E-04 0.00E+OO 53 5.85E-05

O&G mg/L 12 3.90E+O0 0.00E+OO 12 l.ll E+OO

PB mg/L 57 3.70E-02 0.00E+OO 57 1.33E-03

PERCL pglL 22 0.00E+OO 0.00E+OO 22 0.00E+OO

PH Su 12 7.55E+O0 5.98E+O0

TCE pglL 21 2.13E+01 0.00E+OO 21 4.91 E+OO

TSS mg/L 19 10.OE+OO 0.00E+OO 19 2.21 E+OO

Outfall A-1AEff/uent consists of the fo//owing type of wastewater: groundwater air stripper eff/uent.

FLO MGD 14 4.51 E-01 4.15E-01 14 4.33E-01

PERCL pg/L 14 0.00E+OO 0.00E+OO 14 0.00E+OO

TR[CL yg/L 14 0.00E+OO 0.00E+OO 14 0.00E+OO

Outfall A-n

Effluent consists of the following types of wastewate~ fire station building drains, air conditionercondensate, well flush watecnoncontact cooling wate< steam condensate, liquid effluent treatment facilityprocess effluent from Outfall M-04, air stripper effluent from outfall M-05, and stormwate[

BOD mg/L 12 0.00E+OO 0.00E+OO 12 0.00E+OO

Cu mg/L 12 2.50E-02 0.00E+OO 12 3.50E-03

FLO MGD 48 6.59E+O0 4.27E-01 48 1.38E+O0

HG mg/L 12 1.00E-04 0.00E+OO 12 1.67E-05

PB mg/L 12 3.00E-03 0.00E+OO 12 5.00E-04

PH Su 12 7.95E+O0 6.43E+O0




Page 2 of 10

Permit SCOOO0175


Outfall A-n (cont.)

TCE pg/L 10 0.00E+OO 0.00E+OO 10 0.00E+OO

TSS mg/L 16 3.54E+02 3.00E+OO 16 6.74E+01

Outfall D-1AEff/uent consists of the fo//owing type of wastewatec sanita~ wastewatez

BOD mg/L 13 4.90E+O0 0.00E+OO 13 2.87E+O0

DO mg/L 14 7.50E+O0 1.40E+O0 14 4.93E+O0

FEC #/l 00 mL 13 8.50E+01 0.00E+OO 13 1.05E+01

FLO MGD 365 4.78E-02 0.00E+OO 365 8.21E-03

PH Su 13 7.50E+O0 6.51 E+OO

TSS mg/L 13 1.80E+01 1.00E+OO 13 5.00E+OO

Outfall F-01Eff/uent consists of the fo//owing &pes of wastewaten nonprocess coo/ing wate~ coo/ing tower b/owdown,and stormwate~

CHL mg/L 14 1.20E+O0 O.OOE+OO 14 6.29E-01

FLO MGD 14 4.32E-01 8.64E-02 14 1.67E-01

PH Su 14 8.03E+O0 6.09E+O0

TMP DEG C 14 3.05E+01 1.15E+01 14 2.24E+01

TSS mg/L 15 5.40E+01 0.00E+OO 15 4.40E+O0

Outfall F-02Eff/uent consists of the fo//owing types of wastewate~ nonprocess cooling wate~ coo/ing tower b/owdown,and stormwate~

FLO MGD 15 2.74E-01 2.88E+2 15 8.19E+2

PH Su 16 9.61E+OO 6.70E+O0

TMP DEG C 15 2.91 E+O1 1.17E+01 15 2.08E+01

TSS mg/L 15 2.23E+02 0.00E+OO 15 1.57E+01

Outfall F-03Effluent consists of the following types of wastewater nonprocess cooling water steam condensate,cooling tower blowdown, process watec and stormwate~

FLO MGD 12 0.00E+OO 0.00E+OO 12 O.OOE+OO


.... . , .,.. ......; .’?.>,. ,.,.,,,,, ,.., ,.~.-.. ;: .:,[.,-,., ,y#.., .:;?.j:,’:.,,....J-,- ; ,,,. .,.:.;,:k.:.:- ,:”.... .:.:,:.i,i ,:}.+< ~-:.,., ,.<>?,.; ,.: : ,. ,, , : :.:..$ Y~ .. ,,.

‘,>7,,, ..’..,.:, ~,. ! .. .. .. ,, .,, ,, , q;r.!.. : , :<,,<-,: . . ,, ~,:;.

,<,./,-, $:.: ......

,.,, .,.,, ,. ,,. ,/:, :,, ,, ;,,. :+?.. , ,.’ .. ... . .., f;:,+*: . -,.. g;.-.’

~T’. .>,,:G:,:, >-<,<<.<. .: :, ~% ?:y,.~-... .,, , .,,,.,/. , ,4.. ,:! ,). ::$.~:~i ;.



Page 3 of 10

Permit SCOOO0175


Outfall F-05Eff/uent consists of the fo//owing types of wastewaten nonprocess coo/ing water and steam condensatefrom the plutonium fabrication facility well flush watec and stormwatec

FLO MGD 15 2.88E+1 3.31 E-02 15 9.70E-02

O&G mg/L 16 8.40E+O0 0.00E+OO 16 1.35E+O0

PH Su 15 7.95E+O0 4.26E+O0

TMP DEG C 15 2.73E+01 1.17E+01 15 2.15E+01

TSS mg/L 17 4.40E+01 0.00E+OO 17 4.59E+O0

Outfall F-08Effluent consists of the fo//owing types of wastewatec water from power operations and wastemanagement cooling towers, separations cooling water steam condensate, process wastewatec Iaundtyeffluent, water tank overflow, stormwate< and radiological retention basin cooling wate~

Cu mg/L 12 1.40E-02 0.00E+OO 12 3.50E-03

FLO MGD 365 9.05E+O0 7.76E-01 365 2.04E+O0

HG mg/L 12 1.00E-04 0.00E+OO 12 2.50E-05

PB mg/L 12 0.00E+OO 0.00E+OO 12 0.00E+OO

PH Su 12 7.80E+O0 6.18E+O0

TMP DEG C 12 2.89E+01 1.78E+01 12 2.31 E+O1

TSS mg/L 12 4.00E+O0 1.00E+OO 12 2.50E+O0

Outfall G-1 OEffluent consists of the following type of wastewaten Centralized Sanita~ W’astewater Treatment Faci/itywastewatec

AN-Summer mg/L 16 8.74E41 1.21E-01 16 2.64E-01

AN–Winter mg/L 8 l.ll E+OO 0.00E+OO 8 3.36E-01

BOD mg/L 24 7.00E+OO 0.00E+OO 24 2.95E+O0

Cu mg/L 4 6.70E-02 0.00E+OO 4 2.23E-02

DO mg/L 24 1.20E+01 5.00E+OO 24 7.34E+O0

FEC #/100 mL 26 8.00E+02 0.00E+OO 26 7.99E+01

FLO MGD 365 5.13E-01 0.00E+OO 365 1.88E-01

PB mg/L 4 4.00E-03 0.00E+OO 4 1.00E-03

PH Su 26 7.42E+O0 6.70E+O0

TSS mg/L 24 3.70E+01 2.00E+OO 24 8.54E+O0


—


ITable 54National Pollutant Discharge Elimination System Monitoring Data

Page 4 of 10 II

Permit SCOOO0175


Outfall H-02Effluent consists of the following types of wastewatec nonprocess cooling water and stonnwate~

FLO MGD 365 9.05E-01 3.23E-02 365 1.07E-01

O&G mg/L 14 2.80E+O0 0.00E+OO 14 2.00E-01

PH Su 15 7.38E+O0 6.30E+O0

TMP DEG C 15 2.80E+01 10.OE+OO 15 1.93E+01

TSS mg/L 15 10.OE+OO 0.00E+OO 15 1.67E+O0

Outfall H-04EMuent consists of the fo//owing types of wastewatec nonprocess coo/ing watec C/F nonprocesswastewate~ steam condensate, and stormwate~

FLO MGD 15 2.03E-01 0.00E+OO 15 1.93E-02

PH Su 14 7.60E+O0 6.11E+OO ITMP DEG C 14 2.60E+01 8.50E+O0 14 1.83E+01 ITSS mg/L 14 9.00E+OO 0.00E+OO 14 1.86E+O0

Outfall H-07Effluent consists of the following types of wastewaten air compressor cooling water cooling towerblowdown, and stormwatec

FLO MGD 15 5.33E-02 0.00E+OO 15 1.40E-02

O&G mg/L 9 2.90E+O0 0.00E+OO 9 3.22E-01

PH Su 9 7.42E+O0 5.99E+O0

TSS mg/L 9 3.1OE+O1 1.00E+OO 9 9.67E+O0

Outfall H-08Eff/uent consists of the fo//owing &oes of wastewatec water from power operations and wastemanagement cooling towers, steam condensate, ash basin overflow, water tank overflow, neutralizationsystem discharge, water laboratory discharge, well-flush watec powerhouse drains, and stormwatefi

FLO MGD 58 4.28E+O0 2.02E-01 58 1.08E+O0

PB mg/L 12 1.50E-02 0.00E+OO 12 2.33E-03

PH Su 12 7.60E+O0 5.58E+O0

TSS mg/L 12 8.00E+OO 2.00E+OO 12 4.92E+O0

Outfall H-12EfY/uentconsists of the fo//owing types of wastewatec nonprocess coo/ing water coo/ing tower and aircompressor blowdown, storm wate~ In-tank Precipitation Facility neutralized flush wate~ and radiologicalretention basin cooling wate~


I



Page 5 of 10

Permit SCOOO0175


Outfall H-12 (cont.)

Cu mg/L 14 4.31 E-01 0.00E+OO 14 5.19E-02

FLO mg/L 12 1.12E+O0 1.83E-01 12 6.64E-01

PB mg/L 15 1.90E-02 0.00E+OO 15 2.13E-03

PH Su 16 7.12E+O0 3.65E+O0

TMP DEG C 16 2.53E+01 1.31E+O1 16 2.14E+01

TSS mg/L 12 1.30E+01 0.00E+OO 12 2.75E+O0

Outfall H-16Effluent consists of the following type of wastewatec F-Area/H-Area Effluent Treatment Facility processwastewatefi

AG mg/L 48 6.00E-03 0.00E+OO 48 1.25E-04

BOD mgJL 48 3.77E+01 0.00E+OO 48 2.20E+O0

CD mgJL 48 3.00E-02 0.00E+OO 48 6.25E~4

CR mg/L 48 4.20E-02 0.00E+OO 48 1.00E-03

Cu mg/L 48 3.20E-02 0.00E+OO 48 1.27E-03

FLO MGD 48 1.49E-01 4.00E-02 48 1.12E-01

HG mg/L 48 3.00E-04 0.00E+OO 48 2.50E-05

NI mg/L 48 3.90E-02 0.00E+OO 48 1.04E-03

O&G mg/L 48 7.30E+O0 0.00E+OO 48 1.29E+O0

PB mg/L 48 0.00E+OO 0.00E+OO 48 0.00E+OO

PH Su 48 8.24E+O0 6.12E+O0

TSS mg/L 48 10.OE+OO 0.00E+OO 48 1.38E+O0

ZN mg/L 48 1.1OE-O1 0.00E+OO 48 1.80E-02

Outfall K-06Effluent consists of the fo//owing types of wastewaten powerhouse wastewatec package boiler Mowriown,cooling tower ovetilow, and stormwatec

CHL mg/L 2 5.00E-02 0.00E+OO 2 2.50E-02

FLO MGD 13 9.65E-02 0.00E+OO 13 2.07E-02

O&G mg/L 3 0.00E+OO 0.00E+OO 3 0.00E+OO

PH Su 3 7.34E+O0 6.28E+O0

TSS mg/L 3 1.00E+OO 0.00E+OO 3 6.67E-01




Page 6 of 10

Permit SCOOO0175

No. ofMeasurement

No. inUnits Samples Maximum Minimum Average Average

Outfall K-10Eff/uent consists of the fo//owing &pe of wastewaten Infrequent diversion from outfa// K-18.

FLO MGD 12 0.00E+OO 0.00E+OO 12 0.00E+OO

Outfall K-12Et7/uentconsists of the fo//owing ~pe of wastewatec sanitary wastewatec

BOD mg/L 12 1.25E+01 2.50E+O0 12 5.45E+O0

DO mg/L 14 9.90E+O0 1.60E+O0 14 4.84E+O0

FEC #/l 00 mL 14 2.06E+02 0.00E+OO 14 1.60E+01

FLO MGD 365 2.03E-02 0.00E+OO 365 3.25E-03

PH Su 14 8.00E+OO 6.40E+O0 14 7.19E+O0

TSS mg/L 13 1.04E+01 3.20E+O0 13 5.12E+O0

Outfall K-18Eff/uent consists of the fo//owing types of wastewatec bui/ding 105-K noncontact coo/ing water andprocess sewer flow, 188-K Basin overflow and waterplant wastewater and treated sanitary wastewaterfrom outfall K-12.

AL mg/L 7 2.61 E-01 5.00E-02 7 1.86E-01

FLO MGD 7 5.70E-01 3.74E-01 7 4.89E-01

O&G mg/L 7 7.20E+O0 0.00E+OO 7 1.51E+OO

PH Su 7 7.87E+O0 6.19E+O0 7 6.99E+O0

TSS mg/L 7 7.00E+OO 1.00E+OO 7 4.00E+OO

Outfall L-07Eff/uent consists of the fo//owing types of wastewatec 186-L Basin overf/oW treated sanitary wastewaterfrom outfall L-7A, and process sewer/reactor building drains.

FLO MGD 365 2.59E+01 5.36E+O0 365 7.72E+O0

O&G mg/L 5 2.80E+O0 0.00E+OO 5 5.60E-01

PH Su 5 7.11E+OO 6.24E+O0 5 6.74E+O0

TSS mg/L 5 6.00E+OO 1.00E+OO 5 2.80E+O0

Outfall L-7AEff/uent consists of the fo//owing type of wastewatec sanitary wastewate~

BOD mg/L 12 3.30E+O0 0.00E+OO 12 1.06E+O0

DO mg/L 14 1.58E+01 4.1OE+OO 14 7.06E+O0

FEC #/l 00 mL 13 2.00E+OO 0.00E+OO 13 1.54E-01


Nonradjologjcal Effluent Monitoring


Page 7 of 10

Permit SCOOO0175


Outfall L-7A (cont.)

FLO MGD 365 3.62E-02 3.58E-02 365 3.60E-02

PH Su 14 7.90E+O0 6.50E+O0

TSS mg/L 14 1.72E+01 3.00E+OO 14 8.21E+OO

Outfall L-08Eff/uent consists of the fo//owing types of wastewatec engine house coo/ing water and stormwate~

FLO MGD 5 8.35E-02 2.26E-02 5 4.96E-02

O&G mg/L 5 2.40E+O0 O.OOE+OO 5 4.80E41

PH Su 5 7.00E+OO 6.36E+O0

TSS mg/L 5 1.20E+01 0.00E+OO 5 3.00E+OO

Outfall M-04Eff/uent consists of the fo//owing types of wastewatec Liquid Eff/uent Treatment Faci/ityprocesswastewater.

AL mg/L 20 1.06E+O0 0.00E+OO 20

AN mg/L 20 5.87E+01 1.06E-01 20

CN mg/L 20 1.77E+O0 0.00E+OO 20

CR mg/L 20 2.88E-01 0.00E+OO 20

FLO MGD 20 7.20E-03 5.04E-04 20

NI mg/L 20 1.44E+O0 2.80E-02 20

PB mg/L 20 0.00E+OO 0.00E+OO 20

PH Su 20 7.31 E+OO 6.64E+O0 20

TSS mg/L 20 9.00E+OO 0.00E+OO 20

2.92E-01

1.73E+01

1.80E-01

5.72E-02

4.79E-03

2.84E41

0.00E+OO

6.94E+O0

2.1OE+OO

Outfall M-05Eff/uent consists of the fo//owing type of wastewatec grouncfwater air stripper effluent.

FLO mg/L 16 7.49E-02 7.42E+2 16 7.46E-02

PERCL mg/L 16 2.00E+OO 0.00E+OO 16 1.25E-01

TCE ug/L 16 6.80E+O0 0.00E+OO 16 4.25E+1

Outfall PP-1Effluent consists of the following type of wastewaten manganese greensand filter backwas~rinse wate~

FE mg/L 7 2.95E-01 0.00E+OO 7 1.60E-01

FLO MGD 4 1.13E+3 8.55E-04 4 1.01E-03




Page 8 of 10

Permit SCOOO0175


Outfall PP-I (cont.)

MN mg/L 7 4.75E+01 2.07E+O0 7 1.47E+01

PH Su 5 6.71E+OO 5.73E+O0

TSS mg/L 4 2.00E+O0 0.00E+OO 4 1.00E+OO

Outfall S-04Effluent consists of the following types of wastewate~ DWPFnonprocess wastewater—including coolingtower blowdown, neutralization wastewate~ and infrequent flushin@insing activities.

FLO MGD 12 2.46E-01 4.32E-02 12 1.07E-01

PH Su 12 8.30E+O0 7.27E+O0 12 7.90E+O0

TSS mg/L 12 5.00E+OO 0.00E+OO 12 1.92E+O0

ZN mg/L 12 4.78E-01 0.00E+OO 12 2.52E-01

Outfall X-64Effluent consists of the following ~pes of wastewatec welding quench sink wateL steam condensate, andstonnwatez

FLO MGD 13 7.20E-03 0.00E+OO 13 1.64E-03

PH Su 15 7.94E+O0 5.43E+O0 15 6.45E+O0

TSS mg/L 12 6.00E+OO 0.00E+OO 12 2.42E+O0

Outfall X-08Effluent consists of the following types of wastewatec noncontact cooling wateL domestic well overflowtreated sanikuy wastewater from outfall X-8A, treated process water from outfall X-8B, treatedgroundwater from outfall X-8C, and stonnwatec

FLO MGD 14 5.20E+01 5.16E+01 14 5.18E+01

PH Su 16 7.11E+OO 6.26E+O0 16 6.68E+O0

TSS mg/L 17 1.60E+01 0.00E+OO 17 5.18E+O0

Outfall X-8AEff/uent consists of the fo//owing type of wastewatec sanitary wastewate~ (Note: one data point, for feedcolifonn, was a > value and was used in the computation at face value.)

BOD mg/L 13 5.40E+O0 0.00E+OO 13 2.41 E+OO

DO mg/L 12 9.20E+O0 5.00E+OO 12 6.81E+OO

FEC #/l 00 mL 13 1.16E+02 O.OOE+OO 13 2.13E+01

FLO MGD 365 1.22E-02 O.OOE+OO 365 9.30E-04

PH Su 13 7.46E+O0 6.72E+O0 13 7.08E+O0


.-



Page 9 of 10

Permit SCOOO0175


Outfall X-8A (cont.)

TSS mg/L 13 2.04E+01 3.20E+O0 13 8.11E+OO

Outfall X-8BEff/uent oonsists of the fo//owing type of wastewatec treated process water from the TNX Eff/uent Vest-ment Plant.

BEN @L 21 7.30E-01 0.00E+OO 21

BOD mg/L 21 0.00E+OO O.OOE+OO 21

c mg/L 21 6.50E+O0 1.60E+O0 21

FLO MGD 22 3.90E-02 1.20E-02 22

HG mg/L 21 5.00E-01 O.OOE+OO 21

PH Su 22 7.77E+O0 7.05E+O0

PHE mg/L 21 1.60E-02 0.00E+OO 21

TSS mg/L 21 8.1OE+O1 3.00E+O0 21

Outfall X-8CEffluent consists of the fo//owing type of wastewatec treated groundwater air stripper eff/uent.

FLO MGD 12 1.21E-01 2.43E-02 12

PERCL pglL 12 3.60E+O0 0.00E+OO 12

TCE vg/L 12 7.40E+O0 0.00E+OO 12

Outfall X-19Eff/uent consists of the fo//owing type of wastewaten treated groundwatez

1,2-DCE ug/L 4 2.80E+O0 0.00E+OO 4

FLO MGD 4 5.66E-03 1.44E-03 4

PERCL pg/L 4 0.00E+OO 0.00E+OO 4

TCE pg/L 4 0.00E+OO 0.00E+OO 4

Vc pglL 4 0.00E+OO 0.00E+OO 4

3.48E-02

0.00E+OO

4.20E+O0

1.80E-02

2.40E-02

2.14E-03

1.99E+01

9.36E-02

4.67E-01

6.17E-01

1.28E+O0

4.07E-03

0.00E+OO

0.00E+OO

0.00E+OO


Nonrad[ological Effluent Monitoring

ITable 54National Pollutant Discharge Elimination System Monitoring Data

Page lOof10


Permit SCG250162

Note: Permit /eve/s can be found in WSRC NPDES Environmental Monitoring Program (ESH-EMS-910110) orin the permit itself. The permit is available from the South Carolina Department of Health andEnvironmental Control.


Outfall 001Eff/uent consists of the fo//owing types of wastewate~ once-through noncontact coo/ing wate~

BOD mg/L 1 0.00E+OO 0.00E+OO 1 0.00E+OO

FLO MGD 4 4.32E-03 0.00E+OO 4 1.08E-03

PH Su 1 6.94E+O0 6.94E+O0 1 6.94E+O0

TMP DEG C 1 2.98E+01 2.98E+01 1 2.98E+01

TSS mg/L 1 6.00E+OO 6.00E+OO 1 6.00E+OO


I

...


Table 55National Pollutant Discharge Elimination System Toxicity Monitoring Data

Page 1 of 1

Measurement Number of Samples Pass Fail

Permit SCOOO0175

Note: Toxicity requirements can be found in WSRC’S NPDES industrial discharge permit, which is available fromthe South Carolina Depatiment of Health and Environmental Control. Toxicity analysis is a pasa/fail test;failure indicates that the tested water was toxic to the test organisms.

Outfall A-01

Effluent consists of the fo//owing types of wastewatec noncontact cooling water steam condensate,laboratory drain wateL cooling tower overflow steam cleaning oiYwater separation, well-flushingoperations, air conditioning condensate, A-1A air stripper discharge, and stormwatet

Chronic Toxicity 16 2 14

Outfall A-n

Effluent consists of the following types of wastewate~ fire station floor drains, air conditioning condensate,well flushing operations, cooling water steam condensate, Liquid Effluent Treatment Facility discharge,M-Area air stripper discharge, and stonnwatec

Chronic Toxicity 14 4 10

Outfall G-1 O

Effluent consists of the following types of wastewaten sanitary treatment facility

Acute Toxicity 3 1

Chronic Toxicity 1 0

2

1

Outfall X48

Effluent consists of the following types of wastewatec noncontact cooling wate~ domestic well ovedlowwatec treated sanitary waste water from outfa// X-L)8A, treated process water from outfa// X-8B, treatedgroundwater from outfall X-8C, and stormwatec

Acute Toxicity 12 12 0

Outfall X-19

Effluent consists of the fo//owing types of wastewaten treated groundwate~

Acute Toxicity 4 4 0


./ .—,-.- . . . .

1.Table 56National Pollutant Discharge Elimination System Stormwater Monitoring Data

Page 1 of 18

Measurement Units lYt3e Samtde/Concentration

PermitSCROOOOOO

Outfall B408

O&G

TSS

BOD

N02,N03

P04-P

COD

TOC

TKN

PH

WATER TEMP

RAIN GAUGE

TOTAL RAIN

RAIN DATE

LAST .01 RAIN

BACKGROUND DATE

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

Su

“c

in.

in.

BackgroundGrab

No FiOW

No Flow

No Flow

No Flow

No Flow

No FtOW

No Flow

No Flow

No Flow

No Flow

No Flow

No Flow

No Flow

No Flow

11/12/98

Composite

13

C2.O

0.375

0.417

44.2

7.6

0.429

1.3

1.5

5/1/98

4/24198

Grab

4.6

2

<2.0

0.177

0.023

52.3

9.4

<0.100

5.42

20.1

0!2

1.5

4/30198

4124/98

Table 56National Pollutant Discharge Elimination System Stormwater Monitoring Data

Page 2 of 18

Measurement Units Type Sample/Concentration

Permit SCROOOOOO

Outfall CS-006

O&G

TSS

BOD

N02,N03

P04-P

COD

TOC

TKN

Phenol

Tetrachloroethylene

Trichloroethylene

1,1,1–Trichloroethylene

Benzene

AL

CR

Cu

FE

PB

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

pglL

pg/L

pg/L

pglL

mg/L

mg/L

mg/L

mg/L

mg/L

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

Composite

10

2.5

<0.020

<0.010

<lo

6.2

0.310

0.28

<0.010

<0.005

0.715

<0.003

Composite

5

<2,0

0.023

0,063

58.5

8.8

0.108

0.956

<0.010

<0.005

1.89

<0.003

Grab

2.4

<1

<2.0

0.028

0.1

<lo

5.1

0.960

<0.006

<2.0

4.0

<2.0

<0.5

0.434

<0.005

<0.005

1.10

<0.003

Grab

2.2

6

<2.0

0.03

0.184

29.4

4.3

0.209

<0.006

<2.0

<2.0

<2.0

<0.5

0.432

<0.010

<0.005

1.98

<0.003

●


—

WSRC-TR-98-00314SRSEnvironmental Datafor1998 159

—


co

NC9alo

r-UYp0

*w

N-t

0

OJ0

0

-1-1

‘m ‘aEE

mg

m000v

z00

m000“

u)000“

gG=

5!

-1-1

‘m -55EE

urnILL

0

-1-1

‘m ‘mEE

zZi


>.~.p—- “-.<.:2,,


co

%UJ

(2olz

.

lil ea

WSRC-TR-98-00314SRSEnvironmental Datafor1998 161


co

‘5wa)0)

2

WSRGTR-96-00314162 SRSEnvironmental Datafor1998

q


Page 7 of 18


Permit SCROOOOOO

Outfall E-001 (cont.)

AG

SN

u

ZN

MG (dissolved)

Tetrachloroethylene

Trichloroethylene

1,1,1-Trichloroethylene

pH

WATER TEMP

RAIN GAUGE

TOTAL RAIN

RAIN DATE

LAST 0.1 RAIN

BACKGROUND DATE

mg/L

mg/L

mg/L

mg/L

mg/L

pg/L

pglL

pglL

Su

“c

in.

in.

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

11/12/98

Grab Grab Grab

<0.005 <0.005

<0.050 <0.050

<0.500 <0.500

0.089 0.124

0.749 0.903

C2.o <2.0

4.0 <2.0

C2.o <2.0

7.05 6.4”

10.3 11.9

0.21

1.0 0.8

418/98 3/5/98

4/4/98 3/1198


Page 8 of 18


Permit SCROOOOOO

Outfall GS-002

O&G

BOD

TSS

S04

NH3-N

N02,N03

P04-P

COD

TOC

TKN

SB

CR

Cu

HG

NI

PB

SN

pH

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

Su

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

Composite

4.0

9

2.01

0.178

0,249

0.428

<10.0

7.2

0.160

<0.020

<0.010

0.037

<0.0001

<0.010

0.064

<0.050

Composite

<2.0

<1

1.58

0.290

0.169

<0.010

<10.0

7,4

1.58

<0,020

<0.010

<0.010

<0.0001

<0.010

0.038

<0.050

Composite Grab

<1.0

<2.0

6

1.39

0.138

0.129

4.42

22.0

1.9

0.167

<0.005

<0.005

0.006

<0.0001

<0.010

0.011

<0.050

6.76

Grab

<1.0

<2.0

<1

1.31

0.448

0.381

0.123

<10.0

1.8

0.214

<0.005

<0.005

<0,005

<0.0001

<0.010

<0.003

<0.050

6.64

Grab

<1.0


W0“

d

WSRGTR-98-00314SRSEnvironmental Datafor1998 165

.1


Page100f18


Permit SCROOOOOO

Outfall H-007A (cont.)

FE

pH

WATER TEMP

RAIN GAUGE

TOTAL RAIN

RAIN DATE

LAST 0.1 RAIN

BACKGROUND DATE

Outfall G-020

O&G

BOD

TSS

COD

N02,N03

Po~-P

TKN

TOC

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

BackgroundGrab

mg/L No flow

Su No flow

‘c No flow

in. No flow

in. No flow

No flow

No flow

11/12/98

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

Composite

0.139

1.10

1.2

3/19/98

3/9/98

Composite

6.8

155

82.8

1.63

4.85

1.99

11

Composite Grab

0.256 5.83

7.01

10.2

NA 0,23

0.4 0.8

316/98 4/8/98

311/98 414198

Composite Grab

8.6

244

51.0

1.77

2.52

0.661

13

Grab

0.342

6.48

14.3

0.11

0.4

3/5/98

311/98

Grab


02

‘Gt-0m2

—

-1-l-l-l_l_l_l _l

-am-am‘m al ‘Ii -55 -55 -55EEEEEEEE

WSRGTR-98-00314SRSEnvironmental Datafor1998 167


Page120f18


Permit SCROOOOOO

Outfall K-002 (cont.)

pH

WATER TEMP

RAIN GAUGE

TOTAL RAIN

RAIN DATE

IAST 0.1 RAIN

BACKGROUND DATE

Outfall K-004

O&G

BOD

TSS

COD

N02,N03

P04-P

TKN

TOC

pH

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

Su

BackgroundGrab

Su No flow

“c No flow

in. No flow

in, No flow

No flow

No flow

11/12/98

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

Composite

0.1

1113/98

10//8198

Composite

4.0

26

25.7

0.193

0.15

0.778

7.6

Grab

0.11113/98

10/8/98

Grab

<1.0

<2.0

17

19.9

0.079

0.221

0.439

5.9

6.91

Nonradio!ogical Effluent Monitoring

co

‘5maIl?’n

0

0+

0z

zzE



m



u)

Loomz0700 m00.00 h. q~qoo”

Vvol-

30

=

2’

6’z-

6z

zx1-

ccc)

U.1(!33aC3zzz


?,


Page160f18


Permit SCROOOOOO

Outfall X-001 (cont.)

RAIN DATE

tAST 0.1 RAIN

BACKGROUND DATE

Outfall N-14

BOD

COD

Nitrate

O&G

P04-P

TKN

TOC

TSS

PH

WATER TEMP

RAIN GAUGE

TOTAL RAIN

RAIN DATE

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

Suo~

in.

in.

BackgroundGrab

No flow

No flow

11/12/98

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

Composite

4/9/98

4/4/98

Composite

6.1

69,2

<0.020

0,347

0.429

6.6

42

1.25

1.5

5/1198

Composite

4115/98

4/9/98

Composite

2.4

11.1

0.173

2.0

0.090

0.239

3,6

11

5.25

17.8

0.2

1.5

4130/98

Grab Grab

Grab Grab


Page 170f 18

Measurement Units ~pe Sample/Concentration

Permit SCROOOOOO

Outfall N-14 (cont.)

LAST 0.1 RAIN

BACKGROUND DATE

Outfall A-08

O&G

BOD

TSS

COD

Nitrate/Nitrite

P04-P

TKN

TOC

Copper

Nickel

Zinc

pH

WATER TEMP

RAIN GAUGE

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

Su

“c

in.

BackgroundGrab

No flow

11/12/98

BackgroundGrab

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

No flow

Composite

4124198

Composite

23.9

5

148

0.278

0.548

3.25

285

0.088

<0.010

1.98

NA

Composite

4/24/98

Composite

<2.0

4

<10

0.541

0.717

0.500

10

0.177

0.029

3.44

1

Grab Grab

Grab

2.8

5

25.5

1.24

0.553

0.293

3.6

0.022

<0.010

0.367

4.55

19

0.25

Grab

5.1

6.2

20

74.5

1.89

2.44

0.876

18

0.044

0.012

0.754

8.87

21.4

Grab

<1.0


Page180f18

Measurement Units Type Sampla/Concentration

Permit SCROOOOOO

Outfall A-(I8 (cont.)

TOTAL RAIN

RAIN DATE

LAST 0.1 RAIN

BACKGROUND DATE

in.

Grab

0.3

2/16/98

2/13/98


Table 57National Pollutant Discharge Elimination SystemLand Application Monitoring Data

Page 1 of 3

Permit NDO072125

Note: Permit levels can be found in WSRC NPDES Environmental Monitoring Program (ESH-EMS-91011O) orin the permit itselt The permit is available from the South Carolina Department of Health andEnvironmental Control.

Outfall ND-1

Results ResultsAnalytical Laboratory Shealy Shealy Units

Date of Sample 2/18198 411198

Arsenic

Cadmium

Chromium

Copper

Lead

Mercury

Molybdenum

Nickel

Potassium

Selenium

Silver

Zinc

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Percent Solids

Fecal Coliform

14.6

<0.25

45.2

493

133

<0.5

4.50

21.2

912

20.2

116

2430

15.8

10.5

10.7

12.7

84.9

30.0

10.4

81.6

10.6

11.4

11.2

6290

<2.50

<0.25

25.0

229

76.4

2.02

11.0

25.3

524

4.50

70.3

1650

11.8

15.1

11.5

10.3

13.1

10.7

10.0

19.8

17.4

15.3

19.9

21.8

23.4

<16

mg/kg

mg/kg

mglkg

mgkg

mglkg

mgJkg

mgkg

mg/kg

mg/kg

mgkg

mgkg

mgkg

%

70

70

Yo

Yo

70

0/0

%

0/0

0/0

70

‘%0

0/0

#/G


...’ .’-);’. . ...,-,,,., ., 1-““‘ ,..,:’.,.>::;:4.,,;:. ..+-.-.$’...,.;.+.,,. ::’ , ., , .,..p;;s.;,’,..h, ... ;.,., .—. ,X,,;~L.in: , ,:, .,,;: ;,,,,*-J,.::, - , ,*,;,::,, :;+?: >~--~j,%;-:’;:;:,.~:?; ;

—— —.—

, .,< .. . ,.s;“:;;.-,

‘ :.:. ., “ -~.’,-f~. .:., ..-’ ..y’::T;:i.< , .4,,,, .,..,.->,. ‘,.

‘/, ‘! ,.~,:,$; ;’

+’:$f: .-. ; ,

. . . . f. ;:’;7 >:”, . ,,.. ,, ..,,..~’ .-:- w- ,. .-#.,,‘ .t ;&.,.,, ,::, .,.,,...,,.: ‘ .-. ,.:,. , . . :‘>>’=+<1-.: ‘. :,’, -, ,. .:, . ..:,; ~ ,“’,:;,:?:,,.><& .. . -,. .,$7:’: :



Page 2 of 3

Permit NDO072125

Outfall ND-1

Results ResultsAnalytical Laboratory Shealy Shealy Units

Date of Sample 2/18/98 411198

170

1700

16.2

7.17

Fecal Coliform 7460 <13 #/G

Fecal Coliform 11500 37 #/G

Fecal Coliform 400 4?0 #/G


Fecal Coliform 13700 28 #lG


Fecal Coliform 7870 <6 #/G



Fecal Coliform <8 #/G

Fecal Coliform <5 #lG

Fecal Coliform 4 #/G

Ammonia as Nitrogen 8.27 mg/kg

Total Kjeldahl Nitrogen mg/kg

Nitrate + Nitrite 5.54 mg/kg

pH 4.68 Su

Total Volatile Solids 9.2 0/0

Total Nitrogen 160 mg/kg

Percent Total Solids 19 Y.




Page 3 of 3

Permit NDO072125

Outfall ND-1

ResultsAnalytical Laboratory Shealy Units

Date of Sample 5/20/98

Percent Solids 15.2 ‘Y.

TCLPa Metals

Arsenic

Barium

Cadmium

Chromium

Lead

Mercury

Selenium

Silver

<0.100

0.865

<0.010

<0.020

<0.040

<0.002

<0.100

<0.010

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

TCLPa Volatiles

Benzene

Carbon tetrachloride

Chlorobenzene

Chloroform

1,4-Dichlorobenzene

1,2-Dichloroethane

1,1-Dichloroethane

Methyl ethyl ketone

Tetrachloroethene

Trichloroethene

Vinyl chloride

<0.500

<0.100

<0.100

<0.100

<0.100

<0.100

<0.100

<0.100

<0.100

<0.100

<0.200

J.lglL

J.lg/L

l.lg/L

pgll-

pglL

pglL

pglL

pg/L

pg/L

pglL

j.lgll-

a Toxic Characteristic Leaching Procedure


Table 58Surface Water Surveillance — Inorganic Contaminants, Pesticides, and Herbicides

Page 1 of 32

Parameter Units Jan Feb Mar April May June July Aug Sept Ott Nov Dec

Note: “ND” denotes “not detected, ”

Beaver Dam Creek (400-D)Sample Uate 1/13/98 2/10/98 3/10/98 4/7198 5/19/98 6/16/98 7/14/98 8/12198 9/22/98 10/20/98 11/18198 12J9198Temp

pHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

PesticidesAldrin

Alpha-BHC

Beta-BHC

Delta–BHC

Gamma–BHC(Lindane)

“c

Sumg/L

mg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

13.86.49.2113ND11

ND0.31

0.0833.48

0.916NDNDND

1.72ND

0.145NDND

0.151

14.26.89.376

ND15

ND0.28

0.0344.6

1.42NDNDND

1.570.01

0.064NDND

0.028

13.15.69.1672030

ND0.30

0.2037

2.95NDNDND

3.11ND

0.088NDND

0.01

NDNDNDNDND

20.55.77.2813817

ND0.35

0.0698.6

1.38NDNDND1.7ND

0.0940.0002

ND0.014

24.36,17.182

ND10

ND0.44

0.0934.8

0.379NDNDND

0.6350.01

0.067NDND

0.033

27.36.66.192

ND12

ND0.450,08

3.40.287

NDNDND

0.512ND

0.082NDND

0.067

NDNDNDNDND

28.36.55.8122ND10

ND0.54

0.3414.7

0.204NDNDND

0.431ND

0.056NDND

0,018

28.46.45.4117ND

8ND

0.460.26

7.20.458

NDNDND

0.568ND

0.059NDNDND

NDNDNDNDND

26.86.15.9101ND10

ND0.40

0.0453.5

0.446NDNDND

0.576ND

0.0980.0003

ND0.006

25.17.16.0126ND

5ND

0.470.067

3.3NDNDNDND

0.434ND

0.096NDNDND

21.77.26.4120ND

8ND

0.460.086

4.10.283

NDND

0.0080.435

ND0.115

NDND

0.054

21.26.75.4123ND

5ND

0.35ND3.4

0.328NDNDND0.3ND

0.062NDND

0.013

NDNDNDNDND

,-


Page 2 of 32


Beaver Dam Creek (400-D)hlordane ND ND ND ND

4, 4’-DDD ND ND ND ND4, 4’-DDE ND ND ND ND4, 4’-DDT ND ND ND NDDieldrin ND ND ND NDEndosulfan I ND ND ND NDEndosulfan II ND ND ND NDEndosulfan ND ND ND ND

sulfateEndrin ND ND ND NDEndrin ND ND ND ND

aldehydeEndrin ketone ND ND ND NDHeptachlor ND ND ND NDHeptachlor ND ND ND ND

epoxideMethoxychlor ND ND ND NDToxaphene ND ND ND ND

Herbicides2, 4-D ND ND ND ND2,4, 5-TP ND ND ND ND

(Silvex)


Page 3 of 32


Four Mile Creek-2 (FM-2)Date 1113/98 2110/98 3/10/98 417198 5/19/98 6/16/98 7114/98 8/12198 9/22/98 10/20/98 11/18/98 1219198TempPHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

Pesticides

AldrinAlpha–BHCBeta-BHCDelta–BHCGamma–BHC(Lindane)Chlordane4, 4’-DDD

“cSumg/Lpmhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

12.26.99.053

ND2

ND0.31

0.0444.4

0.131NDNDND

0.533ND

0.07NDND

0,03

8.36,59.527

ND3

ND0.18ND3.9

0.202NDNDND

0.397ND

0.061NDND

0.009

9.74,98.720

ND6

ND0.14

0.0816.7

0.444NDNDND

0.646ND

0.073NDND

0.017

NDNDNDNDND

NDND

13,84.37.225265

ND0.20

0.0655.2

0.268NDND

0.0171.01ND

0.086NDND

0.03

20.64.94.437

ND16

ND0.29

0.0637.5NDNDNDND

3.39ND

0.1970.0003

ND0.047

24.75.83.852

ND15

ND0.380,028,1NDNDNDND

2.29ND

0.414NDND

0.051

NDNDNDNDND

NDND

22.35.54.953

ND9

ND0.42ND3.1

0.222NDNDND

2.130.01

0.325NDND

0.037

24.76.04.556

ND5

ND0.28

0.0262.9

0.113NDNDND

1.08ND

0.06NDND

0.021

NDNDNDNDND

NDND

24.05.33.242

ND8

ND0.350.06

40,294

NDNDND

0.489ND

0.027NDND

0.005

21,36.24.753

ND6

ND0.39

0.0194.1NDNDNDND

1.19ND

0.0570.0001

ND0.038

.

16.16.05.544

ND11

ND0.45ND4.3

0.206NDND

0.0051.73ND

0.1080.0004

ND0.024

16.96,45.444ND

5ND

0.32ND3.8

0.311NDNDND

1.81ND

0.147NDND

0.023

NDNDNDNDND

NDND


~nnonn:Zzzzz

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Page 5 of 32


Four Mile Creek-2B (FM-2B)Date

Temp

pHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

Pesticides

AldrinAlpha-BHCBeta-BHCDelta-BHCGamma-BHC(Lindane)Chlordane4, 4’-’DDD

1/13/98 2/1 0/98 3/1 0/98 4/7/98 5119/98 6116/98 7/1 4/98 8112198 9122198 10/20/98 11/1 8/98 12/9/98


12.26.99.251

ND1

ND0.39

0.0443.8

0.18NDNDND

0.761ND

0,015NDND

0,032

8.16.39.036

ND3

ND0.32ND4.4

0.251NDND

0.0370.555

ND0.014

NDND

0.015

9.45.59.224

ND5

ND0.19

0.0856.6

0.697NDNDND

0,895ND

0.057NDND

0.014

NDNDNDNDND

NDND

14.04.45.735302

ND0.27

0.0345.8

0,167NDNDND

1.14ND

0.0450.0002

ND0.026

22.75.53.143

ND3

ND0.18

0,1127.6

0.087NDNDND

2.110.014

0.080.0003

0.0410.027

25.76.01.455

ND12

ND0.13

0.1517

NDNDNDND

3.38NDNDNDNDND

NDNDNDNDND

NDND

23.75.71.963

ND14

ND0.14ND

50.101

NDNDND

4.560.003

0.6NDND

0.019

24.56.02.552

ND6

ND0.19ND4.2NDNDNDND

1.29ND

0.102NDND

0.008

NDNDNDNDND

NDND

24.75.63.144

ND3

ND0.19ND5.2

0.295NDND

0.0052.33ND

0.1340.0002

ND0.014

19.16.12.558

ND6

ND0,26

0,0143.5NDNDNDND

1.99ND

0.269NDNDND

14.96.34.665

ND3

ND0.27

0.0463.3

0.147NDND

0.0050.649

ND0.045

NDND

0.014

16.46.84.071

ND3

ND0.16ND3.8

0.181NDNDND

0.962ND

0.069NDND

0.007

NDNDNDNDND

NDND


I

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Page 7 of 32


Four Mile Creek-6 (FM-6)Date 1/13/98 2/10/98 3/10/98 4f7198 5/19/98 6/16/98 7/14/98 8112198 9122198 10/20198 11/18/98 12J9198Temp

PHDO

Conductivity

COD

TSS

N02-N

N03-N

Total PhosTOCAlCdCrCuFePbMnHgNiZn

PesticidesAldrinAlpha-BHCBeta–BHCDelta–BHCGamma-BHC(Lindane)

“cSumg/LUmhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

12.6

6.4

10.158

ND2

ND1.53

0.0813.61

0.234NDNDND

0.788ND

0.07NDND

0.026

13.3

6.6

9.4

46

ND3

ND1.16

0.1263.7

0.364NDNDND

0.546ND

0.048NDND

0.01

11.65.4

936

ND9

ND0.46

0.0797.1

0.519NDNDND

0.884ND

0.083NDND

0.034

NDNDNDNDND

18.05.08.344244

ND0.91

0.0654.8

0.257NDNDND

0.855ND

0.077NDND

0.01

24.66.4

8.8a

52ND

3ND

1.620.087

5.20.091

NDNDND1.2

0.18ND

0.0002ND

0.028

26.86.57.246ND

4ND

0.860.025

4.10.321

NDNDNDNDND

0.065NDNDND

NDNDNDNDND

26.07

7.861

ND3

ND1.37

0.0893.8

0.269NDNDND

0.522ND

0.015NDND

0.024

27.06.58.554

ND3

ND0.98

0.1155.5NDNDNDND

0.511ND

0.019NDND

0.013

NDNDNDNDND

26.06,26.354

ND3

ND1.30

0.1114.9

0.313NDNDND

0.702ND

0.0310.0001

ND0.007

21.37.18.363

ND4

ND1.80

0,1282.5NDNDNDND

0.428ND

0.0150,0002

NDND

17.16.99.162

ND7

ND1.430.23.5

0.216ND

0.0050.0060.624

ND0.033

NDND

0.026

18.36.46.968

ND2

ND2.01

0.0413.2

0.265NDNDND

0.823ND

0.041NDND

0,012

NDNDNDNDND

a Supersaturated, probably due to instreamprimaryproduction

.

.... ...,,. ,‘“1

,-’, ,. .,,;.; ,.

isW


Page 8 of 32


Four Mile Creek-8 (FM-8)Chlordane ND ND ND ND4, 4’-DDD4, 4$-DDE4, 4’-DDTDieldnnEndosulfan IEndosulfan IIEndosulfan IsulfateEndrinEndrin

aldehydeEndrin ketoneHeptachlorHeptachlor

epoxideMethoxychlorToxaphene

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDND

NDND

NDNDND

NDND

Herbicides2, 4-D ND2,4, 5-TP ND

(Silvex)


Page 9 of 32


Lower Three Runs Creek-2 (L3R-2)Date 1/13/98 2/10/98 3/10/98 417198 5/19198 6116/98 7114198 8112198 9/22/98 10/20/98 1Ill 8/98 1219/98TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

PesticidesAldrinAlpha-BHCBeta–BHCDelta-BHC

‘cSumg/L~mhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

12.87.38.964

ND1

ND0.18

0.0484.57

0.144NDNDND

0.284ND

0.042NDND

0.03

9.86.9

12.la50

ND1

ND0.14ND5.2

0.087NDNDND

0,206ND

0.02NDND

0.007

11.06.1

9.2

40

ND3

ND0.14

0.1027.4NDNDNDND

0.415ND

0.028NDNDND

NDNDNDND

13.45.48.643344

ND0.19

0.0275.1

0.143NDNDND

0.385ND

0.035NDND

0.007

22.46.35.958

ND8

ND0.23

0.0855.3NDNDNDND

0.5940.0120.078

NDNDND

a Supersaturated, probably due to instream primary productionb Due to an error in the field, no data were reported.

25.26.86.263

ND5

ND0.23

0.0386.5

0.085ND

0.01ND

0.544ND

0.092NDND

0.066

NDNDNDND

22.66.77.191

ND4

ND0.280.05

3.50.198

NDNDND

0.455ND

0.056NDND

0.026

23.36.46.496

ND6

ND0.31

0.0465.2

0.143NDNDND

0.44ND

0,051NDND

0.013

NDNDNDND

26.06.65.072

ND4

ND0.24ND4.6

0.252NDNDND

0.399ND

0.031NDNDND

19.96.84.991

ND2

ND0.300.03

3.6NDNDNDND

0.38ND

0.042NDNDND

15.67.27.492

ND2

ND0.27

0.0374.7

0.197NDND

0.0050.472

ND0.053

NDND

0,01

17.77.0

b

94ND

2ND

0,20ND4.5

0.246NDNDND

0.347ND

0.048NDNDND

NDNDNDND



aaaannnnZzzzzzzz

nnZz

naZz

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nnnnnnnnZzzzzzzz

nnnZzz

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nnnZzz

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Page 11 of 32


Pen Branch4 (PB-3). .Date 1/13/98 2fl 0/98 3/10/98 4/7/98 5/19J98 6/16/98 7/14/98 8/12i98 9122198 10120/98 1Ill 8/98 1219198Temp

pH

DO

Conductivity

COD

TSS

N02-N

N03-N


PesticidesAldrinAlpha-BHCBeta-BHCDelta–BHC

“c 12.6

Su 6.7

mglL 9.1

Kmhos/cm 48

mg/L 31mg/L 2mg/L NDmg/L 0,22mg/L 0.034mg/L 3.7mg/L 0.247mg/L NDmg/L NDmg/L NDmg/L 0.63mg/L 0.006mg/L 0.048mg/L NDmg/L NDmg/L 0.106

12.96.69.454

ND3

ND0.18ND4.9

0.218NDNDND

0.413ND

0.037NDND

0.007

11.6

5.3

7.728

ND7

ND0.18

0.0567.6

0.814NDNDND

0.814ND

0.048NDND

0.01

NDNDNDND

17.25.47.73631

5ND

0.220.106

60.192

NDNDND

0.661ND

0.045NDND

0.012

24.05.86.545

ND3

ND0.22

0.0196.6

0.259ND

0.0560.029

1.30.0130.047

0.00040.0580.019

28.06.65,954

ND3

ND0.24

0.0965.9NDNDNDND

0.985ND

0.066NDND

0.037

a

a

a

a

25.37.08.058

ND3

ND0.24

0.0535.4

0.187NDNDND

0.701ND

0.085NDND

0.016

27.16.17.158

ND12

ND0.31

0.0344.1

0.119NDNDND

0.773ND

0.102NDND

0.007

NDNDNDND

a This sample was contaminated in the laboratory therefore, reliable results were not available.

.

26.66.66,256

ND4

ND0.26

0.0714.2

0.37NDNDND

0.716ND

0.0520.0002

ND0.01

20.56.97.660

ND3

ND0.34

0.1582.3NDNDNDND

0.57ND

0.0430.0001

ND0.378

16.67.18.959

ND4

ND0.31

0.2864,2

0.213NDND

0.0060.514

ND0.058

NDND

0.019

19.07.06,560

ND2

ND0.23ND2.8

0,289NDNDND

0.628ND

0.046NDND

0.006

NDNDNDND


Page 12 of 32


Pen Branch+ (PB-3)

(Lindane)Chlordane4, 4’-DDD4, 4’-DDE4, 4’-DDTDieldnnEndosulfanIEndosulfanIIEndosulfanIsulfateEndrinEndrin



Herbicides2, 4-D2,4, 5-TP

(Silvex)

NDNDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

a Thissample was contaminated in the laborato~ therefore, reliable results were not available.

aaaaaaaa

aa

a

a

a

a

a

a

a

NDNDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND


Page 13 of 32


Steel Creek-4 at Road A (SC-4)Date 1;13/98 2/10/98 3/10/98 4/7/98 5119/98 6/16/98 7114/98 8/12198 9122/98 10/20198 11/18/98 1219198TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

Pesticides

AldrinAlpha-BHCBeta–BHCDelta–BHCGamma-BHC(Lindane)Chlordane4, 4’-DDD

“cSumg/LUmhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

13.77.38.754

NDNDND

0.180.021

5.230.149

NDNDND

0,398ND

0.258NDND

0.031

13.16.79.947

ND3

ND0.16ND6.8

0.235NDNDND

0.367NDNDNDND

0.01

12.76.39.144

ND4

ND0.12

0.0897

0.27NDNDND

0.367ND

0.021NDND

0.016

NDNDNDNDND

NDND

17.85.48.144303

ND0.15

0.1396.6

0,203NDNDND

0.545ND

0.042NDND

0.037

23.55.95.747

ND3

ND0.21ND6.6

0.134NDNDND

0.7310.0160.031

NDND

0.0203

26.56.35.948

ND5

ND0.22

0.0115.8NDNDNDND

0.764ND

0.069NDND

0.145

NDNDNDNDND

NDND

26.66.47.153

ND4

ND0.22

0.0824.2

0.22NDNDND

0.452ND

0.042NDND

0.016

27.06.06.956

ND4

ND0.22

0.1486

NDNDNDND

0.48ND

0.037NDND

0.022

NDNDNDNDND

NDND

26.06.05.450

ND4

ND0.23

0.0585,4

0.507NDNDND

0.733ND

0.059NDND

0.01

22.76.87.159

ND4

ND0.25ND3.3

0.053NDNDND

0.293ND

0.03NDNDND

16.96.89.050

ND4

ND0.240.084.5

0.193NDNDND

0.465ND

0.043NDND

0.007

19.17.06.555

ND2

ND0.16ND4.2

0.252NDNDND

0.498ND

0.036NDNDND

NDNDNDNDND

NDND


I

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Page 15 of 32


Tires Branch-5 (TB-5)-.,Date 1/13/98 2J10198 3/10/98 417198 5/19/98 6/16/98 7114/98 8/12/98 9122198 10/20/98 1Ill 8/98 1219198TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

PesticidesAldrinAlpha-BHCBeta–BHCDelta–BHCGamma–BHC(Lindane)

“cSumg/L~mhos/cmmg/Lmg/LmglLmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/LmglLmg/Lmg/Lmg/Lmg/Lmg/L

13.16.98.538

ND3

ND0.42

0.1293.97

0.221NDNDND1.1ND

0.016ND

0.0310.035

8.96.8

10.636

ND5

ND0.35

0.0153.3

0.247NDND

0.040.988

ND0.041

ND0.0110.012

9.85.7

13.7a29

ND15

ND0.300.06

5.91.56NDNDND2.2ND

0.05ND

0.0140.011

NDNDNDNDND

a Supersaturated, probably due to instream primary production

13.95,06.7343710

ND0,340.114.4

0.281NDNDND

1.54ND

0.047NDND

0.046

20.25.86.434

ND9

ND0.30

0.0525.7

0.064NDNDND

1.950.0120.029

ND0.0290.023

23.36.06.034

ND7

ND0.26

0.0475.3NDNDNDND

0.55ND

0.065NDND

0.077

NDNDNDNDND

21.65.96.735ND12

ND0.25ND4.1

0.201NDNDND

1.070.0030.049

NDND

0.056

23.45.66.635

ND8

ND0.26

0.0585.1

0.151NDNDND

1.46ND

0.038NDND

0.008

NDNDNDNDND

23.6 18.95.8 6.75.6 6.040 34ND ND

5 3ND ND

0.24 0,34ND 0.0384.8 3.5

0.284 NDND NDND NDND ND

1.33 0.794ND ND

0.029 0,021ND NDND NDND ND

14.26.56.842

ND3

ND2.400.15

3.30.219

NDNDND

1.11ND

0.031NDND

0.017

16.76.96.934

ND5

ND0.30ND3.9

0.305NDNDND

0.959ND

0.033NDND

0.012

NDNDNDNDND


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Page 17 of 32


Tinker Creek-1 (TC-1). .Date Ill 3/98 2A 0/98 3/10/98 4/21/98 5/19/98 6/16198 7114/98 8/12198 9/22/98 10/20/98 11/18/98 12/9/98TemppHDOConductivityCODTSSN02–NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

PesticidesAldrinAlpha-BHCBeta-BHCDelta-BHCGamma–BHC(Lindane)


12.36.69.731

NDNDND

0.180.0854.86

0.106NDNDND

0.208ND

0.01NDND

0.033

10.07.09.928

ND2

ND0.20

0.0364.2

0.057NDNDND

0.566ND

0.008NDND

0,008

10.05.3

11.124

ND2

ND0.20

0.0675.5NDNDNDND

0.317NDNDNDNDND

NDNDNDNDND


16.76.5

1o.2a26

ND7

ND0.22

0.4955,5

0.15NDNDND

0.635ND

0.028NDNDND

19.95.46.126

ND9

ND0.16

0.0385.6

0.094NDNDND

0.520.0180.075

NDNDND

23.26.14.371

ND8

ND0.19

0.0565.3NDNDNDNDNDNDNDNDNDND

NDNDNDNDND

21.45.96.429ND10

ND0.17

0.1423.2

0.222NDNDND

0.728ND

0.037NDND

0.007

23.05.85.729

ND9

ND0.23

0.1074.6NDNDNDND

0.634ND

0.041NDND

0,011

NDNDNDNDND

23.24.85.229

ND9

ND0.23

0.0455.2

0.264NDNDND

0.399ND

0.0220.0003

ND0.005

18.86.76.727

ND7

ND0.29

0.0423.1NDNDNDND

0.452ND

0.037NDNDND

14.36.67.729

ND4

ND0.28

0.3193.5

0.148NDND

0.0080.214

ND0.026

NDND

0.017

16.46.07.631

ND3

ND0.19ND4.8

0,211NDNDND

0,155ND

0.016NDND

0.029

NDNDNDNDND


uc(u

I

)oanoaon nn nnn nn!Zzzzzzz Zz Zzz Zz

]n no onno:Zzzzzzz

Innnnnnn:Zzzzzzz

nn nnn nnZz Zzz Zz

nn nnn nnZz Zzz Zz

lnnnnnnn nnn:Zzzzzzz $?9 Zzz $?$?

nnZz

nnZz

nnZz

nnZz

.=—



Page 19 of 32


Upper Three Runs-lA (U3R-lA)Date 1/;3/98 2/10/98 3/10/98 4/7/98 5/19/98 6/16198 7/14/98 8112198 9/22/98 10/20/98 11/18/98 12/9/98Temp

pH

DO

Conductivity

COD

TSS

N02-N

N03-N


PesticidesAldrinAlpha-BHCBeta-BHCDelta-BHCGamma-BHC(Lindane)

“cSumg/LUmhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/LmgJLmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

14.16.97.619

ND2

ND0.40ND1.8

0.133NDNDND

0.266ND

0.008NDND

0.029

10.76.6

11.2a27

ND5

ND0.30

0.0694

0.189NDND

0.0520.318

ND0.015

ND0.0130.006

11.74.07.419

ND4

ND0.22

0.0896.9

0.316NDNDND

0.601ND

0.013NDND

0.005

NDNDNDNDND

14.45.06.616264

ND0.28

0.0443

0.081NDNDND

0.47ND

0.015NDND

0.016

19.2

4.2

7.2

15

ND5

ND0.31

0.0113.5

0.332NDNDND

0.548NDNDNDND

0.028

21.35.36,117

ND6

ND0.33

0.0512.8NDNDND

0.011NDND

0.031NDND

0.064

NDNDNDNDND


20.45.76.418

ND6

ND0.34

0.0552.4

0.205NDNDND

0.372ND

0.01NDND

0.022

21.35.56.916

ND7

ND0.37ND2.7NDNDNDND

0.488ND

0.01NDND

0.006

NDNDNDNDND

21.05.76.517

ND9

ND0.410.03

4.30.321

NDNDND

0.461ND

0.0170.0004

ND0.01

18.85.85.517

ND2

ND0.44ND2.1NDNDNDND

0.324ND

0.011NDND

0.008

14.85.57.117

ND4

ND0.450.46

3.20.175

NDND

0.0080.394

ND0.017

NDND

0.026

17,25.28.017

ND2

ND0.34ND2.7

0.243NDNDND

0.257ND

0.011NDND

0.063

NDNDNDNDND


nnnnnnnZzzzzzz

nnnnannZzzzzzz

nnnnnnnZzzzzzz

nnnnnnnZzzzzzz

nn nnnZz Zzz Z$?

nnnSS Zzz SZ

nnn nnSs Zzz Zz

nn nnnZz Zzz s!?

nnZz

nnZz

nnZz



Page 21 of 32


Upper Three Runs-4 (U3R-4)

TemppHDOConductivity

COD

TSS

N02-N

N03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

PesticidesAldrinAlpha-BHCBeta–BHCDelta-BHCGamma–BHC(Lindane)Chlordane4, 4’-DDD

‘c 11.9Su 6.2mg/L 8.8wmhos/cm 24mg/L NDmg/L NDmg/L NDmg/L 0.31mg/L 0.061mg/L 3.54mg/L 0.131mg/L NDmg/L NDmg/L NDmg/L 0.322mg/L NDmg/L 0.014mg/L NDmg/L NDmg/L 0.027

11.66.48,423ND

3ND

0.21ND4.7

0.287NDNDND

0.39ND

0.018NDND

0.014

13.25.57.719287

ND0.130.12

140.648

NDNDND

0.763ND

0.036NDND

0.011

NDNDNDNDND

NDND

18.24.67.52034

4ND

0.190.116.4

0.218NDNDND

0.811ND

0.032NDND

0.011

22.05.36,421

ND8

ND0.25

0.0194.8

0.413NDNDND

0.8040.011

NDNDND

0.025

24.36.16.921

ND9

ND0.26

0.0113.2NDNDNDND

0.226NDNDNDNDND

NDNDNDNDND

NDND

23.36.16.426

ND7

ND0.31

0.0684.9

0.235NDNDND

0.495NDNDNDND

0.027

23.95.75.822

ND10

ND0.29

0.0894.3

0.423NDNDND

0.608ND

0.026NDNDND

NDNDNDNDND

NDND

22.85.25,722

ND6

ND0.25ND3.8

0.353NDNDND

0.773ND

0.02NDND

0.006

19.86.47.322ND

4ND

0.380.139

2NDND

0.006ND

0.412ND

0.015NDNDND

16.66.27.420

ND4

ND0.28

0.7184.8

0.23NDNDND

0.488ND

0.026NDND

0.014

17.75.86.125

ND3

ND0.25ND6.7

0.314NDNDND

0.47ND

0.021NDND

0,049

NDNDNDNDND

NDND


Nm‘5NINa)01

Z

I

)nnnnn!Zzzzz

]nnoan!Zzzzz

~aonnn:Zzzzz

.

nna nn~$? Zzz Zz

naaSs Zzz 22

nn nnnZz Zzz S$?

nnZz

nnZz

nnZz

nnZz

—=—


..


Page 23 of 32


River Mile 120 (RM-120; RM-10; Below SRS)Date 11~3198 2/10;98 3/10/98 417198 5/19/98 6/16/98 7/27/98 8/11/98 9122198 10/20/98 1Ill 7/98 12/8/98TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

AldrinAlpha-BHCBeta–BHCDelta–BHCGamma–BHC(Lindane)

‘cSumg/Lpmhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

10.76.3

14.la72

ND5

ND0.28

0.0483.990.33NDNDND

0.607ND

0.0630.0003

ND0.031

10.26.4

11.4a48

ND9

ND0.23

0.0423

1.71NDNDND1.7ND

0.044NDNDND

11.26.08.653

ND7

ND0.36

0.1245,2

1.35NDNDND

1.32ND

0.028NDND

0.012

NDNDNDNDND

15.66.28.2633412

ND0.39

0.0795.6

1.44NDNDND

1.78ND

0.067NDND

0.008

19,96.77.958

ND5

ND0.48

0.1473.1

0.18ND

0.069ND

0.6390.0120.037

ND0.072

ND


25.16.69.996

ND16

ND0.52

0.2283.7NDNDNDND

0.649ND

0.08NDNDND

NDNDNDNDND

24.46.45.893

ND15

ND0.50

0.1944

NDNDNDND

0,458ND

0.062NDND

0,006

24.86.36.899

ND13

ND0.47

0.3133.3

0.418NDNDND

0.52ND

0.078NDNDND

NDNDNDNDND

23.76.36,787

ND11

ND0.431,473.3

0.93NDNDND

0.897ND

0.089NDND

0.014

21.17.06.5115ND

8ND

0.47ND3.4

0.149ND

0.006ND

0.886ND

0.079NDNDND

18.36.87.5100ND

7ND

0.470.037

3.50,278

NDNDND

0.2970.0030.066

NDND

0.006

18.16,77.8110ND

8ND

0.450.368

3.40,212

NDND

0.0050.301

ND0.072

NDND

0.011

NDNDNDNDND


N(9

%Q’Nalm2

an nnnZz Zzz s~

ann an~~ Zzz Zz

nn nnn nnZz Zzz Zz

nn non nnZz Zzz Zz

noZz

noZz



Page 25 of 32


River Mile 129 (RM-129; Below SRS)Date 1/13/98 2/10/98 3/10/98 417198 5119/98 6/76/98 7121198 8/71/98 9/22/98 10/20/98 1Ill 7t98 12/8/98TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn



10.56.2

10.466

ND9

ND0.26

0.0673.61

0.344NDNDND

0.641ND

0.069NDND

0.045

9.86.7

10.050

ND6

ND0.27

0.0462.2

1.33NDND

0.0291.36ND

0.041NDND

0.018

11.36.2

10.456

ND8

ND0.37

0.2035.1

1.14NDNDND

1.26ND

0.036NDND

0.005

NDNDNDNDND

15.66.47.4643418

ND0.39

0.1337.7

0.838NDNDND

1.58ND

0.075NDND

0.01

19.46,8

g.ga

!57ND

7ND

0.460.362

3.20.147

NDNDND

0.779NDNDND

0.011ND

25.16.6

8.6a

64ND12

ND0.30

0.1954.5NDNDNDND

0.813ND

0.0710.0001

NDND

NDNDNDNDND

24.46.75.774

ND9

ND0.33

0.0313.7NDNDNDND

0.501ND

0.071NDND

0.03

23.75.96.274

ND19

ND0.270.14

8.50.616

NDNDND

0.714ND

0.067NDND

0.013

NDNDNDNDND

23.96.75.878

ND9

ND0.27

0.3124.3

0.655NDNDND

0.774ND

0.16NDND

0.023

18.26.76.982

ND14

ND0.38

0.3532.8

0.089ND

0.011ND

0.936ND

0.095NDNDND

18.67.06.086

ND15

ND0.27

0.1224.3

0.273NDNDND

0.292ND

0.063NDND

0.006

18.76.77.6116ND

7ND

0.44ND6.1

0.223NDNDND

0.589ND

0.107NDND

0.02

NDNDNDNDND

a Supersaturated, probably dueto instreamprimaryproduction


I

iamnannn nn:Zzzzzzz Zz ana

Zzz 2s

lnnnnnnn,Zzzzzzz

oannnnaZzzzzzz

nannnnnZzzzzzz

nn nnn nnZz Zzz Zz

no nnaZz Zzz 5s

nn nanZz Zzz SZ

anZz

!2!2

-=—



Page 27of 32


River Mile 140 (RM-140)Date 1/13/98 2/10/98 3/10/98 4/7/98 5/19/98 6/16/98 7121198 8/11198 9/22/98 10/20198 1Ill 7198 1218198TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn


‘cSumg/L~mhos/cmmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/LmglL

10.76.3

11.065

ND6

ND0.25

0.0444.02

0.321NDNDND

1.15ND

0.069NDND

0.023

10.56.59.951

ND6

ND0.28

0.1271.3

0.933NDND

0.0340.99ND

0.0350.0002

ND0.044

11.95.88.158

ND10

ND0.36

0.3585.3

1.71NDNDND

1.79ND

0.043NDND

0.007

NDNDNDNDND

15.76.47.4653517

ND0.37

0.1766

1.01NDND

0.0371.74ND

0.068NDND

0.028

19.16.88.859

ND7

ND0.46

0.1972.5NDND

0.053ND

0.4570.0230.027

NDNDND

25.36.6

lo.la87

ND14

ND0.49

0.2053.3NDNDNDND

0.615ND

0.078NDND

0.012

NDNDNDNDND

24.66.36.384

ND12

ND0.47

0,1354.1NDNDNDND

0.489ND

0.1330.0002

ND0,045

24.75.86.896

ND11

ND0.45

0,1293.8

0.305NDNDND

0.508ND

0.058NDNDND

NDNDNDNDND

23.66.57.087

ND13

ND0.42

0,2743.6

0.59NDND

0.0060.681

ND0.104

NDND

0.019

21.06.86.5115207

ND0.47

0.0773.5

0.066NDNDND

0.584ND

0.083NDNDND

18.66.97.794

ND6

ND0.46

0.0233.8

0.263NDNDND

0.302ND

0.064NDND

0.01

18.66.78.2117ND

6ND

0.430.227

3.60.186

NDNDND

0.394ND

0.094NDND

0.009

NDNDNDNDND

a Supersaturated, probably dueto instreamprimaryproduction


Page 28 of 32


River Mile 140 (RM-140)

4, 4’-DDD4, 4’-DDE4, 4’-DDTDieldfinEndosulfan IEndosulfan IIEndosulfan IsulfateEndrinEndrin



Herbicides2, 4-D2,4, 5-TP

(Silvex)

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND

NDNDNDNDNDNDND

NDND

NDNDND

NDND

NDND


Page 29 of 32


River Mile 160 (RM-1 60)Date 1/13/98 2110198 3I1OI98 417198 5119/98 6/16198 7121/98 8/11/98 9/22/98 10/20/98 11117/98 1218198Temp

pH

DO

Conductivity

CODTSS

N02-N

N03-N

Total PhosTOCAlCdCrCu

Fe

PbMnHgNiZn

PesticidesAldrin

Alpha-BHC

Beta–BHCDelta–BHC

Gamma-BHC(Lindane)

“cSumglL~mhos/cmmglLmglLmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

10.66.6

11.9a62

ND11

ND0.28

0.0563.82

0.352NDNDND

0.936ND

0.094NDND

0.019

10.07,0

10.754

ND11

ND0.29ND3.6

1.04NDND

0.0311.11ND

0.075NDNDND

12.15.89,349

ND57

ND0.25

0.1888.5

5.24NDNDND

5.68ND

0.138NDND

0.036

NDNDNDNDND


15.56.59.4673020

ND0.39

0.1915.4

1.11NDNDND

1.63ND

0.086NDND

0.018

19.9 24.96.8 6.5

11.5a 11.2a79 86

ND ND9 12

ND ND0.50 0.34

0.065 0.1884.2 2.7

0.094 NDND NDND NDND ND

0.52 0.5180.024 ND0.075 0.066

ND NDND NDND ND

NDNDNDNDND

24.76.46.490ND10

ND0.43

0.0953.3

0.261NDNDND

0,29ND

0.071NDND

0.021

24.35.87.4101ND

8ND

0.440.104

3,50.367

NDNDND

0.439ND

0.066NDNDND

NDNDNDNDND

23.76.37.280

ND12

ND0.36

0.0234.2

0.462NDND

0.0050.497

ND0.159

NDND

0.024

21.96.76.4127ND

7ND

0.480.153

3.20.224

NDNDND

0.408ND

0.138NDND

0.008

19.56.97.998

ND5

ND0.44ND3.2

0.289NDNDND

0.209ND

0.071NDND

0.008

18.87.08.1108ND

5ND

0.380.249

3.10.1420.002

ND0.0060.222

ND0.1NDND

0.031

NDNDNDNDND


I

]nnnnnnn!Zzzzzzz

~nnnnnnn:Zzzzzzz

innnnann:Zzzzzzz

lnnaannn:Zzzzzzz

an nnn nnZz Zzz Zz

nnn nn2s Zzz Zz

nn nnn nnZz Zzz Zz

na nnn nnZz Zzz Zz

nnZz

nnZz

-=—



Page 31 of 32


Vogtle Discharge (R-3B; Below Vogtle Electric Generating Plant)Date 1/13/98 2/10/98 3/10/98 4/7198 5/19/98 6116/98 7/21/98 8/11/98 9122198 10/20/98 11/17198 12/8/98TemppHDOConductivityCODTSSN02-NN03-NTotal PhosTOCAlCdCrCuFePbMnHgNiZn

Pest~cjdesAldrinAlpha–BHCBeta-BHCDelta–BHCGamma–BHC(Lincfane)

‘cSumg/Lymhos/cmmg/Lmg/Lmg/LmgJLmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/Lmg/L

10.76.6

13.2a69

ND7

ND0.270.1

4.890.383

NDNDND

0.578ND

0.069NDND

0.026

10.17.0

10.955

ND6

ND0.29

0.0292.1

0.808NDNDND

0.895ND

0.043NDNDND

11.65.89.3542021

ND0.32

0.2446.5

2.05NDNDND

2.35ND

0.073NDND

0.022

NDNDNDNDND

a Supersaturated, probably due to instreamprimaryproduction

16.06.38.1683619

ND0.30

0.1746.5

1.31NDNDND

1.99ND

0.086NDND

0.011

19.77.0

g.ga

70ND

8ND

0.480.426

3.8NDNDNDND

0.4240.03

0.045NDNDND

23.76.5

1o.2a85

ND14

ND0.40

0.2973

NDNDNDND

0.503ND

0.072NDND

0.019

NDNDNDNDND

24.66.46,590

ND11

ND0.51

0.1344.2NDNDNDND

0.321ND

0.073NDND

0.023

24.26.07.1102ND

7ND

0.460.116

3.50.567

NDNDND

0.659ND

0.085NDNDND

NDNDNDNDND

23.6 22,26.3 6.96.8 6.487 121

ND ND12 14

ND ND0.39 0.480.36 0.062

3.2 3.40.666 0.506

ND NDND NDND ND

0.674 0.844ND ND

0.112 0,13ND NDND ND

0.013 0.016

19.07.07.598

ND8

ND0.45ND3.9

0.272NDNDND

0.238ND

0.066NDND

0.009

18.97.17.9115ND

7ND

0.410.319

3.70.148

NDNDND

0.268ND

0.094NDND

0.013

NDNDNDNDND


I

]Qnnaann nn nnn:Zzzzzzz Zz Zzz SS

~nnonnnn:Zzzzzzz

innaannn.Zzzzzzz

lnnnnnnn,Zzzzzzz

—=.

nn nnn nnZz Zzz Zz

na nnn nnZz Zzz Zz

nnn nnS2 Zzz Zz

nnZz

naZz


Table 59Sediment Surveillance — Inorganic Contaminants, Pesticides, and Herbicides

Page 1 of 2

mu/L

Upper Beaver Lower UpperThree Dam Four Mile Pen steel Three Three Tinker River Mile River Mile

Runs-4 Creek Creek Branch Creek-4 Runs-2 Runs-l A Creek-1 160 VogtleConstituent

120(U3R-4) (400-D) (FMC/RdA) (PB/RdA) (SC-4) (L3R-2) (U3R-lA) (TC-1) (RM-160) Discharge (RM-120)

Note: All analyses are performed by the Toxicity Characteristic Leaching Procedure (TCLP) method.

Aluminum

Arsenic

Barium

Cadmium

Chromium

Copper

Iron

Lead

Magnesium

Manganese

Mercury

Nickel

Selenium

Silver

Uranium

Zinc

0.6

<0.005

0.949

<0.002

0.014

0.029

0.218

0.005

0.761

0.765

<0,0001

0.021

<0.005

<0.005

<0.500

0.866

0.829

0.006

0.962

<0.002

0.016

0.037

0.402

0.008

2.94

3.4

<0.0001

0.019

<0.005

<0.005

<0.500

0.554

0.406

<0.005

0.884

<0.002

0.014

0.023

0.937

<0.003

0.221

1.56

<0.0001

0,011

<0.005

<0.005

<0.500

0.826

0.472

<0.005

1.25

<0.002

0.015

0.032

0.295

<0.003

1.05

6.74

<0.0001

<0.010

0.006

<0.005

0.500

0.927

0.292

<0.005

1.34

<0.002

0.016

0.029

0.266

<0.003

0.86

6.06

<0.0001

0.012

0.006

<0.005

<0.500

0.749

0.339

<0.005

1.29

<0.002

0.015

0.038

0.277

<0.003

1.18

3.07

<0.0001

<0.010

<0.005

<0.005

<0.500

1

0.507

<0.005

1.25

<0.002

0.017

0.034

0.318

0.007

0.478

0.178

<0.0001

0.013

<0.005

<0.005

<0.500

1.04

1.14

<0.005

0.225

<0.002

<0.005

0.02

<0.020

<0.003

0.285

0,043

0.0003

<0.010

<0.005

<0.005

<0.05

0.258

0.73

<0.020

0.443

<0.005

<0.010

<0.010

<0.020

<0.020

0.716

1.2

<0.0002

<0.010

<0,050

<0.005

<0.500

0.072

0.1

<0.020

0.124

<0.005

<0,010

<0.010

<0.020

<0.020

<0.050

0,097

<0.0002

<0.010

<0,050

<0.005

<0.500

0.155

0.667

<0.020

0.193

<0.005

<0.010

<0.010

<0.020

<0.020

0.473

0.515

<0.0002

<0,010

<0,050

<0.005

<0.500

0.076


m‘6Nalu)

E

zo0v

00Fl-

0 o“Vv

o0$1


—


Table 60Fish Surveillance — Mercury

Page 1 of 3

Mercury (pg/g - Parts Per Million)

TypeLocation of Fish Analytical Results Maximum Minimum

Note: ND denotes “not detected; the reporting limit is less than 0.33 pg?Q.”

New Savannah Bluff Lock& Dam (formerly AugustaLock & Dam)





Beaver Dam Creek Mouth



Beaver Dam Creek(400-D)

Four Mile Creek Mouth





Highway 17A(Freshwater)



Bass

Bream

Catfish

Bowtina

SuckeP

Bass

Bream

Catfish

Bream

Bass

Bream

Cattish

Bowfina

SuckeP

Bass

Bream

Catfish

0.50

ND

ND

0.47

ND

1.27

ND

ND

0.67

ND

ND

ND

1.03

ND

0.53

ND

ND

0.53

ND

ND

0.43

ND

1.30

ND

ND

0.40

0.33

0.60

0.33

0.90

ND

0.43

ND

ND

0.83

ND

ND

0.43

ND

0.80

ND

0.43

ND

0.90

0.57

ND

0.57

0.40

0.50

ND

0.33

0.77

ND

ND

ND

0.47

0.63

0.33

ND

0.43

0.60

0.60

0.40

0.67

0.50

0.47

ND

ND

0.50

ND

0.33

0.60

ND

0.97

ND

0.70

0.33

0.90

0.87

ND

0.57

ND

0.70

0.33

0.33

0.83

<0.33

0.33

0.60

0.47

1.30

0.33

0.70

0.67

0.90

0.87

0.40

1.03

0.50

0.70

0.33

0.33

0.50

<0.33

<0.33

<0.33

<0.33

0.63

<0.33

<0.33

<0.33

<0.33

<0.33

<0.33

0.57

<0.33

0.43

<0.33

<0.33

a Sample collected at request of DOE

.




Page 2 of 3

Mercury @g/g - Parts Per Million)


River Mile O-8

River Mile O-8

River Mile O-8

Highway 301

Highway 301

Highway 301

Highway 301

Highway 301

L-Lake

L-Lake

L-Lake

Lower Three Runs CreekMouth



Lower Three Runs atPatterson Mill Road

Lower Three Runs atPatterson Mill Road

PAR Pond

PAR Pond

Pond B

Pond B

Steel Creek Mouth

Steel Creek Mouth

Steel Creek Mouth

RedDrum

Mullet

Catfish

Bass

Bream

Catfish

Bowfina

Bass

Bream

Catfish

Bass

Bream

Catfish

Bass

Bream

Bass

Bream

Bass

Bream

Bass

Bream

Catfish

a Sample colleoted at request of DOE

0.83

ND

0.40

1.03

ND

0.40

0.97

0.47

0.80

ND

ND

1.03

ND

0.60

1.13

1.00

1.20

0.60

1.20

ND

1.07

ND

0.37

0.67

ND

0.37

0.83

ND

0.57

0.67

ND

1.57

ND

ND

1.17

ND

0.57

0.87

0.80

1.30

ND

1.83

ND

1.17

ND

0.47

ND

ND

ND

0.53

ND

0.43

0.47

ND

0.77

ND

ND

0.70

ND

0.60

1.10

0.73

1.33

0.40

0.90

ND

1.17

0.47

ND

ND

ND

ND

0.37

ND

0.40

0.47

ND

0.77

ND

ND

0.60

ND

0.43

0.57

0.57

1.83

0.47

0.83

ND

0.83

ND

0.43

0.43

ND

ND

0.60

ND

0.53

1.27

0.47

0.60

0.33

ND

0.57

ND

0.47

0.93

0.60

1.00

0.33

1.00

ND

0.93

ND

ND

0.83

<0.33

0.40

1.03

<0.33

0.57

1.27

0.47

1.57

0.33

<0.33

1.17

<0.33

0.60

1.13

1.00

1.83

0.60

1.83

<0.33

1.17

0.47

0.47

<0.33

<0.33

<0.33

0.37

<0.33

0.40

0.47

<0.33

0.60

<0.33

<0.33

0.60

<0.33

0.43

0.57

0.57

1.00

<0.33

0.90

<0.33

0.83

<0.33

<0.33




Page 3 of 3

Mercury (pg/g - Parts Per Million)


Steel Creek Mouth

Steel Creek Mouth

Steel Creek-4 at Road A

Steel Creek-4 at Road A

Stokes Bluff

Stokes Bluff

Stokes Bluff

Upper Three Runs Mouth



Upper Three Runs-4

Upper Three Runs-4

Upper Three Runs-4

Bowfina

SuckeF

Bass

Bream

Bass

Bream

Catfish

Bass

Bream

Catfish

Bass

a Sample collected at request of DOE

0.37

ND

1.23

0.43

0.97

0.50

0.63

0.37

ND

ND

1.03

ND

1.10

0.43

0.33

1.47

0.40

1.03

ND

0.63

0.93

ND

ND

0.63

ND

ND

1.27

0.53

1.00

0.43

1.07

0.43

0.37

0.83

ND

ND

0.47

ND

0.43

0.70

ND

1.10

0.40

1.20

0.33

0.70

ND

ND

ND

0.53

ND

0.37

1.13

ND

1.13

0.70

0.77

0.43

0.40

0.33

ND

ND

0.63

ND

0.40

1.27 0.37

0.53 <0.33

1.47 1.00

0.70 0.40

1.20 0.77

0.50 <0.33

0.70 0.37

0.93 <0.33

<0.33 <0.33

<0.33 <0.33

1.03 0.47

<0.33 <0.33

1.10 <0.33


Quality Assurance

Table 61Blind Sample Results for pH Field Measurements

Page 1 of 1

pH Units

Sample Identification Measured Value Known Value Difference

BpH~l-1 3.92 4.00 0.08 unitsBpH-ol-2 6.91 6.85 0.06 unitsBpH-02-l 4.04 4.01 0.03 unitsBpH-02-2 6.89 6.87 0.02 unitsBpH-03-l 7.33 7.41 0.08unitsBpH-03-2 6.87 6.87 0.00 unitsBpH-04-l 7.49 7.40 0.09 unitsBpH-04-2 6.74 6.85 0.11 unitsBpH-05-l 7.45 7.44 0.01 unitsBpH-05-2 4.04 4.04 0.00 unitsBpH-06-l 6.79 6.85 0.06 unitsBpH-06-2 3.98 4.02 0.04 unitsBpH-07-l 3.98 4.00 0.02 unitsBpH-07-2 4.00 4.02 0.02 unitsBpH-06-l 3.99 4.04 0.05 unitsBpH-08-2 3.97 4.02 0.05 unitsBpH-09-l 7.36 7.40 0.04 unitsBpH-09-2 6.78 6.87 0.09 unitsBpH-10-l 6.90 6.90 0.00 unitsBpH-1 O-2 7.42 7.45 0.03 unitsBpH-11-l 7.46 7.43 0.03 unitsBpH-1 1-2 4.00 4.03 0.03 unitsBpH-12-l 4.05 4.02 0.03 unitsBpH-12–2 7.42 7.39 0.03 units

.

Quality Assurance

Table 62Blind Sample Results for Tritium

Page 1 of 1

pCdmL Range

Lower UpperMeasured Control Control

Sample Date Value Known Value Ratio Limita Limita Evaluationb

01–15-98 9.73 * .45 10.2 0.95 7. 19.5 A

02-27–98 5.46* .34 5.539 0.99 3.8 10.6 A

03-12–98 6.777* .48 7.742 0.88 5.3 14.8 A

04-16-98 11.465* .541 12.31 0.93 8.5 23.5 A

05-19-98 3.584 k .296 3.681 0.97 2.5 7. A

06-17-98 3.335 k .296 3.375 0.99 2.3 6.4 A

07-15-98 5.405 f .419 5.949 0.91 4.1 11.4 A

08-14-98 5.189 k .452 5.852 0.89 4. 11.2 A

09-21-98 2.578 & .382 2.582 1. 1.8 4.9 A

11-02-98 2.676 k .419 2.939 0.91 2. 5.6 A

11–12–98 7.73 ? .452 8.051 0.96 5.6 15.4 A

12-04-98 5.459 k .483 6.056 0.9 4.2 11.6 A

a Control limits are based on DOE/Environmental Measurements Laboratory historical data for tntium.b A = Acceptable


.

Table 63QAP Interlaboratory Comparison of Analytical Results

Page 1 of 5

Range

NuclideSRSIQAP Number of Mean of Lower Control Upper Control

SRS Valuea QAPb Value Ratio Labs Labs Limitc Limitc Evaluation

Note: A is “acceptable,”W is “acceptable with waming,”and N is “not acceptable.”

QAP Set #48, June, 1998

Alpha

Am-241

Beta

Ce-144

co-57

CO-60

CS-134

CS-137

Mn-54

Pu-238

Pu-239

Sb-125

Sr-90

U-234

U-238

2.17 *0.2

0.082 ~ 0.008

2.14 t 0.14

8. ~ 2.6

11.1*1.

809~l.

19.3* 1.4

11.5* 1.5

5.5 * 0.2

0.066 * 0,008

0.067 ~ 0.008

13.3 A1,8

1.21 * 0.1

0.032 t 0,005

0.032 ~ 0.005

1.4

0.069

1.96

8.21

11.11

9.09

19.74

11.86

5.44

0.07

0.062

12.16

1.758

0.031

0.031

1.55

1.19

1.09

0.97

1.00

0.98

0.98

0.97

1.01

0.95

1.07

1.09

0.69

1.04

1.05

72

47

69

81

83

93

82

90

89

46

49

86

31

36

39

1.357

0.079

2.129

7.775

10.988

9.045

18.97

12.05

5.75

0.068

0.067

12.914

1.734

0,037

0,035

0.686

0.049

1.392

4.926

7.222

6.818

14.608

8.658

4.134

0.05

0.045

7.418

1.143

0.025

0.024

a Values are Bq/L, BqiKg, and Bq/filter.b Quality Assessment Program conducted by Department of Energy’s Environmental Measurements Laboratory (EML), New Yorko Control limits were established by EMUQAP from historical data.

2.184

0.146

3.352

10.673

14.887

11.817

24.28

15.774

7.453

0.097

0.089

17.146

3.429

0.062

0.078

w

A

A

A

A

A

A

A

A

A

A

A

w

A

A


Page 2 of 5

Range

SRSIQAP Number of Mean of Lower Control Upper ControlNuclide SRS Valuea QAPb Value Ratio Labs Labs Limitc Limitc Evaluation

Soil

CS-137

K-40

Pu-239

U-234

U-238

Vegetation

Am-241

Cm-244

CO-60

CS-137

K-40

Pu-239

Sr-90

Water

Alpha

Beta

CO-60

Cs-137

H-3

368. k 41.

371. * 40.

2.88 A 0.54

9.*1.4

9,4 * 1.4

1.19 t 0,23

2.04 t 0,31

11.5* 1.3

193. t18.

805. k 84.

1.7 t o.29

494. & 52.

1399. * 236.

2460. & 604.

15.*1.

50.5 k 4.8

208. f 15.

329.5

313.5

5.305

31.13

31.9

1.105

2.174

10.575

181.5

707.5

1.77

359.

1421.

2200,

13.6

46.

218.3

1.12

1.18

0.54

0.29

0.29

1.08

0,94

1.09

1.06

1.14

0.96

1.38

0.98

1.12

1.10

1.10

0.95

96

94

54

39

43

48

29

78

82

75

49

40

59

62

89

98

73

353.554

344.537

5.506

29.574

29.699

1.332

2.108

11.41

191.12

751.365

1.754

326.331

1436.631

2109.8

14.851

50.876

238.165

263.6

238.26

3.66

14.32

13.717

0,785

1.

6.874

145.2

537.7

1.044

154.37

738.92

1166,

10.88

36.8

150.627

a Values are Ba/L, B(r/Kft, and Bet/filter.b Quality Assessment P~ogramc&ducted by Department of Energy’s Environmental Measurements Laboratow (EML), New Yorkc C6ntrol limits were established by EMUQAP from historioel data.

434,94

482.79

8.859

40.469

44.341

2.984

3,586

15.44

252.285

926.825

3.044

470.29

1861.51

3520.

16.32

57.5

392.94

A

A

N

N

N

A

A

A

A

A

A

N

A

A

A

A

A

iI

..,: ., ... .-,<! , f.

,,

q’

Table 63QAP lnterlaboratory Comparison of Analytical Results

Page 3 of 5

SR31QAP Number of Mean of Lower Control Upper ControlNuclide SRS Valuea QAPb Value Ratio Labs Labs Limitc Limitc Evaluation

Mn-54 62.5 A 6.3 57. 1.10 94 62.472 45.6 70.68 A

Pu-238 2.28 k 0.27 2.526 0.90 59 2.417 1.92 3.157 A

Pu-239 1.57 * 0.19 1.65 0.95 59 1.65 1.32 2.244 A

Sr-90 5.1 * 1.9 4.357 1.17 60 4.488 3.268 6.798 A

U-234 0.38 k 0.07 0.396 0.96 45 0.426 0.317 0.563 A

U-238 0.37 k 0.06 0.396 0.93 48 0.426 0.317 0.511 A

QAP Set #49, December, 1998

Alpha

Am-241

Beta

CO-60

CS-137

Mn-54

Pu-238

Pu-239

Sb-125

Sr-90

U-234

U-238

1.59*0.13

0.511 A 0.023

2.17 * 0.15

8.76 A 0,158

21. ~ 0.418

4.87 k 0.144

0.469 t 0.023

0.434 ~ 0.024

5.24 A 0.179

1.24*0.15

0.262 k 0.018

0.264 t 0.018

1.65

0.51

2.16

9.16

22.47

4.92

0.46

0.42

8.89

1.12

0.26

0.26

0.96

1.00

1.00

0.96

0.93

0.99

1.02

1.03

0.59

1.11

1.01

1.02

73

54

75

99

99

95

43

44

88

34

29

30

1.696

0.562

2.069

9.096

22.582

5.127

0.49

0.454

8.926

1.096

0.27

0.276

0.825

0.372

1.555

6.87

16.403

3.739

0.34

0.319

5.423

0.683

0.216

0.218

2.558

1.316

3.607

12.091

30.784

6.986

0.644

0.605

12.713

2.162

0.499

0.679

A

A

A

A

A

A

A

A

N

A

A

A

a Values are Bq/L, Bq/Kg, and Bq/filter.b Quality Assessment Program conducted by Department of Energy’s Environmental Measurements Laboratory (EML), New Yorkc Control limits were established by EMUQAP from historical data.


Page 4 of 5

Range

SRSIQAP Number of Mean of Lower Control Upper ControlNuclide SRS Valuea QAPb Value Ratio Labs Labs Limitc Limitc Evaluation

Soil

Ac-228

Bi-212

Bi-214

CS-137

K-40

Pb-212

Pb-214

Sr-90

TI-208

61.4tl.6

40.8 k 3.6

31.4tl.2

1090. * 20.

394. * 12,

51.3* 1.4

31.3* 1.4

50.4 & 19.2

19.3 * 0.9

52.6

58.3

28.8

954.

314.

52.8

29.1

39.63

18.3

Vegetation

Am-241 3.142 * 0.525 2.33

Cm-244 2.2 * 0.44 1.76

CO-60 23.9 * 0.7 20.

CS-137 460. &8.8 390.

K-40 563. + 16.6 460.

1.17

0.70

1.09

1.14

1.25

0.97

1.08

1.27

1.05

49

42

52

96

94

52

53

44

50

55,283

49.089

31.594

1028.412

349.796

55.81

32.039

43.434

26.37

.35 44 2.812

.25 26 1.85

.20 80 21.02

.18 83 423.93

.22 77 511.98

Pu-239 3.986 k 0.655 3.72 1.07 38 3.966

Sr-90 754.8 * 51.8 606. 1.25 43 576.912

26.3

29.15

14.4

791.82

244.92

26.4

14.55

23.778

9.15

1.584

0.774

13.8

312.

363.4

2.53

303.

a Values are Bq/L, Bq/Kg, and Bq/filter.b Quality Assessment Program conducted by Department of Energy’s Environmental Measurements Laboratory (EML), New Yorkc Control limits were established by EMIJQAP from historical data.

78.9

87.45

43.2

1259.28

480.42

79.2

43.65

145.046

27.45

6.291

2.851

29.2

546.

653.2

5.915

805.98

A

A

A

A

w

A

A

A

A

A

A

A

A

A

A

w

‘.

. i


Page 5 of 5

RangeSRSIQAP Numberof Mean of

Nuclide SRS ValueaLower Control Upper Control

QAPb Value Ratio Labs Labs Limitc Limitc Evaluation

Water

Alpha 809. * 118. 1080. 0.75 65 1014.12 658.8 1425.6 w

Am-241 1.69 * 0.083 1.25 1.35 58 1.314 0.938 1.863 w

Beta 1816. * 409. 1420. 1.28 70 1285.1 781. 2186.8 A

CO-60 50.6 * 0,9 49.4 1.02 99 51.327 39.52 59.28 A

Cs-137 51.*1.35 50. 1.02 99 52.55 40. 63. A

H-3 77.3 & 3.6 76.2 1.01 59 85.039 54.102 136.398 A

Mn-54 35.5 *1. 32.4 1.10 93 35.413 25.92 40.5 A

Pu-238 1.31 i- 0.073 1.1 1.19 51 1.154 0.858 1.375 w

Pu-239 1.88* 0.094 1.41 1.33 55 1.53 1.128 . 1.96 w

Sr-90 2.386 * 0.721 2.11 1.13 52 2.325 1.583 3.165 A

U-234 0.547 * 0.03 0.51 1.07 37 0.533 0.408 0.714 A

U-238 0.609 ~ 0.037 0.52 1.17 37 0.534 0.416 0.655 w

a Values are Bq/L, Bq/Kg, and Bq/filter.b Quality Assessment Program mnducted by Department of Energy’s Environmental Measurements Laboratory (EML), New Yorkc Control limits were established by EMUQAP from historical data,

(

Table 64QAD interlaboratory Comparison of Analytical Results

Page 1 of 2

Range

SRSIQAD Lower Control Upp~;l;fltrolSample Date Nuclide SRS Value QADa Value Ratio Limitb

. Evaluation

Note: A is “acceptable,” W is “acceptable with warning,” and N is “not acceptable.”

Water Samples (pCi/L)

01–16-98 Sr-90 28.3 ~ 3.5 32*5 0.88 23.3 40.7 A

01-30-98

01-30-98

03-13-98

04-21-98

04-21-98

04-21-98

04-21-98

04-21-98

04–21-98

04-21-98

06-05-98

06-05-98

06-05-98

06-05-98

06-05-98

07–17-98

Alpha

Beta

H-3

Alpha

u

Beta

Sr-90

CO-60

CS-134

CS-137

CO-60

Zn-65

CS-134

CS-137

Ba-133

Sr-89

16*8

4.9 k 3.5

1897*149

48.9 * 9.4

3.4 * 0.54

82.7 ~ 11.0

16.3 * 4.0

53*5

21*3

12*3

15*5

123*28

28&7

36& 10

42~10

28?5

30.5 & 7.6

3.9 * 5.0

2155 * 348

54.4 k 13.6

5.0 k 3.0

94.7 * 10.0

18.0 * 5.0

50*5

22*5

10*5

12*5

104*1O

31*5

35&5

40*5

21*5

0.52

1.26

0.88

0.90

0.68

0.87

0.91

1.06

0.95

1.20

1.25

1.18

0.90

1.03

1.05

1.33

17.3

-4.8

1553

30.9

-0.2

77.4

9.3

41.3

13.3

1.3

3.3

86.7

22.3

26.3

31.3

12.3

a EPA Quality Assurance Divisionb Control limits were established by EPA National Exposure Research Laboratov Characterization Research Division-Las Vegas.

43.7

12.6

2757

77,9

10.2

112.0

26.7

58.7

30.7

18.7

20.7

121.3

39.7

43.7

48.7

29.7

N

A

A

A

A

A

A

A

A

A

A

N

A

A

A

A

I

q’

Table 64QAD Interlaboratory Comparison of Analytical Results

Page 2 of 2

Range

SRSIQAD Lowflm~~trol Upp~~l;~trolSample Date Nuclide SRS Value QADa Value Ratio

. . . .Evaluation

U7-1 7-98

07-24-98

07-24–98

08-07-98

10-20-98

10-20-98

10-20-98

10-20-98

10-20-98

10-20-98

11-06-98

11-08-98

11-06-98

11-06-98

11-08-98

11-13-98

11-13-98

Sr-90

Alpha

Beta

H-3

u

Sr-89

Sr-90

CO-60

CS-134

CS-137

CO-60

Zn-65

CS-134

CS-137

Ba-133

Alpha

Beta

9.7 * 3.7

3.7 * 2.3

7.7 & 3.7

16967 * 240

15.8* 1.4

4*2

2.7 * 0.5

5.3 * 0.7 (21.3* 2.7)c

1.7 * 0.5 (6.7* 2.O)c

13.3 ~ 1.5 (53.3 ~ 6.0)C

42*8

152*3O

96*11

116*17

55*11

22,8 * 6.0

4.0 k 3.5

7*5

7.2 & 5

12.8*5

17996 * 1800

18.1 ~ 3.0

19.0 * 5.0

8.0 k 5.0

21.0 * 5.0

6.r) y 5.r3

50.0 * 5.0

38.0 ~ 5.0

131*13

105*5

111 *6

5(j&6

47.2 *11 .8

3.5 * 5

0.51

0.60

0.94

0.87

0.21

0.34

1.01

1.12

1.07

1.11

1.16

0.91

1.05

0.98

0.48

1.14

-1.5

4.1

14880

12.9

10.3

-0.7

12.3

-2.7

41.3

29.3

108.5

96.3

100.6

45.6

26.8

-5.2

a EPA Qualitv Asurance Divisionb Control Iimfis were established by EPA National Exposure Research Laboratory Characterization Research Division-Las Vegas.c The values in parentheses reflect corrections after a 4x dilution error in the EMS laborato~,

15.9

21.5

21112

23.3

27.7

~ 16.7

29.7

14.7

58.7

46.7

153.5

113.7

121.4

66.4

67.6

12.2

A

A

A

A

N

A

A

A

A

A

A

N

A

A

N

A

Quality Assurance

Table 65Quarterly QAIQC Standards

Page 1 of 2

Reported Known Performance Acceptance EvaluationParameter Units Value Value Limits (mgfL)

Note: A is “acceptable,” and N is “not acceptable.”

Quarter 3 (Shealy Environmental Services, Inc.)

Ammonia mglL

BOD mg/L

COD mg/L

Nitrate + Nitrite mg/L

TOC mg/L

TSS mg/L

Aluminum pg/L

Arsenic pglL

Barium pg/L

Cadmium pglL

Chromium J.lgiL

Copper pglL

Iron pglL

Lead pg/L

Manganese pglL

Mercury pg/L

Nickel pglL

Selenium pglL

Silver pg/L

Zinc pg/L

2.97

36.6

130

3.49

75

1

793

71

1860

47

151

1190

74

60

182

8

232

82

70

883

7.39

44.4

148

4.62

58.4

53.9

710

70.0

1850

45.0

150

1200

100

60.0

180

6.00

230

80.0

65.0

860

6.21-8.57

30.6 -53.5

126-170

4.11-5.13

49.6 – 67.2

45.8 – 61.9

609 – 824

56.0 -84.0

1570 – 2130

36.0 – 54.0

128–173

1080 – 1320

77.8-122

42.0 -78.0

153-207

4.20-7.80

196 – 265

64.0 – 96.0

55.9 -73.5

730 – 1030

N

A

A

N

N

N

A

A

A

A

A

A

N

A

A

N

A

A

A

A

Quarter 4 (Shesly Environmental Services, Inc.)

BOD

COD

Nitrate + Nitrite

TOC

TSS

Aluminum

Arsenic

Barium

Cadmium

Chromium

Copper

mg/L

mg/L

mg/L

mg/L

mg/L

pg/L

pgiL

pg/L

pgiL

J.lg/L

pg/L

24.7

78.7

2.265

14.6

16

794

64

1900

45

148

1130

24.2

80.6

4.62

31.2

24.6

710

70.0

1850

45.0

150

1200

16.2 -29.3

68.5 -92.7

4.11-5.13

26.5 -35.9

20.9 – 28.3

609-824

56.0 -84.0

1570 – 2130

36.0 – 54.0

128-173

1080 – 1320

A

A

N

N

N

A

A

A

A

A

A


Quality Assurance

Table 65Quarterly QA/QC Standards

Page 2 of 2

Reported Known Performance Acceptance EvaluationParameter Units Value Value Limits (m@L)

Iron pgiL 86 100 77.8-122 A

Lead pglL 60 60.0 42.0 – 78.0 A

Manganese pg/L 179 180 153 – 207 A

Mercury pg/L <0.0001 6.00 4.20 – 7.80 N

Nickel J.lg/L 229 230 196 – 265 A

Selenium J.lg/L 84 80.0 64.0 – 96.0 A

Silver ~g/L 65 65.0 55.9 -73.5 A

Zinc pglL 859 860 730-1030 A


Quality Assurance

Table 66NPDES Duplicate Sample Results

Page 1 of 4

DuplicateNPDES Site Parameter Sampled Units SRS Reading Reading Difference

Note: The Environmental Monitotfng Section laboratory performs most analyses for total suspended solids. Otheranalyses, including some total suspended solids, are performed by Shea/y Environmental Services.

X-6C 1,1 ,1–Trichloroethene uglL <2.0 d.o o

M-05

A–1A

X-8C

A–1A

K–18

M-04

M-04

X-6B

X-6B

X-6B

A-01

X-8B

A-1 1

X-6B

X-8B

A-01

A–11

H–16

H–16

H-1 6

M-04

H–16

X-6C

H–16

A-01

A–n

H-1 2

H–12

A-01

A–n

F-08

H-1 6


1,1,1–Trichloroethene



1,1,1-Trichloroethene

Aluminum

Aluminum

Ammonia

Benzene

Benzene

Benzene

BOD

BOD

BOD

BOD

BOD

BOD

BOD

Cadmium

Cadmium

Chromium

Chromium

Chromium

cis–1 ,2–Dichloroethene

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

ug/L

ug/L

ug/L

ug/L

mg/L

mg/L

mg/L

ug/L

uglL

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

<2.0

<2.0

<2.0

<2.0

0.177

0.305

17.8

<0.5

<0.5

<0.5

<2.0

<2.0

<2.0

<2.0

<2.0

<2.0

<2.0

<0.005

<0.002

<0.01

0.288

<0.005

<2.0

<0.005

<0.005

0.007

0.008

0.149

0.009

0.005

0.009

<0.005

4.0

42.0

4.0

-=2.0

0.227

0.284

16.9

<0.5

<0.5

<0.5

4.0

4.0

Q.o

+.0

4.0

4.0

4.0

<0.005

<0.002

<0.01

0.311

<0.005

4.0

<0.005

<0.005

<0.005

<0.005

0.121

0.008

0.005

0.009

<0.005

0

0

0

0

0.05

0.021

0.9

0

0

0

0

0

0

0

0

0

0

0

0

0

0.023

0

0

0

0

<0.007

<0.008

0.028

0.001

0

0

0

Quality Assurance


Page 2 of 4


M-04

M-04

M-04

M-04

A-01

H-1 6

A-01

A–11

H-1 2

M-04

H48

H-1 2

A-01

A-11

F-08

H-1 6

H-16

X-6B

A-01

A-n

A-01

X-8B

A-n

H-1 6

H-1 6

M-04

H-1 6

A-01

H-02

K-1 8

H-07

A-01

H-02

H-02

X-8B

Cyanide

Cyanide

Cyanide

Cyanide

Iron

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Nickel

Nickel

Nickel

Oil and Grease

011and Grease

Oil and Grease

Oil and Grease

Oil and Grease

Oil and Grease

Oil and Grease

Phenol

mg/L

mglL

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

<0.01

0.392

<0.01

<0.01

<0.02

<0.003

0.003

0.003

<0.003

<0.003

<0.003

0.01

<0.003

<0.003

<0.003

<0.003

<0.0001

0.0004

0.0001

<0.0001

<0.0001

0.0003

0.0001

<0.0001

<0.01

0.101

<0.01

<1.0

<1.0

<1.0

2.9

<1.0

<1.0

<1.0

<0.006

<0.01

0.388

<0.01

<0.01

0.029

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

0.009

<0.003

<0.003

<0.003

<0.003

<0.0001

0.0004

<0.0001

<0.0001

0.0001

0.0005

0.0001

<0.0001

<0.01

0.106

<0.01

<1.0

<1.0

<1.0

<1.0

<1.0

<1.0

<1.0

<0.006

0

0.004

0

0

<0.029

0

<0.003

<0.003

0

0

0

0.001

0

0

0

0

0

0

<0.0001

0

<0.0001

0.0002

0

0

0

0.005

0

0

0

0

4.9

0

0

0

0


Quality Assurance.


Page 3 of 4


Phenol

Phenol

Silver

Silver

Tetrachloroethene

Tetrachloroethene

Tetrachloroethene

Tetrachloroethene

Tetrachloroethene

TOC

TOC

TOC

Trichloroethene

Tnchloroethene

Trichloroethene

Trichloroethene

Trichloroethene

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

mg/L

mg/L

mg/L

mg/L

ug/L

ug/L

uglL

uglL

ug/L

mg/L

mg/L

mg/L

ugiL

ug/L

ug/L

ug/L

uglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

<0.006

0.016

<0.005

<0.005

4.0

4.0

<2.0

4.0

4.0

4.9

3.4

4.3

<2.0

<2.0

<2.0

<2.0

<2.0

1

3

1

7

1

7

2

24

6

59

3

2

7

<1

4

3

12

6

X-8B <0.006 0

X-8B

H–1 6

H–1 6

X-8C

M-05

A-1 A

X-8C

A–1.4

X-8B

X-8B

X-8B

X-8C

M-05

A–1A

X-8C

A–1A

X-04

S-04

H-02

K–18

H-04

X-8B

X-08

X-8B

H-07

A–11

S-04

X-04

H-08

F-01

3-04

M-04

H–12

F-02

0.024

<0.005

<0.005

Q.O

4.0

4.0

4.0

4.0

5

3.5

3.1

C2.o

4.0

C2.o

4.0

4.0

<1

2

1

7

2

1

2

14

6

49

4

2

7

<1

3

1

13

2

0.008

0

0

0

0

0

0

0

0.1

0.1

1.2

0

0

0

0

0

<1

1

0

0

1

6

0

10

0

10

1

0

0

0

1

2

1

4


Quality Assurance


Page 4 of 4


X-6B TSS mg/L 33 31 2

A-01

H-04

X-08

H-08

A-1 1

X-04

F-01

H-12

X-8C

H-1 6

S-04

S-04

A-01

H-1 6

TSS

TSS

TSS

TSS

TSS

TSS

TSS

TSS

Vinyl Chloride

Zinc

Zinc

Zinc

Zinc

Zinc

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

<1

1

1

2

23

2

<1

4

C2.o

0.054

0.166

0.166

0.021

0.042

<1

<1

1

2

25

1

<1

4

4.0

0.029

0.144

0.213

0.022

0.044

0

<1

0

0

2

1

0

0

0

0.025

0.022

0.047

0.001

0.002


I

Quality Assurance

Table 67NPDES Blind Sample Results

Page 1 of 4

NPDES Site Parameter Sampled Units Result 1 Result 2 Difference

Note: 7%eEnvironmental Monitoring Section laboratory performs most analyses for total suspended solids.Other analyses, including some total suspended solids, are performed by Shea/y Environmental Services.

1,1 ,1-Trichloroethane

1,1 ,1–Trichloroethane

Aluminum

Ammonia

Benzene

Benzene

Benzene

Biological Oxygen Demand







Cadmium

Cadmium

Cadmium

Chromium

Chromium

Chromium

Chromium



Copper

Copper

Copper

Copper

Copper

Copper

Copper

Cyanide

Cyanide

ug/L

ug/L

mg/L

mg/L

ug/L

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

ug/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

X-8C 1,1,1–Trichloroethane uglL <2.0 0

M-05

A–1A

M-04

M-04

X-8B

X-8B

X-8B

X-8B

A–n

X-8B

X-8B

A–n

A-01

H-1 6

H–1 6

H–1 6

H-1 6

H–1 6

H–1 6

M-04

H–16

M-05

A–1A

H–16

H-1 6

H-1 2

F-08

H–16

A–n

A-01

M-04

M-04

<2.0

<2.0

<2.0

0.143

17.8

<0.5

<0.5

<0.5

<2.0

<2.0

<2.0

<2.0

<2.0

<2.0

<2.0

<0.005

<0.005

<0.002

<0.01

<0.01

0.114

<0.005

<2.0

<2.0

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

0.013

<0.01

<0.01

<2.0

<2.0

0.116

12.7

<0.5

<0.5

<0.5

<2.0

<2.0

<2.0

<2.0

<2.0

<2.0

<2.0

<0.005

<0.005

<0.002

<0.01

<0.01

0.115

<0.005

<2.0

4.0

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

0.019

<0.01

<0.01

0

0

0.027

5.1

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0.001

0

0

0

0

0

0

0

0

0

0.006

0

0


-,./ ,.

Quality Assurance


Page 2 of 4


H-1 6

H-08

H-1 6

H-1 2

F-08

M-04

H-1 6

A-1 1

A-01

H-1 6

X-8B

H-1 6

X-8B

X-8B

F-08

H-1 6

A-n

A-01

H-1 6

H-1 6

M-04

H-1 6

F-05

A-01

F-05

A-01

F-05

H-02

X-8B

X-8B

X-8B

H–16

H-1 6

H-1 6

X-8C

M-05

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Nickel

Nickel

Nickel

Nickel

Oil and Grease

Oil and Grease

Oil and Grease

Oil and Grease

Oil and Grease

Oil and Grease

Phenol

Phenol

Phenol

Silver

Silver

Silver

Tetrachloroethene

Tetrachloroethene

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

uglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

uglL

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

0.006

<0.0001

0.0004

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.01

<0.01

0.422

<0.005

<1.0

3.9

<1.0

1.4

2.5

<1.0

<0.006

<0.006

<0.006

<0.005

<0.05

<0.010

C2.o

4.0

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.0001

0.0004

<0.0001

<0.0001

<0.0001

0.0004

<0.0001

<0.0001

<0.0001

<0.01

<0.01

0.428

<0.005

<1.0

3.1

<1.0

<1.0

<1.0

12

<0.006

<0.006

<0.006

<0.005

<0.05

<0.010

d.o

‘4?.0

o

0

0

0

0

0

0

0

<0.006

0

0

0

0

0

<0.0004

0

0

0

0

0

0.006

0

0

0.8

0

<1.4

C2.5

<12

0

0

0

0

0

0

0

0


Quahly Assurance


Page 3 of 4


Tetrachloroethene




Trichloroethene

Trichloroethene

Trichloroethene






























ug/L

mg/L

mg/L

mg/L

ug/L

ug/L

uglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

42.0

2.9

3.4

5.4

<2.0

4.0

<2.0

54

3

21

<1

2

2

1

7

2

4

6

12

3

3

14

3

<1

2

4

6

<1

<1

<1

<1

3

7

<1

1

3

A–1A o

X-6B

X-6B

X-8B

X-8C

M-05

A–1 A

F-01

A-01

A–n

F-02

F-05

F-08

H-04

H-07

H-02

H-08

X-04

X-08

S-04

M-04

X-8B

A–11

A-01

F-08

F-05

F-02

F41

H-02

H-04

H-1 2

H+8

H-07

S-04

X48

X-04

<2.0

3.1

3.6

3.5

<2.0

<2.0

4.0

58

3

20

<1

2

2

1

7

2

4

5

8

4

<1

15

3

<1

2

2

3

<1

<1

<1

<1

2

5

<1

1

3

0.2

0.2

1.9

0

0

0

4

0

1

0

0

0

0

0

0

0

1

4

1

<3

1

0

0

0

2

3

0

0

0

0

1

2

0

0

0


-—

Quality Assurance


Page 4 of 4

NPDESSite ParameterSampled Units Result1 Result2 Difference

M-04 Total Suspended Solids mg/L <1 <1 0

H-1 6 Total Suspended Solids mg/L 1 2 1

M-05 Vinyl Chloride ug/L 4.0 C2.o o

A-1 A Vinyl Chloride ug/L C2.o 42.0 0

H-1 6 Zinc mg/L 0.054 0.035 0.019

H-1 6 Zinc mg/L <0.005 0.016 <0.016

S-04 Zinc mgl 0.166 0.150 0.016

H-1 6 Zinc mg/L 0.042 0.042 0

S-04 Zinc mgl 0.183 0.175 0.008


.—

Quality Assurance

Table 68SRS Stream and Savannah River Water Quality Duplicate Sample Results

Page 1 of 14

SRS DuplicateLocation Parameter Sampled Units Reading Reading Difference

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

2,4-D

2,4-D

2,4-D

2,4-D

2,4-D

2,4–D

2,4-D

2,4-D

4,4’-DDD

4,4’-DDD

4,4’-DDD

4,4’-DDD

4,4’-DDD

4,4’-DDD

4,4’-DDD

4,4’-DDD

4,4-DDE

4,4-DDE

4,4–DDE

4,4–DDE

4,4–DDE

4,4’-DDE

4,4’-DDE

4,4-DDE

4,4’-DDT

4,4’-DDT

4,4’-DDT

4,4’-DDT

4,4’-DDT

4,4’-DDT

4,4’-DDT

4,4’-DDT

Aldrin

Aldrin

Aldrin

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

uglL

ug/L

uglL

ug/L

ug/L

uglL

ug/L

<1.00

<1.00

<0.10

<0.10

<0.10

<0.10

<0.10

<0.200

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<1.00

<1.00

<0.10

<0.10

<0.10

<0.10

<0.10

<0.200

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

00

0

0

0

0

0

0

0

0

00

0

0

0

0

0

0

0


_ .—.—.—..

Quality Assurance

—


Page 2 of 14


RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

RM-160

RM-140

L3R-2

RM-129

U3R-lA

RM–120

TC–1

VOGTLE

PB3

4M-2

RM-160

RM-140

BDC

4M–2B

RM-120

VOGTLE

U3R-4

RM-160

SC-4

4M-6

RM-140

VOGTLE

Aldrin

Aldrin

Aldrin

Aldrin

Aldrin

alpha-BHC

alpha-BHC

alpha-BHC

aIpha-BHC

alpha-BHC

alpha-BHC

alpha-BHC

alpha-BHC

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

Aluminum

‘Aluminum

beta-BHC

uglL

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

uglL

uglL

ug/L

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

uglL

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

0.289

0.186

0.197

0.089

<0.050

0.93

0.264

0.567

0.119

0.222

0.261

<0.050

0.287

0.087

1.44

2.05

0.648

1.04

0.235

0.234

0.321

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

0.263

0.159

0.184

“O.1O7

<0.050

0.815

0.234

0.351

0.05

0.255

<0.050

<0.050

<0.050

0.429

1.26

3.19

0.804

0.888

0.274

0.223

0.397

<0.05

0

0

0

0

0

0

0

0

0

00

0

0.026

0.027

0.013

0.018

0

0.115

0.03

0.216

0.069

-0.033

<0.261

0

=4!.87

0.342

0.18

1.14

0.156

0.152

0.039

0.011

0.076

0

Quality Assurance


Page 3 of 14


beta-BHC

beta-BHC

beta-BHC

beta-BHC

beta-BHC

beta-BHC

beta-BHC

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Cadmium

Chlordane

Chlordane

Chlordane

Chlordane

Chlordane

Chlordane

Chlordane

uglL

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

RM-160

RM-140

L3R–2

RM-129

U3R-1 A

RM-120

TC–1

VOGTLE

PB-3

4M–2

RM-160

RM-140

BDC

4M–2B

RM-120

VOGTLE

U3R4

RM-160

SC-4

4M-6

RM-140

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.002

<0.002

<0.002

<0.002

<0.002

<0.002

<0.002

<0.005

CO.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.50

<0.60

<0.50

<0.50

<0.50

<0.50

<0.50

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.002

<0.002

<0.002

<0.002

<0.002

<0.002

<0.002

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.50

<0.60

<0.50

<0.50

<0.50

<0.50

<0.50

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0


Quality Assurance


Page 4 of 14


RM-160

RM-140

L3R-2

RM-129

U3R-lA

RM-120

TC-1

VOGTLE

PB-3

4M-2

RM-160

RM-140

BDC

4M-2B

RM-120

VOGTLE

U3R-4

RM-160

SC-4

4M-6

Rtvl-140

RM-160

RM-140

L3R-2

RM-129

U3R-lA

RM-120

TC-1

VOGTLE

PB-3

4M-2

RM-160

RM-140

BDC

Chlordane

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Chromium

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

<0.005

<0.005

<0.005

0.011

<0.005

<0.005

<0.005

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.005

<0.005

0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.50

<0.005

<0.005

<0.005

<0.005

0.005

<0.005

<0.005

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.005

<0.005

0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

<0.005

0

0

0

0

<0.011

<0.005

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0


Quality Assurance


Page 5 of 14


Copper

Copper

Copper

Copper

Copper

Copper

Copper

Copper

delta-BHC

delta-BHC

delta-BHC

delta-BHC

delta-BHC

delta-BHC

delta-BHC

delta-BHC

Endosulfan I

Endosulfan I

Endosulfan I

Endosulfan I

Endosulfan I

Endosulfan I

Endosulfan I

Endosulfan I

Endosulfan sulfate

Endosulfan sulfate

Endosulfan sulfate

Endosulfan sulfate

Endosulfan sulfate

Endosulfan sulfate

Endosulfan sulfate

Endosulfan sulfate

Endrin

Endrin

Endrin

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

uglL

ug/L

uglL

uglL

ug/L

<0.005

<0.005

<0.005

<0.005

0.031

<0.005

<0.005

<0.005

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

4M–2B <0.005 0

RM-120

VOGTLE

U3R4

RM-160

SC-4

4M-6

RM-140

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

<0.005

<0.005

<0.005

0.026

<0.005

<0.005

<0.005

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

0

0

0

0.005

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0


Quality Assurance


Page6 of 14


RM–129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM–140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

Endrin

Endrin

Endrin

Endrin

Endrin

Endrin aldehyde

Endrin aldehyde

Endrin aldehyde

Endrin aldehyde

Endrin aldehyde

Endrin aldehyde

Endrin aldehyde

Endrin aldehyde

Endrin ketone

Endrin ketone

Endrin ketone

Endrin ketone

Endrin ketone

Endrin ketone

Endrin ketone

Endrin ketone

Enfosulfan II

Enfosulfan II

Enfosulfan II

Enfosulfan II

Enfosulfan II

Enfosulfan II

Enfosulfan II

Enfosulfan II

gamma-BHC (Lfndane)

gamma-BHC (Lfndane)

gamma-BHC (Lindane)

gamma-BHC (Lindane)

gamma-BHC (Lfndane)

gamma-BHC (Lindane)

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

uglL

uglL

uglL

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

uglL

uglL

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0


..\.,AIz&A-: .

Quality Assurance


Page 7 of 14


gamma-BHC (Lindane)

gamma-BHC (Lindane)

Heptachlor

Heptachlor

Heptachlor

Heptachlor

Heptachlor

Heptachlor

Heptachlor

Heptachlor

Heptachlor epoxide

Heptachlor epoxide

Heptachlor epoxide

Heptachlor epoxide

Heptachlor epoxide

Heptachlor epoxide

Heptachlor epoxide

Heptachlor epoxide

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Iron

Ugll-

ug/L

ug/L

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ugiL

uglL

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mgJL

mg/L

mg/L

mg/L

mg/L

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

Rtd-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

RM-160

RM-140

L3R–2

RM-129

U3R-lA

RM-120

TG1

VOGTLE

PB-3

4M–2

RM-160

RM-140

BDC

4M-2B

RM-120

VOGTLE

U3R4

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

0.209

0.394

0.472

0.936

0.324

0.897

0.399

0.659

0.773

2.13

0.29

0.615

0.512

2.11

1.78

2.35

0.763

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

0.187

0.332

0.462

1.16

0.341

0.802

0.888

0.571

0.683

2.01

0.283

0.652

0.641

2.06

1.74

3.1

0.831

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0.022

0.062

0.00999999

0.224

0.017

0.095

0.489

0.088

0.09

0.12

0.007

0.037

0.129

0.04999999

0.04

0.75

0.068


. . .. . ..

Qualify Assurance


Page 8 of 14


RM-160

SC-4

4M-6

RM-140

RM-160

RM-140

L3R-2

RM-129

U3R-lA

RM-120

TC-1

VOGTLE

PB-3

4M-2

RM-160

RM-140

BDC

4M-2B

RM-120

VOGTLE

U3R-4

RM-160

SC-4

4M-6

RM-140

RM-160

RM-140

L3R-2

RM-129

U3R-lA

RM-120

TC-1

VOGTLE

PB-3

4M–2

Iron

Iron

Iron

Iron

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Lead

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

1.11

0.367

0.788

1.15

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

0.01

<0.003

<0.003

<0.003

0.014

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

0.071

0.094

0.053

0.095

0.011

0.089 “

0.022

0.085

0.102

0.325

0.34

0.684

1.79

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

<0.003

0.068

0.078

0.052

0.091

0.012

0.088

0.053

0.068

0.093

0.306

0.04

0.027

0.104

0.64

0

0

0

0

0

0

0

0

0

<0.01

0

0

0

<0.014

0

0

0

0

0

0

0

0.00299999

0.016

0.001

0.004

0.001

0.001

0.031

0.017

0.00899999

0.019


Quality Assurance


Page 9 of 14


RM-140

BDC

4M–2B

RM-120

VOGTLE

U3R-4

RM-160

SW

4M-6

RM-140

RM-160

RM-140

L3R–2

RM-129

U3R–1A

RM-120

TC–1

VOGTLE

PB-3

4M–2

RM-160

RM-140

BDC

4M–2B

RM-120

VOGTLE

U3R+

RM-160

SC-4

4M-6

RM-140

VOGTLE

PB-3

RM-120

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Manganese

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Mercury

Methoxychlor

Methoxychlor

Methoxychlor

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

ug/L

uglL

ug/L

0.078

0.082

0.08

0.067

0.073

0.036

0.075

<0.005

0.07

0.069

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

0.0003

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

0.0003

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.20

<0.24

<0.20

0.064

0.076

0.147

0.078

0.066

0.078

0.036

0.076

0.033

0.06

0.073

<0.0001

<0.0001

<0.0001

0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

0.0003

0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.0001

<0.20

<0.24

<0.20

0.00699999

0.002

0.065

0.002

0.001

0.005

0

0.001

<0.033

0.01

0.004

0

0

0

<0.0001

0

0

<0.0003

0

0

0

0

0

0

0

<0.0001

0

0

“o

o

0

0

0

0

0

WSRC-TR-98-O0314242 SRS Environmental Data for 1998

––-~

Quality Assurance


Page 10 of 14


RM-129

RM-140

VOGTLE

RM-160

VOGTLE

RM-160

RM-140

L3R-2

RM–129

U3R-lA

RM-120

TC-1

VOGTLE

PB-3

4M–2

RM-160

RM-140

BDC

4M-2B

RM-120

VOGTLE

U3R-4

RM-160

SC-4

4M-6

RM-140

VOGTLE

PB-3

R,M-l 20

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

Methoxychlor

Methoxychlor

Methoxychlor

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

Nickel

PCB 1016

PCB 1016

PCB 1016

PCB 1016

PCB 1016

PCB 1016

PCB 1016

PCB 1016

PCB 1221

uglL <0.20

uglL

ug/L

ug/L

uglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L ,

mg/L

mg/L

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

uglL

.<0.20

<0.20

<0.20

<0.20

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

0.041

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.20

<0.20

<0.20

<0.20

<0.20

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.010

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

<0.041

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0


Quality Assurance


Page 11 of 14


PB-3 o

RM–120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

PCB 1221

PCB 1221

PCB 1221

PCB 1221

PCB 1221

PCB 1221

PCB 1221

PCB 1232

PCB 1232

PCB 1232

PCB 1232

PCB 1232

PCB 1232

PCB 1232

PCB 1232

PCB 1242

PCB 1242

PCB 1242

PCB 1242

PCB 1242

PCB 1242

PCB 1242

PCB 1242

PCB 1248

PCB 1248

PCB 1248

PCB 1248

PCB 1248

PCB 1248

PCB 1248

PCB 1248

PCB 1254

PCB 1254

PCB 1254

PCB 1254

ug/L

uglL

uglL

ug/L

ug/L

ug/L

ug/L

uglL

uglL

ug/L

ug/L

ug/L

uglL

ug/L

uglL

ug/L

uglL

ug/L

ug/L

ugiL

uglL

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

uglL

uglL

ug/L

ug/L

ug/L

ug/L

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0

0


Quality Assurance


Page 12 of 14


RM-140

VOGTLE

RM-160

VOGTLE

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

RM-160

RM-140

L3R-2

RM-129

U3R-1 A

RM-120

TC-1

VOGTLE

PB-3

4M-2

RM-160

RM-140

BDC

4M-2B

RM-120

VOGTLE

U3R-4

RM-160

SC-4

4M-6

RM-140

VOGTLE

PB-3

PCB 1254

PCB 1254

PCB 1254

PCB 1260

PCB 1260

PCB 1260

PCB 1260

PCB 1260

PCB 1260

PCB 1260

PCB 1260

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Phosphorus

Silvex (2,4,GTP)

Silvex (2,4,5-TP)

ug/L

ug/L

uglL

ug/L

ug/L

uglL

ug/L

ug/L

ug/L

uglL

uglL

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

reg./L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

uglL

ug/L

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.010

0.227

0.037

0.353

<0.010

1.47

0.045

0.116

0.034

<0.010

0.095

0.205

0.08

0.112

0.079

0.244

0.12

<0.010

<0.010

0.081

0.044

<1.00

<1.00

<0.05

<0.05

<0.05

<0.05

<0.05

<0.06

<0.05

<0.05

<0.05

<0.05

<0.05

<0.05

<0.010

0.221

1.11

<0.010

<0.010

0.341

<0.010

0.131

0.236

<0.010

0.127

0.17

0.096

0.065

0.083

0.188

0.116

0.034

0.108

0.116

0.052

<1.00

<1.00

0

0

0

0

0

0

0

0

0

0

0

0

0.006

1.073

<0.353

0

1.129

<0.045

0.015

0.202

0

0.032

0.035

0.016

0.047

0.004

0.056

0.00399999

<0.034

<0.108

0.035

0.008

0

0


Quality Assurance


Page 130f 14


Silvex (2,4,5-TP)

Silvex (2,4,5-TP)

Silvex (2,4,5-TP)

Silvex (2,4,5-TP)

Silvex (2,4,5-TP)

Silvex (2,4,5-TP)






















Toxaphene

Toxaphene

Toxaphene

Toxaphene

Toxaphene

Toxaphene

Toxaphene

Toxaphene

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

ug/L

RM-120

RM-129

RM-140

VOGTLE

RM-160

VOGTLE

RM-160

RM-140

L3R–2

RM-129

U3R–lA

RM-120

TC–1

VOGTLE

PB-3

4M–2

RM-160

RM-140

BDC

4M–2B

RM-120

VOGTLE

U3R4

RM-160

W-4

4M-6

RM-140

VOGTLE

PB-3

RM-120

RM-129

RM-140

VOGTLE

RM–160

VOGTLE

<0.10

<0.10

<0.10

<0.10

<0.10

<0.200

3.2

3.6

4.7

2.8

2.1

3.3

5.2

3.5

4.1

3.1

3.3

3.3

3.4

7.6

5.6

6.5

14

3.6

6.8

3.61

4.02

‘4?.50

<3.00

<2.50

4.50

‘4.50

4.50

4.50

4.50

<0.10

<0.10

<0.10

<0.10

<0.10

<0.200

3.4

3.4

4.6

2.6

1.7

3.5

3.9

3.9

4

3.3

3.3

3

3.2

7.8

6.4

6.7

12

4.7

6.8

3.96

3.97

4.50

<3.00

<2.50

<2.50

<2.50

4.50

<2.50

<2.50

0

0

0

0

0

0

0.2

0.2

0.1

0.2

0.4

0.2

1.3

0.4

0.09999999

0.2

0

0.3

0.2

0.2

0.8

0.2

2

1.1

0

0.35

0.04999999

0

0

0

0

0

0

0

0


—.

Quality Assurance


Page 14 of 14


0.010 0.002RM-160

RM–140

L3R–2

RM-129

U3R-1 A

RM-120

TC-1

VOGTLE

PB-3

4M–2

RM-160

RM-140

BDC

4M-2B

RM-120

VOGTLE

U3R-4

RM-160

SC-4

4M-6

RM-140

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

Zinc

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mg/L

mglL

mg/L

mg/L

mg/L

mg/L

mg/L

0.008

0.009

0.01

<0.005

0.008

0.014

0.005

<0.005

0.007

0.037

0.021

0.012

0.067

0.027

0.008

0.022

0.011

<0.005

0.010

0.026

0.023

0.008

0.028

0.029

<0.005

0.018

0.006

<0.005

0.006

0.043

0.017

<0.005

<0.005

0.028

0.023

0.028

0.011

<0.005

0.009

0.029

0.024

0.00099999

0.018

<0.029

<0.008

0.004

0.001

0

0.001

0.006

0.004

<0.012

<0.067

0.001

0.015

0.006

0

0

0.001

0.003

0.001


.-

Errata from 1997 Environmental Data

The following information was reported incorrectly in Savannah River Site Environmental Data for 1997(WSRC-TR-97-00324):

Page 6, table 2, ‘Representative Minimum Detectable Concentrations for Radiological AnalyseN: The“Stream Water” column on the second page of the table appeared in duplicate.


Documents

i · procedures, can be found in sections 1101-1111(SRS EM Program) of the Savannah River Site Environmental Monitoring Section Plans and Procedures, WSRC–3Q1–2, Volume 1. Because