ML19093A177
| ML19093A177 | |
| Person / Time | |
|---|---|
| Site: | Surry  |
| Issue date: | 02/28/1982 |
| From: | Kohl K, Liu C Eberline Instrument Corp |
| To: | Office of Nuclear Reactor Regulation, Virginia Electric & Power Co (VEPCO) |
| References | |
| Download: ML19093A177 (75) | |
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(RErs M'ASTER F1LE]
(lN~-8D I ,. VIRGINlA ELECTRIC.POWER
. - COl\1PANY Surry .Po..\1er. Station RADIOLOGICAL ENVIRONMENTAL MONITORING Annual Report 1981 J-
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Submitted _by EBERLINE INSTRUMENT CORPORA T!ON Midwest Facility West Chicagci, ll!ino:s
.."SURRY POWER STATION OPERATIONAL.ENVIRONMENTAL RADIOLOGICAL*SURVEILLANCE PROGRAM Annual Report JANUARY 1 - DECEMBER 31, 1981
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Prepared for VIRGINIA ELECTRIC POWER COMPANY By EBERLINE INSTRUMENT CORPORATION NUCLEAR SERVICES DIVISION - MIDWEST FACILITIES 245 WEST ROOSEVELT ROAD BLDG. 2, SUITE 9 WEST CHICAGO, IL 60185 as a contractor to VIRGINIA ELECTRIC POWER COMPANY February 1982.
Compil~~~by:
- Written, Reviewed and Approved by:
Chung-King Liu, _PhD, Y4nager
TABLE OF CONTENTS Page No.
SECTION 1 - Preface 1
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SECTION 2 - Sampling Program 5 SECTION 3 - Analysis Program 10 SECTION "4 - Results and Discussion 23 SECTION 5 - Data Tables 38 SECTION 6 - Quality Assurance Data 65 I
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SECTION I PREFACE I
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ABSTRACT This report presents the data obtained from the analyses of environmental samples collected through the Virginia Electric Power Company Surry Station Environmental Radiological Surveillance Program for the period 01 January 1981 through 31 December 198l.
The_ activity present above detection limits in the routinely collected sample media was observed to be of natural and atmospheric fallout origin. The results show that the radiation dose to a member of the general population did not exceed the technical specifications of 17. of the 10 CFR 20 limit during 1981.
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INTRODUCTION *
- The Surry Power Station of Virginia Electric and Power Company consists of *two Westinghouse pressurized water reactors each with a generating capacity of 788 MWE. The station is located on a peninsula in the James River approxi-mately 25 miles upstream of the Chesapeake Bay. Cooling water is taken in down-stream of the site and discharged 5.7 miles upstream of the intake. The Surry Power Station has been designed to minimize radioactive releases and insure that radiation doses attributed to the operation of the station will be "as low as reasonably achievable".
- Various environmental samples are collected at indicator and control or bacl!}ground locations and analyzed to determine if changes in radioactivity levels may be attributable to the operation of the station. This environmental radio-logical monitoring program provides surveillance to assure compliance with the NRC Regulations and the Surry Power Station Technical Specifications.
The program outlined in Tables 1 and 2 has in some cases more frequent collection and analysis of certain samples than called for in the Technical Specif lea tlons. The accompanying map shows the plant environs. '£able 4 surnrnar-izes the results of the radiological environmental surveillance measurements during calendar year 1981.
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SUMMARY
1981 Environmental monitoring results showed that the radiation dose to a member of the general population did not exceed Technical Specifications of 1% of the 10 CFR 20 limit during 1981.
Radionuclides released to the air and water from Surry Station may con-tribute to the radiation background through both external and internal ex-posure.
The most significant envirorunental dose pathways are direct dose from the gaseous effluent and thyroid dose due to ingestion of milk. The area contains only a very small milk shed which limits general population dose potential from this source and since James River water is not used for drinkinll, dose potential from this source is also minimal.
Table 4 summarizes the range and average concentrations for measurements at the indicator and control locations, and the location with the highest annual mean. Complete information is given in the Sample Data Tables.
(Appendix I)
Specific findings for various environmental media are discussed in Section 4.
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SECTION 2 SAMPLING PROGRAM
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All .samples are collected by VEPCO Environmental Services Personnel and shipped to the Eberline laboratory in West Chicago, Illinois.
Upon receipt of the samples, the laboratory staff enters the samples in a log book identifying them as to sample type, collection date, and sample code number or location, then verifies the ~pecific analyses to be performed on each sample. The samples are then stored, awaiting analysis, on shelves expressly for this purpose to assure accountability through the laboratory processes.
Table 1 lists the sampling locations and frequencies. Figure 1 shows the locations of the various sampling environs.
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TABLE 1 r,
Monitoring or Sampling Locations and Frequencies Air Ambient Well Surface Particulate Radiation Precipitation* Milk Water Water Soil Surry Station w (a) M *sA A Hog Island Reserve w SA Bacon's Castle w M(2 ea.) .SA A Chippokes Creek SA*
Alliance w A Colonia~ Parkway w M A Williamsburg SA Jamestown SA Dow w A Fort Eustis w A Newport News w M SA Scotland Wharf Lee Hall M Routes 10 and 676 Smithfield M SA Guard Booth Station Intake Kings Mill Budweiser Station Discharge BW - Bi-weekly M - Mo*nthly BM - Bi-monthly Q - Quarterly SA - Semi-annually A - Annually A(3) - Annually corn, peanuts, and soybeans SM - Summer Months (two Samplings: July - September)
(a) Thermoluminescent dosimeters (TLDs) are monitored quarterly. A full listing of the 43 locations is shown on page 47.
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~ ' . i, James River Crops Fowl Water Silt Oyster Clams Fish Crab Bacon Is Castle A(3)
Hog Island Reserve SA Jamestown Newport News BM BM SA BM Chickahominy BM SA Station Discharge BM BM SA BM Hog Island Point BM SA Station Intake BM BM SA SA SM Lm,>nes
- Creek Deep Water Shoals BM Point of Shoals BM SA BM BW Bi-weekly M Monthly BM - Bi-monthly Q Quarterly SA-Semi-annually A - Annually A(3) - Annually corn, peanuts, and soybeans SM - Summer Months (three Samplings: July - August - September)
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CHARLES CITY COUNTY A SURRY STATION B HOG ISLAND C CHIPPOKES STATE PARK D BACONS CASTLE*
E TOWN OF SUAAY F HERON ROOKERY G FERRY (SCOTLAND GI-JAMESTOWN G2)
H JAMESTOWN ISLAND .
I WILLIAMSBURG J OUSCH GARDENS K YORKTOWN BATTLEFIELD L COLONIAL PARKWAY 0 5 M FORT EUSTIS , MILEAGE N JAMES RIVER BRIDGE p* TUNNEL
~ COOHAM BAY Figure 1:- Environs of Surry Power Station.
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SECTION 3 ANALYSIS PROGRAM
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Table 2 lists the sample analysis program - sample class, frequency, and the type of analysis required.
Table 3 lists the LLD's (Lower Limits of Detection) for the analytical program. These LLD's are based on Regulatory Guide 4.8. For analyses not required in Regulatory Guide 4.8, Federal EPA, former re-quirements for similar programs, or other appropriate guides are used.
The LLD's are calculated as per RG 4.8 at the 3cr level.
The Guide specifically states that the LLD's are a priori NOT a posteriori (after the fact) limit for a particular measurement. When, however, RG 4.8 or other LLD's have not been achieved, a footnote giving a brief explanation has been inserted.
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TABLE 2
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Environmental Measurement and .
Sample Analysis Program Sample Class Frequency Analysis Air Particulate Weekly Gross alpha and beta (1)
Quarterly Comp. Gamma Isotopic (2)
Airborne Iodine Weekly Iodine-131 Thermoluminiscent Quarterly Radiation Dose Dosimetry (TLD)
Precipitation Monthly Gross beta (3)
Tritium Quarterly Comp. Gross beta Tritium Milk Monthly Iodine-131 Sr-89/90 Gamma Isotopic Stable Calcium t
Soil Annually Gamma Isotopic Crops Annually Gamma Isotopic Sr-89/90 Surface Water Semi-annually Gross alpha and beta Tritium Well Water Semi-annually Gross alpha and beta Tritium Fowl Semi-annually Gamma Isotopic (4)
James River Water Bi-monthly Gamma Isotopic Semi-annual Tritium Comp.*
Oysters and Clams Bi-monthly Gamma Isotopic (4)
Crabs 3 summer months Gamma Isotopic Silt Semi-annually Gamma Isotopic Fish Semi-annually Gamma Isotopic 12
NOTES TO TABLE 2 (1) Gamma isotopic analysis if gross beta exceeds 10 pCi/~ 3 *
(2) Quarterly composites of weekly air particulate samples will be analyzed for ganuna emitters in three groups as follows:
Stations SS and HIR analyzed as one sample.
Stations BC, ALL, CP, DOW, and FE analyzed as one sample.
Station NN analyzed as one sample.
Strontium-90 determined radiochemically if significant amounts of fission products attributable to the Station are detected by the ganuna isotopic analysis.
(3) Perform gamma isotopic analysis if gross beta exceeds 15 nCi/m2.
(4) Entire sample analyzed for gamma emitters. Sr-90 to be determined if a significant amount of fission products attributable to the Station are noted in the ganuna analysis.
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Table 3 Lower Limits of Detection (LLD' s) .
LLD Sample Class Analysis 3cr Units Airborne Gross Beta 0.01 pCi/m3 Particulates Gross Alpha 0.01 pCi/m3 Gamma Isotopic 0.01 pCi/m3 Iodine-131 0.07 pCi/m 3 Background Gamma dose 0.5 mR/wk Radiation (TLD)
Precipitation Gross Beta 5 nCi/m2 LS Tritium 500 pCi/1 Enriched Tritium 330 pCi/1 Other Waters Gross Beta 2 pCi/1
,Gross Alpha 1 pCi/1 LS Tritium 500 pCi/1 Enriched Tritium 330 pCi/1 f
i Gamma Isotopic Cs-134/137 15 pCi/1 La/Ba-140 15 pCi/1 Co-58/60 15 pCi/1 Mn-54 15 pCi/1 Zr/Nb-95 10 pCi/1 Fe-59, Zn-65 30 pCi/1 Strontium-89 5 pCi/1 Strontium-90 2 pCi/1 Milk Iodine-131 1 pCi"/1 Strontiurn-89 5 pCi/1 Strontium-90 2 pCi/1 Cs-137 15 pCi/1 La/Ba-140 15 pCi/1 Oysters, Clams,_ Cs-134/137 130 pCi/kg wet Crabs, Fish Mn-54 130 pCi/kg wet Co-58/60 130 pCi/kg wet Fe-59, Zn-65 260 pCi/kg wet Strontium-89 20 pCi/kg wet Strontium-90 10 --- pCi/kg wet Silt, Soil Cs-134/137 150 pCi/kg dry Fowl cs..:..134/137 80 pCi/kg wet Vegetation Cs-134/137 80 pCi/kg wet Strontium-89 20 pCi/kg wet Strontiurn-90 10 pCi/kg wet 14
ANALYTICAL PROCEDURES Samples received at the laboratory are analyzed for the various radio-active components by standard radiochemical methods. These methods are equal (1) to, and in most cases; identical with, those of the U.S.D.O.E. or those of (2) the Federal E.P.A.
Brief descriptions of analytical procedures are available in the Labor-atory Procedures Manual available at Surry Station and the radioanalytical contractor's laboratory.
Air Particulate Filters Gross Beta - Exposed air particulate filters are counted in low back-ground Geiger or proportional flow beta counters using anti-coincidence background suppression after the short-lived naturally-cccuring radon and thoron daughters have decayed. Filters are counted long enough to ensure that the required sensitivity (LLD) will be met Gamma Isotopic - Quarterly composites of air particulate filters are counted in high resolution (GeLi) gamma spectrometers for periods of time long enough to ensure that the required program sensitivity (LLD) is met. (See also introduction to data tables, Section 5.)-
Water Samples (Includes Surface, Well, Precipitation, James River)
Gross Beta - A measured aliquot of sample is digested, "wet-ashed'!,
evaporated, transferred to a tared 47mm stainless steel planchet, dried, and weighed. The planchetted sample is counted long enough in a low background beta counter to ensure that the LLD of the program will be met.
(1) HASL Procedures Manual, edited by John H. Harley, Health and Safety
-Laboratory,- US Atomic Energy _Commission, 1972 edition, revised annually.
(2) National Environmental Research Center, Environmental Protection Agency; Handbook of Radiochemical Analytical Methods. Program Element !HA 325.
Office of Research and Development, Las Vegas, Nevada 89114.
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Gamma Isotopic - a measured aliquot of the sampl small controlled volume and counted in a standard geometry in a big resolution (Geli) gamma spectrometer long enoun the sensitivity requirements of the program. See to Data Tables.
Strontium-89 and Strontium carrier strontium aliquot of sample. The strontium is then separated
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.;ii at two points during ingrowth of the Sr-90 daughter Y-90. While either :f-:
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method is acceptable, we find the former method to provide more consistent it/ ..
- - tritium as tritiated water is analyzed liquid scintillation by coun_ttng after distillation. If high sensitivity is not required (ie.
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required (ie. ("-300 pCi/1) the sample is isotopically enriched tritiu<' :ir\;;.
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Isotopic enrichment is done by the classical method of Ostlund which involves alkaline electrolysis of a purified aliquot of sample under, controlled conditions of temperature and electrode current density.
Milk Samples I-131 - measur.ed amounts .. of carrier. iodide are added to *a known volume of milk and the iodine extracted on anion exchange resin. The iodine is recovered and nurified by classical iodine chemistry methods which are similar to those given in former Regulatory Guide 4.3. The yield or recovery of iodine is measured gravimetrically and the precipitated sample is mounted and counted in a low level beta detector for a long enough period to ensure that the required LLD is met.
Gamma Isotopic - a measured aliquot of sample is evaporated and oven
} dried to a standard volume and counted in a fixed geometry in a high resolution (GeLi) gamma spectrometer for a long enough period to ensure that the required LLD's are reached (see also Introduction to data Tables).
Sr-89 and Sr Stable strontium carrier is added to an aliquot of the sample which is then dried and ashed at high temperature (>700°c). The ash is dissolved and the solution treated from this point on in the same manner as are water samples (Q.v.).
Organic Samples (including Clams, Oysters, Fish, Crabs, Food Crops and Fowl).
Gamma Isotopic Analysis - a measured aliquot of sample is oven dried or ashed as appropriate, placed in a controlled geometry and counted in a high r*esolution (Ge Li) gamma spec tromc ter for a period long enough to ensure that the LLD's of the program will be met (see also intro. to Data Tables).
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In the case of samples such as fish and fowl, the edible flesh is sepa-ff. :
rated from bones and entrails prior to drying.
Sr-89 and Sr stable strontium carrier is added to a weighed ~liquot
... of. the- sample and the -sample is ashed -at high temperature (~7-_00°c). *The
... ashed sample is .then dissolved-and processed- in the same manner as are water or milk samples.
Soil and Silt Samples Gamma Isotopic Analysis - the sample is oven dried to facilitate .handling and then sieved to remove pieces of stone and/or other large pieces of material. An appropriate sized, weighed aliquot of the sample is then transferred into a standard geometry container and counted for a period long enough to ensure that the LLD of the program will be met. (See also Introduction to Data Tables).
Thermoluminescent Dosimeters (TLD)
Environmental radiation doses are measured using badges comprizing five ,
chips sealed in plastic protective holders having a density of 50 mg/cm 2
- The TLD chips are l/8 11 x 1/8" x 1/32 LiF (thallium activated) known commercially as Harshaw-100. The chips are all selected to provide uniform response to-with-in 5% of the mean for the batch.
Prior.to installation, the chips are annealed by a standard cycle of 60 minutes at 400°c and immediate cooling to ambient temperature by placing the tray containing the annealed chips on an aluminum block 12" x 12" x l".
After exposure the chips are read on an Eberline Instrument Corporation Model TLR-6 reader. The system employs a preheat cycle which removes low temperature peaks and integrates and digitizes only the light output in a sel~cted temperature range.
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rne dose is calculated from the average light output for the five chips and statistical uncertainty is the standard deviation of the five readings.
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QUALITY ASSURANCE PROGRAM A. Design of Plan Quality of product or service has always been a primary key to in-crease is sales, customer satisfaction, and profit. The management of Eberline Instrument Corporation recognizes the ever increasing demand for higher quality and reliability for services related to protection of workers and the environment. It is our firm belief that in order to judge the worth of a supp_ort service, one must know the philosophy behind it. Eber-line will provide only those services for which it is qualified ' and these will be provided in a manner that is reliable, with a quality assurance program that maintains a high degre~ of client confidence. This quality assurance program has been prepared consistent with the following specifications, per the Te~hnical and Quality Assurance Requirements for Special Pur~oses.
ANSI-N45.2, American National Standards Institute NRC Branch Technical Position of November 1979 NRG Regulatory Guide 4.15, Revision 1 of February 1979.
H. lntercomparison Program Results of Eberline's Midwestern Facility participation in the USEPA's Crosscl1cck Program will be included in the monthly reports provided to the client. Other intercomparisons in which we routinely participate include:
Environmental Protection Agency Environmental Measurement Lab DOE Quality Assessment Program Battelle Northwest Laboratories IAEA Analytical Qu:11ity Control Service US National Bureau of Standards Eberline's Albuquerque Laboratory.
Each of the laboratory managers is.responsible for preparing soikes and blanks to be run .routinely. Every.tenth.sample is a spike, a blank, on a split sample.
Regular QC reports*are prepared by the laborary manager on a monthly 20
schedule and forwarded to eac~ client. Each report routinely includes:
results from EIC interlaboratory comparison, resu!ts from EPA Crosscheck program, and results from other intercomparison programs.
Results are reviewed by the laboratory manager. If a problem is in-dic:Sted by the data,- the,nature of the problem is investigated and corrective steps taken immediately. A copy of each report is also provided to the Quality Assurance Manager of the Nuclear Services Division.
C. Quality Assurance Plan The Quality Assurance Program follows the requirments of Company and Division Manuals. The discussion below outlines Quality Assurance !~rograIT1s as conducted in the laboratory and as required in our QA Manual.
Procedure Approval Each procedure goes through a vigorous evaluation and review process bc(~re it is incorporated into the EIC Procedures Manual. Established pro-cedures of the Environmental Protection Agency (EPA) or the Environmental
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Measurements Laboratory of the US Department of Energy (EML) are used unless t~orough testing has demonstrated that an alternate procedure is equal to or better than the EPA or EML procedure. Uniform procedure*s are used at both laboratories to the fullest extent possible, except when deviatipns are nccl!ssary to meet the specific requirements of the client. The maniger of each laboratory and the quality assurance manager review and approve signif-icant procedural changes before they are implemented.
Equipment Calibration and Maintenance Equipment ~scd fur qualitative or quantit:1tivc measurements is care-fully calibrat~d~and maintained with records of each calibration or main-ten~ncc ac~ion kept in appropriate logbooks. To the extent possible, certified standards are used for all primary calibrations. The following standards are used for the application indicated:
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Measurement Calibration Standard Gross Beta Solution of Standard 137 cs certified by NBS or Amersham Searle Tritium Solution standard of 3H certified by NBS Gamma Solutfon standards of various ganuna . emitters
. - Spectrometry certified by NBS or Amersham.Searle. Sta~dards are used to calibrate each counting geometry.used.
Strontium-89 Solution standards of 90sr certified by Amersham and 90 Searle or NBS Gross Alpha Solution standards of 239 Pu certified by NBS or Amersham Searle.
137 -
Radiation Dose Cs gamma source cross-referenced with NBS using R-meters. 22 6Ra is used for some special application.
- When suitable standards are not available for a specific gamma emitter, quantitative' gamma isotopic analysis is based on an energy calibration of the ganuna spectrometer and the gamma ener_gy and abundance information provided in Table of Isotopes, Sixth Edition by Ledrer, Hollander, and Perlman.
The results of the Quality Control Programs are summarizeJ in Section 6
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SECTION 4 l...
RESULTS AND DISCUSSION
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Table 4 Environmental Radiological Monitoring Program Page 1 of 5 Name of 'Facility: Surry Power Station Docket Number: 50-280, 50-281 Location of Facility: ____s_ur_r_y__
County
- - - -Virginia St ate Reporting Period: January 01 - December 31, 1981 Medium or Pathway Type and Lower Limit All Indicator Location with Control Number of Sampled Total Number of Locations Highest Hean Locations Non-routine (Unit of of Analyses Detection Mean 1 Name, Distance Mean Heanl Reported Measurement) Performed (LLD) (Range) and Direction (Range) (Range) Measurements Air Particulates Gross B 414 0.01 0.18 (360/362) Colonial fl.19 (52/52) 0. lR (52/52) 0 (pCi/m 3 ) 0.02-0.70 Parkway 0.02-0.63 0.02-0.60 Gross a 414 0.01 All LLD Not Applicable All LLD 0 Ce-144 12 0.01 0.06 (6/8) Composite 0.09 (3/4) 0.11 (3/4) 0 0.02-0.16 (SS-HIR) 0.05-0.16 0.06-0.15 Be-7 12 0.01 0.13 (8/8) Composite 0.17 (4/4) 0.13 (4/ 4) 0 0.03-0.22 (SS-HIR) 0.14-0.22 0.11-0.14 Composite (2/4) 0 Zr-95 12 0.01 0.03 (6/8) 0.03 (3/4) 0.06 (BC-ALL-CP-0.01-0.07 0.01-0.07 0.06 DOW-FE)
Nb-95 14 0.01 0.09 (6/8) Composite 0.09 (3/4) 0.09 (3/4) 0 0.02-0.17 (SS-HIR) 0.02-0.17 0.03-0.18 Ce-141 12 0.01 0.04 (4/8) Composite 0.05 (2/4) 0.05 (2/4) 0 0.01-0.06 (SS-HIR) 0.04-0.06 0.02-0.07 Ru-103 12 0.01 0.02 (4/8) Composite 0.02 (2/4) 0.02 (2/4) 0 0.01-0.02 (SS-HIR) 0.02 0.01-0.03 Composite '
Ru-106 12 0.01 0.03 (3/8) 0.03 (2/4) 0.03 (1/4) 0
' (BC-ALL-CP- 0.03 0.02-0.03 0.02-0.03 DOW-FE) - ..
Other y 12 0.01 All LLD Not Applicable All. LLD 0 Airborne Iodine I-131 414 0.07 All LLD Not Applicable All LLD 0 (pCi/m 3 )
Medium or Pathway Type and Lower Limit All Indicator* Location with 'Control. Number of Sampled Total Number of Locations Highest Mean Locations Non...:.routine (Unit of of Analyses Detection Meanl Name, Distance Mean Meanl Reported Measurement) Performed (LLD) (Range) and Direction ,,
(Range) (Range) Measurements Background y Dose 0.5 1. 3 (161/16!~) Surry 6.5 (4/ 4) 0.9 (12/12) 0 Radiation (TU)),' I 0.3-9.8, Station 3.8-9.8 o. 3-1. 6 (mR/wk)
Precipitation Gross 6 32 5.0 All LLD Not Applicable All LLD 0 (nCi/m 2 ) 3 (pCi/1) HTO LS HTO 24 500 727 (6/12) . Surry 727 (6/12) 548 (5/ 12) 0 500-1500 Station 500-1500 380-820 Enr .. HTO 8 330 395 (4/4) Surry 395 (4/4) 360 (4/4) 0 260-550 Station 395 240-600 .
Uilk 1-131 59 1. 0 All LLD Not Ap!)licable All LLD 0 N
(pCi/1) u, Sr-89 60 5.0 All LLD Not Applicable All LLD 0 Sr-90 60 2.0 Lf. 1 (37/48) Bacon's 4.7 (7/12) 3.5 * (11/12) 0
- 1. 0-9. 0 Castle 1.0-9.0 1. 0-9. 0 Cs-137 60 15.0 All LLD Not Applicable All LLD 0 Ba-La-140 60 15.0 All LLD Not Applicable All LLD 0 River Hater La-Ba-140 (pCi/1) Cs-134-137 56 15.0 All LLD Not Applicable All LLD 0 Co-58-60 .
Hn-54 Zr-Nb-95 56 10:0 Al 1 LLD Not Applicable All LLD 0 Fe-59 30. 0.
56 All LLD Not Applicable All LLD 0 Zn-65 Sr-89 26 5.0 All LLD Not Applicable
- All LLD 0 1 Mean and range based on detectable measurements only. Fractions indicated in parentheses .
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Table 4 (continued)
Facility:
, Surry Power Station Page 3 of 5 I
I Medium or Pathway Type and Lower Limit All Indicator Location with Control Number of i Sampled Total Number of Locations Highest Mean Locations Non-routine (Unit of of Analyses Detection Meanl Name, Distance Mean Mean 1 Reported Measurement) Performed (LLD) (Range) andrDirection (Range) (Range) Measurements I River Water Sr-90 26 2.0 2 (1/13) Station 2 (1/13) All LLD 0 (pCi/1) 2 Dischar?,e 2 ,
LS HTO 26 500 848 (5/ 13) Station 848 (5/ 13) 768 (5/ 13) 0 500-1000 Dischar~e 500-1000 500-1700 Enr. HTO 4 330 All LLD Not Applicable 370 . (2/2) 0 260-480 Clams Cs-134-137 (pCi/kg) Hn-54 30 130 All LLD Not Applicable All LLD 0
. Co-58 Co-60 30 130 210 (1/24) Hog Island 210 (1/6) All LLD 0 N
CT\ 210 Point 210 Fe-59 30 260 All LLD Not Applicable All LLD 0 Zn-65 Sr-89 5 20 All LLD Not Applicable Not Measured 0 Sr-90 5 10 40 (2/5) Station 40 (2/5) Not Heasured 0 30-50 Discharge. 30-50 Oysters Cs-134-137 Hn-54 18 130 All LLD Not Applicable Not 1'easured 0 Co-58-60 ,,
I r I, Fe-59 18 260 All LLD Not Ap:r,licable Not: 11easured 0 Zn-65 '
Fish Cs-134-137 (pCi/kg) Hn-54 4 130 All LLD Not Applicable Not *Heasured 0 Co-58-60 Fe-59 260 All LLD Not Applicable Not :Measured 0 4
Zn-65
r*ac11.1ty: ~urry Power Station Page 4 of 5
. I Medium or Pathway Type and Lower Limit All Indicator Location with Control Number of Sampled Total Number of Locations Highest Mean Locations Non-routine Mean 1 Mean 1 I
(Unit of of Analyses Detection Name, Distance Mean Reported Measurement) Performed (LLD) (Range) and Direction (Range) (Range) Measurements Crabs ,1111
/ !1 I iCs-134-137 (pCi/kg) Hn-54 3 130 All LLD Not Applicable Not Measured 0 Co-58-60 Fe-59 3 260 All LLD Not Aprilicable Not Measured 0 Zn-65 Silt Cs-134 7 150 245 (2/6) Hog Island 270 (1/1) All LLD 0 (pCi/kg) 220-270 Point 270 Cs-137 7 150 610 (4/6) Point of 890 (1/ 1) 850 (1/ 1) 0 200-890 Shoals 890 850 Co-60 7 150 590 (3/6) Station 960 (1/2) All LLD 0 N
--.J 100-960 Discharge 960 Soil Cs-134 6 150 All LLD Not Applicable Not Measured 0 (pC:i./kg)
Cs-137 6 150 710 (4/6) Bacon's 1600 (1/1) Not Measured 0 130-1600 Castle 1600 Fowl Cs-134 2 Not Applicable 0 80 All LLD Not Measured (pCi/kg Cs-137 Food Crops Cs-134 8 80 0 All LLD Not Applicable Not l*!easured (pCi/kg) Cs-137 Sr-89 8 20 All LLD Not Applicable Not 1-!easured 0 Sr-90 8 10 125 (6/8) Poole 310 (1/1) Not Measured . 0 50-310 310 Well Water Gross 8 8 2 6 (6/ 6) Bacon's 8 (2/2) 7 (2/2) 0 (pCi/1 4"'.'"8 Castle 8 4-9 Gross a 8 1 3 (2/6) Bacon's 3 (2/2) All LLD 0 2-4 Castle 2-4 -
Enr. HTO 8 330 All LLD Not Applicable All LLD 0 1 Mean and range based on detectable measurements only. Fractions indicated in parentheses.
Table 4 (continued)
Facility: - Surry Power Station Page 5 ot 5 I ,,'
'1 ' , :
Medium or Pathway Type and Lower Limit All Indicator Location with Control Number of Sampled Total Number of Locations Highest Mean Locations Non-routine (Unit of of Analyses Detection Meanl Name, Distance Mean Mean 1 Ra.ported Measurement) Performed (LLD) (Range) and Direction (Range) (Range) Measurements Surface Water Gross a 8 2 10 (5/6) Hilliamsburg 21 (1/2) 8 (2/2) 0 (pCi/1) 3-21 Reserve 21 7-8 Gross ex 8 1 4 (5/6) Williamsburg 7 (2/2) 4 (1/2) 0 1-13 Reserve 1-13 4 LS HTO 8 500 487 (3/6) Williamsburg 550 (1/2) 350 (1/2) 0 430-550 Reserve 550 350 N
00
- r , * *
~r~r .
- l*. .
- \if:\:,:..... 1*
Results of all the analyses for January through Iecember 1981 are presented in full in Section 5, Data Tables pages Table 4 summarizes the range and average concentrations for measure-ments at the indicator and control locations with the highest annual mean.
Environmental monitoring results showed that the radiation dose to a mem-ber of the general population did not exceed Technical Specifications of 1% of the 10 CF R 20 limit during 1981.
Specific findings for the various environmental media are discussed below:
1 AIR PARTICULATE SAMPLES Atmosphe_ric particulate matter at a field location is accumulated for a one-week period on a glass fiber filter using a low-volume air sampler at a collection rate of one cubic foot per minute. This particu-late matter contained on the filter is counted for beta activity in a low-b;1ckground counting system after the short-lived naturally-occurring radon and thoron daughters have decayed.
The *gross beta particulate data obtained during the first six-month period of 1981 are higher than the data obtained during the latter half.
According to P. K. Kuroda et al 1 , concentrations of Sr-89 and Sr-90 in rain ~nd sno~_~at Fayetteville, Arkansas, showed a spectacular increase during tlie- spring months of 1981 due to the 25th Chinese nuclear test
- explosio*n
- of October 1980. It is therefore_ suggested that these higher f P. K. Kuroda, "Recent Atmospheric Injections of Nuclear Debris: Fallout from. the 16 October 1980 Nuclear Explosion", unpublished manuscript, 1981.
29
levels are attributable to the stratospheric fallout from this test.
The average gross beta concentration for the year for all indicator stations was 0.18 pCi/m3. and for the control location it was also 0.18 pCi/ni3 . Data for analyses of individual filters are given on pag7-s 40 through 45 in Section 5.
The gross alpha concentrations for the** indicator and background stations remained at or below the detection limit 0.01 pCi/ni3 ~
The gamma spectrometry data of quarterly composites of air particu-late filters begins on page 46. Traces of Ce-144, Be-7, Zr-95, Np-95, Ce-141, Ru-103, and Ru-106 were detected at both indicator and background stations and are attributable to cosmogenic origin and to the statospheric fallout from the Chinese nuclear test.
ENVIRONMENTAL DOSIMETRY Measurements of environmental dose rates were made at 43 locations on a quarterly basis using thermoluminiscent dosimeters (TLDs). The results are tabulated on pages 47 through 48 of Section.5.
As observed in previous years, the Surry Station location displays clearly elevated dose rates throughout the year. Other on-site ~ocations appear to be only very slightly above nearby locations and the badges located near the station intake and discharges consistently give some of the lowest readings observed. The major fraction of the dose at the Surry Station location is undoubtedly due to operation of the station. The doses at other on-site locations may be partially due to the station, but only by .1 few tenths of a millirem per week at most. Doses due to the plant at locations away from the site, if they exist, are masked by doses from
,.- the- -natural environmental sources such- as uranium, thorium, and* their daughters, and possibly worldwide fallout.
30
PRECIPITATION SAMPLES Precipitation samples collected at the Surry Station and at Newport News are analyzed on a monthly basis and as quarterly composites
_for gross.beta depositions and tritium concentrations. Data are sum-marized on page 50 of Section 5.
Gross beta measurements, the only measurement other than tritium required on these samples, are not capable of indicating whether the differences are due to station operations or not. For both the control
~nd the indicator location, the gross beta data obtained during the first six-month period of 1981 are higher than the data obtained during the latter half. These higher levels can be explained by the stratospheric fallout from the Chinese test. The levels in general were in the range
, to be expected from measurements of these nuclides in this medium and t
there are no indications they are ~ttributable to releases from Surry
- . Station.
The tritium levels were comparable at both the indicator and control location throughout the year, and were generally in the range to be expect-ed from measurements of this nuclide in this medium. Nevertheless, an 1111usu.illy high cont<.*ntr;1tion of tritium was found in the snmple from Surry Station during November. It is possible that this tritium level was a result of plant operation. However, the measured concentration was still less than 0.1 percent of the maximum permissible concentration.
MILK SAMPLES Radionuclides Cs-137 and I-131 were below the detection limits (15 pCi/1 for Cs-137 and 1 pCi/1 for I-131) for all milk samples collected
- during the year. Sr-90 was detected in most of the milk samples in the usual low and variable concentrations-to be expected. Sr-89 and Ba-La-140 31
were below the detection limits (5 pCi/1 for Sr-89 and 15 pCi/1 for Ba-La-140) in all samples collected. Radioactivity attributable to operation of Surry Station was not detected in any milk samples collected during the year.
Comparisons of the average concentrations for all nuclides assayed and other statistical information are given in Table 4 and the data sum-mary on each sample by location are given on pages 51 through 53 of Section 5.
JAMES RIVER WATER SAMPLES Samples of water from the James River are collected bi-monthly from five locations including the station inlet and discharge and are analyzed for gamma emitters. Semi-annual composites of the collections from the Chickahominy and Newport News locations are also analyzed for tritium.
Samples collected monthly from the discharge and Scotland Wharf are split with a state agency and are analyzed for tritium, Sr-89/90, and gamma emitters.
Analytical data are presented on pages 54 through 57 of*secti9n 5.
~1mma emitters were below the detection limits of this program in all samples collected.
Barely detectable concentrations of Sr-90 were found in two of the State Split discharge samples and were due to the recent Chinese bomb test.
The monthly tritium concentrations for the year for discharge samples ranged from 500 to 1000 pCi/1, the average being 848 pCi/1. The tritium concentrations for Scotland Wharf ranged from 500 to 1700 pCi/1, the ave-rage concentration being 768 pCi/1. There was no statistically signifi-
.. cant difference in **average concentrations between indicator and control locations.
32
Tritium levels in the semi-annual composites for Chickahominy and Newport News were slightly above the detection limit of 330 pCi/1. These levels were in the range to be expected from measurements of this nuclide' in this medium.
"CLAM SAMPLES Clam samples are collected bi-monthly from five locations near the station including the station discharge and are analyzed for gamma emit-ters. Samples from the station discharge are frequently designated as "State Split Samples" and such samples are analyzed for Sr-89 and Sr-90 as well as gamma emitters.
Co-60 was detected at low concentration in one sample from Hog Island Point during gamma spectroscopy analysis and could be due to r
plant operations. However, the measured concentration is still less
~han 0.1 per~ent of the maximum permissible concentration.
Analysis of state split clam samples for radiostrontium revealed the presence of only Sr-90 at levels attributable to world wide fallout in two samples.
Analytical data are presented on pages 58 and 59 of Section 5.
OYSTER SAMPLES Samples of oysters are collected from Deep Water Shoal, Point of Shoal, and Newport News on a bi-monthly basis and analyzed for gamma emitters. A~alytical data are presented on page 60 of Section 5.
Gamma emitters were below the detection limits of the program in all samples collected throughout the year.
33
FISH SAMPLES Fish samples are collected in the vicinity of the station twice a year and analyzed for gamma emitters. Data are presented on page 61 of Section 5 *
. Gamma emitters were below the detection limits of the program specifications.
CRAB SAMPLES Samples of crab from the vicinity of Surry Station are collected during the summer months and analyzed for gamma emitters. The gaIJUila emitters were below the detection limits of the program and are listed on page 61 of Section 5.
SILT SAMPLES Silt samples were collected three times during 1981 from six loca-tions (five indicator and one control location) and analyzed for gamma emitters. Silt is one of the few environmental media in which radioactive effluents from nuclear power stations are usually detected.
Traces of Cs-137 were found in most samples. The presence of this nuclide is attributed to world wide fallout from atmospheric nuclear tests.
Several indicator samples also contained Co-60, Cs-134, Zr-95, Nb-95, Co-58, and Mn-54 above the detection limit. Their presence could be due to station operations.* Data are summarized on page 62 of Section 5.
SOlL SAMPLES Soil samples are collected annually from six locations and analyzed
. by gamma spectrometry for gamma emitters
- The only nuclide detected at concentrations greater than the detection' 34
limit for the program was Cs-137. The concentrations of Cs-137 have been quite variable throughout the years as is illustrated in the table below. This is probably due to the well-recognized difficulty *of ob-
- ta~ning truly representative samples of soil. Modified sampling tech-niques by station personnel appear to have eliminated this problem from 19,8 to the present. There are no clear trends and the origin of the cesium is unclear.
Cs-137 Concentrations in Soil Samples 10 2 ECi/kg*
(Aug) (Sept) 1975 L976 l977 L978 1978 1979 1980 1981 Surry Station 35 1 17 <2 4 2 2 <2 Fort Eustis 18 10 17 18 2 4 16 Dow 10 2 2 <2 3 <2 2 1 Bacon's Castle 8 24 2 23 9 11 10 8 Aliiance 2 3 2 <2 3 3 6 4 Colonial Pkwy. 15 12 22 7 <2 4 <2
- Data rounded to nearest whole unit, statistical errors omitted.
~ Long and short term world wide fall.out are probably the major factors but contributions to the total by the station cannot be ruled out. If, however, the major fraction were due to the station, significant amounts of Cs-137 and Co-60 might be expected in the samples, but this is not the case. Detailed nnnlytical dntn arc presented on page 63 of Section 5.
FOWL SAMPLES A coot from the Hog Island Reserve was collected in March and a goose was obtained from the same area in September. They were analyzed for gamma emitt~~s, specifically for Cs-134 and Cs-137. Concentrations of these nuclides were below the detection limit of 80 pCi/kg for both samples. Data are given on page 63 of Section 5.
35
~::;:{~-i
,..~--.*~--* -_-.
~ii~ CROP SAMPLES Samples of food cro_ps (kale, cabbage, corn, peanuts, and soybeans) were collected from four area farms in 1981 and analyzed from gamma emit-ters, Sr-89, and Sr-90. Gamma emitters and-Sr-89 were below the detection limits of the program.
Sr-90 was detected in most of the samples in low and variable con-centrations. Long and short ter~ world wide fallout deposits are probably the reason for this.
The results are tabulated on page 63 of Section 5.
WELL WATER SAMPLES Samples.of water were collected from each of four wells (three indicat<>r and one control location) once in April and once in October.
These were analyzed for gross alpha, gross beta, and tritium.
Gross alpha and beta activity were detected in most of the samples at the usual low levels encountered in environmental media. There was no statistically significant difference in concentrations, which were similar to those measured previously, between indicator and background st.1tions and the activity is attributable to naturally occurring nuc-lid es.
Tritium concentrations were at or below the detection limits in samples collected during the year.
Analytical data are given on page 64 of Section 5.
SURFACE WATER SAMPLES Surface water samples were collected in April and October from
.. each of four locations. They were analyzed for gross alpha, gross beta, and tritium.
36
- Gross alpha and gross beta levels were ~11 at the low concentrations usually expected to be found in environmental surface water, with no sig-nificant differences between indicator and background stations or concen- .
'tr~tions measured in the.previous years.
Tritium concentrations were at the detection limits of the program
- in spring collections, and below *the detection limits in the fall. The levels of tritium measured were comparable at both indicator and back-ground locations, and were generally in the range to be expected from measurements of this nuclide in this medium.
Data are presented oh page 64 in Section 5.
37
SECTION 5 DATA TABLES 38 I
J
INTRODUCTION TO THE DATA TABLES The following information will be helpful in understanding the presentation of the data in the tables in this section. ,
Wet Weight a reporting unit used with organic tissue samples such as vegetation and animal samples in which the amount of sample is taken to be the weight as received from the field with no moisture removed.
Dry Weight a reporting unit used for soil and sediment in which the amount of sample is taken to be the weight of the sample after removal of moisture by drying in *an oven at about 110° for about 15 hours1.736111e-4 days <br />0.00417 hours <br />2.480159e-5 weeks <br />5.7075e-6 months <br />.
pCi/m 3 a reporting unit used with air particulate and radioiodine data which refers to the radioactivity content expressed in picocuries of the volume of air expressed in cubic meters passed through the filter and/or the charcoal trap. Note that the volumes are not corrected to standard conditions.
r.amma Emitters samples were analyzed by high resolution (GeLi) gamma or spectrometry. The resulting spectrum is analyzed by a Garrul1a Isotopic computer program which scans from about SO to 2000 kev and lists the energy peak of any nuclides present in concentra-tions exceeding the sensitivity limits set for that particular experiment.
NA, NS, NR used in place of a concentration when a sample was not available (NS), or when a sample was not analyzed for some specific measurement (NA), or when an analysis is not required (NR).
Error Terms figures following 11 +/- 11 are error terms based on counting uncertainties at the 2a (95% confidence) level. Values pre-ceded by the"<" symbol were below the stated concentration
.at the 3a (99% confidence) level.
Exponents Exponents necessary to prevent data tables from being cumbersome are handled in the conventional manner of including them in the column headings.
Sensitivity In general, all analyses meet the sensitivity requirements of the program as given in Table 3. For the few samples that do not (because of inadequate sample quantities, analytical
-interferences, etc.)- the sensitivity actually obtained in the analysis is given.
Comment when all analyses of a particular type during the period resulted in concentrations below the sensitivity limits, a statement is*made on the -appropriate table rather than presenting a whole page of"<" data. If all but one or two data points are below the sensitivity limits, the previously mentioned convention is followed and the finite data are given as footnotes.
39
- AIRBO~!E ICZ)I:;:::-131, G~:iss AL?r-""~- anc. 3::2-='.~ in AI~ PARTICULATE FILTERS (Weekly Collections) 10- 2 n,'.;i/m 3 ss (I) SURRY STATrm; HIR ~I2 HOv ISLA.:-ID RESERVE BC (I) BACON'S CASTLE Collection Voltune Gross Gross Volm::e Gross Gross Volw:ie Gross Gross Date (m3) Alpha Beta I-131 (m3) Alnha Beta I-131 (1r.3) Alnha Beta I-131 01/06/81 245 <l 11+/-1 <7 255 <l 13+/-1 <7 270 <l 10+/-1 <7 01/13/81 255 <l 10+/-1 <7 275 <l 8+/-1 <7 265 <1 16+/-1 <7 01/20/81 275 <1 22+/-2 <7 260 <l 18+/-2 <7 310 <l 16+/-2 <7 01/27/81 230 <l 33+/-3 <7 205 <1 32+/-3 <7 255 <1 31+/-3 <7 02/03/81 230 <1 13+/-1 <7 250 <1 12+/-1 <7 290 <l 24+/-2 <7
-02/10/81 250 <l 17+/-2 <7 235 <1 17+/-2 <7 300 <l 18+/-2 <7 02/17 /81 225 <l 25+/-3 <7 235 <l 22+/-2 <7 285 <l 28+/-3 <7 02/24/81 250 <1 27+/-3 <7 250 <l 21+/-2 <7 290 <l 28+/-3 <7 03/03/81 245 <l 24+/-2 <7 250 <l 21+/-2 <7 285 <l 26+/-3 <7 03/10/81 235 <l 30+/-3 <7 240 <1 36+/-4 <7 290 <1 18+/-2 <7 03/17/81 235 <1 43+/-4 <7 240 <1 41+/-4 <7 295 <1 40+/-4 <7
.i:-,
0 03/24/81 225 <1 21+/-2 <7 230 <1 18+/-2 <7 280 <1 24+/-2 <7 03/31/81 240 <1 48+/-5 <7 255 <l 27+/-3 <7 285 <1 52+/-5 <7 04/07/81 240 <1 44+/-4 <7 25Q <1 47+/-5 <7 270 <1 70+/-7 . <7 04/14/81 225 <1 41+/-4 <7 255 <1 40+/-4 <7 305 <1 1+0+/-4 <7 04/21/81 220 (1 38+/-4 <7 245 <1 36+/-4 <7 300 <1 36+/-4 <7 04/28/81 235 <l 36+/-2 <7 240 <1 36+/-2 <7 275 <1 44+/-2 <7 05/05/81 235 <l 35+/-5 <7 235 <l .36+/-4 <7 280 <l 37+/-4 <7 05/13/81 255 <l 28+/-3 <7 260 <1 27+/-3 <7 335 <1 27+/-3 <7 05/21/81 245 <1 40+/-4 <7 275 <l 37+/-4 <7 345 <1 39+/-4 <7 05/26/81 145 <1 66+/-7 <7 160 (1 58+/-6 <7 190 <1 62+/-6 <7 06/02/~1 230 <1 37+/-4 <7 290 <1 24+/-2 <7 280 <l 32+/-3 <7 06/09/81 195 <1 19+/-2 (7 235 <1 26+/-3 <7 280 <1 18+/-2 <7 06/16/81 205 <l 20+/-2 <7 245 <l 17+/-2 (7 285 <l 22+/-2 <7 06/23/81 06/30/81 195 280 (1
<1 25+/-3 21+/-2
.<7
<7 215 265
<1 (1
11+/-2 20+/-2
<7 (7
280 290 (1
(1 17+/-2 22+/-2 (7
(7
AIRBOR?TE I0DIZE-l3l, GRJSS ALPH.A and BE~A in AIR PARTICULATE FILTERS (Weekly . .Collei:;tions.) ' .
I 10- 2 Ci/m 3 SS* {12 SURRY STATION HIR ~12 HOG ISLA.:'lD RESERVE BC (I) BACON'S CASTLE Collection Volume Gross Gross Volume Gross Gross Volume Gross Gross Date (m3) Al:eha Beta I-131 (m3) Al:eha Beta I-131 (m3) Al:eha Beta I-131 07/07/81 i25oi <l 15+/-2 <7 190 <l 7+/-1 <7 280 <l 15+/-2 <7 07 /14/81 285 <l 28+/-3 <7 220 <l 28+/-3 <7 265 (1 24+/-2 <7 07/21/81 225 <l 18+/-2 <7 215 <l 14+/-1 <7 255 <l 14+/-1 <7 07/28/81 305 <l 13+/-1 <7 220 <l 13+/-1 <7 245 <l 13+/-1 0 08/04/81 280 <l 9+/-1 <7 235 <l 8+/-1 <..7 235 (a) <l 7+/-1 <7 08/ 11/81 315 <l 6+/-1 0 225 <l 7+/-1 0 320 <l 6+/-1 <7 08/18/81 305 <l 9+/-1 0 220 <l 10+/-1 0 315 (1 7+/-1 0 08/25/81. 285 <l 10+/-1 0 225 <l 11+/-1 <7 300 <l 8+/-1 0 09/01/81 285 <l 7+/-1 0 290 <l 7+/-1 0 300 <l 6+/-1 0 09/08/81 260 <l 6+/-1* 0 285 <l 6+/-1 <7 305 <l 6+/-1 0 09/15/81 250 <l 8+/-1 0 280 <l 7+/-1 0 300 <l 7+/-1 <7
.i,-
...... 09/22/81 245 <l 6+/-1 <7 285 <l 4+/-1 <7 280 <1 5+/-1 0 09/30/81 285 <l 5+/-1 <7 315 <l 5+/-1 <7 345 <l 5+/-1 0 10/06/81 205 <l 4+/-1 <7 245 <l 5+/-1
- 0 250 <l 4+/-1 <7 10/ 13/81 240 <l 3+/-1 0 290 <l 3+/-1 0 305 <l 3+/-1 <7 10/20/81 245 <l 5+/-1 0 305 <l 3+/-1 <7 305 <l 3+/-1 <7 10/ 27 /81 245 <1 5+/-1 <7 305 <l 4+/-1 0 290 <1. 3+/-1 <7 11/03/81 225 <l 6+/-1 0 310 <l 3+/-1 0 290 <l 5+/-1 0 11/ 10/81 235 <l 5+/-1 <7 290 <l 4+/-1 0 305 <1 5+/-1 <7 11/17 /81 235 <l 9+/-1 0 300 <1 5+/-1 0 300 <l 5+/-1 <7 11/24/81 230 <1 5+/-1 0 300 <1 5+/-1 <7 300 <1 5+/-1 <7 12/02/81. 260 <l 3+/-1 0 350 <1 7+/-1 0 350 <l 3+/-1 <7 12/ 11/81 370 <l 4+/-1 0 390 <1 6+/-1 0 390 <l 5+/-1 <7
. 12/ 15/81 165 <1 3+/-1 0 180 <1 3+/-1 (7 170 <l 2+/-1 <7 12/22/81 285 <l 3+/-1 0 295 <l 4+/-1 0 305 <l 5+/-1 <7 12/29/81 300 <l 4+/-1 *o 300 <l 3+/-1 <7 295 <l 3+/-1 <7 (aO Calculations based on average volume.
VEPCO AIRBOR:iE IODIN~-131, G~OSS ALP::.A and B~TA in AIR PARTICULATE FILTERS (Weekly Collections) 10- 2 PCi/m 3 A!,L {12 ALLIANCi:'. CP {I) COLONIAL PARKWAY DOW (I)
Collection Volune Gross Gross Volune Gross Gross Vol1.L':J.e Gross Gross Date (m3) Alpha Beta I-131 (m3) Alnha Beta I-131 (m3) Alnha Beta I-131 01/06/81 280 <1 10+/-1 <7 270 (1 11+/-1 <7 285 <l 11+/-1 <7 01/13/81 285 <1 14+/-1 <7 290 <1 13+/-1 <7 300 <1 8+/-1 <7 01/20/81 300 <1 15+/-1 <7 210 <1 24+/-2 <7 260 <1 18+/-2 <7 01/27/81 285 <1 28+/-3 <7 270 <1 30+/-3 <7 265 <1 26+/-3 <7 02/03/81 305 <1 17+/-2 <7 275 <1 15+/-2 <7 265 <1 12+/-1 <7 02/10/81 300 <1 13+/-1 <7 275 <l 20+/-2 <7 270 <l 17+/-2 <7 02/17/81 295 <l 23+/-2 (7 265 <l 22+/-2 <7 255 <l 22+/-2 <7 02/24/81 280 <:J. 23+/-2 <7 250 <1 30+/-3 <7 255 <1 34+/-3 <7 03/03/81 285 <1 20+/-2 <7 255 <l 20+/-2 <7 265 <l 18+/-2 <7 03/10/81 280 <l 17+/-2 <7 250 <1 27+/-3 <7 260 <l 17+/-2 <7 03/17/81 290 <l 35+/-4 <7 260 <l 41+/-4 <7 265 <1 44+/-4 <7
~
N 03/24/81 290 <1 18+/-2 <7 255 <1 23+/-2 <7 265 <l 23+/-2 <7 03/31/81 280 <l 40+/-4 <7 275 <l 25+/-3 <7 275 <l 37+/-4 <7 04/07/81 300 <l 60+/-6 (7 280 <1 62+/-6 <7 305 <l 49+/-5 (7 04/14/81 315 <l 34+/-3 (7 270 <l 35+/-4 <7 360 <l 39+/-4 <7 04/21/81 320 <1 28+/-3 (7 250 <l 46+/-5 <7 290 <l 34+/-3 <7 04/28/81 290 <l 33+/-2 (7 245 <l 49+/-2 <7 320 <l 29+/-2 <7 05/05/81 295 <l 23+/-2 (7 240 <l 41+/-4 <7 300 <l 31+/-3 <7 05/13/81 345 <l 21+/-2 <7 295 <l 27+/-3 <7 345 <l 26+/-3 <7 05/21/81 345 <l 33+/-3 <7 290 <l 41+/-4 <7 355 <l 32+/-3 <7 05/26/81 205 <l 50+/-5 (7 170 <l 63+/-6 <7 200 <l 58+/-6 <7 06/02/81 295 <l 23+/-2 <7 235 <l 28+/-3 <7 290 <l 24+/-2 <7 06/09/81 290 <l 19+/-2 <7 235 <l 26+/-3 <7 290 <l 3+/-1 <7 06/16/81 295 <l 14+/-1. <7 230 <l 22+/-2 <7 285 <l 17+/-2 <7 06/23/81 295 <l 15+/-2 (7 235 <l 18+/-2 (7 300 <l 8+/-1 (7 06/30/81 300 <l 17+/-2 '<7 250 <l 21+/-2 <7 310 <l 19+/-2 <7
-1;, *.*: 1,.* .* ;,*,,,. ,:,.,,,;:;c~e!',.'<.c1*<*Y-',-!;,;,.<*,,.,,...... ;.*c,*,,,,~*-*-0**C'AIHl:m.tUV~ liJ1Jl.N!!;;..2.jl'. UttOt::!:i Al,.l:'.tiA and BETA in AIR PARTICULA1'E FILTERS (Weekly Collections)
- 10- 2 pCi/m3
.A!,!, (I) A"I.,;!..:TANCE CP (I) COLONIAL PARKWAY DOW (I)
Collection., Volume Gross Gross Volume Gross Gross Volume Gross Gross Date (m3) Alpha Beta I-131 (m3) Alpha Beta I-131 (m3) Alpha Beta I-131 I *."I ,
07/07/81 300 I' <l 12+/-1 0 245 '
<1 12+/-1 0 290 <1 9+/-1 0 (
07/14/81 240 <l 28+/-3 <7 235 <l 25+/-3 <7 280 <l 24+/-2 .. 0 07/21/8i 275 <l 17+/-2 <7 230 <l 15+/-2 <7 285 <l 14+/-1 <7 07/28/81 265 <l 15+/-2 0 225 <l 13+/-1 <7 285 <1 12+/-1 <7 08/04/81 290 <1 6+/-1 <7 225 <l 9+/-1 0 300 <l 7+/-1 0 08/ 11/81 295 <I 7+/-1. <7 205 <I 8+/-1 <7 290 <1 . 6+/-1 <7 08/18/81 290 <1 8+/-1 <7 235 (1 9+/-1 <7 300 <l 8+/-1 0 08/25/81. 275 <1 10+/-1 (7 250 <l 9+/-1 (7 285 <l 9+/-1 <7 09/01/81 290 <1 6+/-1 <7 245 <1 7+/-1 (7 280 <l 6+/-1 (7 09/08/81 295 <1 6+/-1 (7 240 <l 6+/-1 (7 285 <l 7+/-1 (7 09/15/81 285 <l 7+/-1 (7 240 <l 10+/-1 (7 270 <l 7+/-1 <7 J:'- 09/22/81 300 <1 5+/-1 (7. 240 <1 5+/-1 (7 260 <l 5+/-1 <7
(,.,.)
09/30/81 345 <1 6+/-1 (7 295 <l 6+/-1 (7 295 <1 5+/-1 (7 10/06/81 260 <l 5+/-1 0 205 <l 6+/-1 (7 225 <1 5+/-1 <7 10/13/81 300 <l 3+/-1 <7 255 <I 2+/-1 (7 260 <i 2+/-1 <7 10/20/81 310 <1 3+/-1 <7 270 <l 4+/-1 (7 260 <1 3+/-1 0 10/27/81 295 <I 4+/-1 0 250 (1 4+/-1 <7 250 <1 9+/-1 <7 11/03/81 300 <l 3+/-1 0 245 <l 4+/-1 0 255 <1 4+/-1 0 11/10/81 305 <l 6+/-1 <7 255 <l 7+/-1 <7 255 <! 5+/-1 <7 11/17/81 310 <l 7+/-1 <7 265 <1 7+/-1 0 260 <l 6+/-1 <7 11/24/81 295 <1 6+/-1 <7 225 <l 5+/-1 <7 245 <1 4+/-1 <7 12/02/81 350 <1 5+/-1 (7 295 <1 5+/-1 <7 275 <1 5+/-1 <7 12/11/81 390 <1 5+/-1 (7 320 <1 5+/-1 <7 330 <J. 2+/-1 <7 12/15/81 170 (1 5+/-1 0 145 <1 2+/-1 <7 155 <1 <l <7 12/22/81 305 (1 5+/-1 ,<7 250 (1 10+/-1 <7 (a) 12/29/81 300 <1 3+/-1 0 250 <1 3+/-1 <7 (a)
(a) Sampling unit out of order.
~i~l:~~-'
,. ,. ( .
VEPCO AIRBORUE IODI!E-131, G~OSS ALPHA and B~~A in AIR PARTICULATE FILTERS (Weekl~ Collections) i *:*!',.
1 i
10- 2 uCi/m 3 I 11 1 FE en FORT EUSTIS NN {C) NEWPORT NEWS Collection Volume Gross Gross Volw:e Gross Gross Date ( rn 3) Alpha Beta I-131 (m3) Alpha Beta I-131 01/06/81 300 <l 11+/-1 <7 275 <1 10+/-1 <7 01/13/81 305 <1 11+/-1 <7 265 <l 10+/-1 <7 01/20/81 300 <l <l(a) <7 260 <l 24+/-2 <7 01/27/80 275 <l 34+/-3 <7 265 <l 27+/-3 <7 02/03/81 305 <l 7+/-1 <7 260 <l 19+/-2 <7 02/10/81 290 <l 14+/-1 <7 260 <l 18+/-2 <7 02/17/81 300 <l 18+/-2 <7 245 <l 43+/-4 <7 02/24/81 300 <l ')
~I _ _,,' <7 250 <1 29+/-3 <7 03/03/81 305 <1 20+/-2 <7 255 <l . 17+/-2 <7 03/10/81 300 <l 24+/-2 <7 245 <l 20+/-2 <7
,p-
,p-03/17/81 305 <l 19+/-2 <7 240 <l 39+/-4 <7 03/24/81 310 <l 20+/-2 <7 250 <l 20+/-2 <7 03/31/81 290 <l 44+/-4 <7 255 <l 48+/-5 <7 04/07/81 295 <l 44+/-4 <7 255 <1 60+/-6 <7 04/14/81 305 <l 39+/-4 <7 95 <l l15+/-5 <7 04/21/81 310 <l 39+/-4 <7 175 <l 36+/-4 <7 04/28/81 305 <l 33+/-2 <7 235 <l 38+/-2 <7 05/05/81
- 390 <l 37+/-4 <7 240 <l 32+/-3 <7 05/13/81 345 <l 27+/-3 <7 280 <l 26+/-3. <7 05/21/81 355 <l 33+/-3 <7 280 <l 40+/-4 <7 05/26/81 205 <l 56+/-6 <7 155 <l 53+/-5 <7 06/02/81 300 <l. 18+/-2 <7 295 <l 25+/-3 <7 06/09/81 110 <l 41+/-4 <7 285 <l 19+/-2 <7 06/16/81 205 <l 19+/-2 <7 280 <l 19+/-2 <7 06/23/81 250 <l 12+/-2 <7 270 <l 12+/-2 <7 06/30/81 275 *<I 24+/-2 <7 285' <I 21+/-2 <7
- * * *.*--~-,,,,*.,v*.. ,.,-......, .. "
0
"'""""~*"'~""""'"'*~.:,,,,_,~;~~t6:~~~1~~~~~~~.J~~~~t~'&,t~l~~'.-i~:~1/ihY::5};ii;.i'!~~i~;-~:~%~*1 AIRBORNE IODINE-131, GROSS ALPHA and BETA in AIR PARTICULATE FILTERS (Weekly Collections) 10- 2 pCi/m 3 FE (I) FORT EUSTIS NN (C) NEWPORT NEWS Collection Volllr.le Gross Gross Volume Gross Gross
- \ D;ate ...
(m_3_)_ Afpha Beta *r-131 (m3) Alpha Beta *I-131 07/07/81 255 (1 13+/-1 <7 275 (1 9+/-1 <7 07/14/81 245 (1 26+/-3 <7 270 (1 23+/-2 . <7 07/21/81 250 <l 14+/-1 <7 260 (1 12+/-1 <7 07/28/81 250 (1 15+/-2 <7 265 (1 10+/-1 0 08/04/81 265 <1 4+/-1 <7 265 <1 7+/-1 <7 08/11/81 245 <1 3+/-1 <7 185 <1 3+/-1 0 08/18/81 225 (1 9+/-1 <7 245 <l 8+/-1 <7 08/25/81 230 (1 10+/-1 <7 260 (1 7+/-1 <7 09/01/81 230 (l 6+/-1 <7 270 (1 9+/-1 <7 09/08/81 230 <l 7+/-1 <7 250 (1 6+/-1 <7 09/15/81 235 <l 8+/-1 <7 235 (1 7+/-1 <7
-I"-
09/22/81 235 (1 5+/-1 <7 250 <l 5+/-1 <7 u,
09/30/81 260 (1 6+/-1 <7 285 (l 6+/-1 <7 10/06/81 190 <1 4+/-1 <7 210 <1 5+/-1 <7 10/13/81 230 <1 3+/-1 <7 260 <1 3+/-1 <7 10/20/81 190 <1 2+/-1 <7 255 <1 3+/-1 <7 10/27/81 210 <l 3+/-1 <7 . 250 <1 3+/-1 <7 11/03/81 210 <l 6+/-1 <7 240 <1 4+/-1 <7 i'l/10/81 215 (1 5+/-1 <7 255 <1 6+/-1 <7 11/17/81 180 <1 5+/-1 <7 230 <1 . 7+/-1 <7 11/24/81 215 <1 6+/-1 <7 250 <1 5+/-1 <7 12/02/81 250 <1 L1+/-l <7 280 <1 5+/-1 <7 12/11/81 290 (1 5+/-1 <7 305 <1 5+/-1 <7 12/15/81 130 (1 2+/-1 <7 14.0 <1 2+/-1 0 12/22/81 225 <1 5+/-1 0 230 <1 5+/-1 0 12/29/81 210 <1 5+/-1 0 250 <1 5+/-1 0
VEPCO - Surry GAMMA EMITTERS IN AIR PARTICULATE FILTER COMPOSITE (Quarterly Composites of Weekly Collections)
- stations in Composite SS-HIR BC-ALL-CP-DOW-FE NN FIRST QUARTER Ce-144 5+/-1 2+/-1 6+/-2 Be-7 16+/-3 3+/-1 11+/-4 Zr-95 3+/-1 2+/-1 6+/-1 Nb-95 17+/-2 8+/-1 18+/-2 Ce-141 6+/-2 3+/-1 7+/-3 Ru-103 2+/-1 1+/-1 3+/-1 Ru-106 2+/-1 Other gamma <1 <1 <1 SECOND QUARTER Ce-144 16+/-2 7+/-1 15+/-1 Bc-7 15+/-3 11+/-2 14+/-5 Zr-95 4+/-1 7+/-1 6+/-1 Nb-95 9+/-1 12+/-1 6+/-1 Ce-141 4+/-1 1+/-1 2+/-1 Ru-103 2+/-1 2+/-1 1+/-1 Ru-106 3+/-1 3+/-1 <2 Other gamma <I <I <I THIRD QUARTER Ce-144 5+/-2 3+/-1 13+/-3 Be-7 22+/-3 19+/-2 14+/-3
. Zr-95 . 2+/-1 1+/-1 <1 Nb-95 2+/-1 2+/-1 3+/-1 Other gamma <1 <I <1 FOURTH QUARTER Be-7 14+/-2 7+/-1 11+/-3 Other y <I (1 (1 46
VEPCO - Surry GAMNA RADIATION TOTAL mR/QTR. USING THERMOLUMINISCENT DOSIMETERS VEPCO-ENVIRONMENTAL TLD'S 1981 1st Quarter 2nd j'uarter Date Annealed: 12/23/80 03 20/81 Date Read: 04/16/81 07/13/81 Location ~mR mR/wk EmR mR/wk (C)Control (Site) -00 5 .li+/-O. 4 o*. 3+/-0.1 7.6+/-0.R 0.5+/-0.1 Surry Station -01 73.1+/-7.5 4.5+/-0.5 62.2+/-6.2 3.8+/-0.4 WNW -oz 16.1+/-3.1 1. 0+/-0. 2 16.7+/-1.7 1. 0+/-0. 1 Discharge Canal -03 12.2+/-1.1 0.8+/-0.1 10.2+/-1.0 0.6+/-0.1 NNW -04 15.9+/-2.9 1.0+/-0.2 17.1+/-1. 7 1. 0+/-0. l North -05 15.6+/-0.9 1. 0+/-0.1 13.2+/-2.5 0.8+/-0.2 NNE -06 16. 0+/-1. 9 1. 8+/-0. 1 17.4+/-1.7 1.1+/-0.1 NE -07 15. 6+/-1. 2 1. 0+/-0. l 17.2+/-1.7 1. 1+/-0. l ENE -08 17.2+/-1.1 1. 1+/-0.1 14. 3+/-1. 9 0.9+/-0.1 East exclusion area -09 19.6+/-0.6 1. 2+/-0. 1. 17.7+/-1.8 1.1+/-0.1 WEST -10 15.7+/-1.0 1.0+/-0.1 13. 2+/-1. 3 0.8+/-0.l WSW -11 5.6+/-2.4 1. 0+/-0.1 15.2+/-2.2 0.9+/-0.1 SW -12 18.7+/-2.2 1. 1+/-0.1 16.1+/-1.6 1. 0+/-0.1 SSW -13 16.5+/-1.6 1. 0+/-0.1 16.5:tl.7 1. 0+/-0.1
'South -14 17.7+/-1.6 1.1+/-0.1 14. 0+/-1. 4 0.9+/-0.1 SSE -15 15.8+/-0.8 1.0+/-0.1 15.8+/-1.6
- 1. 0+/-0.1
_SE -16 16.4+/-1.2 1. 0+/-0.1 15.2+/-1.5 0.9+/-0.1
- East -17 15.9+/-1.9 1. 0+/-0 .1 13. 8+/-1. 4 0.8+/-0.1 Intake Canal -18 10.5+/-1.0 0.6+/-0.1 missing missing Hog Island Reserve -19 14.9+/-1.7 0.9+/-0.1 23.0+/-2.3 1. 4,+/-0.1 Bacons Castle -20 14.3+/-2.0 0.9+/-0.1 13.9+/-1.4 0.8+/-0.1 Route 633 -21 14.7+/-1.3 0.9+/-0.1 16.9+/-1.7 1. 0+/-0.1 Alliance -22 12.1+/-1.3 0.7+/-0.1 12.1+/-2.0 0.7+/-0.1 Surry -23 15.8+/-2.1 1. 0+/-0. 1 13. 3+/-2 .J- 0.8+/-0.1 Route:-. <,37 & 635 -24 13.4+/-2.2 0.8+/-0.1 13.3+/-1.3 0.8+/-0.1 Scotland Wharf -25 15.7+/-1.4 1.0+/-0.1 16.2+/-1.6 1. 0+/-0 .1 Jamestown -26 17.8+/-1.5 1.1+/-0.1 14.4+/-1.4 0.9+/-0.1 Colonial Parkway (NW) -27 12.2+/-0.3 0.7+/-0.1 20.7+/-2.1 1. 3+/-0.1 Route 617 & 618 -28 14.1+/-1.0 0.9+/-0.1 12.7+/-1.8 0.8+/-0.1 Kingsmill (North) -29 12.1+/-2.2 0.7+/-0.1 14.4+/-1.4 0.9+/-0.1 Williamsburg -30 13.4+/-1.0 0.8+/-0.1 11. 0+/-1. 2 0.7+/-0~1 Kingsmill (NNE) -31 14.1+/-1.9 0.9+/-0.1 12.0+/-1.2 0.7+/-0.1 Budweiser -32 16.5+/-1.3 1.0+/-0.1 15.1+/-1.9 0.9+/-0.1 Water Plant -JJ 13.3+/-1.9 0.8+/-0.1 13.1+/-1.3 0.8+/-0.1 Dow Chemical- -34 16.3+/-2.4 . 1. 0+/-0.1 14.8+/-1.5 0.9+/-0.1 Lee Hull -35 18.9+/-1.2 1. 2+/-0.1 16.5+/-1.7 1.0+/-0.1 Goose Island -36 16.1+/-1.0 1.0+/-0.1 15.6+/-1.9 1. 0+/-0.1
.Fort Eustis -37 15.9+/-0.6 1. 0+/-0.1 17.8+/-1.8 1.1+/-0.1
- Newport . News (C)Control (J .R. Bridge) -39
-38 14.6+/-1.0 15.4+/-2.2 0.9+/-0.1 0.9+/-0.1 19.5+/-2.0 15.0+/-1.5
- 1. 2+/-0.1 0.9+/-0.1
.:~tr~
(G)_Control (Benn's Church)-40 12.3+/-1.5 0.8+/-0.1 12.2+/-1.2 0. 7+/-0.1 Smithfield -41 15.1+/-1.0 0.9+/-0.1 14.9+/-1.5 0.9+/-0.1 Rushmere -42 12.9+/-1.5 0.8+/-0.1 12.9+/-2.0 0.8+/-0.1 H.oule 628 -43 17.7+/-2.1 1.1+/-0. 1 13.6+/-3.4 0.8+/-0.2 47 f ~~:
VEPCO - Surry GA.i'1HA RADIATION TOTAL mR/QTR. USING THERMOLUMINISCENT DOSIMETERS VEPCO-ENVIRONMENTAL TLD'S 1981 3rd Quarter 4th Quarter Date Annealed: 06/19/81 09/17/81 Date Read: 10/07/81 _ 0 _02/11/82 Location EmR mR/wk EmR mR/wk (C)Control (Site) -00 8.7+/-2.0 0.6+/-0.1 17.9+/-3.4 0.9+/-0.2 Surry Station -01 154.4+/-5.4 9.8+/-0.3 169.1+/-94.9 9.8+/-4.5 WNW -02 29.2+/-2.8 2.9+/-0.2 43. 7+/-21. 5 2.1+/-1.0 Discharge Canal -03 12.6+/-2.6 0.8+/-0.2 missing missing NNW -04 23.0+/-1.2 1. 5+/-0.1 34.4+/-8.7 1.6+/-0.4 North -05 19.3+/-0.9 1. 2+/-0.1 33.9+/-10.1 1. 6+/-0. 5 NNE -06 24. 1+/-1. 2 1.5+/-0.1 17.4+/-2.6 0.8+/-0.l NE -07 20.0+/-0.2 1.3+/-0.1 35.3+/-3.5 1. 7+/-0. 2 ENE -08 21.9+/-3.1 1. 4+/-0. 2 34.5+/-fi.3 1.6+/-0.3 East exclusion area -09 24.2+/-0.1 1.5+/-0.1 36.1+/-7.9 1. 7+/-0. 4 WEST -10 20.0+/-0.7 1. 3+/-0. 2 36.4+/-5.5 1. 7+/-0. 3 WSW -11 20.9+/-2.0 1. 3+/-0. 1 35~0+/-5.8 1. 7+/-0. 3 SW -12 20.5+/-0.9 1. 3+/-0.1 37.1+/-8.6 1. 8+/-0. 4 SSW -13 19.3+/-3.0 1.2+/-0.2 33.0+/-9.6 1.6+/-0.5 South -14 19.2+/-2.5 1.2+/-0.2 39.6+/-5.7 1. 9+/-0. 3 SSE -15 19.9+/-1.7 1. 3+/-0. 1 41.5+/-19.1 2.0+/-0.9 SE -16 21. 0+/-1. 6 1. 3+/-0.1 32.0+/-5.9 1.5+/-0.3 East -17 24.4+/-2.9 1.6+/-0.2 34.1+/-14.0 1. 6+/-0. 7 Intake Canal -18 15. 4+/-1. 3 1. 0+/-0. 1 27.0+/-4.6 1.3+/-0.2 Hog Island Reserve -19 15.7+/-1.5 1. 0+/-0. l 30.1+/-3.5 1. 4+/-0.,.?.
Bacons Castle -20 16.3+/-1.1 1. 0+/-0.1 27.0+/-5.1' 1.3+/-0.2 Route 633 -21 18.9+/-0.5 1. 2+/-0. 1 34. 7+/-.3.3 1. 7+/-0. 2 Alliance -22 16. 6+/-2:.. o 1. 1+/-0. l 36.8+/-18.9 1.8+/-0.9 Surry ~23 18.1+/-0.5 1.2+/-0.1 30. 7+/-1_2-. 0 1.5+/-0.6 Routes &37 & 635 -24 18.2+/-2.0 1. 2+/-0.1 31. 0+/-4. 9 1.5+/-0.2 Scotland Wharf -25 18.6+/-1.5 1. 2+/-0.1 31.8+/-6.9. 1. 5+/-0. 3 Jamestown * -26 16. 4:t2. 0 1. 0+/-0.1 32.6+/-7.4 1.6+/-0.4 Colonial Parkway (NW) -27 17.7+/-1.8 1. 1+/-0.1 27.7+/-17.1 1. 3+/-0. 8 Route 617 & 618 -28 18.4+/-2.1 1. 2+/-0. 1 29.3+/-5.8 1. 4+/-0. 3 Kingsmill (North) -29 18.0+/-1.6 1. 1+/-0.1 29.6+/-5.0 1. 4+/-0. 2 Williamsburg -30 15.7+/-0.7 1. 0+/-0.1 33.0+/-5.8 1. 6+/-0. 3 Kingsmill (NNE) -31 27.2+/-3.7 1. 7+/-0. 2 24.0+/-7.5 1.1+/-0.4 Budweiser -32 21. 1+/-1. 1 1.3+/-0.1 38. 2+/-10. 5 1. 8+/-0. 5 Water Plant -33 18.8+/-2.6 1.2+/-0.2 29.4+/-3.2 1.4+/-0.2 Dow Chemical -34 22.2+/-2.7 . 1.4+/-0.2 32.4+/-15.3 1. 5+/-0. 7 Lee Hall -35 23. 0+/-1. 5 1. 5+/-0.1 40.0+/-12.3 1.9+/-0.6 Goose Island -36 23.7+/-2.2 1.5+/-0.1 missing missing Fort Eustis -37 21.4+/-1.6 1. 4+/-0.1 34.6+/-2.0 1. 6+/-0. 1 Newport News -38 30.4+/-3.0 1. 9+/-0. 2 38.7+/-6.5 1.8+/-0 .3 -
(C)Control (J.R. Bridge) -39 19.8+/-3.6 1.3+/-0.2 33.0+/-2.9 1. 6+/-0. 1
,c)Control (Benn's Church)-40 15.7+/-0.7 1.0+/-0.1 25.1+/-15.3 1. 2+/-0. 7 Smithfield -41 19.0+/-3.8 1. 2+/-0. 2 32.3+/-2.9 1. 5+/-0.1 Rushmere -42 17.8+/-3.1 1.1+/-0. 2 29.5+/-4.0 1. 4+/-0. 2 Route 628 -43 19.e+/-2.9 1. 3+/-0. 2 28.3+/-12.5 1. 3+/-0. 6 48
- VEPCO - Surry GAHHA RADIATION TOT.t..I., mR/QTR. USING THERNOLUMINESCE~T DOSINETERS VEPCO-AREA TLD'S 19 81 1st Quarter 2nd Ouarter 3rd Quarter 4th Quarter Date Annealed: 12/23/80 03/i0/81 06/19/81 09/17/81 Date Read: 04/16/81 07 /13/81 10/06/81 02/ 11/82
- 08/05/81 Location I:mR mR/wk foR mR/wk EmR mR/wk I:mR mR/wk Control -00 5.2+/-1.4 0.3+/-0.1 6.2+/-1.0 o. 4+/-0.1 8. 0+/-1. 4 0. 5+/-0.1 18.9+/-3.7 0.9+/-0.2 Training Center -01 11.7+/-0.6 0.7+/-0.1 11. 4+/-1. 3 0.7+/-0.1 12.3+/-2.4 1.1+/-0.2 28.7+/-1.6 1.4+/-0.1 Admin Bldg Entrance-02 missing missing 19.5+/-2.0 1.2+/-0.1 25.0+/-1.1 1. 6+/-0. l 43.8+/-9.1 2.1+/-0.4 Admin Bldg Recep -03 25.9+/-3.6 1.6+/-0.2 29.2+/-7.0 1. 8+/-0. 4 39. 9+/-1. 2 2.6+/-0.1 53,4+/-8,6 2.5+/-0.4" Admin Bldg Kitchen -04 18.1+/-3.6 1.1+/-0.2 20.4+/-2.3 1.2+/-0.1 26.4+/-1.5 1. 7+/-0.1 37.6+/-2.7 1. S+/-O. l Admin Bldg (Men) -05 21.9+/-3.4 1. 3+/-0. 2 26.8+/-2.7 1. 6+/-0. 2 32.1+/-0.3 2.1+/-0.1 L;7.G+/-7.l 2.3+/-0.3
.,... Admin Bldg Conf -06 19.3+/-2.9 1.2+/-0.2 29. 1+/-3.4 1. 5:!:0. 2 29.2+/-0.0 1. 9+/-0. 0 35.1+/-3.7 1.7+/-0.2
'° Cafeteria -07 19.2+/-2.7 1. 2+/-0. 2 23.4+/-2.4
- 1. 4+/-0.1 31.0+/-2.1 2.0+/-0.1 43.9+/-3.8 2. 1+/-0. 2 Maintenance Shop -08 19.0+/-2.9 1. 2+/-0. 2 22.0+/-3.4 1. 3+/-0. 2 26.1+/-0.8 1. 7+/-0. l 42.1+/-5.1 2.0+/-0.2 Storeroom East End -09 20.1+/-0.4 1. 2+/-0.1 23.2+/-2.4 1. 4+/-0. 2 20.5+/-0.8 1.8+/-0.l 45.8+/-4.6 2.2+/-0.2 Storeroom West End -10 13.8+/-1.7 0.8+/-1.3 17.4+/-1.7 1.1+/-0.1 23.6+/-1.4 1. 5+/-0.1
- 44. 2+/-21. 0 2.1+/-1.0 Control Room East -11 12.3+/-0.5 0.8+/-0.1 12.5+/-1.3 0.8+/-0.1 17.0+/-1.3 1. 1+/-0.1 35.8+/-9.1 1.7+/-0.4 Control Room West -12 7 .6+/-1.0 0,5+/-0.1 9. 5+/-1. O 0.6+/-0.1 10.1+/-1.6 0.6+/-0.1 27.0+/-6.0 1. 3+/-0. 3 Intrument Shop -13 287.8+/-20.7 17.7+/-1.3 302+/-30 18. 4+/-1. 8 350.6+/-6.2 22.5+/-0.4 462.1+/-54.6 22.0+/-2.6 Clean Change Room -14 30.1+/-2.5 1. 8+/-0.1 39.2+/-3.9 2.4+/-0.2 48.0+/-3.3 3.1+/-0.2 87.3+/-11.l 4.2+/-0.5 Security Bldg. -15 24.5+/-3.1 1. 5+/-0. 2 27.9+/-2.8 1.7+/-0.2 42.4+/-0.6 2.7+/-0.1 71. 3+/-L1. 2 3.4+/-0.2 East Fence -16 62.0+/-5.6 3.0+/-0.3 66.4+/-8.6 4.1+/-0.5 45. 0+/-1.1 2.9+/-0.1 112.!;+/-13.8 5. L1+/-0, 6
VEPCO - Surry GROSS BETA DEPOSITION AND TRITIUM CONCENTRATIONS IN PRECIPITATION SAMPLES (Monthly Collections)
Surry Station (I) . Newport News (C)
Collection Gross 8 Gross 8 Tritium Gross 8 Gross 8 Triti~
Period pCi/1 nCi/m 2 pCi/1 pCi/1 nCi/m 2 pCi/1 January 23.9+/-2.4 2.1+/-0.2 <soo 7.7+/-2.5 0.6+/-0.2 <soo February 23.0+/-2.0. 0.3+/-0.1 <SOO 13.0+/-2.0 0.2+/-0.1 <5oo March 39.0+/-4.0 0.6+/-0.1 500+/-400 20.0+/-2.0 0.3+/-0.1 400+/-400 April 36.0+/-3.0 1. 7+/-0. 2 680+/-310 15.0+/-2.0 1. 2+/-0. 1
- 820+/-310 May 38.4+/-6.1 0.6+/-0.l <SOO 16.0+/-4.5 0.2+/-0.1 <5oo June 5.0+/-2.0 0.1+/-0.l 550+/-370 7.0+/-2.0 0.1+/-0.1 380+/-180 July 29.0+/-3.0 1. 2+/-0.1 600+/-400 4. 0+/-1. 0 0.13+/-0. 01 <SOO August 7.0+/-2.0 0.4+/-0.1 530+/-390 5.0+/-2.0 0.5+/-0.2 640+/-390 September 10.0+/-2.0 0.3+/-0.1 <SOO <5.o <0.2 <500 October 5.0+/-2.0 0.1+/-0.1 (500 5.0+/-2.0 0.1+/-0.1 <5oo November 9.0+/-2.0 0.3+/-0.1 1500+/-400 3.0+/-1.0 0.1+/-0.1 500+/-300 December 4.0+/-1.0 0.3+/-0.1 <500 3. 0+/-1. 0 0.3+/-0.l (500 GROSS BETA DEPOSITION AND TRITIUM CONCENTRATIONS IN PRECIPITATION SAMPLES (Quarterly *composites of Monthly.Collections)
Surr:zi: Station (I) Newport News (C)
I Collection Gros8 8 Gross S Tritium Gross S Gross 8 TritiU:::
Period pCi/1 nCi/m 2 pCi/1 pCi/1 nCi/m 2 ~
1st Quarter 25.9+/-2.6 0.387+/-0.039 260+/-100 29.3+/-3.3 0.370+/-0.042 250+/-100 2nd Quarter 16.0+/-2.0 0.230+/-0.020 5~0+/-370 10. 0+/-2. 0 0.120+/-0.010 600+/-370 3rd Quarter 15.0+/-2.0 2.0+/-0.3 400+/-150 (5.0 <0.6 240+/-150 4th Quarter 5.0+/-1.0 0.650+/-0.210 370+/-90 2. 0+/-1. 0 0.250+/-0.160 350+/-110 so
VEl'CU - Surry RADIOACTIVITY IN MILK SAMPLES (Monthly Collections)
(I) Bacon 1 s Castle (EPPS) - State Split Samples Collection ECi/1 as of collection date g/1 ..
Date I-131 Sr-89 Sr-90 Cs-137 Ba-La-140 *Stable Ca 01/12/81 <l <5 <2 <15 <15 1.5 02/08/81 <l <5 4+/-2 <15 <15 1.0 03/02/81 <l <5 3+/-1 <15 <15 1.2 04/06/81 <l <5 4+/-1 <15 <15 1.6 05/04/81 <l <5 7+/-2 <15 <15 0.9 06/01/81 <l <5 <2 <15 <15 1.1 07/07/81 <l <5 9+/-3 <15 <15 1.0 08/04/81 <l <5 1+/-1 <15 <15 1.0 08/31/81 <1 <5 5+/-2 <15 <15 0.8 10/05/81 <l <5 <2 <15 <15 1.1 11/10/81 <l <5 <2 <15 <15 1. 0 li/30/81 <2.8(a) <5 <2 <15 (15 0.9 (I) Bacon's Castle (Judkins) pCi/1 as of collection date g/1 I-131 Sr-89 Sr-90 Cs-137 Ba-La-140 Stable Ca t
01/15/81 <l <5 3+/-1 <15 (15 1. 0 02/10/81 <l <5 2+/-1 <15 <15 1.0
- ~,"
03/17/81- <l <5 2::1 <15 (15 0.6 04/14/81 <l <5 7+/-1 (15 (15 0.6 05/13/81 <l <5 5+/-3 <15 <15 1.1 06/09/81 <l (5 6+/-1 <15 <15 1.1 07/14/81 <l <5 5+/-1 <15 <15 1.0 08/13/81 <1 <5 5+/-1 <15 <15 0.9 09/08/81 <l <5 5+/-2 <15 (15 1. 2 10/13/81 (1 (5 <2 <15 <15 0.9 11/10/81 <l <5 2+/-1 <15 <15 0.8 12/1'1/81 <l .<5 <2 <15 <15 1. 2 (a) Lower sensitivity due to length of time (23 days) between collection and receipt of sample at EIC.
51
:~
VEPCO - Surry RADIOACTIVITY IN MlLK SAMPLES (Monthly Collections)
(C) *smithfield (Gwaltne)'.:)
Collection p_Ci/1 as of collection date g_/1 Date I-131 Sr-89 Sr-90 Cs-137 Ba-La-140 Stable Ca 01/21/81 <l <S 3+/-2 <15 <15~ 1. 3 02/17/81 <l <S 3+/-1 <15 (15 1. 6 03/24/81 <l <s 5+/-2 <15 <15 1. 4 04/21/81 <1 <S 5+/-1 <15 (15 1.0 05/26/81 <l <S 8+/-2 (15 <15 0.7 06/16/81 (a) <S 1+/-1 (15 <15 0.8 07/21/81 <l <S 5+/-1 <15 <15 1.1 08/18/81 <l <S 3+/-1 <15 <15 0.9 09/15/81 <l <S 2+/-1 <15 <15 0.8 10/20/81 (l <5 <2 <15 <15 0.7 11/17/81 1. 7 (b) <S 2+/-1 <15 <15 0.9 12/15/81 <l <S 1 +/-1 <15 <15 0.6 (I) Colonial Parkwai (Smith) p_Ci/1 as of collection date g/1 I-131 Sr-89 Sr-90 Cs-137 Ba-La-140 Stable Ca 01/15/81 <l <5 5+/-1 (15 (15 1. 4 02/10/81 <l <S 5+/-2 <15 <15 0.8 03/24/81 <l <5 3+/-2 <15 <15 0.9 04/21/81 <l <5 3+/-1 <15 (15 1.0 05/13/81 <l (5 4+/-2 (15 <15 1.2 06/09/81 (1 (5 4+/-1 <15 (15 1.1 07/14/81 <l <5 4+/-1 (15 <15 0.9 08/11/81 (l (5 5+/-1 <15 <15 1.0 09/08/81 (l (5 5+/-1 <15 <15 0.9 10/13/81 (1 (5 6+/-1 <IS (15 1.0 11/10/81 <l <S 3+/-1 <15 <15 0.9 12/22/81 <1 (5 4+/-1 <15 <15 1.1 (a) Sample lost in processing.
. (b) Lower sensitivity due to low chemical yield .
52
VEPCO - Surry RADIOACTIVI'l'Y IN MILK SAMPLES (Monthly Collections)
(I) Lee Hall (Ross) - State Se lit Sameles Collection eCi/1 as of collection date
. Date g/1*
l-131 Sr-89 Sr-90 Cs-137 Ba-La-140 Stable Ca 01/12/81 <l <5 (2 (15 (15 1. 2 02/Q8/81 <l <s 4+/-2 <15 <15 0.8 03/G2/81 <1 <5 2+/-1 <15 (15 1.5 04/06/81 <l <5 1+/-1 <15 05/04/81 <15 1.3
<1 <5 3+/-1 (15 <15 06/01/81 0.8
<l <5 4+/-1 <15 <15 1.0 07/07/81 <I <5 <2 <15 <15 0.9 08/04/81 <I <5 2+/-1 <15 <15 1.0 08/31/81 <1 <5 5+/-1 <15 <15 0.9 10/05/81 <I <5 5+/-1 <15 <15 11/09/81 1.0
<1 <5 <2 <15 <15 0.3 11/30/81 <3.1 (a) <5 <2 <15 <15 0.9 (a) Lower sensitivity due to length of time (23 days) between collection and receipt of sample at EIC.
53
VEPCO - Surry GAH~L.\. EMITERS IN J~!ES RIVER WATER SAfPLES
.1 1 i 'I/. I (Bimonthly Collections)
Month Ci/1 Collected Ba-La-140 Cs-134 Cs-137 Zr-Nb-95 Co-58 Hn-54 Zn-65 Co-60 Fe-59 CHICKAHOMINY (C)
January <15 <15 <15 <10 <15 <15 <30 <15 <30 March <15 <15 <15 <10 <15 <15 <30 <15 <30 May <15 <15 <15 <10 <15 <15 <30 <15 <30 July* <15 <15 <15 <10 <15 <15 <30 <15 <30 September (a) <15 <15 <15 <10 <15 <15 <30 (15 <30 November <15 <15 <15 <10 <15 <15 <30 <15 <30 lJ1
.i:-
HOG ISLAND POINT (I)
January <15 <15 <15 <10 <15 <15 <30 <15 <30 March (15 <15 <15 <10 <15 <15 00 (15 <30 May <15 <15 <15 <10 <15 <15 <30 <15 <30 July <15 <15 <15 <10 <15 <15 <30 <15 <30 September <15 <15 <15 (10 (15 (15 (30 <15 00
- November <'is <15 (15 (10 <15 <15 (3() <15 00 NEWPORT NEWS (I)
January (15 <15 <15 <10 <15 <15 <30 <15 <30 March <15 (15 <15 <10 <15 <15 00 <15 00 Hay *
<15 <15 <15 <10 <15 <15 00 (15 <30 July <15 <15 <15 <10 <15 <15. 00 <15 00 September <15 <15 qs <10 <15 <15 00 <15 00 November (15 (15 (15 <10 <15 <15 <30 <15 .<30
\
\ c... ) r... -\1.,,- '.1\ *** ,
'-.i~r~.1ii&~~~~t* tury FLU. &StlfJ!l.i'e Qi "'Iii,,_ "-"ll'.itP*tJBw.<fl-
/s(!-:*~~\ .: ..- ::.iJ:-.. *~~jg~-.:;:/'.\-~*\.\( - ;1;
- -......~ _ ,........
_...........- * ............1111 ,."l-"'il"'""'".!l!?ll~:~
i:.: ,: .; : .,
VEPCO -Surry i,'
- G~~L.\ EMITTERS IN J~!ES RIVER WATER SAMPLES (Bimonthly Collections)
Nonth Ci/1 Collected .I Ba-La-140 Cs-134 Cs-137 Zr-Nb-95 Co-58 Mn-54 Zn-65 Co-60 Fe-59 11 *;;
- STATION !~TAKE (I)
January <15 <15 <15 <10 <15 <ls <30 <15 <30 March <15 <15 <15 <10 <15 <15 <30 .(15 <30 May <15 <15 <15 <10 <15 <15 <30 <15 (30 July <15 <15 (15 <10 <15 <15 <30 <15 <30 September (a) <15 (15 <15 (10 (15 <15 <30 (15 <30 November <15 <15 <15 (10 * <15 <15 <30 (15 <30 V1 V1 STATION DISCHARGE (I)
January (15 <15 <15 <10 <15 (15 <30 - <15 <30 March <15 <1.5 <15 <10 <15 <15 00 <15 <30 May <15 <15 <15 <10 <15 <15 <30 <15 <30 July_ <15 <15 <15 <10 <15 <15 <30 <15 <30 September <15 <15 <15 <10 <15 <15 <30 <15 <30 November <15 <15 <15 <10 <15 <15 <30 <15 <30 (a) Ce-141 = 18+/-16.
. "~i ;,.*,;;:fij~lt~iW}t:iJ~*: ::. :
VEPCO - Surry
, RADIOACTIVITY in .JAMES RIVER HATER
-STATE SPLIT S~WLES-Ci/1
}:n-54 Co-58-60 Cs-134-137 Zn-65 Collection Date Sr-89 Sr-90 Tritium Zr-Nb-95 Ba-La-140 Fe-59 Station Discharge 01/06/81 <5 <2 990+/-430 <10 <15 00 02/03/81 <5 <2 <SOO <10 <15 00 03/02/81 <5 <2 <500 '<10 <15 00 04/06/81 <5 2+/-1 <soo <10 <15 00 05/04/81 <5 <2 <500 <10 <15 00 06/02/81 <5 <2 500+/-300 <10 <15 <30 07/07/81 <5 <2 <500 <10 <15 00 07/81 <5 <2 <500 <10 <15 00 V, 08/81 <5 <2 850+/-390 (10 <15 00 (J'\
09/81 <5 <2 <5oo <10 <15 00 10/81 <5 <2 (500 <10 <15 00 12/14/81 <5 <2 1000+/-lf00 (10 <15 00 12/81 <5 <2 9,00+/-300 (10 (15 00 Scotland Wharf 01/06/81 <5 <2 510+/-480 <10 <15 00 02/03/81 <5 <2 <5oo <10 <15 00 03/02/81 <5 <2 <500 (10 <15 <30 04/06/81 <5 <2 <500 <10. <15 <30 05/04/81 <5 1+/-1 <5oo (10 <15 : It; 00 06/02/81 <5 <2 500+/-300 <10 <15 I
'I'
',* I 00 07/07/81 <5 ' <2 <5oo <10 <15 00 07/81 <5 <2 <500 <10 <15 00 08/81 <5 <2 530+/-390 (10 <15 <30 09/81 (5 <2 (500 <10 <15 <30 10/81 <5 <2 (500 <10 (15 <30 12/14/81 <5 <2 600+/-400 - <10 <15 <30
<2 1700+/-400 <10 <15 (30 12/81 <5
VEPCO - Surry TRITIUM IN JAMES RIVER WATER SA..'fi>LES .
(Semiannual-Composites of Bimonthly Samples) pCi/1 Sample Location 1st h:11f 1981 2nd half 1981 CH <330 (330 NN 260+/-90 480+/-140 57
. .: ', '.*.t~
VEPCO - Surry GAMMA EMITTERS IN CLAM SAMPLES (Bi-Monthly Collections)
Sample Month . ECi/kg Wet Weight Site Collected Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-134 Cs-1)7 .. ' ..
CHICKAHOMINY January <130 <260 <130 <130 <260 (130 <130 (C) March <130 <260 <130 <130 <260 <130 <130 May <130 <260 <130 (130 (260 (130 <130 July <130 (260 <130 (130 (260 <130 <130 ...
September <130 (260 (130 (130 (260 (130 <130 November (130 <260 <130 <130 <260 <130 (130 LAWNES CREEK January <130 <260 <130 (130 <260 (130 <130 (I) March <130 <260 (130 <130 (260 (130 (130 ::-
May <130 <260 <130 <130 <260 <130 <130 July (130 (260 (130 <130' (260 <130 <130 ,:~;
September <130 <260 <130 <130 (260 (130 <130 November (130 (260 <130 (130 (260 (130 (130 JAMESTOWN January <130 (260 (130 <130 <260 (130 <130 l' (I) March <130 <260 (130 (130 (260 (130 <130 May (130 <260 <130 <130 (260 <130 (130 July <130 (260 <130 (130 <260 (130 (130
-. Scpu~mber <130 <260 <130 <130 <260 <130 (130 I November <130 <260 <130 <130 <260 <130 (130 .
HOG ISLAND POINT January (130 <260 (130 (130 (260 (130 (130 (I) March <130 <260 (130 210+/-40 <260* (130 * (130 May <130 (260 <130 (130 <260 (130 (130
- July (130 <260 <130 <130 (260 <130 (130 September <130 (260 <130 (130 (260 <130 (130 November <130 (260 <130 (130 (260 (130 (130 STATION January <130 (260 <130 <130 (26.0 (130 (130 DISCIIARCE M.1rch (See State Split results next page)
(I) May (See State Split results next page)
July (See State Split results next page)
September (See State Split results next page)
, November * (See State Split results next page) 58
VEPCO - Surry GAMNA EMITTERS IN CLAM SAMPLES State Split Samples from Station Discharge .
Month :eCi/kg Wet.
Collected Mn-54 Fe-59 Co-58 Co-60 Zn-65
- -- Cs-134 Cs-137 March <130 <260 <130 <130 <260 <130 <130 May <130 <260 <130 <130 (260 <130 <130 July (130 <260 <130 <130 (260 <130 <130 September <130 <260 <130 <130 (260 (130 (130 November <130 <260 (130 <130 (260 (130 <130 Strontium-89 and Strontium-90 in Clams (State Split Samples from Station Discharge)
Collection pCi/kg Wet Weight Date Sr-89 Sr-90 March (20 50+/-10 May (20
- 30+/-10 July <20 <10 September (20 <10 November <20 (30(a)
(a) Insufficient sample for more sensitive analysis.
59
~!:.
VEPCO - Surry GAMMA EMITTERS IN OYSTER SAMPLES (Bi-Monthly Collections)
Month ECi/kg Wet Weight Location Collected Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-134 Cs-137 Deep Water January <130 <260 <130 (130 (260 <130 <130 Shoal March <130 (260 (130 <130 <260 (130 <130 (I) May (130 <260 (130 <130 <260 (130 <130 July <130 (260 (130 <130 <260 <130 <130 September <130 <260 (130 <130 (260 <130 <130 November (130 (260 (130 <130 (260 (130 (130 Point of January (130 (260 (130 (130 (260 <130 <130 f
Shoal March <130 <260 (130 <130 (260 (130 (130 (I) May (130 <260 (130 (130 (260 (130 (130 l July (130 (260 <130 <130 (260 (130 <130 September (130 <260 (130 <130 (260 (130 (130 November <130 (260 (130 (130 <260 (130 . (130 Newport February (130 (260 (130 *<130 <260 <130 (130 News March <130 (260 <130 <130 (260 (130 (130 (I) May <130 <260 (130 <130 <260 <130 <130 July <130 <260 (130 *<130 <260 (130 <130 September <130 <260 (130 (130 <260 (130 (130 November <130 (260 (130 (130 (260 <130 (130 "I
60 tl l
Vl~l'CO - Surry GAMMA EMITTERS IN FISH SA.l-WLES COLLECTED IN THE VICINITY OF SURRY STATION (I)
(Semi-Annual Collection)
Collection .Sample J:!Ci/kg Wet Weight Date Type- Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-134 Cs-137
.02/20/81 Catfish <130 <260 <130 (130 (260 <130 <130 White <130 (260 <130 <130 <260 <130 (130 perch .
08/81 Catfish <130 <260 (130 (130 <260 (130 <130 perch (130 (260 (130 <130 <260 <130 (130
-. GAMMA EMITTERS IN CRAB SAMPLES COLLECTED IN THE VICINITY OF SURRY STATION .(I)
(July, August, September Collection)
Month pCi/kg Wet Weight Collected Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-134 Cs-137 July (130 (260 (130 <130 (260 (130 <130 August .<130 .(260 (130 <130 (260 (130 (130 September <130 (260 <130 (130 (260 <130 <130 61
VEPCO - Surry GAi.'1MA EMITTERS in SILT SAMPLES (Semiannual Collections)
Collection Period: 03/25-31/81 pCi/kg drl Collection Site Cs-134 Cs-137 Co-60 (C) Chickahominy * <150 850+/-160 <150 (I) Station Discharge <150 810+/-150 960+/-220 (I} Hog Island Point 270+/-70 200+/-100 100+/-100 (I) Station Intake 220+/-50 540+/-70 710+/-80 (I) Point of Shoals <150 890+/-160 <150 (I) Newport News <150 <150 <150 Collection Period: 05/05/81
- Discharge Canal (state split) <150 <150 <150 Collection Period: 09/18-22/81 ' *~ .
- eCi/kg drz'.
Collection Site Cs-134 Cs-137 Co-60 Zr-95 Nb-95 Co-58 Mn-54 (C) Chickahominy <150 760+/-80 <150 <150 <150 <150 <150 (I) Station Discharge 690+/-80 1750+/-180 3190+/-320 550+/-150 190+/-50 290+/-60 140+/-50 (I) Hog Island Point 280+/-40 700+/-80 650+/-80 <150 <150 <150 <150 (I) Station Intake 210+/-40 770+/-80 430+/-70 390+/-120 270+/-50 - <150 <150 (I) Point of Shoals <150 910+/-90 <150 <150 <150 <150 (150 (I) Newport News (150 390+/-50 140+/-30 <150 <ISO <150 <150 Collection Period: 11/12-19/81 pCi/kg dry Collection Site Cs-134 Cs-137 Co-58 C:o-60 Upstream Discharge Canal 490+/-90 1620+/-160 230+/-90 <150 Discharge Canal 640+/-90 1900+/-190 130+/-50 <150 In°f.1kc Canal (11 / 12) 240+/-20 830+/-80 <150 410+/-40 Intake Canal (11/19) 250+/-30 1010+/-100 <150 340+/-30 62 1*
VEPCO - Surry GAMMA EMITTERS IN SOIL SAMPLES (Annual Collection)
Samples Collected: 08/04/81 pCi/kg Location Cs-134 Cs-137 ss <150 <150 BC <150* 1600+/-200 ALL <150 130+/-20 CP <150 750+/-80 DOW <150 360+/-40 FE <150 <150 GAMMA EMITTERS IN FOWL (Semi-Annual Collections)
'f Collection Area Month Collected Sample Type Cs-134 pCi/kg Cs-137 HIP March Coot <SO <80 HIP September Goose <so <SO 1
RADIOACTIVITY IN FOOD CROPS (Annual Collection)
State Split Samples Date pC{/kg 2 Wet Weight Collected Farm Type Cs-134 Cs-137 Sr-89 Sr-90 05/26/81 Poole kale (80 <SO (20 310+/-20 06/29/81 Carters Grove cabbage <SO (80 <20 50+/-10 10/04/81 Slades Peanuts (80 <so <30(a) 60:!:20
- 10/04/81 Slades Corn <SO <so <20 <10 10/04/81 Slades Soybeans <SO <so <20 100+/-20 10/04/81 Brocks Peanuts <SO <so (20 100+/-10 II 10/04/81 Brocks Corn <BO <BO <20 <10 11/17 /81 Brocks Soybean <SO <so <20 130+/-20 (a) Lower sensitivity due to low chemical yield ..
63
.. - ---**-*** **-- --.. - - - ... ~-.,_ ... - ---. *-*-.*-* .-<::*- .,.-_-,-~.-...._ .*. . . . . c *** , . --.;, 7*'
VEPCO - Surry RADIOACTIVITY IN WELL WATER SAMPLES (Semi-Annual Collections) 1st Half Coll. 04/14/81 2nd Half Coll. 10/06/81 ECi/1 ECi/1, Gross a Gross B Tritium* Gross a Gross B Tritium*
(I)Surry Station (1 6+/-2 <330 <1 6+/-2 (330 (l)Hog Island Res.* (1 4+/-2 <330 <l 4+/-2 <330
(!)Bacon's Castle 4+/-1 8+/-2 (330 2+/-1 8+/-2 <330
.* I (C)Jamestown (1 4+/-2 260+/-110 (1 9+/-2 (330
- Tritium Analyzed by enrichment method.
'\
I I*
. RADIOACTIVITY IN SURFACE WATER SAMPLES (Semi-Annual Collections) 1st Half Coll. 04/14/81 2nd Half Coll. 10/06/81 eCi/1 eCi/1 Gross u Gross (1 Tritium* Gross u Gross (l Tritiun~
(I)Chippokes Creek (1 4+/-2 430+/-300 2+/-1 7-r2 (500 (I)Wi 1 Uamsburg Re!;crvc 1+/-1 (2 550;t310 13+/-2 21+/-2 (500
.(!)Newport News Reservt! 1+/-1 3+/-2 480+/-300 2+/-1 13+/-2 (500 (C)Smi thficld <l 7+/-2 350+/-300 4+/-1 8+/-2 (500
- Tritium Analyzed by direct L. S. Counting
- 64
SECTION 6 QUALITY ASSURANCE DATA
,. L J
('
65
-'.,'r ENVIRONMENTAL QUALITY CONTROL ANALYSES
SUMMARY
1981 The tables below summarize results of samples run for process quality
-control purposes during the subject month. These listings are in add-ition to such measurements as detector backgrounds, check source values, I>:
,."*:,tont radionietric-gravimetric comparisons, system calibrations, etc. Detailed listings of .each measurement are maintained at the laboratory and are iceml:
available for inspection if required. ~ecem
.. ;Jecem
" BLANK SAMPLES Nuclide Nu111ber of Number of analyses exceeding uCcc111 Analyzed Ue tcrmina tions the LLD for that analysis !anua
. lanua Gross beta 46 l* lanua Gross alpha 47 0 Janua Strontium-89 95 0 Janua Strontium-90 95 0 Janua Tritium 61 l* Janua Ganuua emitter 64 0 Janua Iodine-131 191 0 Jilnua Calcium-45 3 0 Jimua:1 F_cbru:
SPLIT SAMPLES ~l!bruJ
,1 Nuclide Number of No. agreeing No. agreeing No. differing
°Febru Det'ns _3<1 ____.
~ebru
.. Anal~ed_ within 2<1 within Jo ~
- --*--*-*--. ---* Jebrn Gross beta 142 138 4 0 'i~brJ Gross alpha 39 38 1 0 febrJ Gamma emitters 126 122 4 0 l!arcl Iodine-131 146 146 0 0 !lard Strontium-89 38 38 0 0 !lard Strontium-90 44. 42 2 0 Harer Tritium 89 89 0 0 llarcl Calcium-45 8 8 0 0 , llarc1 Uranium 71 71 0 0 Apr i:
- Apri:
SPIKED SAMPLES . Apri:
,\pri Nuclide No. of Within 2o Within 3a differing from Apri Analyzed Det' ns of known of known known by> 30' Apri
- . Apri Gross beta 55 53 1 l*
- Apr-Gamma emitters 44 43 1 0 Hay Iodine-131 11 11 0 0 May Strontium-89 18 18 0 0 !1ay Strontiurn-90 Trftium 94 45 93 44 1
1 0
0 I Hay
!-lay
{ }lay
- *W
- Corrective actions were taken to eliminate the problem. t 3
66 ll
.I
./!
__.A**'**.
EPA INTEKCOMPARISON RESULTS 1981 Control MWF Sample Ar,ency Limits Measured
- rypc Analysis Value (3o,n=3) +/-2cr error* Units
- ~-
-en1ber 1980 Eater Iodine-131 22 6 17+/-2 pCi/liter
- i;"' Water
,.;celllber 1980 Tritium 2240 604 2600+/-300 pCi/liter
~.:.:ember . .J..980 Air Filter Gross Alpha 21 9.1 21+/-2.. pCi/filter
- ....-e111ber
~
1980 Air Filter Gross Beta 19 8.7 28+/-3 pCi/filter
- ll.....:emb e r 1980 Air Filter Strontium-90 0 0 LT 1 pCi/filter
- ...*l!Jubcr 1980 1981 Air Filter Water Cesium-137 Gross Alpha 19 9
8.7 8.7 19+/-2 10+/-1 pCi/filter pCi/li ter
~11 uary
- .-nuary 1981 Water Gross Beta 44 8.7 43+/-4 pCi/liter
- Jluary 1981 Water Strontium-89 16 8.7 LT 5 pCi/liter
µiuary 1981 \Jnter Strontium-90 34 2.9 35+/-4 pCi/liter
,.;.:1uary 1981 Milk Strontium-89 0 0 LT 2 pCi/liter
- nuary 1981 Milk Strontium-90 20.2 2.6 14+/-1 pCi/liter
- .nuary 1981 Milk Iodine-131 25.8 10.4 29+/-3 pCi/liter
~nuary 1981 Milk Cesium-137 43.5 8.7 47+/-5 pCi/liter
..:.ouary 1981 Milk Barium-140 0 0 LT 25 pCi/liter
- ,.nuary 1.,-bru..iry 1981
!.,;bruury 1981 t;~ruary 1981 1981 Milk Water Water Water Potassium Tritium Chromium-51 Cobalt-60 1551 1760 0
25 134 590 8.7 0
1350+/-140 1680+/-170 LT 100 29+/-5 pCi/liter pCi/liter pCi/liter pCi/liter
'.;~ruary 1981 Water Zinc-65 85 8.7 92+/-9 pCi/liter
\.~'::~\"°" .t:~ruary 1981 Water Ruthcnium-106 0 0 LT 100 pCi/liter
!.~bruury 1981 Water Cesium-134 36 8.7 29+/-5 pCi/liter t;~ruary 1981 Water Cesium-137 4 8.7 9+/-3 pCi/liter
.!mh 1981 Water Gross Beta 25 8.7 27+/-3 pCi/liter trch 1981 Water Gross Alpha 25 10.4 20+/-2 pCi/liter W'ch 1981 Air Filter Gross Alpha 30 13 30+/-3 pCi/filter
- ~rch 1981 Air Filter Gross Beta 50 8.7 66+/-7 pCi/ filter*.
1:::ch 1981 Air Filter Strontium-90 18 2.6 17+/-4* pCi/filter
- \:rch 1981 Air Filter Cesium-137 14 8.7 15+/-2 pCi/filter
~rll 1981 Water Tritium 2710 615 3000+/-300 pCi/liter 1rn 1981 *Water ,Cesium-134 10 8.7 7+/-2 pCi/liter inl 1981 Water Cesium-137 15 8.7 13+/-1 pCi/liter
,,~-:il 1981 Water Strontium-89 38 8.7 35+/-7 pCi/liter
... ,, FTil 1981 Water Strontium-90 28 2.6 24+/-3 pCi/liter
_'?ril 1981. Water Radium-226 15.0 4.0 13.2+/-1.3 pCi/liter
~.n 1981 Water Radium-228 12.0 3.1 10+/-2 pCi/liter
?:U 1981 Water Uranium 12 10 6+/-2 pCi/liter
~ 1981 Water Strontium-89 36 8.7 29+/-3 pCi/liter
\7 1981 Water Strontium-90 22 2.6 26+/-3 pCi/liter
'I
- -' \.1 1981 1981 Water Water Strontium-89 Strontium-90 25 11 8.7 3.6 30+/-8 14+/-2 pCi/liter pCi/liter
.. -- "t-, 1981 Water Iodine-131 26 10 40+/-20 pCi/liter
._., '~ "\
f1 1981 Water Cesium-137 22 8.7 20+/-5 pCi/liter
- *~
.-, !en analyses of a particular type result in concentrations below the detection limits,
-.: term "LT" is used to indicate "Less Than" values for that measurement based on
-* (_99. 5%) confidence level.
67
- ;;/'
~;fj
~j~
-:~
,ir EPA INTERCOMP.AllISON RESULTS 1981 Control MWF Sample Agency Limits Measured I*
Month/Year Type Analysis Value (3 a, n== ) +/-7.a error Units May 1981 Water Bar:J.um-140 0 0 LT 20 pCi/lit, May 1981 Water Potassium 1559 135 1400+/-14o' mg/lit,
'I June 1981 Water Chrornium-51 0 0 LT 20 pCi/lit1 June 1981 Water Cobalt-60 17 8.7 16+/-2 pCi/lit,1 June 1981 Water Zinc-65 0 0 LT 20 pCi/liti Ju1w 1981 Water Ruthenium-106 15 8.7 13+/-4 pCi/litE June 1981 Water Cesium-134 21 8.7 13+/-2 pCi/litc June 1981 Water Cesium-137 31 8.7 25+/-3 pCi/litf June 1981 Water
- Tritium 1950 596 2300+/-200 pCi/litt June 1981 Water Radium-226 6.7 1. 7 5.9+/-0.4 pCi/lite June 1981 Water Radium-228 8.0 2.1 10. 6+/-1. 6 pCi/lite June 1981 Air filter Gross alpha 28 12 31+/-6 pCi/filt June 1981 Air filter Gross beta 54 8.7 74+/-8 pCi/filt June 1981 Air filter Strontium-90 19 2.6 21+/-5 pCi/filt June 1981 Air filter Cesium-137 16 8:7 15+/-2 pCi/filt:.
July 1981 Food Strontium-89 44 8.7 38+/-4 pCi/kilc July 1981 Food Strontiurn-90 31 2.8 28+/-3 pCi/kilc July 1981 Food Iodine-131 82 14 75+/-8 pCi/kilc July 1981 Food Cesium-137 45 8.7 40+/-4 pCi/kilo July 1981 Food Bariurn-140 0 0 (25 pCi/kilo July 1981 Food Potassium 2640 229 2267+/-227 mg/kilo~
July 1981 Milk Strontium-89 25 8.7 13+/-3 pCi/lit July 1981 Milk Strontium-90 17 2.6 16+/-3 pCi/lite July 1981 Milk Iodine-131 0 0 (5 pCi/lite July 1981 Milk Cesium-137 31 8.7 3'5+/-12 pCi/lite July 1981 Milk Bariurn-140 0 0 (16 pCi/lite July 1981 Milk Potassium 1600 139 1463+/-305 mg/liter August 1981 Water Iodine-131 73 13 53+/-li pCi/litei
/\u:.:,ust 1981 Water Tritium 2630 613 2973+/-878 pCi/litei August 1981 Water Uranium 23 10 14+/-2 pCi/lite:
September 1981 Water Strontium...:89 23 8.7 18+/-5 pCi/lite:
September 1981 Water Strontium-90 11 2.6 14+/-2 pCi/lite:
September 1981 Urine Tritium 2050 599 2166+/-624 pCi/lite:
September 1981 Water Radium-226 8.3 2.2 8.4+/-0.8 pCi/litei September 1981 Water Radium-228 11. 7 3.0 4.6+/-3.7 pCi/litei September 1981 Water Gross alpha 33 4 .32+/-14 pCi/lite September 1981 Water Gross beta 28 8.7 30+/-6 pCi/lite1 September 1981 Air filter Gross alpha 25 11 25+/-6 pCi/filt<
September 1981 Air filter Gross beta 52 8.7 71+/-7 pCi/filtE September 1981 Air filter Strontium-90 16 2.6 18+/-2 pCi/filt<
September 1981 Air filter Cesium-137 19 8.7 20+/-2 pCi/filt
,~i),'L~.
- _~,/~:~~ 68
- ~
- .'* <-~
~ _,~-.~---~
EPA INTERCOMPARISON RESULTS 1981 Control MWF Sample Agency Limits Measured Month/Year T:t:ee Analysis Value Pcrzn= ) +/-'J.a error Units ober 1981 Water Gross alpha 80 35 91+/-26 pCi/liter obeT. 1981 Water Gross beta 96 8.7 112+/-11 uCi/liter obe'r 1981 Water Cobalt-60 0 0 LT 5 pCi/liter ober 1981 Water Strontium-89 21 8.7 13+/-6 pCi/liter 1981 Water Strontium-90 14.4 2.6 14.6+/-2.0 pCi/liter ober 1931 Water Cesium-134 12 2.6 14+/-2 pCi/liter ober 1931 Water Cesium-137 15 8.7 20+/-14 pCi/liter ober 1981 Water Radium-226 12.7 3.3 11. 8+/-3.5 pCi/liter ober 1981 Water Radium-228 9.2 2.4 8.3+/-5.1 pCi/liter ober 1981 Water Gross Uranium 15 10 9+/-2 pCi/liter
_ober 1981 Uilk Strontium-89 23 8.7 24+/-8 pCi/liter ober 1981 Milk Strontium-90 18 2.6 14+/-5 µCi/liter ober 1981 Milk Iodine-131 52 10 58+/-11 pCi/liter ober 1981 Hi.lk Cesium-137 25 8.7 29+/-9 pCi/liter ober 1981 Milk Barium-140 0 0 LT 16 pCi/liter
~be. 1981 Milk Potassium 1530 133 1700+/-240 mg/liter emb~r 1981 Food Strontiurn-89 38 8.7 41+/-6 pCi/kilogram embfk 1981 Food Strontium-90 23 2.6 21+/-5 pCi/kilogram emblr 1981 Food Cobalt-60 30 8.7 35+/-8 pCi/kilogram em her 1981 Food Cesium-137 33 8.7 32+/-8 pCi/kilogram eu1t\.\!r 1981 Food llarium-140 0 0 LT 31 pCi/kilogram ember 1981 Food Potassium 2730 236 2700+/-270 mg/kilogram ember 1981 Water Tritium 2700 615 2950+/-127 pCi/liter
.s, 69
1981 EPA !NTERCOMPARISON RESULTS (Lab Perfonnance Evaluation Study-EMSL-LV)
- j. Control MWF Sample Agency Limits Measured Type Analysis Value (3cr ,n== 1) +/-2cr error Units Water Gross alpha 39 10 39:!:4 /~-- pCi/lfter Water Gross beta 60 5 70:!:7 pCi/liter Water Cobalt-60 12 5 LT20 pCi/liter Water Cesium-134 12 5 11+/-2 pCi/liter Water Cesium-137 20 5 20+/-2 pCi/liter Water Ruthenium-106 0 LTlOO pCi/liter Water Zinc-65 0 LT20 pCi/liter Water Strontium-89 6 5 5+/-1 pCi/liter Water Strontium-90 0 LT 1 pCi/liter Water Radium-226 12.8 1.8 12. 6+/-1. 3
- pCi/liter Water Uranium 5 6 4+/-2 pCi/liter 70
USDOE QUALITY ASSESSMENT PROGRAM 1981 Sample Measure~
TyEe Nuclide Known +/-2cr error Units Air (81-04) lle-7 0.244 E+04 0.247+/-0.015 E+04 pCi/filter Air (81-04) Mn-54 0.117 E+03 0.093+/-0.006 E+03 pCi/filter
"' Air (81-04) Sr-89 0.450 E+02 0.515+/-0~087 E+o2 pCi/filter
' Air (81-04) Sr:-90 0.630 E+Ol <0.100 E+02 pCi/filter Air (81-04) Zr-95 0.122 E+03 0.828+/-0.048 E+02 pCi/filter
~ Air (81-04) Sb-125 0.139 E+04 0.133+/-0.006 E+04 pCi/filter Air (81-04) Cs-134 0.190 E+04 0.133+/-0.007 E+o4 pCi/filter Air (81-04) u 0.223 E+Ol 0.750+/-0.053 E+ol pCi/filter Soil (81-04) K-40 0.213 E+02 0.290+/-0.017 E+02 pCi/g Soil (81-04) Cs-137 0.200 E+OO 0.250+/-0.070 E+OO pCi/g Soil (81-04) Ra-226 O. 770 E+OO 0.668+/-0.057 E+OO pCi/g Tissue (81-04) K-40 0.158 E+Ol 0.433+/-0.058 E+Ol pCi/g Tissue (81-04) Sr-90 0.240 E+Ol 0.188+/-0.016 E+Ol pCi/g Tissue (81-04) Ra-226 0.450 E+OO 0.433+/-0.058 E+OO pCi/g Tissue (81-04) u 0.290 E-01 0.850+/-0.333 E-01 pCi/g
- ~ Vegetation (81-04) K-40 0.224 E+03 o. 277+/-0. 018 E+03 pCi/g
,, t rl Vegetation Vegetation Vegetation (81.:..04)
(81-04)
(81-04)
0.560 0.230 0.310 E+Ol E+OO E+OO 0.258+/-0.016 E+Ol 0.200+/-0.058 E+OO 0.133+/-0.058 E+OO pCi/g pCi/g pCi/g Water (81-04) H-3 0.246 E+02 0.197+/-0.012 E+02 pCi/ml
~
Water (81-04) Co-57 0.118 E+Ol 0.*243+/-0. 018 E+Ol pCi/ml Water (81-04) Co-60 0.129 E+Ol 0.133+/-0.006 E+Ol pCi/inl Water (81-04) Sr-90 0.440 E-01 0.405+/-0,063 E-01 pCi/ml Water (81-04:) Cs-137 0.137 E+Ol 0.150+/-0.012 E+Ol pCi/ml Water (81-04) Ce-141 0.527 E+Ol 0.193+/-0.012 E+ol pCi/ml Water (81-04) u 0.145 E-01 0.200+/-0.026 E-01 µg/ml Water (81-04) u 0.102 E-01 0.750+/-0.140 E-02 _ }>Ci/ml 71
-~.: .... . . -.
1981 TLD Intercomparison Badges Irradiated by Bnttelle Northwest Labs Total mR less transEortation control 1st gtr 2nd gtr 3rd gtr 4th Qtr Badge Known Measured Known Measured Known Measured Known Measured A 18. o* 18.5+/-4.1 18.0 17.8+/-5.0 20.0 25.5+/-4.8 90.0 86.2+/-15.5 B 26~0 29.1+/-2.9 24.0 24.5+/-5.5 28.0 31. 4+/-2. 5 51.0 53.6:!:5.3 C 35.0 29.1+/-6.1 38.0 34.1+/-9.0 16.0 17.9+/-2.7 100.0 93.4+/-10.l D 47.0 46.8+/-5.4 44.0 43.2+/-6.0 32.0 36.5+/-3.5 42.0 41. 9+/-19. 7 E 57.0 42 .1+/-6. 0 59.0 61.4+/-6.5 40.0 41.2+/-4.0 18.0 20.1+/-3.4 F 69.0 77.6+/-12.5 69.0 71.2+/-19.0 53.0 55.4+/-15.2 29.0 32.0+/-3.0 G 76.0 65.6+/-6.6 73.0 74 .1+/-21. 6 69.0 75.1+/-13.2 34.0 32.0+/-3.0 H 88.0 88.6+/-12.6 79.0 80.8+/-17.3 82.0 80.4+/-10.7 82.0 79.0+/-8.0 100.0 102+/-10 J 79.0 79.9+/-18.2 93.0 86.1+/-15.5 34.0 38.7+/-9.3 K 100.0 99.:tlO 99.0* .100. 2+/-25. 4 100.0 100.4+/-15.3 7'** 0 69.2+/-8.8 72
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