ST-HL-AE-3742, 1990 Annual Radiological Environ Operating Rept
| ML20073G670 | |
| Person / Time | |
|---|---|
| Site: | South Texas  |
| Issue date: | 12/31/1990 |
| From: | Jump W HOUSTON LIGHTING & POWER CO. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| ST-HL-AE-3742, NUDOCS 9105030412 | |
| Download: ML20073G670 (257) | |
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, The Light c o mp a nySouth Texas Project Eintric Generating Station P, O, llox 289 Wadsworth, Tesai 77483 flouston Lighting & Power April 30, 1991 ST-i!L AE-3742 File No. 007 10CFR50.73 U. S. Nuclear Regulatory Commission Attention: Document Control Desk l Washington, DC 20555 South Texas Project Electric Generating Station Units 1 6 2 Docket Nos. ETN 50-498 6 50-499 l Annual Radiological Environmental Operating Report for 1990 pursuant to the South Texas Project Electric Generating Station Technical Specification 6.9.1.3, attached is a copy of the Annual Radiological Environmental Operating Report for the calendar year 1990. If you should have any questions on this matter, please contact Mr. J. R. Lovell at (512) 972-8467. b William J . Jump Manager, Nuclear Licensing MKJ/kmd Attachments: Annual Radiological Environmental Operating Report for 1990 910505 1
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m I i g ST-HL AE 3749 Ilouston Lighting & Power Company File No'-' G07 South Texas Project Electric Generating Station p,g, 2 cc:
- Regional Administrator, Region IV Rufus S. Scott Nuclear Regulatory Commission Associate General Counsel 611 Ryan Plaza Drive, Suite 1000 Houston Lighting 6 Power Company Arlington, TX 76011 P. O. Box 61867 He ston, TX 77208
- George Dick, Project Manager U.S. Nuclear Regulatory Commission INPO Washington, DC 20555 Records Center 1100 circle 75 Parkway
- J. I. Tapia Atlanta, CA 30339-3064 Senior Resident Inspector c/o U. S. Nuclear Regulatory Dr. Joseph M. Hendrie Commission 50 Be11 port Lane P. O. Box 910 Bellport, NY 11713 Bay City, TX 77414 D. K. Lacker J. R. Newman, Esquire Bureau of Radistion Control Newman & Holtzinger, P.C. Texas Department of Health 1615 L Street, N.V. 1100 West 49th Street Washington, DC 20036 Austin, TX 78756-31P9 D, E. Ward /T. M. Puckett Central Power and Light Company 4
P. O. Box 2121 Corpus Christi, TX 78403 J . C . Lanie r/M. B . Le e City of Austin Electric _ Utility Department P.O. Box 1088 Austin, TX 78767 R. J. Costello/M T. Hardt City Public Service Board P. O. Box 1771 San Antonio, TX 78296 cNOTE: The above copies distributed without attachments except if noted by asterik (*). Revised 01/29/91 Lh/NRC/
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lI 'I I I I I I PREFACE I The 1990 Annual Radiological Environmental Operating Report for the South Texas Project Electric Generating Station (STPEGS) satisfies reporting requirements specified in the Environmental Report Operational License Stage Am ndment 9, NRC Nov. 1979 Branch Technical Position, and section 6.9.1.3 of I the STPEGS Technical Specifications. The conclusion (Section K) may be assumed to be the same as the executive summary., I I I I I I I I I
TABLE OF CONTENTS I E.*El Preface......................................................... 1 Table of Contents............................................... 11 List of Tables..................,............................... 111 List of F1gures................................................. iv Section Introduction.................................................... A General Site Information........................................ B Program Design.................................................. C Sample and Analysis Accountability System....................... D Land Use Census................................................. E Quality Assurance Program....................................... F Results Data Summary Tables..................................... G I EPA Euvironmental Radiation Ambient Monitoring System........... H Program Performance............................................. I I Analysis of Environmental Data.................................. J Conclusion...................................................... K Addendum 1 - STPEGS REMP Results Data........................... L Addendum 2 - EPA Intercomparison Results Data................... M i i i I I
I-LIST OF TABLES Table Title Py C-1 Sadiological Environmental Monitoring Program....... C-6 C-2 Environmental Lower Limit of Detection (LLD) Sensitivity Requirements............................ I C-11 C-3 Reporting Levels for Radioactivity Concentrations in Environmental Samples............................ C-12 C-4 STPEGS Plant Approved Procedures.................... C-13 D-1 Sample Media & Originator Codes..................... D-3 D-2 Sample Station Locations............................ D-4 F-1 Duplicate / Split Results............................. F-6 F-2 NIST Performance by Test Nuclide.................... F-14 F-3 EPA Trending Graphs................................. F-23 G-1 Annual Radiological Environmental Operating Report Summary........................................G-3 I-1 REMP Performance Evaluation......................... I-4 I-2 Sample Collection Schedule Table.................... I-7 J-l Environmental TLD Measurements...................... J-15 J-2 Measured Activity In Environmental Media............ J-18 i
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I - LIST OF FIGURES I Figure Title ,P_ age C-1 Organization / Function Chart of STPEGS REMP.......... C-4 C-2 Environmental Samples Processed .................... C-5 D-1 Site Periphery Sample Location Hap.................. D-9 D-2 Sample Location Hap................................. D-10 D-3 Zone Location Hap...................................- D-Il i F-1 F-2 EPA Performance Evaluation.......................... Radiological Laboratory Q.C......................... F-9 F-10 F-3 EPA Intercomparison............................ .... F-ll F-4 Battelle Intercomparison for Environmental TLDs..... F-12 I F-5 Internal Audit Assessment........................... F-13 F-6 USCEA/NIST Performance Summary...................... F-15 I-1 STPEGS REMP Samples Collected....................... I-3 J-1 Weekly Gross Beta Activity In Airborne Particulate.. J-6 J-2 Annual Average Gross Beta In Air Particulate........ J-7 J-3 Historical Comparison of Indicator and Control Air Sampling Stations................................... J-8 J-4 Direct Gamma Radiation In Relation to Wind -I' Direction........................................... J-9 J-5 Co-located TLD Stations Comparison Chart............ J-10 J-6 Environmental TLD f: hart - Mean of All STPEGS/NRC/ State TLD Results by Quarter........................ J-11 I J-7 Historical Comparison of Tritium Activity in Hain Cooling Reservoir Surface Water..................... J-12 J-8 Historical Comparison of Co-58 Activity............. J-13 J-9 tilstorical Comparison of Co-60 Activity. . . . . . . . . . . . . J-14 E
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SECTION A DrTRODUCTION This report is the third Annual Radiological Environmental Operating Report issued for the South Texas Project Electric Generating Station (STPEGS). It includes a detailed evaluation of the data collected for the calendar year 1990 by the Houston Lighting and Power Company (HL&P) for the STPEGS Radiological Environmental Monitoring Program (REMP). Where applicable, a historical perspective utilizing preoperational data has been selectively integrated into the report. kW Rarely will an environmental surveillance program identify a significant increase in the ambient concentrations of radionuclides in the off-site environs of an operating nuclear power plant. Historically, increases were I usually associated with atmospheric f allout from above ground nuclear bomb tests and most recently with the fallout associated with the Chernobyle accident in 1986 rather than the operating status of the facility. STPEGS is no exception. No plant related of f-site contamination has been noted with the l F exception of a f ew marFinally detect able tritium measurements of samples collected in "near" of f-site sloughs adj acent to STPEGS property. However, radioactive contamination of the Hain Cooling Reservoir (HCR) continues to I build up at a predicable rates for example, tritium in surface water and Cobalt-56 in sediments. Other positive measurements have been reported for on- and of f-site samples, but these are regarded as ambient and have been noted in previous reports. Section B: General Site Information General information describing the STPEGS site and surrounding environs is discussed. This information may be utilized as a basis for judging l relersnee of specific data and overall program design. Sstrion C: Program Design / Organization / Procedures
*he Radiological Environmental Monitoring Program including the organization, responsibilities, operating philosophy, and program design is outlined and discussed. Any changes in the REMP from the previous year is addressed. A graphic summary and discussion of the sample and analysis load is presented.
Section D Sample Stations Descriptions of sample stations and their associated media types are tabled. Media codes and maps are included. Section Et Land Use Census A summary of the land use census is provided. The census method and the results are described along with recommendations to the program for the following year. A-1
) Section F: Quality Assurance / Quality Control Quality assurance and quality control programs and activities are B. described. The results of these programs are presented as a discussion and/or illustration. Section G: Results Data Summary Tables The results data for all environmental media and direct radiation is formatted as illustrated in the NRC, Nov. 1979 Branch Technical Position 'i Table 3. A complete listing of analysis data are tabled in Addendum 1. Section B: EPA ERAMS Information found in the EPA's Environmental Radiation Ambient Monitoring System (ERAMS) reports is discussed. The reports are monitored for sources oi environmental radioactivity that may have an influence on the accurate i interpretation of STPEGS REMP results data. Section I: Program Performance This section identifies and discusses deviations from the REMP commitments found in Section C, Table C-1. The deficiencies are evaluated to I determine the significance of their impact on the program. Corrective action, if taken, is also discussed. A sample collection schedule is a means to demonstrate program compliance. Section J: Analysis of Environmental Data Section J presents a discussion of the air particulate / air lodine and environmental TLD programs along with an evaluation of the data. Two tables I are also included: one table lists the environmental TLD results data by quarter, and the other table liste environmental samples in which relevant g radionuclides were identified. This section is supported by graphic 3 illustrations for measurements of interest. Also, other environmental media, points of interest, aaomalies, etc. , will be discussed if applicable. Section K: Conclusion The report is finalized with a conclusion and includes highlights of any significant observations. Section L: Addendum 1 Addendum 1 lists all the resulte data of radioassay analyses of STPEGS environmental samples including sample and analysis identification information as described in section D. Calculated activities are reported regardless if a
,k positive identification had been made per guidance of the Health Physics W Society Conunittee Report HPSR-1 (1980) Upgrading Environmental Radiation Data (USEPA 5201/1-80-012).
Section M Addendum 2
.g Addendum 2 lists all the results .c4 .or the EPA Intercomparison Studies g Program.
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E I SECTION B GENERAL SITE INFORMATION I The South Texas Project Electric Generating Station is located in a , $ W predominantly rural area in southwest Hatagorda County approximately 12 miles south of Bay City and 90 miles southwest of Houston. The site is approximately 11 miles north of Matagorda Bay / Gulf of Mexico and lies on the vest bank of the Colorado River. 1 i Vithin a ten-mile radius of STPEGS there are several communities of a few hundred people or less. Matagorda, being the exception, is located 8 miles , southwest of the site and has a population of nearly 2,000. The nearest full-i w time residence is in the west-southwest sector approximately 2.4 miles from the containment buildings. The nearest development is Selkirk Island / Exotic l Island which represents approximately 500 homesites and is located 4 miles southeast of the containment buildings. Although these developments are 3 primarily utilized for recreational purposes or retirement investment, full-time occupants are on the increase. The nearest population center, as defined I in 10CFR20 is the city of Victoria, Texas, which had a population of 50,695 in 1980. Victoria's nearest corporate boundary is 59 miles west of the site. However, projections indicate that the population of Bay City, 13 miles north-northeast, will exceed 25,000 by the year 2010. )' Wg been designated as the " population center.' For this reason Bay City has l g STPEGS consists of two twin 1250 megawatt Westinghouse Corporation ! g pressurized water reactors (PVR). Unit I received a low-power testing license l on August 21, 1987, obtained initial criticalitw on March 8, 1988 and was declared commercially operational by HL&P management on August 25, 1988. Unit 2 received a low-power testing license on Decemter 16, 1988, obt ained l I initial criticality on March 12, 1989 and was declared womercially operational on June 19, 1989. , During 1990 Unit 1 and Unit 2 underwent refueling outages in March - June (1RE02) and October - December (2RE01) respectively. The units are situated l on an approximately 12,300-acre site. Sixty-five (65) acres are modified or l' occupied by the plant anc plant facilities while approximately 7,000 acres make up the aboveground cooling reservoir. Numerous smaller bodies of water on-site consist of the essential cooling pond, Kelly Lake and a number of l drainage ditches, sloughs and depressions. The majority of the land east of l 5 the cooling reservoir and bounded by the Colorado River is leased for cattle i grazing. Approximately 1700 acres remain in a more natural state as a lowland l g habitat. The surrounding area is characterized by coastal plain with farmland 5 and Pasture predominating. The local relief of the area is characterized by flat land, approximately 23 feet above sea level, h W The economic base for this area is agricultural related. Consequentay, the majority of the land in the vicinity of the site is utilized for the production of four major agricultural commodities. They are animal production g for human consumption (predominantly beef), grain production for human g consumption (predominantly rice), animal feed for livestock consumption, and
. pasture grass for grazing. In addition to agriculture, commercial fishing is extensive in datagorda Bay and the Gulf of Mexico. Currently shrimp, oysters, and crab are the target commercial fish while fin fishes have been less important commercially in recent years.
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I I Although the surrounding area is heavily cultivated, significant amounts of woodlands, thicket, brush, fields, marsh and open water exist to support wildlife. The area lies in the southern region of the central flyway and I hosts an abundanco of migratory birds wr.ile the local estuary environments provide the necessary habitat for a variety of fish types to complete their life cycles. The area is well suited for recreational hunting and fishing but is currently not being utilized to its fullest potential. However, the Army Corp of Engineers is planning to develop a number of recreational areas near the mouth of the Colorado River within the next few years. The climate of the region is subtropical maritime, with continental influence, and is characterized by short mild winters and long hot and humid g summers. The wint er season's average temperature is 55 F, summer's average is 5 80 F1 with an annual monthly average of 68 F. Rainfall is usually abundant throughout the year with a yearly average of 42", contrary to the long periods of drought conditions exper2enced in 1988, 1989, and 1990. The prevailing wind direction is from south-southeast from spring through fall, shifting to north-I northeast during the winter months. I I I I 8 I I I 8 I I B-2
l i SECTION C PROGRAM DESIGN OBJECTIVES The South Texas Project Electric Generating Station initiated a comprehensive and fully implemented preoperational REMP on July 1985. That program terminated on March 7, 1988 fulfilling the following objectives outlined in the NRC Regulatory Guide 4.1.
- 1. Personne'. training.
- 2. Evaluation of procedures, equipment and techniques.
- 3. Identification of probable critical pathways to be monitored after the plant is in operation.
- 4. Measurement of background levels and their variations along anticipated critical pathways.
As of March 8, 1988, the REMP's operational objective is to establish I correlations between levels of radiation and radioactivity in the environment and radioactive releases from plant operations. The transition from the preoperational to operational REMP has been smooth and in particular the data bases have proven to be compatible which has allowed for effective and I. efficient data analyses. DESIGN The REMP was designed and implemented by Houston Lighting & Power. The overall program design is written to meet the intent of the NRC November 1979 Branch Technical Position, An Acceptable Radiological Environmental Monitoring Program. The REMP's quality assurance program has been written to parallel I the program described in NRC Regulatory Guido 4.15, Quality Assurance for Radiological Monitoring Program. Critical pathway analysis requires that samples be taken from aquatic, atmospheric, and terrestrial environments. Samples of various media are selected to obtain data for evaluation of potential radiation done to man. I. Sample types are based on established pathways and through experience gained at existing nuclear facilities. Furthermore, a study (STPEGS REMP Aquatic and Terrestrial Collection and Information Manual.) was performed by Houston Lighting & Power in conjunction with Texas A&M University to evaluate site 5 specific wildlife sample types. Sample locations were determined after considering site meteorology, Colorado River hydrology, local demography and land use. Sampling locations were further evaluated and modified according to I field and analysis experience. Sampling locations may be referred to as an " indicator" or " control" Indicator stations are locations that are assumed to be influenced 5 station. by plant discharges during plant operation. Control stations are locations where plant influence is not expected. Though most samples analyzed are I accompanied by a control sample, it should be noted that this practice is not always possible or meaningful with all media types. Fluctuations in the concentration of radionuclides and direct radiation exposure at indicator stations will ultimately be evaluated with respect to analogous fluctuations C-1
et control stations. Indicator stations will also be compared and evaluated relative to characteristics identified during the preoperational REMP. The STPEGS REMP is described in detail in Table C-1 of this section. L Table C-2 detalle the minimal (Tech. Spec. requirements as described in the ODCM) analysis sensitivities (LLD). Additional samples from same or alternate i I locations may be collected, additional analytical analysis may be performed, and greater analysis sensitivity may be achieved than what has been described in Tables C-1 and C-2. Table C-3 lists the NRC reporting levels for g radioactivity concentrations in environmental media. Table C-4 lists the y current STPEGS
- plant approved" procedures that 1 utill:cd for implementing the REMP obj ect ives.
ORGANIZATION AND OPERATING PHILOSOPHY Figure C-1 illustrates a simplified version of the management levels relevant to this report. Preoperational REMP design and operating philosophy parallels the EPA / Health Physics Society Committee Report, Upgrading Environmental Radiation i Data, HPSR-1(1980) recommendation that, "if possible, the implementation of all program aspects should be under the direction of one organization rather than fragmented into areas of separate group responsibilities so that I continuity and overall urderstanding are maintained." Furthermore, this philosophy states that reliable results and interpretations come from programs formulated and implemented by individuals who are knowledgeable in all facets of the program. This operating philosophy maintains that all aspects of the REMP (e.g. sample collection, sample analysis, data interpretation, etc.) have equal priorities and share primary objectives. ;n practice, sample selection and appropriate collection techniques have been viewed as important as the employment of state-of-the-art detection equipment and data analysis methods. SAMPLE AND ANALYSIS LOAD IN 1990 Figure C-2, Environmental Samples Processed, shows that 2046 samples were received and 2186 analysis were performed by the Radiological Laboratory. Approximately 70% of this effort satisfies the requirements on Table C-1 and is noted as STP on Figure C-2. The majority of the remaining samples processed as either Interlaboratory Quality Assurance (LQA) or interlaboratory quality assurance samples. The Intra category includes quality control samples originating from in-house such as analyst qualification analyses, rangent blank, spikes, field and laboratory replicates analyses etc. The Inter category includes quality control samples originating from independent organizations such as the U.S. Environmental Protection Agency Interlaboratory Comparison Program (EPA) and the U.S. Counell of Energy Awareness / National Institute of Science and Technology Measurement Assurance Program (USCEA/NIST MAP), interutility cross-check programs (Yankee Atomic Electric), and Standard Reference Material (SRM) provided by vendors. Inter and Intra quality control samples may either be blind or nonblind and collectively represent 291 cf the analyses performed. l C-2
I Although charcoal filters are specifically analyzed for I-131 and make up approximately 25% of the analyses, Figure C-2 indicates <1% of the analyses performed were for I-131. Because I-131 in charcoal f11ters are analyzed t 5 Ea:ca isotopically versus radiochemically utilizing an alternate analysis technique, the data management system has correctly included these analyses in the gamma category. I cI l l I I I I I I I l I l 5 I l I lI C-3 lI
TIGURE C-1 ORGANIZATIONAL / FUNCTION CHART OF STPEGS REMP E ~ NUCLEAR G1DIERATION Vice President i STPEGS Plant Manager TECHNICAL SERVICES DEPARTM*:NT Manager i RADIOLOGICAL IABORATORY*
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General Supervisor I l Design & Development l l REMP l lDataEvaluation& Reporting l l l REMP QA/QC Sample Sample Collection Analysis B
- Off-site Support C-4
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kM E E E E TABLE C-l RADIOLOGICAL ENVIRONMFETAL MONITORING PROGRAM Collection Anal:rsis Routine Nominal Minimum Exposure Pathway Collection Analysis Analysis Nominal Number of Sampling and/or Mode Frequency Figure Type Frequency Sample Media Sample Locations Continuous Quarterly D1 & D2 Gamma Quarterly
- 1. Direct Radiation Total Stations: 40 (TLDs) 16 Stations located in sixteen sec-tors approximately 1 mile from l
containment. 16 Stations located in sixteen sectors 4-6 miles from containment. 6 Stations located in special interest areas (e.g. school, l population center) within a 14-mile radius of containment. 2 Control Stations located in areas of minimal wind direction (W. ENE) 10-15 miles from containment. Continuous Weekly D1 & D2 Radiolodine Weekly
- 2. Airborne Total Stations: _12 Canister:
- a. Radiolodine & (5) .
I-131 Particulates 3 Stations located at the exclusion zone, approximately 1 mile from Particulate containment in the N, NNV, and NW Sample: sectors. Weekly 1 Station located in Bay City, 14 Gross Beta Gamma-Isotopic Quarterly miles from containment. Composite 1 Control station located in a (by minimal wind direction (V) 11 miles location) from containment. Grab Annually D1 & D2 Gamma-Isotopic According
- b. Soils (7) to 5 Same as air stations. collection 2 Stations located on or adj acent to frequency farms within 5 miles of containment.
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L____3 L.__. > k. > TABLE C-1 (Cont'd) Analysis Collection Routine Nominal Minimum Exposure Pathway Collection Analysis Analysis Nominal Number of Sampling and/or Mode Frequency Figure Type Frequency Sample Media Sample Locations
- 3. Waterborne Total Stations: 22
- a. Surface (7) Composite Monthly D1 & D2 Gama-Isotopic Monthly 1 Station located in reservoir at point of reservoir blowdown to (grab, if composite Tritium Quarterly Colorado River. Composite not 1 Control Station located above the Site on the Colorado River not available)
Influenced by plant discharge. 1 Station approximately 2 miles downstream from blowdown entrance into Colorado River. Quarterly Gama-Isotopic According 1 Station located near Site boundary Grab Tritium to in the Little Robbins Slough. collection 1 Station located near Site boundary frequency in the East Fork of Little Robbins Slough. 1 Station located near Site boundary in the West Branch of the Colorado River. 1 Station located in drainage ditet north of reservoir that empties into the Colorado River upstream of the reservoir makeup pumping facility.
- b. Ground (4) Quarterly DI Gama-Isotopic According 1 Station located at well upgradient Grab Tritium to from the reservoir in the upper collection shallow aquifer. frequency 1 Station located at well down-gradient in the' upper shallow aquifer.
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l_._f L_.J k__._) TABLE 'C-1 (Cont'd) Collection Anal:rsis Routine Nominal Minimum Exposure Pathway Analysis Analysis Nominal Number of Sampling Collection and/or Frequency Figure Type Frequency Sample Media Sample Locations Mode 1 Station located at well upgradient from the reservoir in the lower shallow aquifer. 1 Station located at well down-gradient in the lower aquifer.
- c. Potable Water (2) D2 Gamrna-Isotopic Monthly 1 Station located on Site. Grab Monthly 1 Control Station at Bay City. Gross Beta Tritium Quarterly Composite
- d. Sediment (9) 1 C' + 'on located near Site boundary Grab Semiannually D1 & D2 Gamma-Isotopic According in t'he Little Robbins Slough. to 1 Station located near Site boundary collection frequency in the East Branch of the Little Robbins Slough.
I Station located near Site boundary in the West Branch of the Colorado River. 1 Control Station located above the Site on the Colorado River not in-fluenced by plant discharge. I Station located approximately 2 miles downstream from blowdown entrance into the Colorado River. 1 Station located in reservoir at point of reservoir blowdown to Colorado River. C-8
mW W W. W W W W W W W W W W M W W W W TABOK C-1 (Cont'd) i Collection Anal:rsis - Routine Nominal Minimum Exposure Pathway Analysis Analysis Nominal Number of Sampling Collection and/or Mode Frequency Figure Type Frequency l Sample Media Sample Locations 1 Station located in reservoir near circulating water discharge. 1 Station located in the Colorado River where dralnage ditch empties into it north of the reservoir makeup pumping facility. 1 Station located in the Colorado River where the reservoir spillway discharge channel empties into it.
- 4. Ingestion Total Stations: 10
- a. Milk- -- -----------Limited source of sample in vicinity of STEEGS-------- ---
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(Attempts will be made to obtain samples when available) Grab Semimonthly D-3 Gamma-Isotopic AccotJing when on to pasture, Low Level co11cetion monthly at I-131 frequency other times
- b. Broadleaf (4) D1 & D2 Gamma-Isotopic According Vegetation 3 Stations located at the exclusion Grab Monthly during to zone, approximately 1 mile from growing collection containment, in'the N, NW, and NNW season (when frequency sectors.
1 Control Station located in a mini- available) mal wind direction (W), 11 miles from containment. I l l C-9
E E E E- E E E E. E E E E E E -E E' E M E TABLE C-1 (Cont'd) Collection Anal:rsis Routine Nominal Minimum Exposure Fathway Analysis Analysis Nominal Number of Sampling Collection and/or Mode Frequency Figure Type Frequency Sample Media Sample Locations
- c. Agricultural -------------No sample stations have been identified in the vicinity of the Site.---- ---
Products Presently no agricultural land is irrigated by water into which liquid plant wastes will be discharged. Agricultural products will be considered if these conditions change.
- d. Terrestrial & (3) D-3 Gamma-Isotopic According Aquatic Animals 1 Sample representing commercially Grab Sample in season or to (edible portion) and/or recreationally important collection species in vicinity of STFEGS that semiannually if they are frequency may be influenced by plant operation not seasonal
*1 Sample of same or analogous species in area not influenced by STFEGS.
1 Sample of same or analogous species 3n the reservoir.
- e. Pasture Grass (2) D1 & D2 Gamma-Isotopic According 1 Station located at the exclualon Grab Quarterly (when cattle to zone, in any of the three sectors are on collection (N, NW, NNW).
pasture) frequency 1 Control Station located 11 miles W 1
- f. Domestic Meat (1) D3 Gamma-Isotopic According 1 Sample represents domestic stock Annually to fed on crops exclusively grown collection within 10 miles of containment. frequency AApplied to aquatic samples only.
NOTE: Collection frequency may vary to accommodate sample media availability, equipment availnbility, and/or weather conditions. C-10
TABLE C-2 ENVIRONMENTAL LOVER LIMIT OF DETECTION (LLD) SENSITIVITY REQUIREMENTS I i Airborne Particulate l Food l Water or Gag Fish / Game Milk Products Soil Sediment lB Analysis (pCi/kg) Gross 4 (pCi/m ) 0.01 (pCi/kg, wet) (pC1/kg) (pCi/kg, wet) (pCi/kg. dry) l Beta H-3 3000* Mn-54 15 130 Fe-59 30 260 Co-58,60 15 130 Zn-65 30 260 Zr-95 15 lib- 9 5 15 I-131 1** 0.07 1 60 Cs-134 15 0.05 130 15 60 150 Cs-137 18 0.06 150 18 80 180 Ba-140 15 15 La-140 15 15 Direct Radiation (TLD) - Required detection capabilities f or thermoluminescent E
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dosimeters used for environmental measurements shall be in accordance with the recommendations of Regulatory Guide 4.13.
*The detection limit for drinking water affected by plant discharges shall be 2000 pC1/Kg.
**If no drinking water pathway exists, the LLD of gartma isotopic analysin may be used.
NOTE: This list does not mean that only these nuclides are to be considered. Other peaks that are identifiable and can be associated with plant releases, together with those of the above nuclides, shall be analyzed and reported in the Annual Radiological Environmental Operating Report. C-11
I I TABLE C-3
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REPORTING LEVELS FOR RADIOACTIVITY CCHCENTRATIONS IN ENVIRONMENTAL SAMPLES
. I- Airborne Particulate Food I Analysis H-3 Vater (pCi/kg) 20,000*
or Gag (pCi/m ) Fish / Game Milk Products (pCi/kg, vet) (pC1/kg) (oCi/kg, wet) Mn-54 1,000 30,000 Fe-59 400 10,000 Co-58 1,000 30,000 Co-60 300 10,000 Zn-65 300 20,000 Zr-Nb-95 400 I-131 2 0.9 3 100 Cs-134 30 10 1,000 60 1,000 CS-137 50 20 2,000 70 2,000 Ba-La-140 200 300 I
*For drinking water samples. This is 40 CFR Part 141 value. If no drinking water pathway exists, a value of 30,000 pCi/1 may be used.
NOTE: When more than one radionuclide is detected in the medium, the reporting level shall have been exceeded if I concentration (1) + eencentration (2) +. . .>1 reporting level (1) reporting level (2) l5
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LI C-12
^ TABLE C-4 STPEGS PLANT APPROVED PROCEDURES PROCEDURE # TITLE I OPGP03-ZR-0039 ADMINISTRATIVE Radiological Environmental Honitoring Program OPRP10-ZL-0001 Radiological Laboratory Administrative Procedure OPRP10-ZL-0003 Hoescht Celanese Plant Access OPTP01-ZE-0001 Hanagement of Technical Services Laboratory Quality Assurance Program SAMPLE RECEIPT AND ACCOUNTABILITY OPRP40-ZL-0006 Sample Receipt, Accountability and Storage I SAMPLE PREPARATION AND ANALYSIS I OPRP10-ZL-0010 Preparation of Aqueous Samples for Liquid Scintillation Counting OPRP10-ZL-0011 Gk na Analyals in Environmental Media OPRP10-ZL-0012 Iodine-131 Analysis in Environmental Media l OPRP10-ZL-0013 Strontium 89/90 Analysis in Environmental Media OPRP10-ZL-0015 RL Preparatien of Radioactive Standard Solutions and Calibration Sources OPRP10-ZL-0016 Alpha / Beta Analysis in Environrrental Media COUNTING INSTRUMENTATION OPRP10-ZO-0002 Operation and Standardization of the Tennelec Counter Systems OPRP10-ZO-0003 Operation and Standardization of the ND66 HCA Counting Systen. OPRP10-ZO-0004 Operation and Standardization of the Liquid Scintillation Systems C-13
I TABLE C-4 (continued) PROCEDURE # TITLE I COUNTING INSTRUMENTATION (Cont'd) OPRP10-ZO-0005 Operation and Standardization of the RL Beta-Gamma Coincidence System OPRP10-ZO-0006 Operation of the Radiological Laboratory Data Analysis Systems SAFETY OPRP10-ZL-0009 Radiological Laboratory Safety QUALITY ASSURANCE AND QUALITY CONTROL OPRP10-ZL-0002 Qua'Ity Assurance for the Radiological Laboratory OPRP10-ZL-0022 Quality Control of Radiological Laboratory Equipment OPRP10-ZL-0023 Radiological Laboratory EPA Cross-check Program OPRP10-ZL-0024 Standardization of Carriera and Standard Chemical Solutions OPRF10-ZL-0025 Radiological Laboratory Chemical and Reagent Control OPRP10-ZQ-0001 Documentation and Testing of RL Computer Programs OPTP01-ZE-0002 USCEA/NIST Hessurement Assurance Program OPTP01-ZE-0003 Interlaboratory Radioassay Heasurement Assurance Program COLLECTION OPRP10-ZU-0001 REMP Sample Collection I OPRP10-ZU-0005 Environmental Sample Collection of Airborne Particulate and Radioiodine OPRP10-ZU-0007 Environmental TLD Honitoring I I I I C-14
I I SECTION D I INTRODUCTION SAMPLE AND ANALYSIS ACCOUNTABILITY SYSTEM This section briefly describes the data management system employed to administrate and evaluate the REMP. An understanding of the following described system and codes will aid in reading data tables which will follow later in the report. I SAMPLE AND ANALYSES IDENTIFICATION I An example of a sample identification utilizing the Sample Submission Code (SSC) is given below. The code supplies information on origin of sample, type of media, location, date, and time collected. This identification is provided while samples are being collected. Duplicate and split samples are I identified by this system with the use of the letters d or s, respectively, in the farthest right character position in the SSC. When the d or s option is being employed, the minute des'gnation for collection time cannot be fully I utilized. Sample media codes anta originator codes can be found in Table 5. Station codes are identified in Table 6. Example Of Sample Submission Code Media Collection Code Date STP - AP - 015 - 03 85 - 0900 Originator Station Collection Code Code Time Upon receipt of sample at the laboratory the SSC is cross-referenced to a I Laboratory Sample Number (LSN). An LSN is issued in series and is initialized with a prefix (es) identifying analysis type. Analysis Prefix Options 1 S= Strontium; H-Tritium; i G= Gamma Isotopic I' B-Alpha / Beta; I= Iodine I g SAMPLE STATION LOCATIONS i g l Table 6 gives the location for each station code, vector, and reedia type sampled at each station. Figures D-1 and D-2 are maps that identify permanent l "l sample stations. Figure D-3 identifies sample locations that may be mobile to some degree (e.g. active / inactive agriculture areas and wildlife samples). These locations are considered zones and are determined in the following manner.
- a. The first digit of the station code is "Z" to identify it as a zone I
station code,
- b. Followed by the number that designates direction from STPEGS,
- c. Followed by the number designating distance from STPEGS.
D-1
- DATA MANAGEMENT 1 L The SSC and corresponding LSN are stored with a ev.aputer program that is capable of sorting fields within the SSC and LSN. The sorting capability provides much latitude and flexibility for the evaluation of environmental E data by location, media, nuclide, time pariod, etc. This methodology is used j in generating routine results data reports (Initial Analysis Reports) as well as sections of more comprehensive reports (Annual Radiological Environmental Operating Report). Trend evaluat ion, comparison of station data, nuclide ratios, and year-to-year comparisons can be easily accomplished by accessing I files that store information found in and with the SSC and LSN. Management computer programs have also been written that utilize information stored with the SSC and LSN that aids in coordt*'*.ing REMP activities. Lastly these codes I are frequently used to sort and analyze the various types of quality control data supporting the REMP. I I I I I I I I i D-2
I TABLE D-1 SAMPLE MEDIA & ORIGINATOR CODES SAMPLE MEDIA CODES WR Rain Water H4 Domestic Swlos H5 Egga I VS Surface Water VG Ground Water M6 Game Den VD Drinking Vater H7 Alligator SS Shoreline Sediment HB Rabbit I SO T1 F2 Soil Fish - Piscivorous Fish - Crustacean and Insect Feeders CC CS OY Crustactsn Crab Crustacean Shrimp Oyster I F3 MC MG Fish - Planktivores and Detritus Teeders Cow Hilk Goat Hilk AP AI DR Airborne Particulate Airborne Radiolodine Direct Radiation RA Rooted Aquatic Vegetation FD Food I VB Broadleaf Vegetation L1 Banana Leaves L2 Cana Leaves UR Urine B1 Resident Dabbler Duck B2 Resident Diver Duck I L3 Lettuce L4 Turnip Greene L5 Cabbage B3 Higratory Dabbler Duck B4 Higratory Diver Duck B5 Goose L6 Collard Greens B6 Dove VP Pasture Grass B7 Quail VR Rice BB Pigeon VS Grain Sorghum N1 Pecans I VC SB R4 Corn Soybean Turnip N2 Acorns BE Wild Blackberries HL (Hixed Liquid) Aeration H1 Seef Heat Tank < H2 Poultry Heat AS (Ash Sludge) Ash tank H3 Wild Swine ml (water portion of ML) as (water portion of AS) Exarcples of originator codes include, but are not limitted to the following:
- EPA - Origination from Environmental Protection Agency
*LQA - Origination from Radiological Laboratory for In-house QC l
NBS - Origination from National Institute of Standards and Technology (NIST) STP,- Origination from STPEGS Radiological Environmental Honitoring Program (REHP) TEX - Origination from State of Texas sampling program l *These samples are for laboratory quality assurance and have sample station (' location codes as follows: EPA: 000 - EPA samples LQA: 000 - Reagent blank samples 1 I 001 - Intralaboratory QC samples 002 - Intralaboratory replicate QC samples 003 - Analyst qualification samples D-3
TABLE D-2 P L SAMPLE STATION IDCATIONS STP - Origination f rom STPEGS Radiclogical Environmental Monitoring Program b (REMP) Station Media Code Tirure Code Vector Location Description I DR AI AP,VB,SO, VP D-1 001 1 mile N Exclusion Ione - TM %21 DR D-1 002 1 mile NNE Exclusion Zone - FM 521 DR D-1 003 1 mile NE Exclusion Zone - FM $21 DR D-1 004 1 mile ENE Exclasion Zone - FM $21 DR D-1 005 1 mile E STPEGS Visitor Center - FM $21 DR,AI AP,50 D-1 006 3.5 miles ESE Site near reservoir makeup pumping fac111ty DR D-1 007 3. 5 t!1e SE Site on Dike DR D-1 008 .5 mile SSE Site on Dike DR D-1 009 .25 mile S Lite on Dike DR D-1 010 .25 mile SSW Site on Dike DR D-1 011 .5 mile SW Site on bike DR D-1 012 1 mile WSW Site on Dike DR D-1 013 1 mile V Exclusion Zone - FM 521 DR D-1 014 1 mile VNW Exclusion Zone - TM 521 DR,AI,AP,VB,SO, D-1 015 1 mile NW Exclusion Zone - FM $21 VP DR,AI.AP,VB,SO, D-1 016 1 mile NNW Exclusion Zone - FM $21 VP DR D-2 017 6 miles N Buckeye - FM 1468 DR,AI,AP D-2 018 5.5 miles NNE Hoescht Celanese Plant - FM 3057 DR D-2 019 5 miles NE TM 2668 DR D-2 020 5 miles ENE TM 2668 D-4
I I TABLE D-2 I SAMPLE STATION LDCATIONS (Cont'd) I Hedia Code Figure Station Code Vector Location Description DR D-2 021 5 miles E TH $21 DR D-2 022 7 miles ESE Cain Chemical Plant, TX 60 I DR *023 16 miles ENE Intersection of FH 521 and TH 2540 DR DI 024 4 miles SfF Site on Dike DR D-1 025 4 miles S Site on Dike DR D-1 026 4 miles SSW Site on Dike DR D-1 027 2.5 miles SW Site on Dike DR D-2 028 5 miles WSW TH 1095 DR D-2 029 4.5 miles V TH 1095 l DR D-2 030 6 miles VNV Tres Palacios Oaks, FM 2853 l DR D-2 031 5.6 miles NV Wilson Creek Road DR D-2 032 3.5 miles NNW FH 1468 1 DR.A1,AP,SO D-2 033 14 miles NNE Bay City i DR D-2 034 8 miles ENE Wadsworth , DR,AI,AP D-2 035 8.5 miles SSE Hatagorda l DR D-2 036 10 miles VSW College Port DR,AI,AP,VB,VP, D-2 *037 11 miles V Palacios Substation SO l DR D-2 038 11 miles NV BlessinE DR AI.AP,SO D-2 039 9 miles NW El Haton DR D-2 040 4.5 miles SV Citrus Grove l LR D-1 041 2.6 miles ESE Site on Dike VG D-1 205 4 miles SE Well #446A, .5 mile north I of reservoir blowdown canal (30' deep) D-5 1
I I TABLE D-2 I SAMPLE STATION IDCATTONS (Cont'd) Station Media Code Figure Code Vector Location Description VG D-1 206 4 miles SE Vell #446, .5 rcile north of I reservoir blowdown canal (75' deep) 1.5 miles V I *207 WG D-1 Well 0603A, .25 mile V of TX 521 (75' deep) VG D-1 *208 1.5 miles V Vell #603B, .25 mile V of TX 521 (150' deep) VS D-1 209 2 miles E Kelly Lake VD 210 On Site Approved drinking water supply from STPEGS I VS.SS D-1 211 3.5 miles S Site, E. Branch Little Robbins Slough VS,SS D-1 212 3.5 miles S Little Robbins Slough VS,SS D-1 213 3 miles SE Site, V. Branch Colorado River D-1 214** 2 miles E Hakeup Vater Discharge (Reservoir) SS D-1 215** 1 mile SV Site, Reservoir - Circu-lating water discharge VS.SS.F(1,2,3), D-1 216** 3 miles SSE Site, Reservoir - t'.cwdown CC 217** Region 1 (mouth of Colorado River to marker 1) WS.F(1,2,3),CC 21B** Region 2 (marker #1 to marker #27) 219** Region 3 (marker #27 to _ Highway 521 overpass) CC *220** Region 4 (Highway 521 over-pass to Bay City Dam) SS F(1,2,3) *221 Region 5 (above Bay City Dam) I g D.e
I I TAB 1.E D-2 I SAWI.E STATION IDCATIONS (Cont'd) Station Media Code Tirure Code Vector 1,ocation Description F(1,2,3)CC,CS, 222** > 10 miles West NataEorda Bay CO 223** > 10 miles East Hatagorda Bay 224** > 10 miles West Intercoastal Canal 225** > 10 miles East Intercoastal Canal VS D-2 *226 5.5 miles NNE Colorado River at Hoescht Celanese Plant VS,SS D-2 227 6 miles SE West bank of Colorado River 1.5 miles downstream of STPEGS across from channel marker #2? VD *228 14 miles NNE Bay City Public water supply VS D-1 229 1 mile SE krainage ditch north of reservoir that empties into the Colorado River upstream of the reservoir makeup pumping iac111ty SS D-1 230 3.5 miles ESE Colorado River at point where drainage ditch (station #229) empties I into it SO 231 11 miles VSV Soil in vegetation plot at station #37 SO 232 9 miles NV Farmland behind station #39 SS D-1 233 4.3 miles SE Colorado River where blowdown discharge channel empties into it SO 234 1 alle NV Farm across from station
#15 VG 235 3.8 miles S Vell B-3 directly south from reservoir I
g D->
s 5
- TABLE D-2 L
SAMPIE STATION IDCATIONS , (Cont'd) Station Herlin Code Figure Code Vector Location Description J 236 STPEGS Protected Area WS 237 3.7 miles SE Blowdova discharge channel from reservoir WG 238 3.7 miles S Reservoir relief well WG *239 1 mile NV Vell B-1B, near REMP I So, SS, VS 240 1 mile E sampling station #15 Drainage ditch originating NE of protected area that I crosses Hvy 521 south of the main entrance road and empties into Kelly Lake 241 1 mile S Reservoir - Circulating water intake I i I i
- Control Station
** This station may be used to obtain the required aquatic samples in the vicinity of STPEGS that may be influenced by plant operations.
D-B
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figure D-2 Sample Location Map l
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m I SECTION E 1990 LAND USE CENSUS I PURPOSE /DRSION l The 1990 Radiological Environment Monitoring Program (REMP) Land Use Census was performed in accordance with NRC Regulatory Guide 4.8, l Environmental Technical Support Spec 8 fications f or Nuclear Power Plant s, which I states " enumeration by using informatid from county agricultural agents or other reliable sources" is acceptable and fulfills the annual census
)
i requirement as described in the ODCH and OPGP03-ZR-0039. Radiological I Environmental Honitoring Program. Individuals contacted in support of census are supplied later in the text. A more sophisticated method would be this essential at many nuclear f acilities but has proven unnecessary in this case for the following reasons: The census is limited to a 5-m11e radius. The area surveyed consists of large agricultural units. The area surveyed has significant areas of inaccessible natural habitat. Numerous accessible, interactive agents are available for consultation. I - Informed permanent residents / ranchers /larmers are available for consultation. The regulatory guidelines define the census scope in relatively narror terms (e.g. nearest resident, nearest garden, nearest milk cow, etc.), but where additional informatien would be desirable (e.g. change in agricultural 4 practices or irrigation methods), in formulating surveillance protocol, a broader scope was applied. In fact, the Annual Land Use Census process serves as an opportunity to assess the REMP and determine if program modifications I are recommended. This assures that the REMP surveillance activities are relevant and based on current conditions. Information found in this report was obtained primarily from local authorities via direct contact or phone I conversations. Additional sources of information included utility personnel and information obtained while performing routine REMP field activities. Lastly, on September 24, 1990, Richard E. Lockwood surveyed by car the I five-mile radius area around the South Texas Project Electric Generating Station (STPEGS). His primary objective was to identify the nearest resident, and cows producing allk for human consumption in each of sixteen meteorological sectors. Mr. Aubrey R. Passafuma also surveyed this area lE R specifically in support of this census on September 28, 1990. I I E-1
I INDivItyDALS RFIKRENCKD Ref. Means of
# Namie/ Title Comusunication/ Date Affiliation (1) Mr. John McManus, phone 9/04/90 Army Corps of Engineers Engineer Galveston, TX (2) Mr. Thomas Pivonka, phone 9/04/90 Lower Colorado River Engineer Authority, Bay City, TX (3) Mr. Elgin Janssen phone 9/05/90 Central Power & Light, Information Manager Bay City Information Center, Bay City (4) Mr. Glenn Valker, phone 9/10/90 Houston Lighting 6 STPEGS Public Power Relations Manager (5) Mr. Villie Younger, phone 9/2B/90 Matagorda County Marine Agent Extension Service, Bay City TX (6) Mr. Clyde McKinney, phone 9/15/90 Matagorda County Health I Director of Public Health Dept., Bay City, TX (7) Mr. Louis Jones phone 9/05/90 Matagorda Farmers Co-op Agent Bay City, TX (6) Mr. James Engbrock, phone 9/05/95 Matagorda County Agricultural Agent Extension Service, I' Bay City, TX (9) Numerous I
Mr. Trankie Harrison, direct Resident, Bay City, TX Tarmer/ Rancher (10) Mr. W. Baker, direct Numerous Houston Lighting & Power, I Sr. Ecologist Environmental Department Houston, TX I (11) Mr. R. E. Lockwood, Houston Lighting & Power, Staff Engineer Technical Services Dept. (12) Mr. A. R. Passafuma, direct Numerous Houston Lighting & Power, I Technician (13) Hr. Fred Puleo, direct 9/24/90 Technical Services Dept. Houston Lighting & Power, Specialist Emergency 1 rep r $ ess 5 Division, STPEGS (14) Mr. William Hoye, 9/24/90 Houston Lighting & Power, I direct STPEGS Safety Spvar. Safety Department I E-2
I ! l INDIVIDUALS RITEHNCED Ref. Weans of f Name/ Title Commun ic at ion / Date. Affiliation I J (15) Mr. E. J. Thormaehlen, direct 9/24/90 Houston Lighting & Power, Engineer Nuclear Engineering Dept. (16) Mr. Gene Tisseler, direct 9/05/90 Houston Lighting & Power, Engineer Environmental Dept. (17) Hs. Irma Moreno, phone 9/05/90 Houston Lighting Power, Secretary / Resident Technical Services Dept. RESULTS Reference Remarks (11) o Broadleaf vegetation sampling is performed at the site boundary in the three highest D/Q sectors and at a control location in lieu of the garden census. Broadleaf vegetation samples also I satisfy the collection requirement when milk samples are not available. I (2,7,8,9) o Agricultural and ranching practices remained essentially unchanged in 1990. Irrigation practices remained consistent with past years. Production acreage for soybean was slightly down from 1989 in Matagorda County, while cotton was more
-l =
widely planted in the vicinity of the STFEGS in comparison to past years. County-wide total grain acreage was consistent with past yea's. (3,6,8, o No commercia4 dairies were identified in Hatagorda County nor
- 9,11,12) were any individual allk cows (producing milk or not) identified at any of the residences within five miles of STPEGS.
(6,9, o Commercial vegetable f arms (truck f arms) were not identified. I 11,12) From time to time an individual resident may operate a small-volume fruit and vegetable stand. Examples of locally grown produce are corn, pecans, and watermelon. However, these produce stands sometimes offer produce that is not locally i I grown, (1,5) o The Army Corps of Engineers (ACE) have completed the I redirection of the Lower Colorado River into West Hategorda Bay. This project also includes the construction of a diversion dam just south of the intercoastal canal on the Colorado River and the development of recreational areas along I the mouth of the Colorado River. The targeted completion date for the dam construction is late 1991. Permanent water quality l g changes are expected in the Lower Colorado River once the g project is completed. No definitive information was provided that might suggest an impact on the reservoir makeup schedule, REHP, or the ODCH. However, it is speculated that the proposed dam will minimize tidal flow influence above the dam resulting in decreased salinity in that region of the Colorado River near STPEGS. E-3
I I (3,11,12, o The 1990 Land Use Census identifies the nearest resident in 13,17) nine of the sixteen sectors within the five-mile radius of I STPEGS. A nearest resident is identified in the NV and N sectors for the first time. These are overlooked residences that were not accounted for in past years because of inaccurate The reference maps and less than perfect surveillance niethods. sarest resident locations for 1990 are as follows: Distance Sector (approx. miles) Location ESE 3.5 Selkirk Island SE 3.5 Selkirk Island I SV VSV V 4.5 2.5 4.5 Citrus Grove FH 521 FM 1095 I V!N N!N N 4.0 3.5 3.5 Ashby-Buckey Rd. Reynolds Ranch off TH 1466 Reynolds Ranch off FM 1468 IN 4.5 Vondirk Rd. Additional sectors are also presented in a second list because of the resident's close proximity to the five-alle radius reference. Distance S_e e t e r (approx. miles) Location E 5.5 FH 521 ENE 5.2 TH 2668 Hoechst Celanese Petrochemical Plant, which employs 200-300 personnel, is not included on either list because it is not a resident. The plant is located approximately 4.5 miles NNE of I, the STPEGS. (6,13) o There has been little change in the number of home sites within the five-mile radius of the STPEGS since the 1989 survey. The I home sites number approximately 200 and over 150 of these are located in Selkirk Island four alles east of STPEGS. Matagorda
$ County population was approximately 38,000 in 1990 virtually 5 unchanged from the 1980 census.
I 2 (5) o Commercial growing of redfish and shrimp continues in the College Port area,-9 alles SW of STPEGS. The redfish fingerlings are purchased locally while the shrimp post-larvae l are imported. The growing tanks utilize water circulated from l the Tres Palacios Bay. On a similar note, the city of Palacios has been chosen as the site for the Texas Coastal Aqua Cultural Facility. This facility hopes to provide the necessary l g resources for future aqua culture ventures in the Matagorda ! 3 area. E-4
I
.3 (10,14 o A drainage ditch originating northeast of the protected area 5 25) has been identified. It travels east under FH 521, then south back under FH 521 and empties into Kelly Lake. This is not a new ditch but one that has been overlooked. Kelly Lake, however, is currently being sampled.
(16,12) o The current REHP ground water stations are increasingly more I difficult to obtain a sample from because of the deteriorating condition of the walls. Superiorly constructed and maintained wells are in place as monitoring stations in the STPEGS Ground-Vater Monitoring Program. These wells are located more I' adj acent to the Hain Cooling Reservoir (HCR) and are theoretically more censitive to any influence by the operation of the HCR. ( 5 , l. ) o A new port has of ficially opened of f of Highway 60 in the city of Matagorda. The port will serve existing commerce and I provide future services for industries that are anticipated to locate in Matagorda County. 1989 CLOSED ITEM The 1966 - 1989 Land Use Censuses reported a possible concern regarding STPEGS's main reservoir water migration beyond the relief well system into the I irrigation canal west-northwest of the plant. Mr. Thomas Pivorks, Engineer for the Lower Colorado River Authority, stated during this year's interview, that water has collected in this canal in years prior to the construction of the HCR and does not believe there is any communication between the MCR and I the canal; therefore this concern is closed.
SUMMARY
/ RECOMMENDATIONS The REMP as described in part B of the ODCH should be modified to incorporate the following changes. Remove any requirement to sample ground water from REMP stations #285, #286, #287, #288 and add sampling location B-1B I and B-3 of the STPEGS Ground-Vater Monitoring Program. Vs11s B-1B and B-3 are superior indicator stations and are of high quality. construction and are better maintained. Radiological analysis of samples taken f rom these wells I could augment the water quality tests currently being performed.
(g The REHP should be further enhanced by adding sediment (or dried g sediment) sample from the recently identified drainaEe ditch. This ditch collects runoff from portions of the protected area then exits the site i boundary adjacent to the Visitors Center, ultimately emptying into Kelly Lake. l The sample should be collected semi-annually at a location just before the ditch crosses the site exclusion zone under FH 521. l l8 I I g E-,
i I SECTION F QU_ALITY ASSURANCE PROGRAM I The quality assurance program for the Radiological Environrnental Monitoring Program (REMP) has been designed to meet the intent of Regulatory Guides 4.15 Part C and 4.1. EPA documents 600/7-77-088, 600/8-78-008, and 600/4 79-019 vere also consulted in the overall program design. Applicable I REMP quality assurance and quality control procedures have been identified in Table C-4 The environmental direct gamma monitoring program using Panasonic UD-B14 TLDs is currently operating using equipment, processing techniques, and I quality assurance criteria and methods established and used by our NVLAP-accredited personnel desitetry program. has f our maj or componen's: The REMP Quality Assurance Progre.m
- 1. Houston Lighting 6 Power Nuclear Assurance Department o Performs periodic surveillances of specific REMP activities I throughout the year o Performs an annual comprehensive audit of the REMP o Provides for an independent technical review by a technical specialist
- 2. Radiological Laboratory Quality Assurance Program o Routine instrument control checks including calibrations and calibration verification o In'tlal and annual testing of analysts I o Intialaboratory quality control analyses o Quarterly internal assessments o Fleid sample duplicate / split program o Annual comprehensive review in preparation of this report
- 3. Interlaboratory Comparison Programs o Participation in the U.S. Environmental Protection Agency's Intercomparison Studies Program o Participation in the U.S. Citizens for Energy Awareness / National I Institute of Standards and Technology (USCEA/NIST) Measurement Assurance Program for the Nuclear Industry o Participation with Battelle in low level testing of environmental TLDs 4 Periodic audits by outside organizations or agencies (e.g. NRC, ANI.
INFO, etc.) o Perform programmatic content and effectiveness reviews in order to assure license compliance and establish the degree of corepliance with select operational guidelines. No audits of this type were I performed in 1990. I P-1
I RESULTS Houston Litht ing & Power Nuclear Assurance Departrnent Houston Lighting & Power's Nuclear Assurance Department conducted an in-depth audit (90-15) of the REMP and performed numerous surveillances of batple I collection and sample analysis activities during 1990. that the STPEGS ef f ect ively implements t he REMP. ensures compliance with applicable licensing and regulatory requirements, and The audit determined The audit stated the program provisions to initiate corrective action to prevent or limit departures fron the requirements. A single deficiency was addressed and corrected during the I audit. The deficiency was that a quality-related computer program was not verified in accordance with the annual requirement. Radiological Laboratory Quality Assurance / Quality Control Program I There are two accurate means of assessing the effectiveness of the RL's Q/s/QC program which are the quarterly internal QA audits and the intralaboratory performance tests, and to a lesser degree the field duplicate / split program provides valuable information. o Internal Audits - The review criteria for the internal audits are comprehensive and standardized. These internal audits have been performed quarterly since January 1984 in accordance with OPRP10-ZL-0002, Quality I Assurance for the Radiological Laboratory. When audits discover a procedural noncompliance item or an unfavorable condition, an observation report is issued. Twenty-n'ne observation reports were issued in 1990 against the REMP. I None warranted the initiation of an STPEGS Station Problem Report pe r IP 1.45. Figure F-5, Internal Audit Assessment, shows the relationship between sample load and the occurrence of an observed weakness resulting in the issuance of an RL Observation Report. Although the internal audits have been I standardized, there has been some additions to the audit scope. As the audit scope becomes more demanding there is an expected adjustment period which may result in more observation reports to be issued, such as in the case of 1989, o Initial and Annual Proficiency Testing - All analysts performing required analyses have been initially qualified, in part, by demonstrating analytical profielency, and are qualified annually thereafter. Analytical I proficiency has been defined as 115% for accuracy and precision for a set of five QC samples for each analyses type (e.g. gamma isetopics, Sr-89/Sr-90, low level I-131, etc.). The proficiency testing program is regarded as the most I objective means of verifying quality and skill of the analyst while also demonstrating the validity and reliability of the entire analytical process. Good performance in all other QC activities is directly dependent on the effectiveness of the analytical proficiency testing program. All analytical proficiency tests performed in 1989 were successful in demonstrating the analyst's abilities and the analytical prccess. o Performance Tenting 1990 - A graphic summary of laboratory performance is found in Figure F-2, Radiological Laboratory QC 1990. Accuracy I is defined as the percent difference from the known value for a single measurement. Precision is defined as the standard deviation of a replicate analycos divided by its mean and expiessed as a percent. The data base I '-2
_ ._ . . . . . _ - _ ~ _ _ _ .. . l analysed in this case includes single and replicate analyses (blind and non- I blind) representing various quality control categories such as analyst l I I qualifications, spiked sampics, standard reference material (SRM) verification analysis, and interutility cross-check samples. EPA and l'SCEA/NISI tests are included in this evaluation but are evaluated separately and in detail later in this section. Figure 2 shows that the EL's accuracy and precision criteria of 15% f or environmental sartples is met 97.21 and 1001, respectively, o Field Dupileate/ Split Program - A duplicate and split sartple progrtz 1 I has been established. This discussion is limited to field samples and does net include other interlaberatory or intralaboratory quality control check samples. The nominal or target level for duplicate / split samples is 10% of the STPEGS environment samples, rhich was met in 1990. The information I provided by duplicate and split sample results is vital to the differentiation between actual increases in the level of radioactivity in the environraent and apparent increases that are due to the integral variances of the sample media, I collection / preparation methods, and analyses. Duplicate and split measurements also provide a means to cortpere the precisicn in the overall sample collection / sample analysis process of actual environmental samples I versus the precision associated with laboratory controlled and introduced samples. In the future when an extensive data base for both duplicate and split I sample types has been obtained for the majority of the analyses types, a more elaborate evaluation of the data vill be possible. In the interim, duplicate and split data have been combined in this report although evaluated separately I on a routine basis. The data has been evaluated by deterrr.ining the percent difference from the mean for a duplicate or split analysis. It should be noted that a split sample evaluation will r. eve:, oe possible f or some media types such as TLDs, air particulates and air lodines. I Table F-1, Duplicate / Split Results, lists by media: the radiinuclide measured, nurr.ber of narr.ples analyzed and the average dif f erence f oi this type I of analysis. Over two hundred duplicate and split measurements were made in 1990, which int.luded the majority of prescribed analyses identified in Table C-1. However, Table F-1 identifies only those results when radioactivity was confirmed (activity >3 sigma). Also, in cases where I counting instrument background contributed significantly to the measurement, the data was deleted (e.g. Ra-226, K-40, in drinking water). Be-7 and K-40, although naturally occurring, were included where applicable because they are I found in concentrations that can be quantified, and represent external and internal deposition, respectively. This allows for the exercising of the analysis and evaluation process where it would be normally impossible. The 1990 data has been presented independently of historical data for comparison purposes. No significant change is noted. Several radionuclides (e.g. 1-131 in air iodine, Cs-137 in air particulate, Ru-103 in sorghum) I listed in the historical column are associated with the local fallout from the Chernobyle accident in 1986 and were not identified in any other years. I The " average differences" found in Table F-1 vary widely with media and isotope. Typically those measurements which are characterized by sample homogeneity (e.g. air), activity significantly greater than the LLD, and an accompanying reliable standardized sample collection method will have the I F-3
I smallest difference. The direct radiation TLD measurement best exemplifies this condition, while the opposite is true f or the Cs-137 determination in shoreline sediment. I Interlaboratory Program I o EPA Perforttance Summary 1990 program for 1990.
- Figure T-3, EPA Intercomparison 1900, categorites the RL's level of accuracy and precision in the EPA's cross-check In comparison to the data illustrated in Figure 2, Radiological Laboratory QO 1990, the EPA results are not as accurate or precise. This is understood to be a result oft I
. Hatrix difficulties with EPA samples (e.g. Sr-90 in food)
. A test nuclide used by the EPA may be different from calibration nuclide used by the KL.
. A geometry-introduced bias because of EPA's unique air particulate filters.
. Greater random error associated with EPA sample analysis because of I their lov activity level.
o EPA Trend Analysis Graphs - The EPA trend analysis graphs found in I Table F-2, EPA Trending Graphs, illustrates performance for specific analyses in the EPA Environmental Radioactivity Intercomparison Studies Program during the past two years. Table F-2 has been limited to those analyses types (sample media - radionuclide combination) offered by the EPA and also included i as a STPEGS REMP sample type (Table C-1). The graphs are updated throughout the year in order to provide frequent appraisal. Plotted is the mean value of a triplicate analysis. The corresponding laboratory sample number is the first number assigned in the series for each triplicate analysis. Each point is plotted by percent deviation from the known value along with the standard error of the mean (1 sigma) an a I percentage. Results for all EPA samples analyzed and reported in 1990 are presented I in Addendum 2. The EPA stated known values and the reported results are sorted according to media and radionuclide. o Historical EPA Performance Evaluation - The EPA has tested the RL's performance via the EPA Intercomparison Program since 1984. Acceptable performance is defined by the EPA as ' reported results data falling within the EPA's normalized deviation of 1 3.* Acceptable performance is demonstrated in 91.4% of the 463 triplicate analyses performed since 1964 and is illustrated in Figure F-1, EPA Performance Evaluation. Agreement is I established for 95.9% of the analysis when alternate evaluation methods are applied such as: Comparing the RL results with the reported " grand average' of the I participating laboratories in the EPA program. This method has merit when the " grand average" indicates the EPA known value is suspect. I E.4 g
3 I . Application of the RL's agreement criteria of 115% for precision and accuracy. This performance appraisal also includes the data from Sr-89, Sr-90, and gross alpha analysis which are not a REMP requirement. These analysis types I are among the most difficult to perform and represent the majority of our nonagreements, o USCEA/NIST Hessurement Assurance Program f or the Nuclear Indust ry - I This program became available to the industry in July 1987. serves the utility and standards supplier by providing standards and test It primarily samples, to perform calibration, and to develop new standards and calibrations I related to the quality control of radioactivity measurements in the nuclear power industry. Participants are able to demonstrate, to the degree established by periodic acsays of calibrated radioactivity samples prepared by the NIST, continuing competence to maintain the instrument systems and I standards necessary for accurate measurements, i.e. to demonstrate traceability to the NIST. The USCEA/NIST program is being utilized by Houston Lighting and Power as the cornerstone to a number of NIST traceable analytical I activity and programs. The USCEA/NIST program provides direct technien1 interaction with the NIST so that the RL can satisfy specific QC requirements found in Regulatory Guide 4.15, sections 6.1 and 6.3.2, hence providing a technical basis for calibration and interlaboratory QC services it provides. The RL has participated in thirty-nine USCEA/NIST studies since July 1987 resulting in a reported mean difference of approximately 5% from the NIST , I values. Figure F-6, USCEA/NIST Performance Summary July 1987-October 1990, illustrates the overall level of success the Radiological Laboratory has experienced with the USCEA/NIST program in comparison to the other g participants. The total number of analyses performed by the participants is 5 smaller because all the data is not available at this time. In summary, Figure F-6 shows that nearly 95% of all test results fall within the nominal 10% agreement criteria established by the RL and compares favorably with the performance of the other partdcipants. Table F-3 at the end of this section addresses individual test results by l I comparing both the RL performance and other participating laboratories to the reported NIST value.
*o Battelle Pacific Northwest Laboratory TLD Intercomparison Program -
Starting in the 2nd quarter of 1990 the Radiological Laboratory began using , Battelle as a quality cont rol service for environmental TLDs. On a quarterly l bacis five Panasonic UD-814(e) TLDs are irradiated to 15-30 mR by Battelle and then analyzed by the Radiological Laboratory. Figure F-4, Battelle I Intercomparison for Environmental TLDs, shows the percent difference from the known exposure for the 15 measurements. The average percent difference from I these measurements was 6% with no single measurement exceeding 15%. o State of Texas and the U.S. Nuclear Regulatory Commission Co-location Programs - The State and NRC have co-located TLDs with select REMP stations j over the years. TLD co-location data is presented in Section J. Other State co-located sample types (e.g. broad leaf vegetation, air particulate filter) were identified in a duplicate sampling and analysis schedule which was introduced late in 1990. No data is available at this time for comment. F-5
TABLE F-1 I DUPLICATE / SPLIT RESULTS 1990 1985 - 1989 AVERAGE % AVERAGE % NUMBER OF DIFFERENCE NUMBER OF DIFFERENCE I SAMPLE MEDIA ISOTOPE SAMPLES FROM KEAN SAMPLES FROM MEAN I Air Airborne 96 7.29% 406 8.75% I Particulate Alpha Beta Be-7 98 8 2.30% 1.84% 426 34 3.34% 3.51% Cs-134 -- -- 2 10.97% I Cs-137 K-40 Ru-103 8 12.14% 4 34 2 1.28% 12.83% 10.39% Air Iodine I-131 -- -- 6 5.001 TLD mR/qtr. 32 1.60% 160 1.60% Boll /Bediment I Shoreline Sediment Be-7 Cs-137 K-40 2 4 32.88%
.i2%
6 24 34 11.59% l' 02% 2.72% Soil Sr-90 -- -- 4 22.57% Be-7 -- -- 2 27.83% Cs-137 2 1.09% 34 5.80% K-40 2 11.64% 34 2.89% Aquatic Biological Piscivorous Cs-137 2 16.87% 4 20.59% Fish K-40 2 3.14% 22 2.26% I Arthropod-ivorous Fish Cs-137 K-40 2 5.06% 2 10
.07%
3.92% Crustacean Sr-90 -- -- 2 2.04% Crab K-40 -- -- 4 9.57% ( Crustacean K-40 2 7.46% 2 4.08% l Shrimp lI I i F-6 I
I TABLE F-1 DUPLICATE / SPLIT RESULTS I 1990 AVERAGE % 1985 - 1989 AVERAGE % NUMBER OF DIFFERENCE NUMBER OF DIFFERENCE I SAMPLE MEDIA ISOTOPE SAMPLES FROM MEAN SAMPLES FROM XEAN I Terrestrial Biological Banana Leaves Sr-90 -- -- 4 30.65% Be-7 -- -- 20 4.42% K-40 -- -- 20 3.03% Cana Leaves Sr-90 -- -- 4 16.09% Be-7 ( 4.75% 32 8.26% K-40 4 3.94% 32 4.73% Turnip Greens Be-7 -- -- 2 10.76% K-40 -- -- 2 16.61% Cabbage Be-7 -- -- 4 11.15% Leaves K-40 -- -- 4 9.00% Collard Be-7 4 2.69% 4 14.28% Greens K-40 4 6.40% 4 4.95% Pasture Grass Sr-90 -- -- 2 19.00*. Vegetation Be-7 6 9.49% 30 8.12% I-131 -- -- 2 2.26% K-40 6 11.81% 28 6.73% Sorgham Be-7 -- -- 4 16.10% Cs-134 -- -- 2 15.20% I Cs-137 -- -- 4 6.69% K-40 -- -- 4 7.42% Turnip Roots Cs-137 -- -- 2 16.46% K-40 -- -- 2 3.84% Soy Beans K-40 -- -- 2 2.88% Beef Meat K-40 -- -- 4 J.10% Wild Swine K-40 -- -- 6 .71% Game Deer K-40 2 4.06% 6 3.56% I F-7 I
I , TABLE F-1 DUPLICATE / SPLIT RESULTS I 1990 AVERAGE % 1985 - 1989 AVERAGE % NUMBER OF DIFFERENCE NUMBER OF DIFFERENCE I SAMPLE MEDIA ISOTOPE SAMPLES FROM KEAN SAMPLES FROM KEAN I Goose K-40 2 3.99% 8 5.00% l 1 Water Drinking Beta 2 12.02% 14 11.52% f Water j I Surface Water H-3 2 1.26% 2 32.54% l 1 I I l I ! l I I i 1 I I I I I I F-8 I
r o Figure F-1 x EPR PERFORMANCE EVALURTION JANURRY 1984 - DECEMBER 1990 2 e-1.5% 1.7% St.4% 2 . 8 :.
)
l l l 463 Triplicate Analyses Performed E Results ialI within a normalized dev6ation of 3 (EPA agreement criteria) N Hgreement has been established based on RL criteria. E Hgreement has been established based on the ' grand average'.(EPR value suspect) E Results unacceptable due to RL reporting error. E Results unacceptable due to poor an a l y t ic a l perfor=ance. F-S
- mi ;t!I'i!tii ,.- t[l' I \ i' ,il ii
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TOTAL RNRLYSES: 171 l E 0- 5% 5 16-25% I E 6-10: E >as: E 11-15 F-11
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7 -, ,-. Figure F-6 USCER/NIST PERFORMANCE
SUMMARY
JULY 1987 - OCTOBER 1990 OTHER PRRTICIPRNTS HL&P RADIOLOGICRL LABORATORY SI. q
'O 0
r db 9 w ,.
,11-Q ,
! TOTRL RNRLYSES: 35 TOTRL ANALYSES: 39 l Difference from NIST E 0- 5% B s-10% 5 >10% i F-14
I I TABLE F-2 TABLE OF CONTENTS NIST PERFORMANCE BY TEST NUCLIDE P.agi See AMPOULE Co-60 (July 1987)............................................ F-17 I- 131 (Fe bru a ry 19 8 8, Fe b ru a ry 19 9 0 ) . . . . . . . . . . . . . . . . . . . . . . . . . F-17 Fe-59 (January 1989, August 1990)............................ F-17 Ce-139 (January 1989)........................................F-17 & 19 Ce-141 (January 1989)........................................ F-18 Ce-144 (Janaury 1989, August 1990)...........................F-18 & 19 Ba-133 (August 1989)......................................... F-18 Cr-51 (August 1990)................... ...................... F-19 Zn-65 (August 1990).......................................... F-19 Ru-106 (August 1990)......................................... F-19 47arn AIR PARTICULATE FILTER / Ocm DISTANCE FROM DETECTOR Cs-137 (June 1988)........................................... F-20 Co-60 (June 1988)............. .............................. F-20 Co-57 (June 1988)............................................ F-20 47 nun AIR PARTICULATE FILTER / 15cm DISTANCE FROM DETECTOR Ca-137 (June 1988)........................................... F-21 Co-60 (June 1988)............................................ F-21 Co-57 (June 1988)............................................ F-21 Cr-51 (November 1989)........................................ F-21 Sb-125 (November 1989)....................................... F-21 Ca-134 (November 1089)....................................... F-21 Ce-141 (November 1989)....................................... F-21 F-15
TABLE F-2 TABLE OF CONTFNTS , NIST PERFORMANCE BY TEST NUCLIDE L (cont'd)
" .P, alt 47aen AIR PARTICULATE FILTER / 15cm DISTANCE FROM DETECTOR Co-57 (June 1990)............................................ F-22 Zn-65 (June 1990)............................................ F-22 Cs-137 (June 1990)................................. ......... F-22 i 35cc GAS BULB AT 15cm FROM DETECTOR Kr-85 (May 1988, Septembe r 1989, October 1990) . . . . . . . . . . . . . . .F-23 & 24 Xe-133 (August 1988, September 1989, October 1990)...... ....F-23 & 24
.Xe-127 (October 1990)........................................ F-24 Sr-89 / Sr-90 BY CAS PROPORTIM AL Sr-89 (November 1988, March 1989)............................ F-25 Sr-90 (November 1987, March 1989)............................ F-25 TRITIUM BY LIQUID SCINTIILATIN H-3 ( Se pt embe r 19 8 7, J anua ry 19 9 0 ) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . F-26 1
F-16
, , _. , , , > w USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW GRMMR ISOTOPIC FOR SCC RMPOULE AT 15 CM 16%
15% - 14% - 13% - 12% - Z 11% - E g , . , , Nomin al, ,$esement Objec t ive ~ 8.95% _ 32 .. d 8% - b 7% ~ 6% - b 5% - 3.8% 3.55% 4% - 3.1%
- \* -
3% - 2.5% 87% 2% - 1% ~ I-131 Fe-59 Co-60 I-131 FEB 1988 FEB 1990 JUN 1989 JUL 1987 RNRLYSIS TYPES E Radiological Laboratory M Neage dif f erence of participating laboratortes (analysts method unknoun) ,1 F-17
USCER / NIST RADIOLOGICAL-LRBORATORY PERFORMANCE REVIEW GRMMR ISOTOPIC FOR SCC RMPOULE AT 15 CM 16% 15% - 14% - 13% - b 12% - 11% - E 3gg .
'b"i a
- I. .N'.****at .@ jee t 1,w, , ,,
g s.sz _ E 3 , d et - 7% -
&.5%
w g., 5% '~ 4.4% 4% - 3.5% g 2.52 - 3% ~ Ce-139 Ce-141 Ce-144 Ba-133 l JAN 1589 JAri 1989 AUG 1989 JRH 1989 l RNRLYSIS TYPES E Radiologttal 1 aboratory M Neage dif ference of participating laboratortes (analysts method ekneel e Date not avat table F-18
m1 rn 1 t > USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW GRMMR ISOTOPIC FOR SCC RMPOULE AT 15 CM 16% 152 - 14% - 13% - h 12% - Z !!% - g ,,, . . . metn.i w ..-,,t m tt.. k 9x . y 8% - 5 5 ?% 6% - s2 - 4x .- 3,,gg 3% -
'9 -
2% - II ' _ 33g C. Zn-65 Ru-106 Ce-144 Cr-51 Fe-59
- RUG 1990 eRJG 1990 OUG 1990 AUG 1938 RUG 1990 RNRLYSIS TYPES E Rad 6ciogical Laboratory M Average dif ference of participating laboratorses (analysts method unknown) e Vatwo corrected after NIST deterstaattoa. 4 Rt treascetption error in report.
F-19
aus e um uma um uma sus - uma num aus sus . sus luis m uma uma mut mim USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW GAMMR ISOTOPIC FOR RIR PRRTICULRTE AT 0 CM
-15.32 15% -
14% - 13% - 12% - Z 11% - y ggg . . . 9*1"*I. ?S".****at. .objget 1,sre , , , , f 9x ..
-7.6% -
d 8% .- 6.5% h 72 . (E - 6% - y s% 7 4..% s= 4.3x 3 gg .. 32 ._
~~
Cs-137 Co-t- 5 Co-57 JUN 1988 J1JN 1-.88 Jun IS88 RNRLYSIS TYPES M Radtofegtcal Lakeratory M r%erage d1Herence of participating laboratertes f analysts wethod unknownf F-20 l
-uu v 1 -
USCER / ' NIST RADIOLOGICRL LABORATORY PERFORMANCE REVIEW GAMMR ISOTOPIC FOR RIR PARTICULATE AT 15 CM 16% . 15% - 14% - 13% - 12% -
~
Z !!% - 10.3% g gg .. rio?'aal. *se? = at 0bject'v= 9% - d 8% ~
' $2 _
5 7% .
-5 822
$ s2 ..
~
5.32% s2 4.55= g - 4.4% 4.3, 3.42%
~
4% ~ 3.53% y _ s Cs-137 JUN ?998 _.5% Co-60 JUN 1988 Co-57 JUN 1988 Cr-51 t4OV 1989 Sb-125 NOV 1989 Cs-134 NOV 1989 43, Ce-241 NOV 1989 AtlRLYSIS TYPES E Radiological Laboratory M Peerage dif ference of parttcipating laboratertes f analysts oathed unknown! F-21
MEMMM USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW GRMMR ISOTOPIC FOR RIR PARTICULATE AT 15 CM 15% 15% -
~'
142 ._ 13% - h m 12% - Z 11% - 93'.**"ent,, H ect,sye. E .g2 .. .* "8"*I. 3% - d 8% -
?X -
5% --
< "1 -
m c
-4.21%
~
4% -- -3.552 -3.38% g 2.87% , 2.16% Co-57 2n-65 Cz-137 JUN 1990 Juri 1990 JU 4 1990 RftRLYSIS TYPES E Radiological Laboratory M Aerage dif ference of parttelpating laboratories f analysts esthod unknowel F-22
.- -. - - - -.-_ -...-.-_.. - _ ._ ..--._ ..-.- _.- _.-~.- _ - _._ -._ _ - ---.-- -.-.
e ama m . 'm.m m a m m eum m m .m m 1 USCE R.- / NIST RADIOLOGICAL lRBORATORY PERFORMANCE REVIEW GAMMR ISOTOPIC FOR 35CC BULB RT 15 CM IS% 15% - -- i 14% - - 1 13% -- - M 12% - - 1 Z 11% - teat
~
l 10% --
>N "8"*igreement,0bjective 9% - -
d 8% - b 7% - 6.8% _ E% - N 5% --
, 4% -
3.5% 37* 3 #* - Kr-85 Xe-133 Kr-85 Xe-133 r1RY 1988 Rt.tG 1988 SEP 1983 SEP 1983 RNALYSIS TYPES E Radiological Laboretcry M Aerage difference of partecipating laboratories (analysis mothed unknown) F-23
- _ _ _ - - _ - _ ._ _ _ _ __ __ _ - - -- _ . . -- - . - ~ .--
. _ , ., _ , v ,---, , , ,.
USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW GAMMR ISOTOPIC FOR 35CC BULB RT 15 CM 16%
~
25% --- 14% - 13% - h 12% - Z t1% - Noo r n al, ,Rgreemen t Objec t a ve La. 3% - d 8% - b 7% - tr - 6% - e-o 5% - Q -3.572 - 4% -
-3.51%
3% -
~
~
1.22%
~
1% g . . . ._ . . Xe-133 Kr-95 Xe-127 OCT 1990 OCT 1993 OCT 1990 RNRLYSIS TYPES (non blind) M Radiolog6 cal Laboratcry M R<erage dif ference of participating laboratertes f analysts mothed unknown) l a Cata not avettable F-24
u t__s 1 i t 1 USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW SR-89 / SR-90 RS R PRECIPITATE USING GAS PROP 0RTIONRL COUNTER 76%
~
15% -
~
14% - 13% - M 12% - Z !!% -
-- H "'"*t Agreement Obpeteve __
10% - b **#* ~ 9t - e.4% La.I gg y -7.2% W 7% - L
-S 7% -
l 6% - h 5% - a ~ l 4% ~ 3.4% x ~ 3% - 2.4% 2% -
.18% ,get Sr-89 Sr-9.' Sr-83 Sr-90 NOV 1988 NOV ISa/ MR8i 1989 MAR 1989 ANALYSIS TYPES M Radiological Labcratory M Aer sos d 6f ference cf participating laboratories (analys ts method unkncum) i F-25
mis as as uma e um sul m um m - m gui aim m em m m m , USCER / NIST RADIOLOGICAL LABORATORY PERFORMANCE REVIEW TRITIUM BY LIQUID SCINTILLATION 28% is.4sx 15% - 14% - 13% - U1 I2% ~
~
z tit - h 10% -- - " ' "
- k Y * * **"
- D'* * * ** -
E 9% -
$ et -
5 m 7% _ 4 s= _ E '* - s.3x
~
I g st - 4% - 3 72 - 3% - 2% - 1% - CX ' - - H-3
- H-3 SEP 1987 JRN 1990 RNRLYSIS TYPES *(non blind)
M Rad:olegtcal Laboratory M Rverage dif ference of partsctpating laboratorf es f analysis method unknown) i F-26 ; t
4 1 TABLE F-3 TABLE OF CONTENTS EPA TRENDING GRAPHS 4 AIR PARTICULATE Beta......................................................... F-28 Strcntium-90...............................................i. F-29 Cesiua-137................................................... F-30 i I COW .5 LK Potassium-40................................................. F-31 i Strontium-89.................................................. F-32 Strontium-90................................................. F-33 Cesium-137................ .................................. F-34 DRINKING WATER I Beta......................................................... F-35 Tritium...................................................... F-36 L Cobalt-60.................................................... F-37 l I .Zine-65...................................................... F-38 i l Strontium-89................................................. F-39 Strontium-90................................................. F-40 I Ruthenium-106................................................ Iodine-131................................................... F-41 F-42 Ba-133....................................................... F-43 l l Cesium-134................................................... F-44 l Cesium-137................................................... F-45 4
- I
- I F-27
M M M M M M M' W W M M M M M M- M W M M EPR INTERLABORATORYCOMPRRISON BETR IN RIRBORNE PARTICULRTE 1989 1990 JAN FEB MAR RPR MRY JUN TUL RUG SEP OCT NOV DEC JPN FEB MRR RPR MAY JUN JUL RUG SEP OCT NOV DEC 100% 5 00% E x 60% 40% G 2 20% e y c 0% . - - . . _ . - . -- D
~
s i m -20%
$ -40% .
a C -60% E
.g -80%
-100%
o e ru 8 $ 8 8 8 8 m m m Sample Lab Number F-28
m sus e m- m- - m em m m e e e e m-EPR INTERLRBORATORY COMPARISON SR-90 IN RIRBORNE PARTICULRTE 1989 1990 JRN FEB MAR RPR MAY JUN JUL RUG SEP OCT NOV DEC JRN FEB MAR BPR MAY JUN JUL RUG SEP OCT NOV DEC 100% 5 00% E M 60% 40% E E 20%
<+.
c ex p O (D N -20% 5
$ -40%
e C -50% - E y -80%
-100%
0 $ $
$ $ 8 8 8 8 Sample Lab Number g F-29
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I I SECTION G RESULTS DATA
SUMMARY
TABl.ES DESIGN Table G-1, 1990 Annual Radiological Environmental Operating Report Summary, !c a digest of the REMP analytical data. Raw data, as found, in I Addendum 1, STPEGS REMP Results Data was used for this evaluation. No additional data manipulation was performed to eliminate data from this section. Therefore, in a few situations false positive measurements or misidentification of the nuclide are noted. For an edited list of only I relevant and verified positive measurements see Table J-2, Measurement Activity in Environmental Media. The summary has been designed in a format l that is similar to the format found in the NRC November 1979 Branch Technical Position. Modifications were for the sole purpose of reading ease. The type of media is printed at the top lef t of each page, and the units of measurement are printed at the top right. The left-hand column contains the radionuclide followed by the total number of analyses of the radionuclide and the number of I nonroutine measurements in the second column. For the purpose of this report, "nonroutine' is a result exceeding the values listed in Table C-3. At a future date 'nonroutine" will probably be redefined. A more relevant and I meaningful definition might be measurements which exceed ten times the yearly average background or preoperational value. The next column lists the average achieved Lower Limit of Detection (LLD) for each analysis type. Written i l I directly below is the committed LLD that is referenced in Table C-2. data are reported using two significant digits in order to establish consistency in the report and to parallel estabirshed conventions in similar Results I j reports. j l I Those sampling stations which could conceivably be affected by the ! operation of STPEGS are identified as ' Indicators." Stations which ese I assumed to be beyond plant influence are called ' Controls." Ser.pling stations and their status have been listed in Table D-2. I A set of statistical parameters are calculatso for each radionuclide for each media. This set of statistical parameters includes separate analyses for (1) the indicator stations, (2) the station having the highest annual mean concentration, and (3) the control stations. For each of these groups of data, the following is calculated:
- 1) The mean value (including negative values and values below the LLD).
- 2) The fraction of analyses that the results were greater than 3 times the random error.
- 3) The lowest and the highest calculated' concentration.
I I G-1
I I ESULTS I Typically, the achieved LLDs are significantly lover than those comitted in Table C-2. As an example, LLDs for gross beta in water will average a factor of five below the requirement while the LLD for gross beta in air particulate will be orders of magnitude below the committed level. In the case of I-131 in drinking water, no committed LLD is indicated. The reasoning is drinking water in the vicinity of STPEGS originates from deep wells in which I-131, with its 8.04-day half-life along with the slow migration of I surface water to the aquifer, does not constitute a pathway. Similarly, there would also be no I-131 LLD indicated for stored grains (e.g. rice, soy bean, etc.) becauce of the long periods between sample harvest, sample combine and l sample analyses. l l I In the event of a milk sample, results data for I-131 could be listed twice because milk is analyzed gamma isotopically and possibly by a ruore I sensitive rtethod (radiochemical / beta-gamma coincidence). The analysis requiring radiochemistry is noted with a "c." l In summary, positive measurements (e.g. tritium in the HOR) were within 8 anticipated ranges and control data appeared consistent with historical data. There were no nonroutine measurements and all the achieved average LLDs were less than the connitted sensitivities found in Table C-2. 1 I ! I I I I I I I I G-2
.. _ .- _-. - . - . _ .- . - = . _ . _. . -.
I TABLE G-1 TABLR OF CONTENTS
.h W ANNUAL RADIO 1DGICAL ENVIRONMENTAL OPERATING REPORT I
SUMMARY
P a r. ' VATERS I Drinking...................................................... G-5 Ground Water.................................................. G-6 Surface....................................................... G-7 SYDIMFNT/ SOILS Sediment...................................................... G-8 So11.......................................................... G-9 YEGRTATION Banar.a Leaves................................................. G-10 Cana Leaves................................................... G-11 Collard Greens................................................ G-12 Pasture Grass................................................. G-13 BIRDS Resident Dabbler Duck.................................... .... G-14 Higratory Dabbler Duck........................................ G-15 Goose......................................................... G-16 Dove.......................................................... G-17 Qus11......................................................... G-18 AQUATIC ANIMALS Piscivorous Fish.............................................. G-19 B Arthropodivorous Fish......................................... G-20 Crustacean Crab............................................... G-21 1 i Crustacean Shr1mp............................................. G-22 1E I G-3
e I J W TAB 1.E G-1 (Cont'd) Par.e TERRESTRIAL ANTMAIS Beef.......................................................... G-23 Wild Swine.................................................... G-24 G arc e D e a r . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . G-25 A111 gator..................................................... G-26 AIR Air Particulate............................................... G-27 Air 1odine.................................................... G-28 ENVIRONMENTAL TI.D............................................... G-29 I NOTE: For consistency, all values are reported as having two significant digits. I I I
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'M M M M M M M M M M M M M M M M M M M TABLE G-1 1990 ANNUAL RADIOLOGICAL ENVIRONNENTAL OPERATING REPORT SUIDULRT MEDIUM: Beef Neat UNITS: pCi/Kg wet wt ANALYSIS TOTAL 'UtALYSES/ LOWER LIMtf tuDICATOR LOCAft0wS LOCAft0N WITM NIGNEST AwwuAL MEAM CONTROL LOCAfl0NS TYPE NautolfftWE OF DETECTION
- MEAN ( f ) ** LOCAft0N ME AN ( f ) ** MEAM ( f ) **
E ASUREMENTS RAuGE IwFORMATION RAwCE RANGE t-131 1/ 0 3.5E+01 no seaples 4-6 miles SE-SSE -3.0E+01( 0/ 1) -3.0E+01 ( 0/ 1) 6.0E+01 (#Z63) (-3.0E+01 ~ 3.0E+01) (-3.0E+01 ~ 3.0E+01) Cs-134 1/ 0 4.4E+00 no senptes 4-6 miles SE-SSE -3.8E*00( 0/ 1) -3.8E+JO ( 0/ 1) 6.0E+01 (fz63) (-3.8E+00 ~ 3.8E*00) (-3.8E+00 --3.8E+00) Cs-137 1/ 0 5.0E+00 no sa m tes 4-6 miles SE-SSE -2.7E+00( 0/ 1) -2.7E+00 ( 0/ 1) 8.0E+01 (tz63) (-2.7E+00 ~ 2.7E+00) (-2.?E+00 a-2.7E+00) Mn-54 1/ 0 5.1E+00 no sneptes 4-6 miles SE-SSE -5.7E+00( 0/ 1) -5.7E+00 ( 0/ 1) (#263) (-5.7E+00 ~ 5.7E+00) (-5.7E+00 ~ 5.7E+t0) Fe-59 1/ 0 1.5E+01 no sa mtes 4-6 miles SE-SSE -1.1E+01( 0/ 1) -1.1E+01 ( 0/ 1)
--- (fI63) (-1.1E+01 ~ 1.1E+01) (-1.1E+01 ~ 1.1E+01)
Co-58 1/ 0 6.0E+00 re senptes 4-6 miles SE-SSE -3.2E+00( 0/ 1) -3.2E+00 ( 0/ 1)
--- (f263) (-3.2E*00 ~ 3.2E+00) (-3.2E+00 ~3.2E*00)
Co-60 1/ 0 3.2E+00 no serptes 4-6 mites SE-SSE -5.7E+00( 0/ 1) -5.7E+00 ( 0/ 11 (fz63) (-5.7E+00 ~ 5.7E+00) (-5.7E+00 ~ 5.7E+00) In-65 1/ 0 1.3E+01 no serptes 4-6 miles SE-SSE -1.5E+01( 0/ 1) -1.5E+01 ( 0/ 1) (r763) (-1.5E+01 ~ 1.5E+01) (-i.5E+01 *-1.5E+01) s Zr-95 1/ 0 1.2E+01 no sneptes 4-6 mites SE-SSE -2.5E+00( 0/ 1) -2.5E+00 ( 0/ 1) (f763) (-2.5E+00 ~ 2.5E+00) (-2.5E+00 ~ 2.5E+00) wt>-95 1/ 0 6,4E+00 no sepptes 4-6 miles SE-SSE -5.4E-01( 0/ 1) -5.4E-01 ( 0/ 1)
--- (rZ63) (-5.4E-01 ~ 5.4E-01) (-5.4E-01 ~ 5.4E-01) so-140 1/ 0 4.4E+01 no snaptes 4-6 miles SE-SSE -2.7E+01( 0/ 1) -2.7E+01 ( 0/ 1)
(*I63) (-2.7E+01 ~2.7E+01) (-2.7E+01 ~ 2.7E+01) to-140 1/ 0 1.9E+01 no samtes 4-6 miles SE-SSE -3.9E+00( 0/ 1) -3.9E+00 ( 0/ 1) (fI63) (-3.9E+00 ~ 3.9E+00) (-3.9E+00 ~ 3.9E+00)
- AVERAGE MEASURED LLD AND taste C-2 VAttKS. (--- USED WNEW THEtt IS NO REctHRDuENT.)
** FRACTION OF DETECTA8tE MEASUREMENTS At SPECIFIED toCAftous IS tu0!CATED 14 PARENTNESES. ( f )
*** SEE TABLE 0-2 FOR STATION DESCRIPTION.
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M : - M M M M M M M M M M M M M M M TABLE G-1 1990 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT
SUMMARY
MEDIUM: Airborne Particulate UNITS: pCi/M'3 ANALYSIS TOTAL ANALYSES / LOWER LIMIT INDICATOR LOCATIONS LOCATION elTN MICHEST ANNUAL MEAN EDNit0L LOCATIONS TYPE WONROUTINE OF DETECTION
- MEAN ( f ) ** LOCATION MEAN ( f ) ** 8'EAN ( f ) **
MEASUREMENTS RANGE INFORMATION RANCE RANE sete 515/ 0 9.7E-04 1.9E-02 (463 / 463 ) 9 miles W 1.9E-02 ( 52 / 52 ) 1.9E-02 ( 52 / 52 ) 1.0E-02 ( 6.4E 4.9E-02) (#039) ( 8.5E 4.8E-02) ( 8.5E 4.9E-02) I-131 41/ 0 7.6E-03 -1.1E-04 ( 0/ 37 ) 1 mile NW 2.2E-03 ( 0/ 4) -3.3E-03 ( 0/ 4) 7.0E-02 (-4.8E 6.1E-03) (#016) (-1.8E 6.1E-03) (-5.9E-03 ~ 1.9E-04) Cs-134 41/ 0 2.7E-04 -2.7E-04 ( 0/ 37 ) 1 mite N -1.1E-04 ( 0/ 4) -2.0E-04 ( 0/ 4) 5.0E-02 (-2.7E 7.0E-06) (#001) (-1.4E-04 ~ 7.3E-05) (-2.4E-04 ~ 1.5E-04) Cs-137 41/ 0 3.0E-04 4.OE-05 ( 0/ 37 ) 1 mite W 1.9E-04 ( 0/ 5) 1.2E-05 ( 0/ 4) 6.0E-02 (-1.6E 1.1E-03) (8015) (-7.5E 1.1E-03) (-4.2E 4.1E-05) Mn-54 41/ 0 3.1E-04 1.4E-05 ( 0/ 37 ) 1 mite W 8.6E-05 ( 0/ 5) -5.6E-05 ( 0/ 4) (-1.6E 4.3E-04) (8015) (-4.5E 4.3E-04) (-1.4E-04 ~ 1.7E-05) Fe-59 41/ 0 1.2E-03 -3.6E-05 ( 0/ 37 ) 8.5 miles SSE 1.4E-04 ( 0/ 4) -1.5E-04 ( 0/ 4) (-1.1E 6.9E-04) (8035) (-1.2E 4.4E-04) (-6.3E 1.7E-04) Co-58 41/ 0 4.4E-04 -6.6E-05 ( 0/ 37 ) 1 mile kW -1.6E-05 ( 0/ 4) -1.5E-04 ( 0/ 4) (-4.4E 1.9E-04) (8016) (-l.9E 1.1E-04) (-3.0E 3.8E-05) Co-60 41/ 0 3.2E-04 3.3E-05 ( 0/ 37 ) 1 mile W 3.1E-04 ( 0/ 5) -4.4E-05 ( 0/ 4) (-1.1E 1.5E-03) (8015) (-4.5E 1.5E-03) (-2.0E 5.t?E-05)
, Zn-65 41/ 0 6.9E-04 -2.0E-04 ( 0/ 37 ) 5.5 mites NME -6.7E-05 ( 0/ 4) -3.6E-04 ( 0/ 4)
(-2.8E 3.5E-04) (8018) (-4.5E 3.0E-04) (-4.5E-04 ~ 2.9E-04) 2r-95 41/ 0 8.3E-04 -1.0E-05 ( 0/ 37 ) 5.5 miles NME 2.6E-04 ( 0/ 4) -8.9E-05 ( 0/ 4) (-8.4E 7.4E-04) (#C18) (-9.EE 7.4E-04) (-1.9E-04 ~7.5E-05) Mb-95 41/ 0 4.8E-04 -2.7E-05 ( 0/ 37 ) 14 miles NME 1.8E-05 ( 0/ 4) -1.4E-04 ( 0/ 4) (-3.OE 2.2E-04) (8033) (-3.6E 1.3E-04) (-3.8E-04 ~1.7E-05) I Ba-140 41/ 0 7.1E-03 1.2E-03 ( 0/ 37 ) 1 mite N 2.8E-03 ( 0/ 4) -1.3E-03 ( 0/ 4) 1 (-3.9E 5.0E-03) (#001) ( 5.5E 4.0E-03) (-5.8E 1.2E-03) La-140 41/ 0 3.4E-03 2.4E-05 ( 0/ 37 ) 5.5 mites NME 8.8E-04 ( 0/ 4) -7.5E-04 ( 0/ 4) (-2.8E 3.4E-03) (#018) (-7.5E 2.4E-03) (-1.8E 6.0F-04)
- AVERAGE MEASURED LLD AND 1 ABLE C-2 VALUES. (--- USED WHEN THERE 15 NO REQUIREMENT.)
** FRACit04 OF DETECTABLE MEASUREMENTS AT SPECIFIED LOCATIONS IS INDICATED IN PAPENTMESES. ( f )
*** SEE TABLE D-2 FOR STATION DESCRIPTION.
G-27 l
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I O R 0 t T N 3 - D M G O AA CE I M 0E E
- 4
- E
- l
- f L D 61 -
( t O N I 1 (
- SP
.C E I KS D t M A R
- tT .
AAN V SI O TN 2T T I O 22 - NP L NI 00 CEI MR A I T LC EE EEC U 1 0 LRS M N RT EE WD' E 17 SUE ASD TA N O A e LF O DMNO N n aft tA I 0 i / DBT M 9 d 9 o S EET SNN S LAS LT CR 1 I Yt E DEO lim ETF Af t E 0 kE NoR UD2 r ARU NS 9
/ S Af D i EO M A LOA AME T
O M 1 5 M NL OB E T EI ATT A
- RC EAE M S VRE AFS M U I SE 1 I YP 3 * *
- LY 1 *
- D AT N
E A l M M M l l llIl t
m m m m m m mM M m m m m - m m m. s TABLE G-1 1990 ANNUAL RADIOLOGICAL ENVIRONMENTAL CPERATING REPORT
SUMMARY
MEDIUM: Immersion Dose by TLD UNITS: mR/STD Quarter ANALYSIS TOTAL ANALTSES/ LOWER Ll4ff IN01CATOR LOCATIONS LOCATI M VITH NICHEST ANNUAL MEAN CONTROL LOCAfl0NS TYPE NONROUTINE OF DETECTION K2AN ( f ) ** LOCATION MEAN ( f ) ** MEAN ( f ) ** MEARIREMEWYS RANGE INTORMATION RANGE RANGE Came 178/ 0
- 1.5E+01 (167 / 169 ) 1 mile W 1.9E+01 ( 5/ 5) 1.7E+01 ( 9/ 9)
( 1.2E+01 ~ 2.0E+01) (#013) ( 1.9E+01 ~ 2.0E+01) ( 1.4E+C1 ~ 1.9E+01)
- AVERACE HEASURED LLD AND TABLE C-2 VAttES. (--- USED WHEN THERE IS NO REQUIREMENT.)
** FRACTION OF DETECTAstE MEASUREMENTS AT' SPECIFIED LOCATIONS IS INDICATED IN PARENTMESES. ( f)
*** SEE TABLE D-2 TOR STATION DESCRIPTION.
G-29
SECTION H EPA ENVIRONMENTAL RADIATION AMBIENT HONITORING SYSTEM l DESIGN /OBRCTIVE l l The EPA Environmental Radiation Ambient Monitoring System (ERAMS) is i administered by the EPA Eastern Environmental Radiation Facility in Montgomery, Alabama. This organization is responsible for generating a quarterly Environmental Radiation Data Report. These reports evaluate analysis results data from their national network of sampling locations and 1 (. similar networks operated by contributing states, Canada, Mexico, and the Pan j American Health Organization, l j The ERAMS network of sampling locations provides optimal population !' coverage while functioning to monitor fallout from nuclear devices and forms l of radicactive contamination of the environment. This network was of i particular interest to operating nuclear plants during the Chernobyle accident by providing additional data that aided in differentiating plant-related ; releases from the Chernobyle contribution. The monitoring effort also provides routine ancillary information on natural background levels and i releases into the environment from stationary sources such as nuclear power reactors, fuel fabrication facilities, and reprocessing plants. The EPA has established a surf ace water monitoring station on the l Colorado River south of STPEGS. Samples are collected quarterly with a gamma l isotopic analysis being performed in the second quarter and a tritium analysis in the remaining quarters. The exact sampling location has not been made available nor has the collection or sample preservation methods. Without , knowledge of the specifics or having an available sample aliquot, the EPA data l is being evaluated solely as an additional source of environmental data and should not be regarded as a quality check of the REMP data. The EPA's program may be expanded in the future to include additional sampling locations, media, and analysis if funding is available. RESULTS ERAMS reports #59, #60, #61, #62, #63, and #64 (July 1989-December 1990) I were reviewed or discussed with the EPA. No positive measurements were ! reported other than for K-40 with the exception of a single tritium result for I' a sample collected 10-10-89. The reported concentration in ERAMS Report #60 was 500 pCi/kg + 200 pCi (2 sigma) or about two times the EPA's quoted LLD. The measurement is suspect and likely a false positive resulting from counting g instrument background fluctuation. REMP samples collected from more sensitive ,3 locations during this same period do not support EPA's value. Details of surface water analysis for this period can be found in the 1989 Annual Radiological Environmental Operating Report. ,I I Mn
l I ! SECTION I PROGRAM PERFORMANCE l OILTECTIVE/ DESIGN This section is a performance evaluation of the STPEGS REMP implementing obj e c t ive s . The prescribed REMP operating parameters are discussed and/or tabled in detail in Section C. The majority of the program commitments (sample collection, sample analysis) can be found in Table C-1, Radiological I Environmental Monitoring Program. The combined number of samples to be collected and radioanalytical analysis to be performed is approximately 2000. Factored into this count is a 101 duplicate and split requirement. A significant number of quality control samples (e.g. EPA, USCEA/NIST, I intralaboratory QC, etc.) were also analyzed in connection with routine REMP samples. Also, nonroutine or unspecified analyses of environmental samples, such as grains, that are not required per Table C-1, were processed. Program compliance is accomplished primarily by utilizing standard administrative control techniques and computer surveillance methods. Furthermore, quality assurance programs outlined in Section F provide additional assurance that program compliance has been maintained. The results of these surveillances are evaluated on a frequent basis and may be presented in numerous forms for review: u o graphic illustration (e.g. Figure I-1) o established " flag" protocol for analysis reports l o special computer-generated reports desigfed to sort for program I compliance (e.g. Table I-2), in-house memos regarding program status and logs l l l o comprehensive assessment as presented in the Annual Radiological Environmental Operating Report l REMP objectives may not be obtainable regardless of design or ef fort 'g because environmental surveillance work is often compromised by adverse and g dynamic environmental conditions that are inherent to the job. These conditions affect people and equipment alike. This was particularly true in l 1990 when drought and record low temperatures limited the crop yields in the I four REMP-maintained gardens. Also, difficulties associated with the preparation and analysis of samples cannot always be avoided. Recognizing this, the NRC allows for the deviation from the prescribed program by I g requiring it to be documented in the Annual Radiological Environmental i g Operating Report. By evaluating and documenting program compliance, l significant weaknesses in implementing program objectives are identifiable. RESULTS Figure I-1, STPEGS REMP Samples Collected, illustrates by cumulative i months the number of STPEGS environmental samples collected in 1990. The blue l line in the nominal program requirement as described in Table C-1. The green [ bar depicts the monthly status of required samples collected per Table C-1 and I-1 I
l I is regarded as the minimal program. The red bar depicts the total number of STPEGS environmental samples / month. The red bar total includes the minimum program, duplicate / split QC samples, special study samples and a significant number of air particulate and air iodine san.ples not stated in Table C-1. The additional air monitoring effort has been regarded as necessary considering the significance of the sample station locations (e.g. Selkirk Island, City of Matagorda, etc.). Twenty-two deviations in the REMP implementing objectives were identifled and are presented on Table I-1, REMP Performance Evaluation. This represents (1.00% of the actual STPEGS environmental samples collected and analyzed. The deviations did not compromise the program's effectiveness and, in fact, are considered insignificant when compared to what is anticipated for environmental surveille.nce and analysis work. Table I-1 lists the individual I deviations including the media code, sample location code, laboratory sample number, prescribed requirement, and a comment for each deviation. Table I-1 includes entries other than those representing a noncompliance. In fact, only the first twelve entries directly pertain to Table C-1 or Table C-2 compliance. No entries are regarded as serious in the sense of being unnessarily repetitive or not being satisfactorily addressed at this time. An entry may also be a deviation from what is regarded as the ideal program. For example, entries #13-18 show a substitute sample location used rather than the preferred sample location. However, substitutions of this type are expected and are permissible per Table C-1. Also, station #006, (entries #19-20) is I included but is not part of the minimum program identified in Table C-1. Station #006, adj acent to Sikirk Island, has historically been important and therefore its status is reported in Table I-1. Analysis LLDs have also been reviewed. LLDs are routinely evaluated for compliance by computer which compares them with nominal LLDs listed in Table C-2, Environmental Lower Limit of Detection Sensitivity Requirements. All required LLD's were met in 1990. Table I-2 The Sample Collection Schedule Table, was added to the annual report in 1989 in response to a concern identified in the NRC Inspection Report 88-085 which stated that REMP sample collection and analyses data found in Addendum 1 of the 1987 REMP Annual Report were not presented in a format which clearly demonstrated the requirements in Table C-1. Iable I-2 provides I a quick but detailed reference of the REMP requirements and the corresponding sample that satisfies that requirement. This analysis has been performed by the computer which establishes each sample status by comparing its sample I submittal information and the information stored with the assigned laboratory sample number against Table C-1 requirements. Table I-2 is separated into major media categories and further broken down by collection f requency. The sample number and collection date are included with each entry. The letters S or D may accompany a sample number and designate a split or duplicate sample, respectively. Deficiencies are noted and cross-referenced in Table I-1 with additional details. This table along with Table J-1, 1990 Environmental TLD Measurements, are the primary references for the 1990 REMP Performauce Evaluation, Table I-1. Table I-2 may also be used as a reference aid when reviewing the raw data in Addendum 1 of this report. I I-2
! M M M M M M M M M M M M' M- M M M M M .M FIGURE I-1 l STPEGS REMP SRMPLES COLLECTED 1990 l 1562 - U 1454 - 1351 - 1181 - U 1855 - 954 - 7s3 - 652 - w 514 - l U 375 - y 264 - [ 163 - t Jan Feb Mar Spr May Jun Jul Bug Sep Oct Nov Dec j gut Total number of samples co11ected in accordance utth ODCtf TBBLE B5-1 =099 l M Total of all samples collected - 1562 Prescrfbed sample commitments as per TBBLE C-1 ; I-3 l i i
M m M M M M M M M M M M
~
M M M TABLE I-I REMP PERFORMANCE EVAIEATION 1990 Location # Deviation l
~
Media and/or Prescribed and/or j Sample # REMP Activity Deficiency Comments Item Code ' quarterly grab / gamma 1st quarter sample Well not operable. Change request to I WC 205 isotopic not collected ODCM has beca made to sanction alternate well #235. quarterly grab / gamma 2nd quarter sample Well not operable. Change request to 2 WG 205 isotopic not collected ODCM has been made to sanction alternate well #235. quarterly grab / gamma 3rd quarter sample Well not operable. Change request to 3 WG 205 isotopic not collected ODCM has been made to sanction alternate well #235. 4 205 quarterly grab / gamma 4th quarter sample Well not operable. Change request 50 WG isotopic not collected ODCM has been made to sanction alternate well #235. weekly composite / weekly week 51 Electric power interuption during the 5 AP 033 gross beta, quarterly not collected sampling period. gamma isotopic weekly composite / weekly week 51 Electric power interruption during l 6 AI 033 gamma isotopic for I-131 not collected the sampling period. 7 AP 016/ weekly composite / weekly data rejected upon Mechanical and/or electrical failure investigation of of the sampling unit or temporary B08050 gross beta, quarterly gamma isotopic sample integrity interruption of electrical service resulting in a poor sample. weekly composite / weekly data rejected upon Mechanical and/or electrical failure l 8 AI 016/ of the sampling unit or temporary G08050 gamma isotopic for I-131 investigation of sample integrity interruption of electrical service resulting in a poor sample. I I-4
m M M m M~ M- fM M ~W m mM M W- - M M TABLE I-1 REMP PERFORMANCE EVALUATION 1990 (Cont'd) Location # Deviation Media and/or Prescribed and/or Item Code Sample'# REMP Activity Deficiency Comments 9 AP 033/ weekly composite / weekly data rejected upon Mechanical and/or electrical failure B08517 gross beta, quarterly investigation of of the sanpling unit or temporary gamma isotopic sample integrity. interruption of electrical service resulting in a poor sample. 10 AI 033/ weekly composite / weekly data rejected upon Mechanical and/or electrical failure G08507 gamma isotopic for I-131 investigation of of the sampling unit or temporary sample integrity. interruption of electrical service resulting in a poor sample. 11 TLD 030 quarterly / direct radiation 4th quarter sample TLD stolen in the field. not collected 12 TLD 080 quarterly / direct radiation 3rd quarter sample Erroneous result caused by moisture not collected retention. 13 WS 227 monthly composite / gamma station #219 Poor weather conditions prohibited isotopic, quarterly suber.ituted access to this remote location. composite for H-3 (G08038, 01-31-90) 14 WS 227 monthly composite / gamma station #218 Mechanical and/or electrical problem isotopic, quarterly (G08270, 03-21-90) with' composite sampler. composite for H-3 15 WS 227 monthly composite / gamma station #218 Mechanical and/or electrical problem isotopic, quarterly substituted with c;mposite sampler. composite for H-3 (G08415, 04-26-90) I-5
M M \M M M M' M M Y Y M M M M M 'M M M M TABLE I-I REMP PERFORMANCE EVALUATION 1990 (Cont'd) Deviation ! Location # ! Media and/or Prescribed and/or REMP Activity Deficiency Comments Item Code Sample # monthly composite / gamma station #233 Mechanical problem with the boat 16 , WS 227 isotopic, quarterly substituted prohibited access to this remote composite for H (G08919, 07-31-90) location. New composite sampler purchased. 277 monthly composite / gamma station #219 Mechanical problems with the boat 17 WS isotopic, quarterly substituted prohibited access to this remote composite for H-3 (G09409, 10-29-90) location. monthly composite / gamma station #219 Mechanical and/or electrical problem 18 WS 277 isotopic, quarterly substituted with the composite sampler. composite for H-3 (G09546, 11-26-90) 19 ,AP 006/ weekly composite / weekly data rejected upon Mechanical and/or electrical failure gross beta, quarterly investigation of of the sampling unit or temporary B09184 gamma isotopic. sample integrity Interruption of electrical service resulting in poor sample. 20 AI 006/ weekly composite / weekly data rejected upon Mechanical and/or electrical failure gamma isotopic for I-131 investigation of of the sampling unit or temporary G09174 sample integrity interruption of electrical service resulting in poor sample. 037 monthly if available/ Ist quarter control Inadequate sample volume available. 21 .VP gamma isotopic sample Restrictive language in the ODCM did l not collected not allow for sampling #037 VP in an j adj acent area where ample sample was available. A change to the ODCM has been made providing more latitude. monthly composite / gamma station #221 Poor weather conditions prohibited I 22 WS 226 isotopic, quarterly substituted access to preferred sample location composite for H-3 (G08039, 01-31-90) I-6
lI 3 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 LI
.. AIR PARTICULATE FILTERS (Weekly)
I' statim statim statim station Statim statim statim statim statim m 035 018- 033- 039- 037- 015- 016- 001- 006-Week #0s. M e07912 #0791.* 807914 #07915 807916 #07917 #07918 #07919 0
-l (01/04) (01/pu :41'b4) (01/04) (01/04) (01/04) (01/04) (01/04) (01/04) g 1 Week #07933 807934 #07935 #07936 807937 #07938 #07939 #07940 #07941 D l- . (01/09) (01/09) 2 (01/09) (01/09) (01/09) (01/09) (01/09) (M/09) (01/09)
L
- Week #07967 #07968 #07969 #07970 #07971 #07972 #07973 #07974 #07975 D 3 (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) l Week 807998 807999 #08000 808001 808002 808003 808004 808005 #08006 0 l l
4 (01/24) (01/24) (01/24) (01/24) (01/24) (01/24) (01/24) (01/24) (01/24) l Week #08024 808025 808026 808027 #08028 808029 #08030 #08031 #08032 0 5 (01/31) (01/31) (01/31) -(01/31) (01/31) (01/31) (01/31) (01/31) (01/31) j ( Week #05054 808055 808056 #08057 808058 #08059 #08060 808061 #08062 0 6 (02/06) (02/06) (02/06) G2/06) (02/06) (02/06) (02/06) (02/06) (02/06) i
#08087 #08086 #08089 #08090 #08091 #08092 #08093 #08094 #0809's D
! Week (02/15) 7 (02/15) (02/15) (02/15; (02/15) (02/15) (02/15) (02/15) (02/15)
#08125 808126 #08127 #08128 808129 #08130 #08131 #08132 #08133 D l- Week 8 (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) 808152 #00153 . 868154 808155 808156 808157 #08158 #08159 #08160 0 5 Week (02/28) (02/28) (02/28) (02/28) l 9 (02/28) (02/28) 402/23) t02/28) (02/28) 80818' #08182 808183 808184 808185 #08186- #08187 #08188 0 I'
Week 808180 10 (03/07) (03/f7) (03/07) (03/07) (03/07) (03/07) (03/07) (03/07) (03/07)
#08233 #0&t34 808235 808236 808237 808238 #08239 #08240 #08241 0 Week (03/15) (03/Pi) (03/15) (03/15) (03/15) (03/15) (03/15) (03/15) (03/15)
I 11 s08255 808256 808257 808258 808259 #08260 808261 808262 808263 0 Week 12 (03/21) (03/21) (03/21) (03/21) (03/21) (03/21) (03/21) (03/21) (03/21) 808287 808288 808289 808290 808291 808292 808293 808294 808295 0 i Week 13 (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) I Page 1 7 lI I
I - I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I AIR PARTICULATE FILTERS (Weekly) Stetton Statim statim $tstion Station Stetton Stetton station statim 035- 018- 033- 039- 037- 015- 016- 001- 006-Week #08313 #08314 #08315 #08316 808317 #08318 #08319 #08320 #08321 0 i 1 14 (04/03) (04/03) (04/03) (04/03) (04/03) (04/03) (04/03) (04/03) (04/03) Week #08358 #08359 #08360 #08361 #08362- #08363 #08364 808365 #08366 D , 15 (04/10) (04/10) (04/10) (04/10) (04/10) (04/10) (04/10) -(04/10) (04/10) Week #08382 #08383 #08384 #08385 #08386 #08387 #08388 #08389 #08390 0 16 (04/19) (04/19) (04/19) (04/19) (04/19) (04/19) (04/19) (04/19) (04/19) r Week #08435 808436 #08437 #08438 808439 808440 #08441 #08442 #08443 D , 17 (04/26) ( 04/26) (04/26) (04/26) (04/26) (04/26) (04/26) (04/26) (04/26) Week #08461 #08462 #08463 #08464 #08465 808466 808467 #08468 #08469 0 18 (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) 1 Week #08487 #08488 #08489 #08490 808491 #08492 #08493 #08494 (05/08)
#08495 0 (05 /08) 19 (05/08) (05/08) (05/08) (05/08) (05/08) 105/08) (05/08)
Week #08515 #08516 808517 #08518 808519 808520 #08521 #08522 #08523 0 [ l-l3 20 (05/16) (05/16) (05/16) (05/16) (05/16) (05'16) (05/16) (05/16) (05/16) Week #08558 #08559 #08560 #08561 #08562 #08563 #08564 #08565 ' #08566 0 21 (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) (05/24)
= Week- #08582 808583 #08584 808585 #08586 . #08587 808588 #08589 #08590 0 22 (05/30)- (05/30) (05/30) (05/30) (05/31)- (05/30) (05/30) (05/30) (05/30)
Week #08621 808622 #08623 808624 808625 #08626 808627 #08628 #08629 D l l 23 (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) l 3 Week #08650 #08651 #08452 808653 #08654 #08655 808656 808657 808658 D 24 (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) I- Week 25 808699 (06/20)
#08700 (06/20)
#08701 (06/20) 808702 (06/20) 808703 (06/20) 808704 (06/20) 808705 (06/20)
#08706 (06/20)
#08707 0 (06/20)
I Week #08729 #08730 #08731 #08732 808733 #08734 808735 #08736 #08737 0 1 26 (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) I I ,e9e ,.8 I lI
s _ ~ - - - - - - _ _ _ _ _ . _ _ _ _ . _ I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 i AIR PARilCULATE FILTERS (Weekly) Statim statim statim Stette statim statim statim statim Statim 016- 001- 006-W -. 035- 018- 033- 039- 037- 015-Week #08767 #08768 #08769 808770 #08771 #08772 #08773 808774 #08775 0 (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) I 27
#08799 #08800 #08801 D Wak #08793 #08794 #08795 #08796 #08797 #08798 28 (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) (07/09)
I Week 29
#08841 (07/18)
#08842 (07/18)
#08843 (07/18) aK,a844 (07/18)
#08845 (07/18)
#08846 (07/18)
#08847 (07/18)
#08848 (07/18)
#08849 0 (07/18)
I wk #08885 #08886 #08887 #08888 #08889 #08890 #08891 #08892 #08893 0 30 (07/23) (07/23) (07/23) (07/23) (07/23) (07/23) (07/23) (07/23) (07/23) Week #08897 #08898 #08899 #08900 #08901 #08902 #08903 #08904 #08905 0 (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) I 31 Week #08957 #08958 #08959 #08960 #08961 #08962 #08963 #08964 #08965 D 32 (08/08) (08/06) (08/08) (08/08) (08/08) (08/08) (08/06) (08/08) (08/08)
#08993 0 I Week #08985 #08986 #08987 #08988 #08989 #08990 #08991 #08992 33 (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) (08/14)
' Week #09010 #09011 #09012 #09013 809014 #09015 #09016 #09017 #09018 0 34 (08/22) (08/22) (08/22) (08/22) (08/22) (08/22) (08/22) (08/22) (08/22)
. Week #09022 #09023 #09024 #09025 #09026 #09027 #09028 #09029 #09030 0 35 (08/28) (08/28) (08/28) '(Or/28) (08/28) (08/28) (08/28) (08/28) (08/28)
#09064 809065 #09066 809067 #09068 #09069 #09070 #09071 #09072 0 I'
Week 36 (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) Week #09095 #09096 809097 #09098 #09099 #09100 #09101 #09102 #09103 0 37 (09/12) (09/12) (09/12) (09/12) (09/12) (09/12) (09/12) (09/12) (09/12) Week #09135 #09136 #09137 #09138 #09139 #09140 #09141 #09142 #09143 D (09/18) (09/18) (09/18) 38 (09/18) (09/18) (09/18) (09/18) (09/18) (09/18) Week #09176 #09177 #09178 #09179 #09180 #09181 #09182 #09183 #09184 D (09/25) (09/25) (09/25) 39 (09/25) (09/25) (09/25) (09/25) (09/25) (09/25) I
-9 i
I I
r 3 l I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I , 1 1 AIR PARilCULATE FILTEt$ (Weekly) Statim Statim Statim Statim Statim Stati m statim Stettm statim 035- 018- 033- -039- 037- 015- 016- 001 006-1 Week 809215 809216 809217 809218 809219- 809220 809221 809222 #09223 0
.I 40 (10/02) (10/02) (10/02) (10/02) (10/02) (10/02) (10/02) (10/02) (10/02)
Week 809266 809267 #09268 809269 809270 #09271 809272 809273 809274 0 41 (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) 809323 809324 809325 809326 D I Week WO9318 809319 #09320 809321 809322 J 42 (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) I Week 43 Week 809359 (10/24)
#09391 809360 (10/24) 809392
#09361 (10/24) 809393 809362 (10/24) 809394 809363 (10/24) 809395 809364 (10/24) 8093 %
809365 (10/24)
#09397 809366 (10/24) 809398 809367 0 (10/24)
#09399 0 (10/29) (10/?9) (10/29) (10/29) (10/29)
I 44 (10/29) (10/29) (10/29) (10/29) Week 809443 #09444 809445 809446 809*47 809448 809449 #09450 #09451 0 45 (11/06) (11/06) (11/06) (11/06) (11/06) (11/06) (11/06) (11/06) (11/06) E-Week 46
#09474 (11/13) 809475 (11/13) 809476 (11/13) 8094 77 (11/13) 809478 (11/13)
#09479 (11/13)
#09480 (11/13) 809481 (11/13) 809482 D (11/13)
Week #09498 #09499 #09500 809501 #09502 809503 #09504 809505 809506 0 47 (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) 8 Week #09520 809521 (11/26) 809522 (11/26) 809523 (11/26) 809524 (11/26) 809525 (11/26) 809526 (11/26)- 809527 (11/26) 809528 0 (11/26) 43 (11/26) 809557 809558 809559 809560 809561 809562 809563 809564 #09565 0 l g. Week 49 (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) 809583 809584 809595 809M6 809587 809588 809589 #09590 #09591 0 Week 50 (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) ur Week #09617 809618 Table I i 809619 809620 809621 809622 809623 809624 0 51 (12/18) (12/18) lltem5l (12/18) (12/18) (12/18) (12/18) (12/18). (12/18) Week 809671 809672 809673 809674 809675 809676 809677 #09678 809679 0 (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28)
.g 52 L
I . 9e ,.,0 I I
I L I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I I Alt 100lilE (Weekly) Statim Statim Statim Statim Statim Statim Statim Statim Statim 018- 033- 039- 037- 015- 016- 001 006-035
#07902 807903 #07904 807905 807906 #07907 #07908 #07909 D Week 807901 t 1 (01/04) (01/04) (01/04) (01/04) (01/04) (01/04) (01/04 ) (01/04) (01/04)
#07924 #07925 807926 807927 807928 607929 #07930 #07931 0 Week #07923 2 (01/09) (01/09) (01/09) (01/09) (01/09) (01/09) (01/09) (01/09) (01/09)
#07958 #07959 #07960 #07 % 1 #07962 #07963 #07964 #07965 0 Week #07957 3 (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) (01/17) (01/17)
I Week - 4 Week 807988 (01/24) 808014
#07989 (01/24) 808015
#07990 (01/24) 808016 807991 (01/24) 808017 807992 (01/24) 808018 807993 (01/24)
#08019 807994 (01/24) 008020
#07995 (01/24)
#08021
#07996 0 (01/24) 808022 D (01/31) (01/31)
I 5 (01/31) (01/31) (01/31) (01/31) (01/31) (01/31) (01/31) 808045 #08046 808047 808048 ,808049 808050 #08051 #08052 0 Week #08044 6 (02/06) (02/06) (02/06) (02/06) (02/06) (02/06) (02/06) (02/06) (02/06)
#08077 808078 #08079 808080 #08081 808082 #08083 808084 #08085 0 Week (02/15) (02/15)
I 7 (02/15) (02/15) (02/15) (02/15) (02/15) (02/15) (02/15) 808115 808116 808117 #08118 808119 808120 #08121 #08122 wo8123 D Week 8 (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) (02/21) I- Week 9 008142 (02/28) 808143 (02/28) 808144 (02/28) 808145 (02/28) 808146 (02/28)
#08147 (02/28) 808148 (02/28)
#08149 (02/28)
#08150 0 (02/28) 908173 808174 808175 #08176 #08177 #08178 0 l Week 10 808170 (03/07)
#08171 (03/07) 808172 (03/07) (03/07) (03/07) (03/07) (03/07) (03/07) (03/07) 3 Week #08223 808224 808225 808226 808227 #08228 #08229 #08230 #08231 0 11 (03/15) (03/15) (03/15) (03/15) (03/15) (03/15) (03/15) (03/15) (03/15) 5 Week #08245 #08246 #08247 (03/21) 808248 (03/21)
#08249 (03/21)
#08250 (03/21) 808251 (03/21) 808252 (03/21) 908253 0 (03/21) 12 (03/21) (03/21)
I Week 13 808277 (03/28) 808278 (03/28) 808279 (03/28) 008280 (03/28) 808281 (03/28) 808282 (03/28)
#08283 (03/28) 808284 (03/28)
#08285 0 (03/28)
I I Page 1 11 I I
m I 1990 BAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I Alt 10 DINE ( M kly) station Statim Station Statim Station Statim Stetton Statim Station I 035- 018- 033- 039- 037- 015- 016- 001- 006-I Week 14 Week
#08303 (04/03)
#08348
#08304 (04/03)
#08349 808305 (04/03)
#08350 808306 (04/03)
#08351
#08307 (04/03)
#08352 808308 (04/03) 808353
#08309 (04/03) 808354
#08310 (04/03)
#08355
#08311 D (04/03)
#08356 0 15 (04/10) (04/10) (06/10) (04/10) (04/10) (04/10) (04/10) (04/10) (04/10) 1 Week 16
#08372 (04/19)
#08373 (04/19)
#08374 (04/19)
#08375 (04/19)
#08376 (04/19)
#08377 (04/19)
#08378 (04/19)
#08370 (04/19)
#08380 D (04/19) hk #R425 808426 #v8427 808428 908429 #08430 #08431 #08432 #08433 0 (04/26) (04/26) (04/26)
I 17 (04,16) (04/26) ((4/26) (04/26) (04/26) (04/26) hk #08451 e 5452 #08453 #08454 808455 #08456 #08457 808458 #08459 0 18 (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) (05/02) Week. #08477 #08478 808479 #08480 #08481 808482 #08483 #08484 #08485 0 19 (05/08) (05/06) (05/08) (05/08) (05/08) (05/08) (05/08) (05/08) (05/08) Week 808505 808506 #08507 #08508 #08509 808510 #08511 #08512 808513 0 20 (05/16) (05/16) (05/16) (05/16) (05/16) (05/16) (05/16) (05/16) (05/16) Week #08548 #08549 #08550 #08551 #08552 #08553 #08554 #08555 808556 0 21 (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) (05/24) Week #08572 808573 ' #08574 #08575 808576 #08577 #08578 808579 808580 0 22 (05/30) (05/30) (05/30) (05/30) (05/30) (05/30) (05/30) (05/30) (05/30) Week #08611 808612 #08613 808614 808615 808616 808617 #08618 #08619 0 23 (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) (06/06) Week 808640 #08641 #08642 808643 #08644 #08645 808646 808647 #08648 0 24 (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) (06/12) Week #08689 808690 #08691 #08692 808693 #08694 808695 #08696 #08697 0 25 (06/20) (06/20) (06/20) (06/20) (06/20) (06/20) (06/20) (06/20) (06/20) Mk 808719 808720 808721 808722 808723 808724 #08725 #08726 #08727 0 26 (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) (06/25) Page 1 12 I
I I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 . g-I AIR 1(DlhE (Week (y) Statim Statim Statim Statim Statim Statim Statim statim Statim 035- 018- 033- 039 037- 015- 016- 001 006-Week #08757 808758 808759 808760 808761 #08762 808763 808764 #08765 0
.I 27 (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) (07/02) (07/02)
Week P08783. #08784 808785 808786 808787 #08788 #08789 #08790 #08791 0 28 (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) (07/09) 1 _ Week #08831 #08832 #08833 808834 808835 #08836 #08837 #08838 #08839 0 (07/18) 29 (07/18) (07/18) (07/18) (07/18) (07/18) (07/18) (07/18) (07/18) I Week 30 Week
#08875 (07/23)
#08909 808876 (07/23) soc 910 808877 (07/23)
#08911 808878 (07/23) 808912 808879 (07/23) 808913 808880 (07/23) 808914
#03881 (07/23) 808915
#08882 (07/23 )
#08916
#08883 0 (07/23) 808917 D 31 (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) (07/31) (07/31)
I. Week 32 808947 (08/08)
#08948 (08/08) 808949 (08/08)
#08950' (08/06)
#08951 (08/08)
#08952 (08/08) 808953 (08/08)
#08954 (08/08)
#08955 0 (08/08)
Week #08975 808976 #08977 808978 s08979 s08980 #08981 #08982 #08983 0 33 (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) (08/14) Week #09000 809001 #09002 #09003 809004 #09005 #09006 #09007 #09008 0
~
34 (08/22) (08/22) (08/22) (08/22) (08/22) (08/22) (08/22) (08/22) (08/22).
=- Week 809034 809035 809036 809037 809038 809039 #09040 #09041 809042 0 35 (08/28) (08/28) (08/28) (08/28) -(08/28) (08/28) (08/28) (08/2.8) (08/28)
I' ' Week 809076 809077. 809078 809079 809080 809081 809082 809083 809084 0 36 (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) (09/05) Week 809107 809108 809109- 809110 809111 809112 809113 809114 809115 D 37 (09/12) (09/12) (09/12) (09/12) (09/12) (09/12) (09/12) (07/12) (09/12) I- Week 38 809125 (09/18) 809126 (09/18) 809127 (09/18) 809128 (09/18) 809129 (09/18) 809130 (09/18)
#09131 (09/18) 809132 (09/18).
809133 0 (09/18) I Week 39 800166 (09/25)
#09167 (09/25) 809168 (09/25) 809169 (09/25).
809170 (09/25)
#09171 (09/25) 809172 (09/25)
#09173 (09/25)
#09174 0 (09/25)
I I . 9e ..,3 I I
8 El 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I AIR 10DlWE (Weekly) Statim Statim Statim Statim Statim Stettm Statim Statim Statim 018- 033 039- 037- 015- 016- 001- 006-035
#09209 #09210 #09211 #09212 #09213 0 I- Week 40
#09205 (10/02) 809206 (10/02)
#09207 (10/02) 809208 (10/02) (10/02) (10/02) (10/02) (10/02)
#09263 (10/02)
#09264 0 Week #09256 809257 809258 #09259 #09260 #09261 #09262 41 (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) (10/11) (10/11)
#09309 #09310 #09311 #09312 #09313 #09314 #09315 #09316 0 Week #09308 42 (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) (10/18) (10/18)
I Week 43 Week
#09349 (10/24)
#09381
#09350 (10/24) 809382 809351 (10/24) 809383 809352 (10/24)
#09384 809353 (10/24) 809385 809354 (10/24)
#09386 809355.
(10/24) 809387 809356 (10/24)
#09388 809357 0 (10/70 fo938b 44 (10/29) (10/29) (10/29) (10/29) (10/29) (10/29) (10/29) (10/29) (10/29) i Week #09433 #09434 #09435 #09436 809437 s09438 111/06)
#09439 (11/06)
#09440 (11/06)
#09441 0 (11/06) 45 (11/06) (11/06) (11/06) (11/06) (11/06)
#09465 #09466 809467 #09468 #09469 #09470 #09471 #09472 0 Week #09464 (11/13) (11/13) (11/13)
I 46 (11/13) (11/13) (11/13) (11/13) (11/13) (11/13)
#09489 #09490 #09491 809492 #09493 #09494 #09495 #09496 0 Week #09488 47 (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) (11/19) (11/19)
I Week 809510 #09511 809512 809513 809514 (11/26)
#09515 (11/26) 809516 (11/26) 809517 (11/26)
#09518 0 (11/26) 48 (11/26) (11/26) (11/26) (11/26)
Week #09547 809548 809549 809550 #09551 #09552 #09553 #095s #09555 0 49 (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) (12/03) 809573 809574 809575 #09576 809577 809578 809579 809580 #09581 0 Week 50 (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) (12/10) 8 Week 809608 809609 febte 1 1 809610 (12/18)
#09611 (12/18) 809612 (12/18) 809613 (12/18) 809614 (12/18)
#09615 0 (12/18) 51 (12/18) (12/18) lltem6l 809664 809665 809666 809667 809668 #09669 0 I. Week 809661 809662 809663 52 (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28)
I Page 1 14 I i 1
f l I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I I SURFACE W TER DRINt'ING W TER (Monthly) (Monthly) I' Station Stetton Stetton Station Stetton 216- 226- 227- 210- 228-JAN #08036 0 Tebte 1 1 febte 1 1 808041 808042 (01/31) ll tem 223 ll tem 13l (01/31) (01/31) W' FEB 808164 0 808166 808075 $ 808167 808168 (02/28) (02/28) (02/12) (02/28) (02/28) I MAR APR 808267 (03/21) 808413 808268 $ Table I 1 (03/21) 808414 Table 1 1 808271 lltem14l (03/21) 808417 808272 (03/21) 808418 (04/27) (04 /26) l item 15l (04/27) (04/26) -E MAY #08527 808528 0 8085/0 #08530 #08531 (05/16) (05/16) (05/23) (05/16) (05/16) JUN #08634 808635 808668 808636 808637 0 I_~ (06/12) (06/12) (06/14) (06/12) (06/12) JUL 808858 #08828 8 febte 1 1 808830 808779 (07/13) (07/09) lltemi!j (07/13) (07/02) I= AUG #08934 (08/08) M8935 ( 4/03) 808997 0 (08/17) 808936 (08/08) 808937 (08/08) I SEP OCT 909119 (09/10)
#09333 809120 (09/18) fo9297 809121 $
(09/19) iebte I 1 fo9123 (09/18) 809298 809124 (09/18) 809374 0 (10/23) (10/18) l item 173 (10/18) (10/24) I NOV 809459 (11/13) M 9460 0 febte 1 1 809462 (11/13) l item 1tg (11/13) 809463 (11/13) DEC 809663 809632 809633 809686 809634 (12/18) (12/19) (12/28) (12/18) - I'. (12/28) I p.g, 3 15 I g
l I 1990 CAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I I BROAD LEAF VEGETATIF I station Station station station 001- 015- 016 037-I JAN L6 808111 (02/20)
- L6 #^8112 (02/20) L6 #08113 (02/20) D FEB I
e e e e MAR L2 #08419 (04/27) L2 #08420 (04/27) L2 #08421 (04/27) L2 #08422 (04/27) 5 I APR L2 808600 (05/30) L2 808598 (05/30) L2 808599 (05/30) L2 #08597 (05/30) MAY L6 #08601 (05'30) L6 #08604 (05/30) L6 #08602 (05/30) S L2 #08747 (06/26) L2 #08748 (06/26) L2 808749 (06/26) L2 #08633 (06/07) I JUN L2 #08921 (07/31) L2 #08922 (07/31) L1 808923 (07/31) L1 #08925 (07/31) L2 808924 (07/31) L2 #08926 (07/31) I JUL
*
- L2 #09044 (08/28) L1 809045 (08/28)
AUG L2 809046 (08/28) L1 #09191 ( W/24) I' L2 #09194 (09/25) L2 #09195 (09/28) L2 #09196 (09/28) SEP L2 809192 (09/24) 5
- L2 #09379 (10/24) L1 #09373 (10/24) L2 #09296 (10/15)
CCT L2 #09380 (10/24) e e I Nov e I e . . OEC
- Unavailable sarples do not constitute a deficiency in accordance with Table C 1 I
Pagt 1 16 I I
pg 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2
.B I
I ORahtD WATER (Quarterty) SURFACE WATER (Quarterty) Statim Statim Stattm Statim Statim Statim Statim Statim Statim 205- 206- 207- 208- *209- 211- 212- 213- *229-I Quarter 1 Table 1 1 litemil
#08273 5 (03/22)
#08325 (03/28)
#08326 (03/28)
#08068 (02/06)
#07955 (01/17) 808533 s
#07956 (01/17)
#08535
#08069 $
(02/06)
#08536
#08071 0 (02/06)
#08537 Quarter- table 1 1 #08571 #08607 0 #08609 #08532 2 lltom2$ (05/24) (06/06) (06/06) (05/16) (05/16) (05/16) (05/16) (05/16)
Quarter 1abte 1 1 #09197 #09188 #09189 D #09086 #09087 #09088 0 #09090 #09091 3 l item 3l (09/28) (09/25) (09/25) (09/05) (09/05) (09/05) (09/05) (09/05) Quarter Table 1 1 #09628 #09629 0 #09631 #09595 #09403 #09404 #09405 #09406 I 4 litem4{ (12/18) (12/18) (12/18) (12/13) (10/29) (10/29) (10/29) (10/29) I . AIR FILTERS (Quarterly Cceposits) I Statim Statim statim Statim statim Statim Stattm Statim Statim 035- 018- 033- 039- 037- 015- 016- 001- 006-Quarter 808329 #08330 #08331 #08332 #08333 808334 #08335 #08336 #02337 D 1 (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) (03/28) I Quarter 2
#08805 (06/25)
#08806 (06/25)
#08807 (06/25)
#08808 (06/25)
#08809 (06/25)
#08810 (06/25)
#08811 (06/25)
#08812 (06/25)
#08813 0 (06/25)
I Quarter 809229 #09230 #09231 #O9232 809233 #09234 809235 #09236 #09237 0 3 (09/25) (09/25) '(09/25) (09/25) (09/25 ) (09/25) (09/25) (09/25) (09/25) Quarter 809701 809702 #09703 809704 809705 #09706 #09707 #09708 #09709 0 4 (12/28) (12/28) (12/21) (12/28) (12/28) (12/28) (12/28) (12/28) (12/28) I I g .a9e ,.,7 I I
I: 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I PASTURE GRASS VICETAfl0N I Stetton 001-Stetton 015-Stetton 016-Stetton 037-Quarter 908327 8 *
- Tebte 1 1 I 1 (03/28) [ item 21l
*
- 808595 0 #08594 Querter I 2 Querter 3
(05/30)
#08920 (07/31)
(05/30)
#08868 (07/13)
Quarter
- fo9376 8 #09541 I 4 (10/24) (11/26)
- Quarterly cettection et stations 001, 015, or 016 set tsfy re<Nirement per f ebte C 1.
I SURFACE WATER ORINK!WG WATER (Quarterly Cenposit) (Quart. Ccmposit) I Stetton Station Station Stetton Stetton 216- 226- 227- 210- 228-E overter 808342 #08343 #08344 #08345 #08346 1 (03/21) (03/21) (03/21) (03/21) (03/21) I Quarter 2 808861 (06/12) 808862 (06/12) 808863 (06/14) 808864 (06/12) 809305 808865 (06/12) 809304 Quarter 809302 809301 809303 3 (09/18) (09/18) (09/19) (09/18) (09/19) Querter 809699 809698 809700 809694 #09695 4 (12/28) (12/18) (12/19) (12/28) (12/18) Page I 18 I lI
I I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE T-2 I I I Terrestrist Aquatic Animals Vildlife I M1 #08780 (06/15) M3 #08104 (01/31) M7 #07986 (01/15) F1 #087t6 (06/19) $ F2 #07987 (01/15) Cs #08662 (06/14) s JAN+JUN 81 808932 (06/18) B3 #08106 (01/27) I' B5 #08105 (01/25) S M1 #09904 (12/28) F1 #09427 (11/07) I. Jut DEC M3 #09532 (11/01) $ M6 809763 (12/02) s B3 #09765 (11/25) F2 809426 (10/26) CC #08999 (08/17) I I I I I I g ...e .,, I I -
l I 1990 SAMPLE COLLECTION SCHEDULE TABLE TABLE I-2 I I I SolLS (Seelemuelly) Station Station Station Station Station Stetton Station Stetton Stetton Station Station W 001- *006- 015- 016- 018- 029 033- 035- 037 039- 234-I JAN*JUN JUL DEC
#08539 (05/16)
#09534
#08540 (05/16) 809687
#08541 0 (05/16)
#09535
#08543 (05/16)
#09536
#08411 (04/26) 809371
#08394 (04/19)
#09537
#08544 (OS/16) 809372
#08412 (04/26)
#09425
#08545 (05/16)
#09538
#08546
( 05/16)
#09373 808547 (05/16)
#09539 $
I (11/26) (12/28) (11/26) (11/26) (10/24) (11/26) (10/24) (10/24) (11/26) (10/24) (11/26) I I SEDD1ENTS (Seavismuelly) Station Stetton Station Stetton Station Station Station Station Stetton Station Stetton 209- 211- 212- 213- 215- 216- 221- 227 229- 230- *233-JAN JUN #08750 #08751 #08752 #08753 0 #08713 808715 #08664 #08665 #08755 808666 #08667 m (06/26) (06/26) (06/26) (06/26) (06/19) (06/19) (06/14) (06/14) (06/26) (06/14) (06/14) JUL DEC #09596 #09597 $ #09599 #09600 #09635 809636 #09637 #09638 809601 #0 % 39 #09640 (12/13) (12/13) (12/13) (12/13) (12/19) (12/19) (12/18) (12/19) (12/13) (12/19) (12/19) I g ..$. 2e I
- I
l SECTION J ANALYSIS OF ENVIRONMENTAL DATA i OBJECTIVES Section J presents a discussion and analysis of the environmental data. Special attention has been given to gross beta in air particulate and environmental TLD measurements because the data was trendable, although at I environmental levels. Trending of data is also possible for a number of relevant nuclides now ftund in the main cooling reservoir. Also, a historical perspective may be taken in order to illustrate the continuity of data from I the preoperational to operational REMP. Two tables are included that Jerve to separate the positive measurements f rom the majority of the measurements that are below the LLD. Table J-l lists the environmental TLD results for 1990 while Table J-2 lists environmental analysis data (e.g. gross beta in air I particulate). RESULTS Tables of Measured Activity Table J-2, Table of Measured Activity in Environmental Media, presents I measured concentrations of nuclides in environmental media. A positive measurement has been defined as a result that is three times greater than its sigma error. Examples of radionuclides that have not been included in Table I J-2 are K-40, Ra-226, and Be-7 because they are naturally occurring and contribute little to the purpose of this section. The table was further edited t.o eliminate erroneous or misidentified radionuclides (e.g. La-140 in Gross alpha measurements are also not presented because gross alpha I soil). analysis is not a prescribed requirement per Table C-1 nor is it a meaningful measurement at this time. The date within the table is grouped together by media type. Table J-2 reads from left to righti Laboratory Sample Number, I Sample Submission Code, Analysis Type, Result, One Sigma Analysis Error, and LLD for each entry. An asterisk (*) is placed before the sample submission code to identify control samples for reference. A complete listing of raw data can be found in Addendum 1, STPEGS REMP Results Data. Het exposures (mR) at sampling locations are found in Table J-1, Environmental TLD Measurements 1990. All four quarterly measurements are I included in the quarterly averages presented for each sample station. Duplicate measurements are used in calculating the quarterly averages _and
'mR/hr. Where applicable, duplicates are identified and the measured value I appears along with the routine measurement. From left to right the table reads: Station Code, lat-4th Quarter Measureraents, Quarterly Average, and Previous Years Average MicroR/hr. Control locations are identified with the term control printed next to the station code for reference.
l I. J-l l l l
I Discussion - Analysis of Environmental Data o Air Samples The majority of REMP samples collected are air samples (air particulate and air iodine) followed in number by environmental TLDs. Air monitoring stations are established at a total of nine locations although only five are required per Table C-1. Details regarding sample locales are found in Section D. Eight of these locations are considered " indicators" since plant operations began. One station (037) has been designated as a control and one I of the indicator stations (06) has a permanent duplicate sampler associated with it. The air pumps at these locations operate continuously at a flow rate of 2.0 cfm, resulting in a weekly air sample of approximately 570-cubic I meters. Airborne particulates are collected passing the air through a 47-mm fiber filter while air iodine is collected using a 47-mm charcoal cartridge. I The iodine charcoal and particulate filters are collected weekly. The air particulate filters are analyzed for gross beta activity 100 hours after collection to allow for decay of radon and thoron daughter products. Weekly air particulate filters from each location are analyzed as a quarterly composite for gamma emitting nuclides. A composite analysis of air particulate filters from all stations is I performed weekly. This approach was instituted during the Chernobyle surveillance effort in order to obtain the most sensitive measurements possible. Particular attention was placed on this analysis when a somewhat higher than anticipated seasonal high for gross beta was noted during the I second week of January (see Fig. J-1). The gamma lootope analysis determined nothing unusual, eliminating the possibility of the global fallout contribution. Because the weekly coreposite air particulate analysis is not ,g sample station specific and does not satisfy a program requirement, it was g eliminated from the REM 2 Annual Summary (Table G-1). However, valid data was obtained by this means when monitoring Chernot;71e f allout and was included in the 1986 Annual Report. Quarterly and weekly conposite samples are identified I in Table J-2 and Addendum 1 using a "c" in the sample submission code. The results for the quarterly composite air particulates can be distinguished from the weekly composite results by the use of the station number associated with the sample submission code. Figure J-1, Veekly Gross Beta Activity in Airborne Particulates, shows I random fluctuations at all sampling locations typical of this type of measurement. The observed fluctuation is primarily due to particulate loading of the air filter that is subj ect to many variables including climate / weather conditions and agricultural activities. The graph indicates that there is no I notable difference between sampling Iccations (indicator vs. control). Unusual or anomalous measurements can easily be identified by this trending method. Other than a new high being established for ambient gross beta in I AP's in January nothing noteworthy was observed. I I I J-2
1 I Figure J-2, is a graph of the annual mean gross beta values by station and is designed to evaluate spacial variance within a given year. The black line in the middle of the bar is the annual mean value and the orange The station code number and I. represents the 3 sigma range about the mean. miles distance from STPEGS is at either end of the bar. The bars are situated above the sectors where the actual sample stations are located, and each I sector is qualified as to the percent of wind abundance in that sector. In other words, a continuous gaseous release would have the most influence off-site in the NW, NNW and N sectors. Figure J-2 demonstrates that the annual mean activities and their associated variances are the same at all sampling I locations regardless of sector or distance from plant. The variance at station 006 is slightly smaller because the sample population was twice as large because it was a duplicate station. Figure J-3, Historical Comparison of Indicator and Control Air Sample Stations, has been presented in order to obtain a historical perspective of the environmental radioactivity levels at STPEGS. The monthly averaged gross I beta values for each indicator station #'s 001, OOS, and 016, along with control station 0037 have been plotted for 1985-1990. Important reference dates have been added such as Unit 1 initial criticality on March 8, 1988, and Unit lI's on March 12, 1989. The peak in May 1986 is associated with the I- global fallout from the Chernobyle accident in April of that year. Other than the Chernobyle peak, all other peaks are associated with the inherent temporal variability observed with this type of analysis. o Direct Radiation: Environmental TLDs Direct radiation in the vicinity of STPEGS is determined by Panasonic thermoluminescent dosimeters (TLDs). Two Panasa.ic UD-814 enviranmental TLDs sealed in a metallized polyester bag are placed at each TLD monitoring I station. Only the three calcium sulfate elements of each TLD are used to calculate dose rates. ,Each quarter, four of the TLD monitoring stations are routinely cycled for an additional placement of two TLDs for duplicate analysis. There are a total of forty-one (41) monitoring stations which include two (2) background stations. Data is collected on a quarterly basis and I normalized to a standard quarter (91 days). The results are presented in Table J-1, Environmental TLD Measurements 1990. TLD monitoring station locations and distances from STPEGS are presented in Table D-2. TLD monitoring stations have been dispersed in two concentric rings (approximately I 1 mile and 6 miles) from the containment building and in special interest areas (e.g. schools, population centers) within a fourteen (14) mile radius. The two background monitoring stations are located 10-15 miles from the I containment building in areas less likely to be influenced by plant operations. I Figure J-4 illu' rates the direct gamma in relation to wind direction. The bottom of the chart represents the percent wind atundance in sixteen (16) sectors. The bars represent the mean TLD dose +2 standard deviation for each TLD station. The results are arranged in groups by sector with the most I distant station from the centerline of containment structures located at the left of each group. Each bar is labeled with the TLD station code and distance in miles from the centerline. The black line in the middle of the I I J-3
I I bar is the average dose for that itation. The mR/STD quarter values for each of the 16 sectors are in agreement with preoperational data and no casual relationship is indicated for the (ff-site doses in sectors most sensitive to plant operations. Figure J-5 illustrates the relationship between STPEGS, State of Texas, I and the NRC TLD exposure rates at seventeen co-located stations. The NRC average includes only the first three quarters in 1990, while the State's TLD results include only the first and second quarters. STPEGS data represents I the average for all four quarters for each co-located station. quarter values per station typically agree within 3 mR. The mR/STD However, the lack of complete data from the NRC and the State, along with the introduction of a possible bias in the State's first quarter data (see Fig. J-6) Fig J-5 shows I more variability in the co-located data than what would be expected. Figure J-6 is a plot of the mean of all STPEGS environmental TLD I measurements by quarter beginning in 1984 The NRC and State TLD measurements beginning in 1986 have been included for comparison when made available. Figure J-6 illustrates a relatively continuous level of exposure of approximately 16 mR/STD quarter during the preoperational years through the I initial operational year. The State's results over the years indicate a slight positive bias and may be the result of the type of TLD utilized which defers from the common type employed by the NRC and STPEGS. Also, noted in I the significant bias in the State's third quarter 1989 data which resulted from an error in the background in calculating the results. A less severe bias can be seen for the first quarter 1990 data point, however no explanation I is available at this time. The decrease in the reported dose at the time of conversion from UD-804 to UD-814 type badges in 1986 has been noted. conducted on the UD-804 badges concluded that self-irradiation caused the Tests higher exposures. Agtsement with historical vendor results, NRC TLD results, and ion chamber measurements provide conclusive evidence that UD-804 badges were biased (see 1986 Annual REMP Report). o Other Environmental Media There are approximately 6,000 measurements found in Addendura 1, STPEGS REMP Results Data. Of these, only thirty-one measurements are associated with plant operations with any degree of certainty and are limited to on-site location. These measurements have been listed in Taole J-2, Measured Activity in Environmental Media, along with ambient positive measurements. Tritium was quantified in the MCR for the first time in 1989 and reported in all four quarterly composite samples in that year. The tritium concentration continued to build in the MCR during 1990 as seen in Figure J-7, I Historical Comparisons of Tritium Activity in the Main Cooling Reservoir. Following a slight decrease in the spring, resulting from the tritium being diluted with fresh makeup water, the final concentration at the years' end was I 4100 pC1/Kg. Tritium has also been positively measured in samples collected in adjacent sloughs, drainage ditches and the spillway. The tritium concentration in these samples were typically below 1000 pCi/Kg and are listed in Table J-2 f or f airther details. Co-58 was first quantified in the MCR's bottom sediments in 1988. The following year Co-60 was also measured. However, it was not until 1990 that 3-4
these nuclides were routinely measured. Figures J-8 and J-9 show the buildup of Co-58 and Co-60 in the MCR bottom sediments respectively. The values are compared to the analysis of sediments collected off-site. The data shows the I concentration of Co-58 and Co-60 in the MCR bottom sediments are approximately 450 pC1/Kg dry weight in 1990. I Other nuclides (Ag-110m, Mn-54, Fe-59) have also been quantified in the MCR bottom sediments. On average their concentrations were less than 50 pC1/Kg dry weight. l I 1 At this time the Co-137 level cannot be distinguished from preoperational levels in MCR bottom sediments or aquatic wildlifel therefore Cs-137 has been excluded from this discussion. Co-58 and Ag-110m were measured in blue crabs I collected from the MCR at concentrations less than 50 pC1/Kg vet weight. with other positive measurements the data can be found in Table J-2. As l l I I I I I I I I I I J-5
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I TABLE J.1 l'NVIRONMENTAL TLD MEASUREMENTS 1990 Net exposure in mR/ standard quarter (91 days) STATION ist 2nd 3rd 4th QUARTER microR PREVIOUS CODE QTR QTR QTR QTR AVG. per hr YEARS AVG. microR/hr
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01 15.2 14.8 14.9 14.6 14.9+-0.3 7.0 6.3 02 16.8 16.6 17.0 16.5 16.7+-0.2 7.0 6.8 Duplicate 16.3 03 16.8 16.8 16.8 16.2 16.6+-0.3 9.7 6.9 04 16.6 16.0 16.4 15.7 16.2+-0.4 7.6 6.7 Duplicate 14.7 05 15.5 15.0 15.6 14.7 15.1+-0.4 8.8 6.4 06 16.3 16.3 16.6 15.9 16.3+-0.3 7.6 6.9 07 13.2 12.7 13.5 12.9 13.1+.0.4 6.1 5.8 08 15.2 14.7 code 1 13.7 14.5+-0.8 6.9 6.2 Duplicate 13.3 09 13.7 12.7 13.0 14.0 13.3+-0.5 7.8 6.0 10 14.2 14.1 14.3 14.8 14.4+-0.3 6.7 6.1 I Duplicate 11 14.2 14.0 13.6 13.6 14.4 14.0+-0.4 S.2 6.0 I 12 14.2 13.8 13.5 13.9 13.9+-0.3 6.2 6.3 Duplicate 19.9 L 13 19.2 19.8 19.4 19.7 10.6+-0.3 11.5 8.0 l l l l 14 18.0 18.3 18.2 18.2 18.2+-0.1 8.5 7.7 l .....__.....__.... ................__...............__........__...._......... Duplicate 15.1 14.8+-0.3 8.7 6.4 I -15 14.8 14.9 14.4 14.0
W - TABLE J-1 l ENVIRONMENTAL TLD MEASUREMENTS 1990 [ Het exposure in mR/ standard quarter (94 days) L STATION ist 2nd 3rd 4th QUARTER microR FREVIOUS CODE QTR QTR QTR QTR AVG. per hr YEARS AVG. microR/hr amena****anamananamananame***********************a*****a*******aa**ea********* 16 15.3 15.2 14.6 14.9 15.0+-0.3 7.0 6.5 17 15.4 15.4 16.5 14.7 15.6+-0.7 7.3 6.4 18 16.0 15.8 16.7 15.6 16.0+-0.5 7.5 6.5
......... ..........___ ...__...........__....___......___..____........____... 1 Duplicate 16.4 I 19 15.9 15.0 16.2 15.2 15.7+-0.6 9.2 6.5 I 20 17.7 17.4 18.1 17.0 17.6+.0.5 8.2 Duplicate 16.0 7.2 21 16.0 15.7 16.4 15.2 15.9+.0.4 9.3 6.5 1 ..__........__....._______.......____._______..__..___........____.___... .. ..
22 15.4 15.5 15.7 15.2 15.5+-0.2 7.2 6.4 I ....__........... .__..__.___........___.....__..................______....... Duplicate 17.7 23 CONTROL 17.3 17.7 18.5 18.0 17.8+-0.4 10.4 7.1 24 13.7 13.6 12.5 17.4 14.3+-2.1 6.7 5.8 I Duplicate 25 15.3 13.5 14.8 13.9 13.9 14.3+_0.7 8.4 6.0 26 12.3 12.7 13.6 12.7 13.2+-0.5 6.2 5.7 27 13.3 12.3 12.5 13.0 12.8+-0.5 6.0 5.8 28 16.4 16.2 16.4 16.6 16.4+-0.2 7.7 6.6 Duplicate 17.9 29 18.1 17.4 17.8 18.1 17.9+-0.3 10.5 7.1 30 15.6 14.9 15.4 code 1 15.3+-0.4 7.2 6.4 J-16 _ >
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- m
m M M M M M M M M M M M M M M M M m 'M TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA OURFACE WATER SHORELINE BEDIMENT LAB SAMPLE RESULT 1 SIGMA LAB SAMPLE PESULT 1 SIGMA NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCl/Yg ERROR NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/Kg dry wt ERROR 08342 STP-US-216-03-21-90-15:1c N-3 3.1E+03 2.6E+02
- 08664 STP-SS-221-06-14-90-15:47 Cs-137 1.3E+01 2.4E+00 08861 STP-US-216-06-12-90-15:3c H-3 2.8E+03 2.3E+02 08665 STP-SS-227-06-14-CO-12:35 Cs-137 3.0E+01 4.2E+00 09087 STP-WS-211-09-05-90-13:48 W-3 4.8E+02 1.4E+02 08666 STP-SS-230-06-14-90-12:55 Cs-137 5.4E+01 4.8E+00 09199 STP-WS-237-09-28-90-13:?9 H-3 7.2E+02 1.4E+02 08750 !1P-SS-209-06-26-90-13:10 Cs-137 7.0E+01 6.3E+00 09302 STP-WS-216-09-18-90-14:4c H-3 3.0E+03 1.7E+02 08751 S P-SF-211-%-26-90-11:54 Cs-137 2.9E+01 3.0E+00 09403 STP-WS-211-10-29-90-15:41 N-3 4. 7E+02 1.3E+02 08752 STP-SS-212-06-26-90-11:18 Cs-137 1.7E+01 1.8E+00 09404 STP-WS-212-10-29-90-15:29 N-3 4.8E+02 1.3E+02 08753 STP-SS-213-06-26-90-12:1d Cs-137 2.6E+01 4.5E+00 09406 STP-WS-229-10-29-90-16:28 u-3 7.6E+02 1.4E+02 08754 STP-SS-213-06-26-90-12:1d Cs-137 5.1E+01 6.0E+00 09407 STP-WS-237-10-29-90-15:5s N-3 1.8E+03 1.5E+02 08755 STP-SS-229-06-26-90-13:00 Cs-137 3.4E+01 6.2E+00 09408 STP WS-237-10-29-90-15:5s M-3 1.8E+03 1.5E+02 09598 STP-SS-211-12-13-90-11:4s ts-137 3.4E+01 5.7E+00 09572 STP-US-229-12-10-90-14:52 f4-3 8.4E+02 1.4E+02 09599 STP-SS-212-12-13-90-11:34 Cs-137 2.7E +01 5.8E+00 09699 STP-WS-216-12-28-90-14:3c n-3 4.1E+03 1.8E+02 09600 STP-SS-213-12-13-90-12:01 Cs-137 7.0E+01 5.4E+00 08858 STP-WS-216-07-13-90-11:30 Co-58 2.4E+00 3.4E-01 09601 STP-SS-229-12-13-90-12:10 Cs-137 3.4E+01 8.1E+00 09635 STP-SS-215-12-19-90-14:30 Cs-1!7 8.9E+01 3.7E+00 09636 STP-SS-216-12-19-90-15:10 Cs-137 9. 7E+01 4.9E+00
- 09637 STP-SS-221-12-18-90-12:45 Cs-137 4.1E+01 4.1E+00 09638 STP-SS-227-12-19-90-11:25 Cs-137 3.9E+01 3.5E+00 09639 STP-SS-230-12-19-90-11:44 Cs-137 3.4E+01 8.9E+00 08713 STP-SS-215-06 19-90-14:10 Mn-54 3.3E+01 3.5E+00 08714 STP-SS-215-06-19-90-14:25 Mn-54 5.5E+01 3.5E+00 09635 STP-SS-215-12-19-90-14:30 Mn-54 9.6E+01 2.3E+00 09635 STP-SS-215-12-19-90-14:30 Fe-59 1.3E+01 4.0E+00 08713 STP-SS-215-06-19-90-14:10 Co-58 5.1E+02 7.BE+00 08714 STP-SS-215-06-19-90-14:25 Co-58 6.4E+02 6.2E+00 08715 STP-SS-216-06-19-90-13:35 Co-58 1.4E+02 3.9E+00 09635 STP-SS-215-12-19-90-14:30 Co-58 4.5E+02 4.4E+00 09636 STP-SS-216-12-19-90-15:10 Co-58 1.ZE+02 5.6E+00 08713 STP-SS-215-06-19-90-14:10 Co-60 8.1C+01 5.0E+00 08714 STP-SS-215-06-19-90-14:25 Co-60 8.2E+01 3.0E+00 08715 STP-SS-216-06-19-90-13:35 Co-60 8.2E+00 1.9E+00 09635 STP-SS-215-12-19-90-14:30 Co-60 4.1E+02 4.2E+00 09636 STP-SS-216-12-19-90-15:10 Co-60 5.1E+01 3.8E+00 09635 STP-SS-215-12-19-90-14:30 Ag-110 1.2E+01 2.2E+00
[
- Denotes control locations Meesured Activity is when the result is 3 times the sigme error.
Page J-19
v V~t 1 1 < TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA BOIL COLLARD GREENS RESULT 1 StGMA RESULT 1 SIGMA LAB SAMPLE LAB SAMPLE NUMBER SAMPLE SU8 MIS $104 CODE ANALYST $ pCl/Kg wet wt ERROR ilUMBER SAMPLE SUBMISS 10st CfrE ANALYSIS pCl/KO ERROR 08601 STP-L6-001-05-30-90-14:45 Cs-137 4.0F+00 1.2E+00 STP-SO-029-04-19-90-12:51 Cs-137 8.5E+01 8.2E+03 7.0E-01 08394 f.1E+01 08603 STP-L6-016-05-30-90-14:Os ts-137 2.5E+00 08411 STP-SO-018-04-26-90-11:48 Cs-137 2.3E+02 STP-SO-035-04-26-90-10:40 Cs-137 2.4E+02 9.9E+00 08412 08539 STP-SO-001-05-16-90-14:11 Cs-137 9.3E+01 8.4E+00 03540 STP-SO-006-05-16-90-14:55 Cs-137 1.8E+01 5.3E+00 STP-SO-015-05-16-90-13:3d Es-137 1.9E+02 1.1E+01 08341 08542 STP-SO-015-05-16-90-13:3d Cs-137 2.0E+02 8.9E+00 STP-SO-016-05-16-90-13:51 Cs-137 1.1E+02 9.EE+00 08543 STP-SO-033-05-16-90-11:54 Cs-137 3.5E+02 7.9E+00 08544 STP->037-05-16-90-13:08 Cs-137 1.2E+02 9.1E+00
- 08545 STP-SO-219-05-16-90-12:33 Cs-137 2.8E+02 9.9E+00 08546 08547 STP-SO-234-O'-16-90-13:42 Cs-137 1.9E+02 9.8E+00 STP-SO-003-08-08-90-10:00 Cs-137 7.8E+01 1.6E+01 08940 08941 STP-SO-004-08-07-90-13:56 Cs-137 1.7E+02 1.2E+01 08942 STP-SO-007-08-07-90-15:13 Cs-137 1.3E+02 7.1E+00 STP-SO-018-10-24-90-11:12 Cs-137 2.1E+02 9.5E+00 09371 09372 STP-$0-033-10-24-90-13:25 Cs-137 9.0E+01 5.9E+00 STP-SO-039-10-24-90-13:55 Cs-137 3.5E+02 1.4E+01 09373 STP-SO-035-10-24-90-10:00 Cs-137 ?.9E+02 7.1E+00 09425 STP-SO-001-11-26-90-14:07 Cs-137 1. c+02 9.9E+00 09534 09535 STP-SO-015-11-26-90-13:28 Cs-137 2.1F+t2 8.1E+00
$1P-SO-016-11 90-13:50 Cs-137 2.3E+b2 7.9E+00 09536 STP-SO-029-11-26-90-13:12 Cs-137 3.1E+02 1.5E+01 09537 STP-SO-037-11-26-90-12:45 Cs *37 2.6E+02 8.4E+00
- 09538 STP-SO-234-11-26-90-13:35 Cs-137 8.2E+01 6.1E+00 09539 09540 STP-SO-234-11-26-90-13:3s .Cs-137 8.6E+01 6.8E+00 STP-SO-006-12-28-90-14:16 Cs-137 2.5E+02 1.0E+01 09687
- Denotes controt locations Measured Activity is when the result is 3 times the sigma error.
Page J-20
m m m m W W W mM M W W W m M M M M e TAQLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA PASTURE GRASS VEGETATION PISCIVOROUS FISH LAB SAMPLE RESULT 1 SIGMA LAS SAMPLE RESULT 1 SIGMA I NUMRER SAMPLE SUBMISSION CODE ANALYSIS pCf/Kg ERRat ut.p*BER SAMPLE SUBMISSION CCDE ANALYSIS pCi/Kg wet wt ERROR
- i
- 09541 STP-VP-037-11-26-90-12:53 Cs-137 7.8E+00 1.2E+00 08716 STP-F1-252-06-19-90-15:3s ts-137 7.4E+00 2.3E+ A 08717 STP-F1-Z52-06-19-90-15:3s ts-137 1.0E+01 2.7E+00 08718 STP-F1-252-06-19-90-15:30 Cs-137 9.4E+00 2.0 +00 i'
I i i l l l l l s t
- Denotes control locations !
Measured Activity is when the result is 3 times the sigme error. rege J-21 i l
.m M M M- M M M M m W M M M M M M M M M TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENT 7.1,MEDYA l
ARTHROPODIVOROUS FISH CRUSTACEAN CRAB LAB SAMPLE RESULT 1 SIGM LAB SAMPtE RESULT 1 SICMA t WUMBER SAMPLE WISSION CODE ANALYSIS pCI/Kg ERROR NUMBER SAMPLE SIAMISSION CTE AMALYSIS gCI/Kg wat wt ERROR 07987 STP-F2-215-01-15-90-12:00 Cs-137 1.3E+01 2.6E+00 08999 STP-CC-214-08-17-90-15:30 Cs-137 1.2E+01 2.7E+00 08?99 STP-CC-214-08-17-90-15:30 Co-58 2.0E+01 2.1E+00 08999 STP-CC-214-08-17-90-15:30 Ag-110 4.0E+01 2.3E+00 f t i i l i l i
- Denotes control tocations Measured Activity is when the result is 3 times the sigme error.
Page J-22 L
M M M M M M M M M M M M M M M EE M TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESULT 1 S!CMA LA8 SAMPLE RESULT 1 SIGMA NtM9ER SAMPLE SUBMISSION CODE ANALYSIS pCi/Kg EPROR NUMBER SAMPLE SUBMISSIC4 CODE ANALYSIS pCi/Kg EPROR 07911 STP-AP-035-01-04-90-10:08 Beta 2.3E-02 7.7E-04 08007 STP-AP-006-01-24-90-16:0d Beta 1.8E-02 7.1E-04 07912 STP-AP-018-01-04-90-10:39 Beta 2.5E-02 8.0E-04 08024 STP-AP-035-01-31-90-10:53 Beta 1.2E-02 6.3E-04 07913 STP- AP-033-01-04-90-11:47 Beta 2.4E-02 8.1E-04 08025 STP-AP-018-01-31-90-11:21 Beta 1.4E-02 6.6E-04 07914 STP-AP-039-01-04-90-12:30 Beta 2.5E-02 8.0E-04 08026 STP-AP-033-01-31-90-11:47 Bete 1.1E-02 6.1E-04
- 07915 ST P- AP-037-01-04 12:55 Beta 2.4E-02 7.9E-04 08027 STP-AP-039-01-31-90-12:53 Beta 1.5E-02 6.6E-04 07916 STP-AP-015-01-04-90-13:14 Beta 2.4E-02 7.9E-04
- 08028 STP-AP-037-01-31-90-13:24 Beta 1.3E-02 6.4E-04 07917 STP-AP-016-Ol-04-90-13:19 Beta 2.5E-02 7.9E-04 08029 STP-AP-015-01-31-90-13:49 Beta 1.4E-02 6.7E-04 07918 STP-AP-001-01-04-90-13:23 Beta 2.6E-02 8.0E-04 08030 STP-AP-016-01-31-90-14:00 Beta 1.1E-02 6.8E-04 07919 STP-AP-006-01-04-90-13:3d Beta 2.5E-02 8.0E-04 08031 STP-AP-001-01-31-90-14:14 Beta 1.3E-02 6.5E-04 07920 STP-AP-006-01-04-90-13:3d Beta 2.6E-02 8.2E-04 08032 STP-AP-006-01-31-90-14:2d Beta 1.4E-02 6.5E-04 07933 STP-AP-035-01-09-90-10:17 Beta 4.6E-02 1.3E-03 08033 STP-AP-006-01-31-90-14:2d Beta 1.4E-02 6.6E-04 07934 STP-AP-018-01-09-90-10:46 Beta 4.8E-02 1.3E-03 08054 STP-AP-035-02-06-90-10:01 Beta 1.5E-02 7.4E-04 07935 STP-AP-033-01-09-90-11:12 Beta 4.6E-02 1.2E-03 08055 STP-AP-018-02-06-90-10:30 Beta 1.7E-02 7.8E-04 07936 STP-AP-039-01-09-90-11:51 Beta 4.8E-02 1.3E-03 08056 STP-AP-033-02-06-90-10:58 8 eta 1.8E-02 7.8E-04
- 07937 STP- AP-037-01-09-90-12:10 Beta 4.9E-02 1.3E-03 08057 STP-AP-039-02-06-90-11:51 Beta 1.7E-02 7.6E-04 07938 STP-AP-015-01-09-90-12:28 Beta 4.7E-02 1.3E-03
- 08058 STP- AP-037-02-%-99-12:16 Beta 1.8E-02 7.8E-04 07939 STP-AP-016-01-09-90-14:06 Beta 4.9E-02 1.3E-05 08059 STP-AP-015-02-06-90-12:36 Beta 1.8E-02 8.0E-04 ;
07940 STP-AP-001-01-09-90-14:09 Beta 4.7E-02 1.3E-03 08061 STP-AP-001-02-06-90-16:47 Beta 1.7E-02 7.7E-04 07941 STP-AP-006-01-09-90-14:2d Bete 4.6E-02 1.3E-05 08062 STP-AP-006-02-06-90-15:3d Beta 1.8E-02 8.0E-04 07942 STP-AP-006-01-09-90-14:2d Beta 4.7E-02 1.3E-03 08063 STP-AP-006-02-06-90-15:3d Beta 1.7E-02 7.8E-06 07767 STP- AP-035-01 90-09:57 Beta 1.8E-02 6.6E-04 08087 STP-AP-035-02-15-90-10:09 Beta 2.00-02 6.4E-04 07968 ST P- AP-018-01 90-10:32 Beta 2.1E-02 6.9E-04 03088 STP-AP-018-02-15-90-10:38 Beta 2.2E-02 6.7E-04 , 07969 STP- AP-033-01 90-10:56 Beta 1.9E-02 6.8E-04 08089 STP-AP-033-02-15-90-11:03 eeta 2.2E-02 6.7E-04 l 07970 STP- AP-039-01-17-99-11:46 Beta 2.1E-02 6.8E-04 08090 STP-AP-039-02-15-90-11:52 Beta 2.1E-02 6.6E-04 ,
- 07971 STP- AP-037-01-17-90-12:13 Beta 2.1E-02 6.9E-04
- 08091 ST P- AP-037 15-90-12:20 8 eta 2.1E-02 6.6E-04
! 07972 STP-AP-015-01-17-90-14:54 Beta 1.9E-02 6.6E-04 08092 S1P-AP-015-02-15-90-15:04 Beta 2.1E-02 6.6E-04 07973 STP- AP-016 17-90-15:00 Beta 1.8E-02 6.5E-04 08093 STP-AP-016-02-15-90-14:59 seta 1.9E-02 6.3E-04 07974 STP- AP-001-01-17-90-15:05 Beta 1.9E-02 6.6E-04 08094 STP-AP-001-02-15-90-15:08 Beta 2.0E-02 6.4E-04 07975 ST P- AP-006-01-17-90-13:Od Beta 2.0E-02 7.0E-04 08095 STP-AP-006-02-15-90-14:3d Beta 2.1E-02 6.4E-04 I 07976 ST P- AP-006-01-17-90-13:1d Beta 2.0E-02 6.9E-04 08096 STP-AP-006-02-15-90-14:3d Beta 2.1E-02 6.5E-04 07998 STP-AP-035-01-24-90-10:22 Beta 2.1E-02 7.5E-06 08125 STP- AP-035-02-21 10:07 Beta 2.9E-02 1.0E-03 l 07999 STP-AP-018-01-24-90-11:02 Beta 2.2E-02 7.7E-04 08126 STP-AP-018-02-21-90-10:37 Beta 2.7E-02 1.0E-03
- 08000 STP-AP-033-01-24-90-12
- 10 Beta 2.1E-02 7.7E-04 08127 STP- AP-033-02-21-90-11:03 Beta 2.8E-02 1.1E-03 i 08001 STP-AP-039-01-24-90-12:37 Beta 2.1E-32 7.6E-04 08128 STP-AP-039-02-21-90-11:45 Beta 2.7E-02 1.0E-03
- 08002 ST P- AP-037-01-24-90-13:17 Beta 2.1E-E 2 7.5E-04
- 08129 STP- AP-037-02-21-90-12:13 Bets 3.0E-02 1.1E-03 08003 STP-AP-015-01-24-90-14:35 Beta 2.OE -0
- 7.5E-04 08130 STP-AP-015-02-21-90-15:14 seta 2.6E-02 1.0E-03 08004 STP-AP-016-01-24-90-14:41 Beta 2.0E-O' 7.5E-04 08131 STP-AP-016-02-21-90-15:22 Beta 2.9E-02 1.0E-03 08005 STP-AP-001-01-24-90-14:49 Beta 2.0E "2 7.5E-04 08132 STP-AP-001-02-21-90-15:34 seta 2.5E-02 1.0E-03 08006 STP-AP-006-01-24-90-16:Od Beta 2.0c-02 7.3E-04 08133 STP-AP-006-02-21-90-14:1d Beta 2.8E-02 1.0E-03 l
- Denotes contret locations Measured Activity is when the result is 3 times the sigma error.
l Page J-23 1 E [ l i I
M M M M M M M M M M M M M M M M M M TAWLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESULT 1 SICMA LA8 SAMPLE RESULT 1 SIGMA NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCf/M'3 EPROR WUMBER SAMPLE SU8M!$$104 CODE ANALYSIS pCi/M'3 EPROR 08134 STP-AP-006-02-21-90-14:2d Beta 2.9E-02 1.1E-03 08263 STP-AP-006-03-21-90-14:2d Bete 1.9E-02 7.0E-04 08152 STP-AP-035-02-28-90-10:20 Beta 1.8E-02 6.5E-04 08264 STP-AP-006-03-21-90-14:2d Beta 2.0E-02 7.2E-04 08153 STP-AP-018-02-28-90-11:47 Beta 1.8E-02 6.5E-04 08287 STP-AP-035-03-28-90-10:05 seta 2.EE -02 6.9E-04 08154 STP-AP-033 02-28-90-12:42 seta 1.8E-02 6.6E-04 08288 STP-AP-018-03-28-90-10:30 Bete 2.0E-02 6.8E-04 08155 STP-AP-039-02-28-90-13:04 Beta 1.8E-02 6.8E-04 08289 STP-AP-033-03-28-90-13:29 Beta 1.9E-02 6.6E-04
- 08156 STP-AP-037-02-28-90-13:34 Beta 1.7E-02 6.4E-04 08290 STP-AP-039-03-28-90-13:06 Beta 1.9E-02 6.7E-04 08157 STP-AP-015-02-28-90-13:53 Beta 1.7E-02 6.5E-04
- 08291 ST P 47-03 7-03-2M-90-12:45 Bete 2.0E-02 7.0E-04 08158 STP- AP-016-02-28-90-13:59 Beta 1.8E-02 6.5E-04 08292 STP-AP-015-03-28-90-12:19 Bete 1.8E-02 6.6E-04 08159 STP-AP-001-02-28-90-14:05 Beta 1.7E-02 6.5E-04 08293 STP-AP-016-03-28-90-12:14 Beta 2.0E-02 7.0E-04 08160 51P-AP-006-02-28-90-14:3d Beta 1.8E-02 6.5E-04 08294 STP- AP-001-03-28-90-12:07 Beta 1.9E-02 6.7E-04 08161 STP-AP-006-02-28-90-14:3d Beta 1.6E-02 6.2E-04 08295 STP-AP-006-03-28-90-11:3d Beta 2.0E-02 7.0E-04 08180 STP- AP-035-03-07-90-10:06 Bets 1.9E-02 7.3E-04 08296 STP-AP-006-03-28-90-11:4d Beta 2.1E-02 7.0E-04 08181 STP- AP-018-03-07-90-10:37 Beta 1.8E-02 7.1E-04 08313 STP-AP-035-04-03-90-11:43 Bete 1.2E-02 6.3E-04 08182 STP- AP-033-03-07 11:06 Beta 1.9E-02 7.5E-06 08314 STP-AP-018-04-03-90-12:15 Beta 1.2E-02 6.3E-04 08183 STP-AP-039-03-07-90-11:43 Bete 1.9E-02 7.2E-04 08315 51P-AP-033-04-03-90-14:33 8ete 1.2E-02 6.4E-04
- 08184 STP- AP-037-03-07-90-12:11 Bets 1.SE-02 7.2E-04 08316 STP-AP-039-04-03-90-14:23 Sete 1.3E-02 6.4E-04 08185 STP- AP-015-03-07 12:31 Beta 1.9E-02 7.3E-04
- 08317 STP-AP-037-04-03-90-14:01 Sete 1.2E-02 6.3E-04 08186 STP- AP-016-03-07-90-12:36 Beta 1.9E-02 7.4E-04 08318 STP-AP-015-04-03-90-12:40 Beta 1.1E-02 6.2E-04 08187 STP- AP-001-03-07-90-12:39 Beta 1.8E-02 7.1E-04 08319 STP-AP-016-04-03-90-12:45 Beta 1.3E-02 6.5E-04 08188 STP- AP-006-03-07-90-12:5d Beta 1.9E-02 7.3E-04 08320 STP-AP-001-04-03-90-12:50 Beta 1.2E-02 6.4E-06 08189 STP- AP-006-03-07-90-12:5d Beta 1.8E-02 7.1E-04 08321 STP-AP-006-04-03-90-13:1d Bete 1.2E-02 6.3E-04 08233 STP-AP-035-03-15-90-13:18 8ete 1.4E-02 5.4E-04 08322 STP-AP-006-04-03-90-13:1d 8ete 1.3E-02 6.4E-04 08234 STP-AP-018-03-15-90-12:50 Bete 1.2E-02 5.2E-04 08358 STP-AP-035-04-10-90-10:06 seta 1.6E-02 6.3E-06 08235 STP-AP-033-03-15-90-12:24 Beta 1.2E-02 5.1E-04 08359 STP-AP-018-04-10-90-10:36 Beta 1.6E-02 6.3E-04 08236 STP-AP-039-03-15-90-12:03 Bete 1.3E-02 5.3E-04 08360 STP-AP-033-04-10-90-11:05 seta 1.6E-02 6.3E-04
- 08237 STP- AP-037-03-15-90-11:35 Beta 1.3E-02 5.3E-04 08361 STP-AP-039-04-10-90-11:34 Bets 1.6E-02 6.3E-04 08238 STP-AP-015-03-15-90-10:25 Beta 1.2E-02 5.3E-04
- 08362 STP-AP-037-04-10-90-12:03 Bete 1.7E-02 6.5E-04 08239 STP-AP-016-03-15-90-10:33 Beta 1.2E-02 5.2E-04 08363 S!P-AP-015-04-10-90-12:20 Beta 1.6E-02 6.2E-04 08240 STP-AP-001-03-15-90-10:38 Beta 1.2E-02 5.2E-04 08364 STP-AP-016-04-10-90-12:23 Beta 1.7E-02 6.4E-04 08241 STP-AP-006-03-15-90-10:5d Beta 1.3E-02 5.3E-04 08365 STP- AP-001-04-10-90-12:27 Sete 1.6E-02 6.2E-04 08242 STP-AP-006-03-15-90-10:5d sete 1.2E-02 5.3E-04 08366 STP-A*-006-04-10-90-15:4d Beta 1.6E-02 6.1E-04 08255 STP-AP-035-03-21-90-10:09 Beta 2.0E-02 7.5E-04 08367 STP-AP-006-04-10-90-15:4d sets 1.7E-02 6.2E *>4 08256 STP-AP-018-03-21-90-11:08 Beta 2.3E-02 7.8E-04 08382 STP-AP-035-04-19-90-09:45 Bete 1.6E-02 5.3E-04 i 08257 STP-AP-033-03-21-90-11:31 Beta 2.1E-02 7.5E-04 08383 STP-AP-018-04-19-90-10:25 Beta 1.6E -02 5.3E-04 !
08258 STP-AP-039-03-21-90-16:38 Bete 2.1E-02 7.4E-04 08384 STP-AP-033-04-19-90-10:53 Beta 1.5E-02 5.1E-04
- 08259 STP- AP-037-03-21-90-16:20 Bete 2.1E-02 7.3E-04 08385 STP-AP-039-04-19-90-11:26 8 eta 1.8E-02 5.5E-04 08260 STP-AP-015-03-21-90-16:02 seta 2.0E-02 7.2E-04
- 08386 STP- AP-037-04-19-90-12:% Beta 1.6E-02 5.3E-04 08261 STP-AP-016-03-21-90-15:55 Beta 2.1E-02 7.2E-04 08387 STP-AP-015-04-19-90-15:12 seta 1.6E-02 5.3E-04 08262 STP-AP-001-03-21-90-15:44 Bete 2.2E-02 7.4E-04 08388 STP-AP-016-04-19-90-14:00 Beta 1.5E-02 5.2E-04 ,
- Denotes controt locations Meesured Activity is when the result is 3 times the sigme error.
Pege J-24
m M M M M M M M M M M M M M M M M TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESULT 1 SIGMA LAB SAMPLE RESULT 1 StGMA NUM9ER SAMPLE SUBMISSION CODE ANALYSIS pCi/M 3 ERROR NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M 3 EPeat 08389 STP-AP-001-04-19-90-15:27 Sete 1.6E-02 5.3E-04 08522 STP-AP-001-05-16-90-14:03 8-te 1.2E-02 5.0E-04 08390 STP-AP-006-04-19-90-15:5d Beta 1.4E-02 5.1E-04 08523 STP-AP-006-05-16-90-14:4d Bete 1.2E-02 %.1E-04 08391 STP-AP-006-04-19-90-16:0d Beta 1.5E-02 5.2E-04 08524 STP-AP-006-05-16-90-14:5d Sete 1.2E-02 5.1E-04 " 08435 STP- AP-035-04-26-90-10:18 Beta 1.8E-02 6.4E-04 08558 STP-AP-035-05-24-90-10:08 Bete 1.1E-02 4.9E-04 08436 STP-AP-018-04-26-90-11:39 Beta 1.7E-02 6.2E-04 08559 STP-AP-018-05-24-90-10:38 Bete 1.1E-02 5.0E-04 08437 STP- AP-033-04-26-90-12:17 8 eta 1.7E-02 6.?E-04 08560 STP-AP-033-05-24-90-11:00 Beta 1.1E-02 5.1E-04 08438 STP-AP-039-04-26-90-12:51 Bete 1.7E-02 6.3E-04 08561 STP-AP-039-05-24-90-11:32 Bete 1.1E-02 5.1E-04
- 08439 STP-AP-037-04-26-90-13:10 Beta 1.8E-02 6.4E-04
- 08562 STP- AP-037-05-24-90-12:08 Beta 1.0E-02 4.9E-04 08440 STP-AP-015-04-26-90-13:47 Sete 1.6E-02 6.2E-04 08563 STP-AP-015-05-24-90-12:34 Bete 1.1E-02 4.?E-04 08441 STP-AP-016-04-26-90-13:52 Beta 1.8E-02 6.5E-04 08564 STP-AP-016-05-24-90-13:53 Beta 1.1E-02 5.0E-04 08442 STP-AP-001-04-26-90-14:22 Bete 1.7E-02 6.3E-04 08565 STP-AP-001-05-24-90-14:00 Bete 9.7E-03 4.8E-04 08443 STP-AP-006-04-26-90-14:Od Beta 1.8E-02 6.5E-04 08566 STP-AP-006-05-24-90-14:3d Beta 1.1E-02 5.0E-04 08444 STP-AP-006-04-26-90-14:0d Beta 1.8E-02 6.5E-04 08567 STP-AP-006-05-24-90-14:4d Beta 1.1E-02 5.0E-04 08461 $1P-AP-035-05-02-90-10:35 Beta 1.1E-02 6.2E-04 08582 STP-AP-035-05-30-90-10:06 Beta 1.2E-02 6.3E-04 08462 STP-AP-018-05-02-90-11:03 Beta 1.3E-02 6.5E-04 08583 STP-AP-018-05-30-90-10:36 Beta 1.1E-02 6.2E-04 08463 STP-AP-033-05-02-90-11:27 Beta 1.4E-02 6.6E-04 08584 STP-AP-033-05-30-90-11:39 Beta 1.1E-02 6.3E-04 08464 STP-AP-039-05-02-90-11:53 8ete 1.2E-02 6.2E G 08585 STP-AP-039-05-30-90-12:02 Beta 1.2E-02 6.4E-04
- 08465 ST P- AP-037-05-02-90-12:20 Bete 1.3E-02 6.v_-04
- 08586 STP-AP-017-05-30-90-12:33 cete 1.3E-02 6.4E-04 i 08466 STP-AP-015-05-02-90-12:38 Beta 1.2E-02 ',.2E-04 08587 STP-AP-015-05-30-90-13:21 Sete 1.2E-02 6.2E-04 08467 STP-AP-016-05-02-90-15:14 Beta 1.2E-02 6.2E-04 08588 STP-AP-016-05-30-90-13:41 Bete 1.3E-02 6.5E-04 08468 STP-AP-001-05-02-90-15:21 Bete 1. 2E - O'.- 6.1E-04 08589 STP-AP-001-05-30-90-14:24 Bete 1.2E-02 6.3E-04 08469 STP-AP-006-05-02-90-14:4d sete 1.2E-62 6.3E-04 08500 STP-AP-006-05-30-90-15.0d Bete 1.1E-02 6.2E-04 08470 STP-AP-006-05-02-90-14:4d Bete 1.2E-02 6.3E-04 08$91 STP-AP-006-05-30-90-15.0d Beta 1.2E-02 6.4E-04 08487 STP-AP-035-05-08-90-09:31 Bete 1.5E-02 6.8E-04 08621 STP-AP-035-06-06-90-10:28 Sete 1.5E-02 6.1E-04 08488 STP-AP-018-05-08-90-10:00 Bete '.5E-02 6.8E-04 08622 STP-AP-018-06-06-90-10:59 8ete 1.5E-02 6.0E-04 08489 STP-AP-033-05-08-90-13:22 Bete 1.5E-02 6.7E-04 08623 STP-AP-033-06-06-90-11:48 Beta 1.4E-02 6.0E-04 08490 STP-AP-039-05-08-90-13:00 Sete 1.4E-02 6.6E-06 08624 STP-AP-039-06-06-90-12:18 Beta 1.4E-02 5.9E-04
- 08491 STP- AP-037-05-08-90-11:27 Beto 1.4E-02 6.5E-04
- 08625 STP- AP-037-06-06-90-12:50 Bete 1.5E-02 6.2E-04 08492 STP-AP-015-05-08-90-11:03 Bete 1.4E-02 6.5E-04 08626 STP-AP-015-06-06-90-14:54 Beta 1.4E-02 6.0E-04 08493 STP-AP-016-05-08-90-10:56 Beta 1.5E-02 6.9E-04 08627 STP-AP-016-06-06-90-14:42 Sete 1.4E-02 5.9E-04 08494 STP-AP-001-05-08-90-10:49 Sete 1.5E-02 6.8E-04 08628 STP-AP-001-06-06-90-14:30 Beta 1.6E-02 6.3E-04 08495 STP-AP-006-05-08-90-12:Od Beta 1.5E-02 6.8E-04 08629 STP-AP-006-06-06-90-14:0d Bete 1.5E-02 6.2E-04 08496 STP-AP-006-05-08-90-12:0d Beta 1.5E-02 6.7E-04 08630 STP-AP-006-06-06-90-14:Od Bete 1.5E-02 6.2E-04 08515 STP-AP-035-05-16-90-09:55 Beta 1.4E-02 5.4E 04 08650 STP-AP-035-06-12-90-10:22 Bete 9.1E-03 5.9E a4 08516 STP- AP-018-05 90-10:47 Sete 1.3E-02 5.3E-04 08651 STP- AP-018-%-12-90-11:16 Bete 9.2E-03 5.9E-04 08518 STP-AP-039-05-16-90-12:26 Beta 1.2E-02 5.1E-04 08652 STP-AP-033-06-12-90-12:27 Bets 8.6E-03 5.8E-04
- 08519 STP- AP-037-05-16-90-13 :00 Bete 1.2E-02 5.1E-04 08653 STP-AP-039-06-12-90-12:50 Bete 8.5E-03 5.8E-04 08520 STP-AP-015-05-16-90-13:26 Beta 1.2E-02 5.1E-04
- 08654 STP-AP-037-06-12-90-14:28 Sets 8.7E-03 5.8E-04 08521 STP-AP-016-05-16-90-13:49 Bete 1.3E-02 5.1E-04 08655 STP-AP-015-06-12-90-14:48 Sete 8.0E-03 5.7E-04
- Denotes control tocations Measured Activity is when the result is 3 times the sigme error.
Page J-25
m W W W W W W W W W W W W W W W m M TABLE J-2 MEA.SURED ACTIVITY IN ENVIRONMENTAL MEDIA AIRBORNE PARTICULATE AIRBORNE PARTICULATE , LAB SAMPLE RESULT 1 SIGMA LA8 SAMPLE RESULT 1 SIGMA WUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M 3 ERROR WJMBER SAMPLE SUBMISSION CODE ANALYSIS pCl/M 3 ERROR 08656 STP-AP-016-06-12-90-16:14 Bete 9.9E-03 6.OE-04 08798 STP- AP-015-07-09-90-14:12 Beta 1.9E-02 6.6E-04 08657 STP-AP-001-06-12-90-14:54 Beta 8.3E-03 5.7E-04 08799 STP- AP-016-07-09-90-14:18 Beta 2.0E-02 6.8E-04 08658 STP-AP-006-06-12-90-15:4d Beta 8.1E-03 5.7E-04 08800 STP- AP-001-07-09-90-14:05 Beta 1.9E-02 6.7E-04 08659 STP-AP-006-06-12-90-15:4d Beta 8.3E-03 5.7E-04 08801 STP- AP-006-07-09-90-14:3d Beta 2.0E-02 6.8E-04 08699 STP-AP-035-06-20-90-10:03 Beta 1.5E-02 5.7E-04 08802 STP-AP-006-07-09-90-14:3d Beta 2.0E-02 6.8E-04 08700 STP-AP-018-06-20-90-10:34 8 eta 1.6E-02 5.7E-04 08841 STP- AP-035-07-18-90-10:32 8 eta 1.4E-02 5.0E-04 08701 STP-AP-033-06-20-90-11:40 Beta 1.4E-02 5.5E-04 08842 STP- AP-018 18-90-11:14 Beta 1.3E-02 4.9E-04 08702 STP-AP-039-06-20-90-12:02 8: eta 1.6E-02 5.7E-04 08843 STP- AP-033-07-18-90-11:40 Seta 1.3E-02 5.0E-04
- 08703 STP- AP-037-06-20-90-12:30 Beta 1.6E-02 SJE-04 08844 STP- AP-039-07-18-90-12:40 Beta 1.4E-02 5.1E-M 08704 STP-AP-015-06-20-90-13:59 Beta 1.5E-02 5.5E-04
- 08845 STP- AP-037-07-18-90-13:21 Beta 1.3E-02 5.0E-04 08 705 STP-AP-016-06-20-90-14:06 Seta 1.6E-02 5.8E-04 08845 STP- AP-015 18-90-14:58 8 eta 1.2E-02 4.7E-04 08706 STP-AP-001-06-20-90-14:35 Beta 1.5E-02 5.6E-04 08847 STP- AP-016-07-18-90-15:08 8 eta 1.3E-02 4.9E-04 08707 STP-AP-006-06-20-90-13:Od Beta 1.6E-02 5.8E-04 08848 STP-AP-001-07-18-90-15:14 Beta 1.2E-C2 4.7E-06 08708 STP-AP-006-06-20-90-13:Od Beta 1.5E-02 5.6E-04 08849 STP- AP-006 18-90-15:5d Beta 1.2E-02 4.8E-04 08729 STP- AP-035-06-25-90-10:18 Beta 1.4E-02 7.6E-04 08850 STP- AP-006 18-90-15:5d Beta 1.3E-02 4.SE-04 08730 STP-AP-018-06-25-90-10:51 seta 1.3E-02 7.4E-04 08885 STP-AP-035-07-23-90-10:10 Beta 1.3E-02 7.3E-04 08731 STP-AP-033-06-25-90-11:19 Beta 1.4E-02 7.6E-04 08886 STP- AP-018-07-23-90-10:39 seta 1.3E-02 7.4E-04 08732 STP-AP-039-06-25-90-12:01 Beta 1.4E-02 7.6E-04 08887 STP- AP-033-07-23-90-11:56 8 eta 1.2E-02 7.2E-04
- 08733 STP- AP-037-06-25-90-14:36 Beta 1.2E-02 7.2E-04 08888 STP- AP-039-07-23-90-12:18 Bet a 1.2E-02 7.2E-04 08734 STP-AP-015-06-25-90-12:22 Beta 1.2E-02 7.3E-04
- 08889 STP- AP-037-07-23-90-12:46 Beta 1.3E-02 7.3E-04 08735 STP-AP-016-06-25-90-12:27 Beta 1.4E-02 7.7E-04 08890 STP- AP-015-07-23-90-13:04 Beta 1.1E-02 7.2E-04 08736 STP-AP-001-06-25-90-12:33 Beta 1.3E-02 7.5E-04 08891 STP- AP-016-07-23 90-13:10 Beta 1.3E-02 7.5E-04 08737 STP-AP-006-06-25-90-13:1d Beta 1.2E-02 7.3E-04 08892 STP- AP '101-07-23-90-13:15 8 eta 1.3E-02 7.5E-04 08738 STP-AP-006-06-25-90-13:1d Beta 1.3E-02 7.3E-06 08893 STP-AP-006-07-23-90-13:3d Beta 1.2E-02 7.3E-04 08767 ST P- AP-035-07-02-90-10:03 8 eta 1.8E-02 6.5E-04 08894 STP- AP-006-07-23-90-13:3d 8= 1.2E-02 7.4E-04 08768 STP- AP-018-07-02-90-10:32 Beta 1.8E-02 6.6E-04 08897 ST P- AP-035-07-3' 10:00 Be - 2.8E-02 7.1E-04 08769 ST P- AP-033-07-02-90-11:57 Beta 1.7E-02 6.4E-04 08898 STP- AP-018-07-31 10:32 8 eta 2.6E-02 7.0E-04 08770 STP- AP-039-07-02-90-12:20 Beta 1.8E-02 6.5E-04 08899 STP- AP-033-07-31-90-10:57 eeta 2.5E-02 6.8E-04
- 08771 ST P- AP-037-07-02-90-12:50 Beta 1.8E-02 6.6E-04 08900 STP- AP-039-07-31-90-11:34 Beta 2.6E-02 6.9E-04 08772 STP- AP-015-07-02-90-14:09 Beta 1.8E-02 6.4E-04
- 08901 STP- AP-03 7-07-31-90-12:04 Beta 2.5E-02 6.9E-04 '
08773 STP-AP-016-07-02-90-13:13 Beta 1.8E-02 6.5E-04 08902 STP-AP-015-07-31-90-14:14 Beta 2.5E-02 6.7E-04 08774 STP-AP-001-07-02-90-14:34 Beta 1.7E-02 6.4E-04 08903 STP- AP-016-07-31-90-14:41 8 eta 2.7E-02 7.0E-04 08775 STP-AP-006-07-02-90-13:2d Beta 1.7E-02 6.4E-04 08904 STP- AP-001-07-31 15:20 8 eta 2.6E-02 6.9E-04 08776 STP-AP-006-07-02-90-13:3d Beta 1.8E-02 6.5E-04 08905 STP- AP-006-07-31-90-13:4d Beta 2.5E-02 6.9E-04 08793 STP- AP-035-07-09-90-10:44 Beta 2.0E-02 6.8E-04 08906 STP- AP-006-07-31 13:4d Beta 2.7E-02 7.0E-04 08794 STP- AP-018-07-09-90-11:36 8ete 2.0E-02 6.8E-06 08957 STP-AP-035-08-08-90-10:15 Beta 2.5E-02 6.7E-04 08795 STP- AP-033-07-09-90-12:00 8ete 2.1E-02 6.9E-04 08958 STP-AP-018-08-08-90-11:05 Beta 2.3E-02 6.5E-06 08796 STP-AP-039-07-09-90-15:42 Beta 2.0E-02 6.7E-04 08?59 STP-AP-033-08-08-90-11:42 Beta 2.4E-02 6.7E-04
- 08797 STP- AP-037-07-09-90-15:21 Beta 2.0E-02 6.7E-06 08960 STP-AP-039-08-08-90-12:41 Beta 2.5E-02 6.7E-04
- Oenotes controt locat ter's Measured Activity is when the result is 3 times the sigma error.
Page J-26
M M M M M M M M M M M M M M M M M M TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA
~
AIRBORNE PARTICULATE AIRBORNE PARTICULATE RESULT 1 $1GMA RESULT 1 SIGMA t.A8 SAMPLE EppoR LAB SAMPLE NUMBER SAMPLE SUBMISSION CtEE A HLYSIS pCi/M 3 NUMBER SAMPLE SUBMISSION CODE ANALYS!$ pCi/M 3 ERROR 09067 STP-AP-039-09-05-90-11:31 8 eta 1.3E-02 5.5E-04
- 08961 STP-AP-037-08-08-90-13:11 Beta 2.4E-02 6.6E-04 Sete 1.2E-02 5.2E-04 Beta 2.3E-02 6.5E-04
- 09068 STP-AP-037-09-05-90-12:01 08962 STP-AP-015-08-08-90-13:30 09069 STP-AP-015-09-05-90-12:22 seta 1.1E-02 5.2E-04 08963 STP-AP-016-08-08-90-13:42 Beta 2.5E-02 6.8E-04 1.2E-02 5.2E-04 09070 STP-AP-016-09-05-90-12:49 Sete 08964 STP-AP-001-08-08-90-13:47 seta 2.5E-02 6.7E-04 Beta 1.2E-02 5.3E-04 Beta 2.3E-02 6.6E-04 09071 STP-AP-001-09-05-90-12:54 08965 STP-AP-006-08-08-90-14:0d 09072 STP-AP-006-09-05-90-14:0d Beta 1.2E-02 5.4E-04 ;
08966 STP-AP-0E6-08-08-90-14:Od Beta 2.4E-02 6.7E-04 Beta 1.2E-02 5.4E-04 1 Sete 2.6E-02 8.3E-04 09073 STP-AP-006-09-05-90-14:0d 08985 STP-AP-035-08-14-90-10:29 09095 STP-AP-035-09-12-90-10:43 seta 1.2E-02 5.7E-04 08986 STP-An-018-08-14-90-11:02 Beta 2.8E-02 8.5E-04 1.2E-02 5.6E-04 09096 STP-AP-018-09-12-90-11:13 seta 08987 STP-AP-033-08-14-90-11:28 Beta 2.9E-02 8.6E-04 1.3E-02 5.8E-04 09097 STP-AP-033-09-T2-90-12:1T Beta 08988 STP-AP-039-08-14-90-12:29 Beta 3.0E-02 8.7E-04 Beta 1.3E-02 5.8E-04 seta 2.6E-02 8.2E-04 09098 STP-AP-039-09-12-90-12:44
- 08989 ST P- AP-037-08-14-90-15:07
- 09099 STP-AP-037-09-12-90-13:14 Beta 1.2E-02 5.7E-04 08990 STP-AP-015-08-14-90-15:40 Beta 2.5E-02 8.1E-04 Bete 9.6E-03 5.2E-04 seta 2.8E-02 8.5E-04 09100 STP-AP-015-09-12-90-13:33 08991 STP-AP-016-08-14-90-15:46 09101 STP-AP-016-09-12-90-13:41 Beta 1.1E-02 5.4E-04 STP-AP-001-08-14-90-15:S1 Beta 2.6E-02 8.2E-04 1.1E-02 5.5E-04 08992 09102 STP-AP-001-09-12-90-13:47 Beta STP-AP-006-08-14-90-16:Od Beta 2.9E-02 8.6E-04 1.2E-02 5.9E-04 08993 09103 STP-AP-006-09-12-90-14:Od Beta 08994 STP-AP-006-08-14-90-16:0d Beta 2.7E-02 8.3E-0* Beta 1.1E-02 5.6E-04 Beta 1.8E-02 5.9E-04 09104 STP-AP-006-09-12-90-14:0d 09010 STP-AP-C35-08-22-90-10:20 09135 STP-AP-035-09-18-90-10:05 Bete 7.5E-03 5.4E-04 STP-AP-018-08-22-90-10:49 Beta 1.8E-02 6.0E-04 7.6E-03 5.4E-04 09011 09136 STP-AP-018-09-18-90-11:16 Bete 09012 STP-AP-033-08-22-90-11:46 Beta 1.9E-02 6.2E-04 Bets 6.4E-03 5.2E-04 Beta 1.9E-02 6.1E-04 09137 STP-AP-033-09-18-90-11:44 09013 STP-AP-039-08-22-90-12:08 09138 STP- AP-039-09-18-90-12:57 Beta 8.6E-03 5.5E-04
- 09014 ST P- AP-037-08-22-90-12:39 seta 1.7E-02 5.9E-04 8.5E-03 5.6E-04
- 09139 STP- AP-037-09-18-90-13:28 8ets 09015 STP-AP-015-08-22-90-12:58 Beta 1.7E-02 5.8E-04 Bets 7.2E-03 5.4E-04 Beta 1.9E*02 6.1E-04 0914C STP-AP-015-09-18-90-13:49 09016 STP-AP-016-08-22-90-13:03 09'41 STP- AP-016-09-18-90-14:03 Bete 7.M-03 5.5E-04 09017 STP-AP-001-08-22-90-13:06 Beta 1.7E-02 5.9E-04 seta 7.4E-03 5.4E-04 Beta 1.7E-02 5.9E-04 09142 STP-AP-001-09-18-90-14:08 09018 STP-AP-006-08-22-90-13:1d 09143 STP-AP-006-09-18-90-16:2d Bets 6.4E-03 5.2E-04 STP-AP-006-08-22-90-13:1d Beta 1.7E-02 5.8E-04 7.7E-03 5.3E-04 09019 09144 STP-AP-006-09-18-90-14:2d Bete 09022 STP-AP-035-08-28-90-12:22 Beta 2.5E-02 8.1E-04 Beta 1.1E-02 5.8E-04 Beta 2.6E-02 8.1E-04 09176 STP-AP-035-09-25-90-10:22 09023 STP-AP-018-08-28-90-12:53 09177 STP-AP-018-09-25-90-11:15 seta 1.1E-02 5.7E-04 STP-AP-033-08-28-90-13:45 Beta 2.3E-02 7.8E-04 1.2E-02 5.9E-94 09024 09178 STP-AP-033-09-25-90-12:15 Beta STP-AP-039-08-28-90-14:08 Beta 2.6E-02 8.2E-04 1.2E-02 5.9E-04 09025 09179 STP- A P-039-09-25-90-12:37 Beta
- 09026 STP-AP-037-08-28-90-14:40 Beta 2.6E-02 8.1E-04 seta 1.1E-02 5.9E-04 t
Beta 2.3E-02 7.8E-04
- 09180 STP- AP-037-09-25-90-13:04 09027 STP-AP-015-08-28-93-15:15 09181 STP-AP-015-09-25-90-16:20 Beta 1.1E-02 5.7E-04 STP-AP-016-08-28-90-15:20 Beta 2.4E-02 7.9E-04 1.2E-02 5.8E-04 09028 09182 STP-AP-016-09-25-90-16:24 seta STP-AP-001-08-28-90-15:38 Beta 2.5E-02 7.9E-04 1.1E-02 5.7E-04 09029 09183 STP-AP-001-09-25-90-16:29 Beta 09030 STP-AP-006-08-28-90-15:5d Beta 2.7E-02 8.2E-04 3.1E-02 8.1E-06 I 09215 STP-AP-035-10-02-90-10:23 8 eta STP-AP-006-08-28-90-15:5d Beta 2.4E-02 7.9E-04 3.1E-02 8.1E-04 09031 09216 STP-AP-018-10-02-90-11:13 Beta 09064 STP-AP-035-09-05-90-09:44 8 eta 1.1E-02 5.1E-04 3.2E-02 8.3E-04 09217 STP-AP-033-10-02-90-11:36 8 eta 09065 STP-AP-018-09-05-90-10:13 8 eta 1.3E-02 5.4E-04 8 eta 3.2E-02 8.3E-04 Beta 1.3E-02 5.5E-04 09218 STP-AP-039-10-02-90-12:19 09066 STP-AP-033-07-05-90-10:40
- Derotes control locations Measured Activity is when the result is 3 times the sigma error.
f Page J-27
M M M M M M M M M M M M M M M - TABLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL MEDIA AIRBORNE PARTICULATE AIRBORNE PARTICULATE RESULT 1 StGPA dESULT 1 SIGMA L*8 SAMPtE LAB SAMPLE sosetP SAMPLE SUBMISSION CODE ANALYSIS pCi/M*3 E#FDP N'JMBER SAMPLE SL9t!S$10N CIEE ANALYSIS pci/M 3 Fe90R 09394 STP-AP-030-10-29-90-12:16 Bete 3.7E-02 1.1E-03
- 09219 STP-AP-037-10-02 90-12:47 Bete 3.2E-02 8.2E-04 3.5E-02 1.0E-03
- 09395 STP- AP-037- 10-29-90-11:26 Bete 09220 STP-AP-015-10-02-90-13:21 Sete 2.9E-02 8.0E-04 3.6E-02 1.0E-03 09396 STP-AP-015-10-29-90-14:24 Bete 09221 STP-AP-016-10-02-90-13:30 Bets 3.3E-02 8.4E-04 3.6E-02 1.0E-03 Sete 3.0E-02 8.1E-04 09397 STP-AP-016-10-29-90-14:48 Bete 09222 STP-AP-001-10-02-90-13:42 09398 STP-AP-001-10-29-90-10:43 Bete 3.5E-02 1.1E-03 09223 STP- AP-006-10-02-90-14:1d Bete 3.2E-02 1.0E-03 3.5E 02 1.0E-03 09399 STP AP-006-10-29-90-16:1d Bete 09224 STP-AP-006-10-02-00-14:1d Bets 3.2E-02 1.0E-03 3.2E-02 9.9E-04 sets 1.2E-02 4.8E-04 09400 STP-AP-006-10-29-90-16:2d Bete 09266 STP-AP-035-10-11-90-10:53 09443 STW AP-035-11-06-90-10:03 Bete 2.6E-02 7.2E-04 09267 STP-AP-018-10-11-90-11:24 Beta 1.3E-02 4.9E-04 2.8E-02 7.3E-04 09444 STP-AP-018-11-06-90-10:33 Sete 09268 STP-AP-031 %-11-90-15:21 Bete 1.2E-02 4.8E-04 2.3E-02 6.7E-04 09445 STP-AP-033-11-06-90-10:58 Set e 09269 STP-AP-039-10 '1-90-14:59 Bete 1.1E-02 4.7E-04 2.7E-02 7.1E-04 09446 STP-AP-039-11-06-90-11:44 Sete
- 09270 STP-AP-037-10-11-90-13:11 Sete 1.1E-02 4.6E-04 2.6E-02 6.9E-04
- 09447 STP-AP-037-11-06-90-14:41 Sete STP-AP-015-10-11-90-12:00 Bete 1.1E-02 1.5E-03 2.4E-02 6.8E - U 09271 09448 STP-AP-015-11-0& 90-15:01 Bete 09272 STP-AP-016-10-11-90-12:43 Bets 1.2E-02 4.8E-04 2.6E-02 7.0E-04 09449 STP-AP-016-11-06-90-15:05 Bete 09273 StP-AP-001-10-11-90-12:37 Bete 1.1E-02 4.7E-04 2.4E-02 6.7E-04 09450 STP-AP-001-11-06-90-15:15 Bete 09274 STP-AP-006-10-11-90-11:4d Beta 1.1E-02 4.7E-04 2.5E-02 7.M -04 sete 1.1E-02 4.7E-04 09451 STP-AP-006-11-06-90-12:1d Bete 09275 STP-AP-006-10-11-90-11:4d 09452 STP-AP-006 11-06-90-ic:2d Beta 2.4E-02 6.8E-04 09318 STP-AP-035-10-18-90-09:59 Bete 2.5E-02 7.2E-04 2.5E-02 7.3E-04 i "9474 STP-AP-035-11-13-90-t1:38 Beta 09319 StP-AP-018-10-18-90-12:32 Ba t s- 2.5E-02 7.2E-04 2.4E-02 7.2E-04 09475 STP-AP-018-11-13-90-1.:33 8ete 09320 STP-AP-033-10-18-90-13:01 Sete 2.6E-02 7.6E-04 2.5E-02 7.3E-04 09476 STP-AP-033-11-13-90-11:58 Sete 09321 STP-AP-039-10-18-90-13:52 Beta 2.6E-02 7.5E-04 2.3E-02 7.1E-04 Sete 2.6E-02 7.4E-04 09477 STP-AP-039-11-13-90-12:57 Bete
- 09322 STP- AP-037- 10-18-90-14:34
- 09478 STP- AP-037 13M-13:32 Sete 2.5E-02 7.4E-04 1 09323 STP-AP-015-10-18-90-11:02 Bete 2.3E-02 7.2E-04 2.5E-02 7.4E-04 Bets. 2.6E-02 7.5E-04 09479 STP-AP-015-11-13-90 13:53 8ete 09324 STP-AP-016-10-18-90-11:15 09480 STP-AP-016-11-13-90-13:59 Bete 2.4E-02 7.2E-04 09325 STP-AP-001-10-18-90-11:26 Bete 2.6E-02 7.5E-04 Sete 2.2E-02 7.0E-04 sete 2.3E-02 7.0E-04 09481 STP-AP-001-11-13-90-14:04 09326 STP-AP-006-10-18-90-16:3d 09482 STP-AP-006-11-13-90-15:0d Bete 2.2E-02 7.0E-04 09327 STP-AP-006-10-18-90-16:4d Bete ~2.4E-02 7.0E-04 2.2E-02 6.8E-04 09483 $!P-AP-006-11-13-90-15:Od Beta 09359 STP-AP-035-10-24-90-09:49 Sete 2.1E-02 7.8E-04 2.7E-02 8.6E-04 M498 STP-AP-035-11-19-90-10:00 Bete 09360 STP-AP-018-10-24-90-11:04 Beta 2.1E-02 7.7E-04 2 . 71[- 0 2 8.5E-04 09499 STP-AP-018-11-19-90-10:32 Beta 09361 STP-AP-033-10-24-90-13:16 Beta 2.2E-02 7.7E-04 2.5E-C2 8.2E-04 09500 STP-AP-033-11-19-90-11:52 Sete 09362 STP-AP-039-10-24-90-13:47 Bete 2.4E-02 8.0E-04 2.8E-02 8.6E-04 09501 STP-AP-039-11-19-90-12:14 Bete
- 09363 STP- AP-037-10-24-90-14:21 Beta 2.2E-02 7.8E-04 8.6E-04
- 09502 STP-AP-037-11-19-90-12:42 Sete 2.8E-02 09364 STP-AP-015-10-24-90-14:42 Bete 2.1F-02 7.5E-04 Sete 2.7E-02 8.5E-04 2.1E-02 7.5E-04 09503 STP-AP-015-11-19-90-13:07 09365 STP-AP-016-10-24-90-15: M Bete 09504 STP-AP-016-11-19-90-13:03 Sete 2.BE-02 8.7E-04 09366 STP-AP-001-10-24-90-15:29 Beta 2.0E-02 7.5E-04 2.7E-02 8.4E-04 09505 STP-AP-001-11-19-90-14:22 Beta 09367 STP-AP-006-10-24-90-15:5d Bete 2.3E-02 7.9E-04 2.7E-02 8.5E-04
) 05306 STP-AP-006-11-19-90-13:3d 8ete 09368 STP-AP-006-10-24-90-15:5d 8ete 2.1E-02 7.7E-04 2.4E-02 8.2E-04 l M507 STP-AP-006-tt-19-90-13:3d Bete 09391 STP-AP-035-10-29-90-09:52 Sete 3.7E-02 1.1E-03 1.9E-02 6.6E-04 09520 STP-AP-035-11-26-90-10:05 Bete 09392 STP-AP-018-10-29-90-13:44 Bete 3.5E-02 1.0E-03 1.7E-02 6.4E-04 09521 STP-A*-018-11-26-90-10:35 Beta 09393 STP-AP-033-10-29-90-12:39 Bete 3.6E-02 1.TE-03
- Denotes controt locations Measured Activity is whert the result is 3 ti es t$e sl p e errer.
Pe9e J-28
M M M M M M M M M M M . m m m m TAOLE J-2 MEASURED ACTIVITY IN ENVIRONMENTAL McIDIA AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESULT 1 SIGMA LAB SAMPLE RESULT 1 SIGMA NUMBER SAMPLE SUBMIS$10N CODE ANALYSIS pCi/M'3 ERROR WUMBER SAMPLE SUBMISSION CODE ANALYSIS pCI F 3 ERROR 09522 STP-AP-033-11-26-90-11:07 Beta 2.0E-02 6.9E-04 09673 STP-AP-033-12-21-90-09:54 8 eta 2.3E-02 1.3E-03 09523 STP-AP-039-11-26-90-11:59 8 eta 1.9E-02 6.6E-04 09674 STP-AP-039-12-28-90-12:32 Beta 2.7E-02 6.2E-04
- 09524 STP-AP-037-11-26-90-12:29 seta 1.8E-02 6.5E-04
- 09675 STP- AP-037-12-28-90-13:00 Beta 2.7E-02 6.2E-04 09525 STP-AP-015-11-26-90-13:22 Beta 1.8E-02 6.5E-04 09676 STP-AP-015-12-28-90-13:18 seta 2.7E-G2 6.2E-04 09526 STP-AP-016-11-26-90-13:40 Beta 1.8E-02 6.5E-04 09677 STP-AP-016-12-28-90-13:23 Beta 2.8E-02 6.3E-04 09527 STP-AP-001-11-26-90-13:57 Bete 1.0E-02 6.6E-04 09678 STP-AP-001-12-28-90-13:28 8 eta 2.8E-02 6.3E-04 09528 STP-AP-006-11-26-90-14:2d Beta 1.9E-02 6.6E-06 09679 STP-AP-006-12-28-90-14:Od Beta 2.7E-02 6.2E-04 09529 STP-AP-006-11-26-90-14:2d 8 eta 1.8E-02 6.4E-04 09MO STP-AP-006-12-28-90-16:0d Beta 2.6E-02 6.1E-04 09557 STP-AP-035-12-03-90-10:22 Beta 2.2E-02 6.9E-04
.09558 STP-AP-018-12-03-90-10:51 seta 2.12-02 6.8E-04 09559 STP-AP-033-12-03-90-11:19 Beta 2.3E-02 7.1E-04 09560 STP-AP-039-12-03-90-12:08 seta 2.0E-02 6.8E-04
- 09561 STP-AP-037-12-03-90-16:42 Beta 2.0E-02 6.6E-04 09562 S'P-AP-015-12-03-90-17:01 Beta 2.2E-02 6.9E-04 09563 STP-AP-016-12-03-90-17:09 Beta 2.3E-02 7.0E-04 09564 STP-AP-001-12-03-90-17:14 Beta 2.3E-02 7.1E-04 09565 STP-AP-006-12-03-90-16:1d Beta 2.2E-02 7.0E-06 09566 STP-AP-006-12-03-90-16:1d Beta 2.1E-02 6.9E-04 09583 STP-AP-035-12-10-90-10:16 Beta 2.2E-02 7.0E-04 09584 STP-AP-018-12-10-90-10:44 Beta 2.4E-02 7.3E-04 09585 STP-AP-033-12-10-90-11:13 Beta 2.0E-02 1,1E-03 09586 STP-AP-039-12-10-90-12:32 Beta 2.1E-02 4.9E-04
- 09587 STP- AP-037-12-10-90-13:00 seta 2.2E-02 7.3E-04 09588 STP-AP-015-12-10-90-13:20 seta 2.3E-02 7.1E-04 09589 STP-AP-016-12-10-90-13:31 seta 2.2E-02 7.2E-06 09590 STP-AP-001-12-10-90-13:26 Beta 2.4E-02 7.5E-04 09591 STP-AP-006-12-10-90-14:4d seta 2.1E-02 7.0E-04 09592 STP-AP-006-12-10-90-14:4d 8 eta 2.2E-02 7.1E-04 09617 STP-AP-C35-12-18-90-10:08 Beta 1.4E-02 5.4E-06 09618 STP-AP-018-12-18-90-10:53 8ets 1.4E-02 5.5E-04 09619 STP-AP-039-12-18-90-12:59 Beta 1.9E-02 6.1E-04
- 09620 STP-AP-037-12-18-90-13:26 Beta 1.6E-02 5.8E-04 09621 STP-AP-015-12-18-90-14:45 Beta 1.4E-02 5.5E-04 09622 STP-AP-016-12-18-90-14:51 Beta 1.5E-02 5.6E-04 09623 STP-AP-001-12-18-90-14:55 Beta 1.5E-02 5.6E-04 09624 STP-AP-006-12-18-90-15:4d Beta 1.4E-02 5.5E-04 09625 STP-AP-006-12-18-90-15:4d Bets 1.3E-02 5.3E-04 09671 STP-AP-03"i-12-28-90-10:04 8 eta 2.7E-02 6.2E-04 09672 STP-AP-018-12-28-90-10:36 Beta 2.8E-02 6.2E-04
- Denotes control tocations Measured Activity is when the result is 3 times the sigma error.
Page J-29
I SECTION K CONCLUSION The operational Radiological Environmental Monitoring Program (REMP) has I now completed two full years of surveillance activities at STPEGS. report has shown that the REMP collection and analysis requirements as This described in the Off-site Dose Calculation Manual Part B have been effectively implemented. Greater than 99% of the scheduled surveillance activities were satisfactorily completed regardless if they were field or laboratory related. Confidence in the quality and accuracy of the data has also been demonstrated by the participation in numerous quality control progrems and through various quality assurance (internal and external) reviews. The primary objective of the REMP is to establish correlations between IcVels of radioactivity in the environment and radioactive releases from the plant operations. Contamination of the environment has been noted however miasurable contamination was limited to on-site locations, primarily the Main Cooling Reservoir (MCR). The maximum tritium concentcation in the MCR in 1990 I was 4100 pC1/L up from 2300 pCi/L in 1989. Adjacent sloughs and ditches also received tritium via the MCR's relief well system. These bodies of water typically had tiltium concentrations less than 1000 pC1/L and no other I nuclides were measured. Co-58 and Co-60 reached measurable concentration levels (450 pCi/Kg dry w?ight) in the MCR bottom sediments. Other nuclides (e.g. Ag-110m, Fe-59, Mn-54) were also identified but at much lower concentrations and less frequently. Co-58 and Ag-110m were also quantified in blue claw crabs collected from the MCR. The concentration of these nuclides were 50 pC1/kg wet weight for the crabs. I I I I I I K-1
I SECTION L , TABLE OF CONTENTS
. STPEGS REMP RESULTS DATA I
ADDENDUM 1 WATER Drinking..................................................... L-3 I Ground....................................................... L-7 Surface...................................................... L-ll S110 REL I NE S ED I MENT . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . L-23 S0ZL................... ........................................ L-27 BROADLEAF VEGETATION Banana Leaves................................................ L-32 Cana Leaves.................................................. L-33 Collard Greens............................................... L-38 PASTURE GRASS................................................... L-39 WILDLIFE Resident Dabbler Duck........................................ L-42 Migratory Dabbler Duck....................................... L 42 Goose........................................................ L-43 Dove......................................................... L-44 Pigeon...................................;................... L-45 Piscivorous F1sh............................................. L-46 I I L-1
I ll l I i TABLE OF CONTENTS (Cont'd) ADDENDUM 1 Page Arthropodivorous Fish........................................ L-47 I. Crab......................................................... L-4B Shr1mp....................................................... L-49 Beef Heat.................................................... L-49 k' i l d S w i n e . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . L-50 Game Deer.................................................... L-50 ,,g E Alligator.................................................... L-51 AIR t. l I Air Particulate.............................................. L-51 Air Iodine................................................... L-73 NOTE: For consistency, all values are reported as havinE two significant I digits, 11 l t I l 11 : I L-2 1 - I-l i i e * ., . . - - --__ _ _ . __--
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E E N E @ N'N E E - El ~E E E N @' N E ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 DRINKING WATER DRINKING WATER LAB SAMPLE RESULT 1 SICMA LAB SA mtE RESULT 1 SICMA NUMBER SAMPLE SUBMISSION CODE ~ ANALYSIS pCi/Kg ERROR ttD NUMBER SAa9tE SUBMISSION CODE ANALYS15 pCi/Kg EfROR LLD
- 08168 STP-to-228-02-28-90-12:10 Fe-59 8.4E-01 1.6E+00 5.6E +00 09298 ST P40-210-10-18-90-17:45 Co-58 6.4E-02 6.3E-01 2.1E+00 08271 STP-WD-210-03-21-90-15:30 fe-59 1.9E+00 -1.1E+00 4.0E+00
- 09374 STP-WD-228-10-24-90-12:4d Co-58 -1.1E+00 5.5E-01 1.7E+00
- 08272 STP-WD-228-03-21-90-12:10 re-59 8.3E-01 8.2E-01 2.9E+00
- 09375 STP-WD-228-10-24-90-12:4d Co-58 -9.0E-01 8.4E-01 2.6E +00 08417 STP-LD-210-04-27 11:10 fe-59 0.0E+00 7.2E-01 2.4E+00 09462 STP40-210 13-90-16:30 Co-58 -3.3E-01 6.6E-01 2.1E+00
- 08418 STP-WD-228-04-26-90-12:07 fe-59 9.5E-01 1.0E +00 3.6E+00
- 09463 STP-W-228-11-13-90-12:10 Co-58 -1.3E-01 6.3E 2.M+00 08530 STP-WD-210-05-16-90-16:20 fe-59 7.6E-01 1.6E+00 5.6E+00
- 09634 S TP-to-228 18-90-12:30 Co-58 -7.4E-01 5.8E-01 1.7E+00
- 08531 STP40-228-05-16-90-11:23 fe-59 3.1E+00 1.2E+00 4.8E+00 09686 STP-LD-210-12-28-90-13:51 Co-58 9.4E-02 6.1E-01 2.1E+00 08636 STP-ko-210-06-12-90-15:03 fe-59 -1.3E+00 9.3E-01 2.8E+00 08041 STP-WD-210 01-31-90-15:36 Co-60 -1.1E+00 8.7E-01 2.5E+00
- 08637 STP-WD-228-06-12-90-12:1d re-59 -1.5E+00 9.9E-01 2.9E+00
- 08042 STP-WD-228-01-31-90-12:20 Co-60 -1.0E-01 5.4E-01 1.8E+00
- 08638 STP-to-228-06-12-90-12:1d fe-59 7.5E-01 1.3E+00 4.5E+00 0816* STP-to-210-02-28-90-15:15 Co-60 -2.8E-01 6.8E-01 2.2E+00
- 08779 STP-WD-228-07-02-90-11:45 f e-59 -5.5E-01 1.6E+00 5.2E+00
- 08168 5T7-60-228- 02-28-90-12:10 Co-60 -3.1E-01 8.4E-01 2. 7E +00 08830 STP-to-210-07-13-90-14:00 fe-59 -2.2E+00 9.5E-01 2.5E+00 08271 STP-W-210-03-21-90-15:30 Co-60 4.5E-01 4.5E-01 1.6E+00 08936 STP-WD-210-08-08-90-16:45 fe-59 3.2E+00 1.5E+00 5.7E+00
- 08272 STP-WD-228-03-21-90-12:10 Co-60 -2.2E-01 3.3E-01 1.0E+00
- 08937 STP-WD-228-08-08-90-11:30 fe-59 -6.4E-01 6.3E-01 2.0E + 00 08417 STP WD-210-04-27-90-11:10 Co-60 1.0E-01 3.4E-01 1.1E+00 09123 STP-WD-210-09-18-90-15:10 fe-59 8.3E-02 7.3E-01 2.4E+00
- 08418 STP-W -228-04-26-90-12:07 Co-60 -9.5E-02 4.4E-01 1.4E+00
- 09124 STP-WD-228-09-18-90-12:30 f e 2.0E + 00 1.3E+00 3.9E+00 08530 STP40-210 16-90-16:20 Co-60 -6.0E-01 8.0E-01 2.4E+00 09298 STP-WD-210-10-18-90-17:45 Fe-59 1.7E+00 1.1E+00 4.0E+00
- 08531 STP-WD-228-05-16-90-11:23 Co-60 1.1E+00 5.2E-01 2.1E+00
- 09374 STP-WD-228-10-24-90-12:4d f e-59 -2.2E+00 1.1E+00 3.3E+00 08636 $7D 40-210-06-12-90-15 :03 Co-60 3.5E-01 4.5E-01 1.6E+00
- 09375 STP-WD-228-10-24-90-12:4d fe-59 -1.6E+00 1.9E+00 5.7E + 00
- 08637 STP-to-223-06-12-90-12:1d Co-60 7.9E-01 6.1E-01 2.2E+00 09462 STP-WD-210-11-13-90-14:30 re-59 -6.5E-01 1.2E+00 3.9E+00
- 08638 STP-to-228-06-12-90-12:1d Co-60 1.2E+00 7.2E-01 2.7E+00
- 09463 STP-WD-228-11-13-90-12:10 f e-59 -3.1E-01 1.3E+00 6.3E+00
- 08T79 STP-to-228-07-02-90-11:45 Co-60 0.0E*00 8.8E-01 2.9E+00
- 09634 STP-WD-228-12-18-90-12:30 fe-59 8.0E-01 1.4E+00 4.9E+00 08830 STP-to-210-07-13-90-14:00 Co-60 8.1E-02 4.5E-01 1.5E+00 09686 STP-WD-210-12-28-90-13:51 fe-59 0.0E+00 1.3E+00 4.3E+00 08936 STP-to-210 08-08-90-16:45 Co-60 -1.4E-01 6.6E-01 2.1E+00 08041 STP-WD-210-01-31-90-15:36 0o-58 -1.2E+00 8.6E-01 2.6E+00
- 08937 STP-WD-228-08-08-90-11:30 Co-60' 1.2E-01 3.4E-01 1.1E+00
- 08042 STP-uD-228-01-31-90-12:20 0o-58 -1.5E+00 6.2E-01 1.9E+0C 09123 STP-WD-210-09-18-90-15:10 Co-60 4.5E-01 3.9E-01 1.4E+00 08167 STP-WD-210-02-28-90-15:15 Co-58 -9.6E-01 6.9E-01 2.1E+00
- 09124 STP-to-228-09-18-90-12:30 co-60 -4.2E-01 6 M-01 2.1E+00 l
- 08168 STP-WD-228-02-28-90-12:10 Co-58 -1.1E-01 8.8E-01 2.9E+00 09298 STP-WD-210-10-18-90-17:45 Co-60 -4.7E-01 5.7E-01 1.8E+00 C8271 STP-WD-210-03-21-90-15:30 Co-58 3.2E-01 4.7E-01 1.6E+00
- 09374 STP-W -228-10-24-90-12:4d Co-60 - 7.0E - 02 5.7E-01 1.9E+00
- 08272 STP-to-228-03-21-90-12:10 to-58 2.2E-01 3.9E-01 1.3E+00
- 09375 STP-WD-228-10-24-90-t2:4d co-60 -4.9E-01 9.1E-01 2.9E+00 l 08417 STP-WD-210-04-27-90-11:10 Co-58 -6.1E-01 3.4E-01 1.0E+00 09462 STP-WD-210-11-13-90-14:30 Co-60 5.2E-01 6.0E-01 2.1E*00 l
- 08418 STP40-228-04-26-90-12:07 00-58 2.7E-01 4.8E-01 1.7E+00
- 09463 STP-WD-228-11-13-90-12:10 Co-60 8.0E-01 4.2E-01 1.2E+00 i
08530 STP-WD-210-05-16-90-16:20- Co-58 -8.4E-01 7.7E-01 2.4E+00
- 09634 STP 40-228 18-90-12:30 Co-60 4.3E-01 5.3E-01 1.9E+00 l
- 08531 STP-WD-228-05-16-90-11:23 Co-58 - 7. EE - 01 '6.3E-01 1.9E+00 09686 STP-to-210-12-28-90-13:51 Co-60 -1.3E-01 7.0E-01 2.3E*00
( 08636 STP-WD-210-06-12-90-15:03 Co-58 2.4E-01 5.5E-01 1.9E+00 08041 STP-no-213-01-31-90-15:36 Zn-65 -4.0E+00 1.9E+00 5.1E+00
- 08637 STP-WD-228-06-12-90-12:1d Co-58 1.1E+00 6.5E-01 2.3E+00
- 08042 STP-WD-228-01-31-90-12:20 2n-65 -3.3E+00 1.2E+00 3.4E+00
- 08638 STP-WD-228-06-12-90-12:1d co-58 -8.1E-02 6.7E-01 2.2E+00 08167 STP-WD-210-02-28-90-15:15 Zn-65 -1.9E+00 1.2E+00 3.5E+00
- 08779 STP-WD-228-07-02-90-11:45 Co-58 -1.2E-01 8.7E-01 2.8E+00
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ADDENDUM 1 STPEGB REMP RESULTB DATA - 1990 BURFACE WATER SURFACE WATER RESULT 1 $1CMA 1 SICMA LAB SAMrtE LA8 SAMPLE RESULT NUMBER SAMotE SUWISSION CD)E ANALYSIS pCi/Kg EPROR LLO NUMBER SAMPLE SUBMISSION CODE ANALYSIS pci/Kg ERROR ttD H-3 4.1E+03 1.8E+02 4.9E+02 1.8E+02 6.9E+02 09699 STP-WS-216-12-28-90-14:3c 07955 ST P-WS-211-01-17 13:49 H-3 -9. 7E +01 H-3 -1.5E 01 1.3E+02 5.0E+02 1.8E+02 6.9E+02 09700 STP-WS-227-12-19-90-11:2c 07956 ST P-WS-212-01 90-13:38 H-3 -2.9E+02 l-131 2.1E-01 7.3E-01 2.4E+00 1.9E+02 7.1E+02 07955 STP-US-211-01-17-90-13:49 08068 STP-US-209-02-06-90-16:20 H-3 0.00 00 I-131 3.8E-01 6.6E-01 2.2E+00 M-3 6.7E+01 1.8E+02 6.9902 07956 ST P-WS-212- 01 90-13:38 3.9E+00 08069 STP-WS-213-02-06-90-16:Os 08036 STP-WS-216-01-31-90-15:0d 1-131 -1.36 00 1.2E+00 H-3 8.6E+00 1.8E+02 7.0E+02 8.6E+00 08070 STP-US-213-02-06-90-16:Os 08037 STP-VS-216-01-31-90-15:0d I-131 3.2900 2.5D 00 H-3 1.4E+02 1.9E+02 7.2D 02 -2.7E+00 2.1E+00 6.9E+00 08071 STP-WS-229-02-06 90-16:1d 08038 STP-WS-219-01-31-90-15:13 I-131 M-3 1.8E+02 1.9E+02 7.0E+02 -3.7E+00 7.5E-01 2.2E+00 08072 STP-US-229-02-06-90-16:1d
- 08039 STP-WS-221 01-31-90-12:3s I-131 H-3 3.1E+03 2.6E+02 8.5E+02 2.0E-01 8.2E-01 2.7E+00 08342 STP-WS-216-03-21-90-15:1c
- 08040 STP-US-221-01-31-90-12:3s 1-131 H-3 1.9E+02 2.3E+02 8.5E+02 -1.3900 1.8E+00 5.9E+00
- 08343 ST P-US-226-03-21 11:Oc 08068 STP-WS-209 02-06-90-16:20 1-131 STP WS-227-03-21-90-10:1c H-3 2.0E+02 2.3E+02 8.5002 I-131 -3.?E+00 1.8E+00 5.7E+00 08344 7.4E*02 08069 STP-WS-213-02-06-90-16:Os STP-US-209-05-16-90-16:10 H-3 1.5E+02 2.0E+02 t-131 -9.1E-01 1.3E+00 4.1E+00 08532 7.4E+02 08070 STP-WS-213-02-06-90-16:Os STP-WS-211-05-16-90-13:4s M-3 1.2E+02 2.0E+02 I-131 5.7E-01 1.7E+00 5.6E+00 38533 7.4E + 02 08071 STP-WS-229-02-06 90-16:1d STP-US-211-05-t6-90-13:4s H3 4.0E+02 2.0E+02 I-131 7.3E-01 1.1E+00 3.6E+00 08534 7.4D02 08072 STP-US-229-02-06-90-16:1d STP-us-212-05-16-90-15:35 H-3 3.0E+02 2.0D 02 1-131 -3.8D 00 1.2E+00 3.6E+00 08535 7.4E+02 08073 STP-US-227 12-90-13:Os STP-WS-213-05-16-90-15:57 H3 5.5E+01 2.0E+02 I-131 5.4E-01 8.1E-01 2.7E+00 08536 7.4E*02 08076 STP-WS-227-02-12-90-13:Os H-3 2.3E +02 2.0E+02 1-131 6 9E-01 1.0E+00 3.50 00 08537 ST P-US-229-05-16-90 -16:05 7.5D02 08164 STP-WS-216-02-28-90-14:5d STP-US-227-05-23-90-14:15 H-3 6.5E+01 2.0E+02 1-131 1.4E+00 8.3E-01 2.9E+00 08570 7.6U02 08165 STP-WS-216-02-28-90-14:5d STP-WS-216-06-12-90-15:3c H-3 2.8E+03 2.3E+02 1-131 8.9E-02 1.5E+00 5.1E+00 08861 7.6E+02
- 08166 STP-US-226-02-28-90-11:40 H-3 -7.0D 01 2.0E+02 I-131 -4.6E-01 1.3E+00 4.2E+00
- 08862 STP-WS-226-06-12-90-11:Oc 7.9E
- 02 08267 STP-WS-216-03-21-90-15:17 S1P-US-227-06-14-90-12:2c H-3 -1.6E+02 2.1E+02 1-131 3.3E+00 4.?E*00 1.4E+01 08863 5.00 02
- 08268 STP-WS-226-03-21-90-11:Os STP-WS-209-09-05-90-14:21 H-3 -1.6E+01 1.3E+02 I-131 -2.0E+00 3.39 00 1.1E+01 09086 5.0E+02
- 08269 STP-US-226-03-21-90-11:0s STP-US-211-09-05-90-13:48 H-3 4.8E+02 1.4D 02 I-131 -1.39 00 1.9E+00 6.1E+00 09087 5.1902 08270 STP-US-218-03-21-90-10:15 STP-US-212-09-05-90-13:3d H-3 5.8E+01 1.4E+02 I-131 -1.2E+00 8.3E-01 2.6E+00 09088 5.1E+02 08413 STP-WS-216-04-27-90-10:57 STP-US-212-09-05-90-13:3d M3 1.9E+02 1.4E+02 1-131 -5.7E-M 7.5E-01 2.4E+00 09039 5.1902
- 08414 STP-WS-226-04-26-90-11:32 09090 STP-VS-213-09-05-90-13:57 K-3 1.9E+02 1.4E+02 STP-WS-218-04-26-90-10:2s 1-131 -2.1E-01 9.5E-01 3.1900
-1.7E+02 1.3E+02 5.0E+02 08415 2.4E+00 09091 STP-WS-229-09-05-90-14:15 H-3 STP-US-218-04-26-90-10:2s 1-131 -1.1E+00 7.6E-01 7.2E+02 1.4E+02 5.0E+02 08416 8.0E+00 09199 STP-WS-237-09-28-90-13:29 H-3 I-131 -5.1E+00 2.6E+00 1.3902 4.9E+02 08527 STP-US-216-05-16-90-15:15 8.6E+00 09299 STP-WS-046-09-07-90-09:Oc H3 -3.0E+01 STP-WS-226-05-16-90-10:3d t-131 -3.39 00 2.7E+00 H-3 -2.0E+00 1.3E+02 4.9902
- 08528 1.9E600 6.5E+00 09300 STP-US-047-09-07-90-11:3c I-131 1.2D 00 ,
l H3 -1.4E+02 1.3E+02 4.9E+02
- 08529 STP-WS-226-05-16-90-10:3d 1.1E+00 3.6E+00 )
- 09301 STP-WS-226-09-18-90-11:Oc 08532 STP-WS-209-05-16-90-16:10 1-131 4.6E-01 H-3 3.0E+03 1. 7E+ 02 4.9E+02 -4.9900 1.6E+00 4.7E+00 f 09302 STP-WS-216-09-18-90-14:4c 08533 STP-WS-211-05-16-90-13:4s I-131 H-3 2.0E*00 1.3902 4.9E+02 3.1E-01 1.4E+00 4.7E+00 f 09303 ST P-WS-227-09-19-90-14:Oc 08534 STP-WS-211-05-16-90-13:4s I-131 H-3 4.7E+02 1.3E+02 4.8E+02 I-131 -1.29 00 9.7E-01 3.1E+00 l 09403 STP US-211-10-29-90-15:41 4.6D02 08535 STP-WS-212-05-16-90-15:35 STP-WS-212-10-29-90-15:29 H-3 4.8E+02 1.3E+02 I-131 -5.8E+00 2.3E+00 6.8E+00 09404 4.8E+02 09536 STP-WS-213-05-16-90-15:57 STP-WS-213-10-29-90-15:52 H-3 2.8E+02 1.3E+02 t-131 2.3E+00 1.6E 00 5.6E+00 09405 4.9E+02 08537 StP-WS-229-05-16-90-16:05 09406 STP-US-229-10-29-90-16:28 H-3 7.66 02 1.4E+02 t 131 - 1. 3E + 00 2.0E+00 6.2E+00 4.9E*02 08570 STP-US-227-05-23-90-14:15 7.5600 09407 STP-WS-237-10-29-90-15:5s M-3 1.8903 1.5E+02 STP-WS 216 06 12-90-15:30 1-131 1.7E+00 2.2E+00 1.8E+03 1.5E+02 4.8E*02 08634 6.3900 09408 STP-US-237-10-29 90-15:5s M-3 1-131 -4.5900 2.7E+00 1.4E+02 4.9902
- 08635 STP-US-226-06-12-90-11:00 4.5000 09572 STP-WS-229-12-10-90-14:52 H-3 8.4E+02 1-131 -3.3E*00 1.4E+00 1.3E+02 5.0E*02 08668 SIP-US-227-06-14-90-12:20 1.6601 09595 STP-VS-209-12-13-90-12-32 H-3 -2. 7D01 S T P-WS-226 09-90-11 :3s I-III -9.6E+00 5.20 00
-1.1E+02 1.3E+02 4.M+02
- 0%*28 3.1E+00 1.0D01 09684 STP-WS-240-1?-28 90-13:40 H-3
- C*8?? ST P-VS- ??o n 7- 09 11 :3s 1-131 -1.7E+00 H-3 -5.9D01 1.3E+02 4.9r+0?
- 09699 STP VS 226-12-18-90-10:4c
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- m. m M M ADDENDUM 1 BTPEGS REMP RESULTS DATA - 1990 BURFACE WATER SURFACE WATER RESULT 1 $!tMA RESULT 1 stCMA U8 SAPLE LAS SAMPLE WUMBER SAMPLE SUWIS$104 CCEE ANALYSIS pCl/Kg EHOR LLD NUMBER SAMPLE SUBMtSSION C00E ANALYSIS pCi/Kg ERROR tt0 Cs-137 -1.3E-01 4.3E-01 1.4E+00 3.9E-01 1.?E+00 08164 STP-VS-216-02-28-90-14:5d 09088 STP-WS-212-09-05-90-13:3d Cs-1% -o.5E-01 08165 STP-WS-216-02-28-90-14:5d Cs-137 5.0E-02 3.4E-01 1.1E+00 Cs-1% -1.4E+00 7.0E-01 2.1E+00 5.0E-01 1.6E+00 09089 STP-us-212-09-05-90-13:3d
- 08166 STP-WS-226-02-28-90-11:40 Cs-137 -3.6E-01 STP-WS-213 09-05-90-13:57 Cs-134 -1.4E+00 4.9E-01 1.4E+00 Cs-137 1.4E-01 4.3E-01 1.4E*00 E9000 08267 STP-VS-216-03-21-90-15:17 Cs 134 -1.6E+00 5.7E-01 1.7E+00 5.8E-01 2.0E+00 09091 STP-US-229-09-05-90-14:15
- 08268 STP-US-226-03-21-90-11:Os ts-137 2.9E-01 Cs-134 -S.4E-01 5.3E-01 1.6E+00 3.5E-01 4.6E-01 1.6E+00 00119 STP-WS-216-09-18-90-14:40 1.?E400
- 08269 STP-WS 226-03-21-90-11:Os Cs-137
- 09120 STP-WS-226-09-18-90-11:00 Cs-134 -1.EE+00 6.4E-0! Cs-137 7.7E-02 3.4E-01 1.1E+00 7.9E-01 2.5E*00 08270 STP-WS-218-03-21-90-10:15 09121 STP-WS-227-09-19-90 14:0s ts-13** -9.5E-01 STP-WS-216-04-27-90-10:57 Cs-137 3.9E-01 6.3E-01 2.2E+00 4.9E-01 1.6E+00 08413 09122 S TP-US-227 19-90-14:Os Cs-134 -2.3E-01 $!P-WS-226-04-26-90-11:32 Cs-137 9.3E-02 5.1E-01 1.7E+00
-5.8E+00 1.0E+00 2.3E+00
- 08414 1.9E+00 09199 ST P-us- 237-09-28 13:29 Cs-134 ts-137 -9.4E-01 6.3E-01
-1.1E+00 8.3E-01 2.6E+00 08415 STP-WS-218-04-26-90-10:2s
- 09297 STP-WS-226-10-18-90-12:25 Cs-134 Es-137 - 2.M -01 4.8E-01 1.5E+00 6.6E-01 1.7E+00 OS416 STP-WS-218-04-26-90-10:2s 09333 STP-US-216-10-23-90-13:45 Cs-134 -3.0E+00 Cs-137 -3.9E-01 8.8E-01 2.8E+00
-3.7E+00 1.1E+00 3.0E+00 08527 STP-WS-216-05-16-90-15:15 09403 51P WS-211-10-29-90-15:41 Cs-134 Cs-137 0.0E+00 6.7E-01 2.2E+00
-2.7E+00 6.8E-01 1.8E+00
- 08528 STP-WS-226-05-16-90-10:3d 1.8E+00 09404 s1P-WS-212-10-29-90-15:29 Cs-134 STP-WS-226-05-16-90-10:3d Cs-137 5.4E-01 5.2E-01 Cs-134 -1.1E+00 6.0E-01 1.8E *00
- 08529 1.5E+00 09405 STP-US-213-10-29-90-15:52 08532 STP-US-209-05-16-90-16:10 Cs-137 -7.9E-01 5.0E-01 Cs-134 -1.3E+00 3.9E-Oi 1.1E+00 9.1E-01 2.9E+00 09406 STP-WS-229-10-29-90-16:28 1.8E+00 08533 STP-US-211-05-16-90-13:4s ts-137 -3.8E-01 09407 STP-WS-237-10-29-90-15:55 Cs-1% 1.9E-01 5.3E-01 Cs-137 -7.0E-01 7.OE-01 2.2E+00 5.6E-01 1.5E+00 0*5% STP-US-211-05-16-90-13:4s 09408 STP-US-237-10-29-90-15:5s Cs-134 -2.5E+00 Cs-137 -1.7E-01 4.8E-01 1.5E+00 9.3E-01 2.8E*00 08533 STP-WS-212-05-16-90-15:35 09410 STP-WS-219-10-29-90-16:09 Cs-134 -1.5E+00 Cs-137 -4.5E-01 1.1E*00 3.6E+00
-5.1E-01 7.1E-01 2.2E+00 08536 STP-WS-213-05-16-90-15:57 2.9E+00 09459 STP-US-216-11-13-90-14:50 Cs-134 STP-VS-229-05-16-90-16:05 Cs-137 1.4E+00 7.9E-01
-2.1E+00 1.0E+00 3.0E+00 08537 3.3E+00
- 09460 sTP-WS-226-11-13-90-11:1d Cs-134 STP-US-227-05-23-90-14:15 Cs-137 8.1E-01 9.3E-31
-1.2E+00 8.4E-01 2.6t+00 08570 2.3E+00
- 09461 sTP-WS-226-11-13-90-11:1d Cs-134 STP-WS-216-06-12-00-15:30 Cs-137 1.1E+00 6.3E-01 6.6E-01 2.0E+00 08634 09546 STP-US-219-11-26-90-14:45 Cs-1% -1.3E+00
- 08635 STP-WS-226-06-12-90-11:00 Cs-137 -2.3E+00 8.6E-01 2.4E+00 Cs-134 -3.8E+00 9.3E-01 2.3E+00 4.9E-01 1.5E+00 09572 STP-WS-229-12-10-90-14:52 08668 STP-WS-227-06-14-90-12:20 CS-137 - 8.8E - 01 Cs-134 -1.8E+00 8.1E-01 2.4E+00 5.6E-01 1.7E+00 09595 STP-Ws-209-12-13-90-12:32 1.8E +00
- 08828 STP-WS-226- 07-09-90-1 ? :3s ts-137 -1.2E+00 Cs-134 - 1. 7E + 00 6.4E-01 Cs-137 8.2E-02 3.7E-01 1.2E+00
- 09632 STP-US-226-12-18-90-10:45 2.1E+00
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M M M M M M M M M M M M M M M M M' M M ADDENDUM 1 BTPEGS REMP RESULTS DATA - 1990 BURFACE WATER BURFACE WATER LAB SAMPLE REstfLT 1 SIGMA LAB SAMPLE RESULT 1 SICMA NUP4RER SAMPLE SUBMISSION CODE ANALYSIS pCi/Kg ERROR tto NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/Kg EPROR ttD 08037 STP-US-216-01-31-90-15:0d Co-58 -2.2E+00 9.2E-01 2.5E+00 08998 STP-US-227 17-90-13:3d co-58 1.4E+00 4.9E-01 1.9E+EC 08038 ST P-WS-219-01-31 15 :13 Co-58 -3.9E-01 6.3E-01 2.0E+00 09086 STP-US-209-09-05-90-14:21 Co-58 -1.2E-01 5.7E-01 1.8E+00
- 08039 STP-US-221-01-31-90-12:3s Co-58 -1.0E+00 4.3E-01 1.3E+00 09087 STP-WS-211-09-05-90-13:48 Co-58 1.2E+00 8.0E-01 2.9E*00
- 08040 STP-WS-221-01-31-90-12:3s Co-58 6.3E-01 4.8E-01 1.7E +00 09088 STP-US-212-09-05-90-13:3d co-58 1.1E-01 4.0E-01 1.3E+00 08068 STP-WS-209-02-06-90-16:20 Co-58 7.2E-02 5.8E-01 1.9E+00 09089 STP-WS-212-09-05-90-13:3d Co-58 1.7E-01 7.9E-01 2.6E+00 08069 STP-WS-213-02-06-90-16:0s Co-58 -1.3E+00 7.7E-01 2.2E+00 09090 STP-WS-213-09-05-90-13:57 Co-58 -5.7E-01 4.9E-01 1.5E+00 08070 STP-WS-213-02-06-90-16:0s co-58 -5.4E-01 5.8E-01 1.8E+00 09091 STP-WS-229-09-05-90-14:15 Co-58 -1.1E-01 6.1E-01 2.OE+00 08071 STP-US-229-02-06 90-16:1d Co-58 -6.7E-01 7.4E-01 2.3E+00 09119 STP-WS-216-09-18-90-14:40 Co-58 -6.7E-01 7.1E-01 ?.2E+00 08072 STP-WS-229-02-06-90 16:1d Co-58 -8.6E-01 4.7E-01 1.4E+00
- 09120 STP-US-226-09-18-90-11:00 Co-58 -1.5E-01 7.8E-01 2.6E+00 08075 STP-WS- R T-02-12-90-13:Os Co-58 -5.5E-01 5.7E-01 1.8E+00 09121 $1 P-WS-227 19-90-14:Os Co-58 -7.8E-01 7.7E-01 2.4E+00 08076 S T P-Wh 227-02-12-90-13:Os Co-58 4.5E-01 3.9E-01 1.4E+00 09122 STP-US-227-09-19-90-14 :Os co-58 -5.9E-02 4.5E-01 1.5E+00 08164 STP .tS-216-02-28-90-14:5d Co-58 1.5E 01 4.0E-01 1.3E400 09199 STP-US-237-09-28-90-13:29 Co-58 -5.1E-01 9.2E-01 2.9E+00 08165 STP WS-216-02-28-90-14:5d Co-58 -8.4E-02 3.3E-01 1.1E+00
- 09297 $1P-US-226-10-18-90-12:25 Co-58 2.4E-01 8.6E-01 2.9E+00
- 08166 STP-uS-226-02-28-90-11:40 Co-58 -1.1E+00 5.4E-01 1.6E+00 09333 STP-WS-216-10-23-90-13:45 Co-58 5.1E-01 8.3E-01 2.8E+00 08267 STP-WS-216-03-21-90-15:17 Co-58 3.2E-01 4.3E-01 1.5E+00 09403 STP-WS-211-10-29-90-15:41 Co-58 5.3E-01 9.1E-01 3.1E+00
- 08268 STP-WS-226-03-21-90-11:Os Lo-58 -3.7E-01 7.0E-01 2.3E+00 09404 STP-WS-212-10-29-90-15:29 Co-58 -1.6E-01 6.2E-01 2.0E+00
- 08269 STP WS-226-03-21-90-11:Os Co-58 -5.4E-01 5.0E-01 1.5E+00 09405 STP-WS-213-10-29-90-15:52 Co-58 3.0E-01 5.9E-01 2.0E+00 08273 STP-WS-218-03-21-90-10:15 Co-58 -3.BE-01 3.6E-01 1.1E+00 09406 SIP-US-229-10-29-90-16:28 Co-58 -8.4E-01 4.1E-01 1.2E+00 08413 STP-us-216-04-27-90-10:57 Co-58 -9.5E-01 6.6E-01 2.0E+00 09407 STP-WS-237-10-29-90-15:$s Co-58 -7.1E-02 5.3E-01 1.7E+00
- 08414 STP-WS-226-04-26-90-11:32 Co-58 4.9E-02 4.4E-01 1.5E+00 09408 ST P-WS-237-10-29-90-15:5 s Co-58 -5.8E-02 6**I 2.0E+00 08415 STP-WS-218-04-26-90-10:2s Co-58 6.0E-02 6.3E-01 2.1E+00 09410 STP-WS-219-10 29-90-16:09 Co-58 -5.9E-01 1. -00 3.2E+00 08416 STP-WS-218-04-26-90-10:2s Co-58 -2.8E-01 4.7E-01 1.5E+00 09459 STP-WS-216-11-13-90-14:50 Co-58 -2.1E 01 -01 2.3E+00 08527 STP-uS-216-05-16-90-15:15 Co-58 -1.2E-01 9.6E-01 3.1E+00
- 09460 STP-US-226-11-13-90-11:1d co-58 -1.5E-01 ...E+00 3.5E+00
- 08528 STP-WS-226-05-16-90-10:3d Co-58 -3.7E-01 6.8E-01 2.2E+00
- 09461 STP-WS-226-11-13-90-11:1d Co-53 - 1.F0 1.1E+00 3.4E+0C
- 08529 STP-US-226-05-16-90-10:3d Co-58 2.1E-01 4.6E-01 1.6E+00 09544 STP-WS-219-11-26-90-14:45 Co-38 -8.4E-01 7.5E-01 2.3E+00 08532 STP-WS-209-05-16-90-16:10 Co-58 6.0E-01 4.9E-01 1.8E+00 09572 STP-WS-229-12-10-90-14:52 Co-58 1.3E-01 1.0E+00 3.4E+00 08533 STP-us-211-05-16-90-13:4s Co-58 3.2E-01 7.8E-01 2.7E+00 09595 STP-WS-209-12-13-90-12:32 Co-58 3.4E-01 7.9E-01 2.7E+00 08534 STP-us-211-05-16-90-13:4s Co-58 5.1E-01 5.7E-01 2.0E+00
- 09632 STP-WS-226-12-18-90-10:45 Co-58 7.7E-01 7.M-01 2.6E+00 08535 STP-WS-212-05-16-90-15:35 Co-58 -1.2E-01 4.7E-01 1.5E+00 09633 STP-VS-227-12-19-90-11:20 Co-58 5.5E-01 9.4E-01 3.2E+00 08536 ST P-WS-213-05-16 15 :57 Co-58 -1.0E+00 1.1E+00 3.4E+00 09683 STP-US-216-12-28-90-14:35 Co-58 0.0E+00 6.8E-01 2.2E+00 08537 STP-WS-229-05-16-90-16:05 Co-58 -1.2E+00 7.8E-01 2.2E+00 09684 STP-WS-240-12-28-90-13:40 Co-58 -4.4E-01 3.6E-01 1.1E+00 08570 S T P-WS-227-05-23-90-14 :15 Co-58 -9.0E-01 8.4E-01 2.5E+00 07955 ST P-WS-211 17-90-13 :49 Co-60 8.0E-01 5.9E-01 2.2E+00 08634 STP US-216-06-12-90-15:30 Cc-58 2.2E+00 7.5E-01 2.9E+00 07956 $1P-WS-212-01-17-90-13:38 Co-60 4.6E-01 5.4E 01 1.9E+00
- 08635 STP-US-226-06-12-90-11:00 Co-58 -4.8E-01 9.9E-01 3.2E + 00 08036 STP-WS-216-01-31-90-15:Od Co-60 0.0E+00 3.7E-01 1.2E+00 08668 ST P-WS- 227-06-14-90-12:20 Co-58 -1.3E+00 5.3E-01 1.6E+00 08037 STP-US-216-01-31-90-15:0d Co-60 -1.6E-01 7.6E-01 2.5E+00
- 08828 STP-WS-226-07-09-90-11:3s Co-58 -8.7E-01 6.8E-01 2.1E + 00 08038 STP-WS-219-01-31-90-15:13 Co-60 1.8E-01 6.6E-01 2.2E+00
- 08829 SIP-WS-226-07-09-90-11:3s Co-58 -5.1E-01 4.4E-01 1.4E+00
- 08039 SYP-WS-221-01-31-90-12:3s co-60 8.8E-01 4.7E-01 1.4E+00 08858 STP-US-216 13 11: 30 Co-58 2.4E+00 3.4E-01 9.5E-01
- 08040 STP-WS-221-01-31-90-12:3s Co-60 4.4E-01 3.9E-01 1.4E+00 08919 ST P-WS-233-07-31 13:30 co-58 -1.2E-01 5.2E-01 1.7E+00 08068 STP-WS-209-02-06-90-16:20 Co-60 -9.3E-02 5.8E-01 1.9E+00 08934 STP-WS-216-08-08-90-14:36 Co-58 -1.1E+00 9.7E-01 3.0E+00 08069 STP-US-213-02-06-90-16:Os Co-60 1.5E-01 8.4E-01 2.8E+00
- 08935 STP-US-226-08-08-90-11:00 Co-58 -9.3E-01 6.7E-01 2.1E+00 08070 Sir-uS-213-02-06-90-16:Os Co-60 -1.8E-01 5.3E-01 1.7E+00 08997 STP-WS- 227-08-17 13: 3d Co-58 -5.6E-01 6.2E-01 2.0E+no 08071 Sip-WS-229-02-06-90-16:1d co-60 -2.7E-01 R.2E-01 2.6E+00
- Denotes enntret locatiorn P mr t - 17 a
ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 SURFACE WATER SURFACE WATER RESULT 1 SICMA , 1 SIGMA LAB SAMPtC LAB SAMPLE 8tESULT NUMRER SAMPLE SUBMISSION CODE ANALYSIS pCi/Eg ERROR LLD -l pCi/Kg ERPOR tt D , NtFBER SAMPLE SUBMISSION CODE ANALYSIS Co-60 -6.3E-01 6.6E-01 2.0E+00 ,l 2.3E-01 4.0E-01 1.4E+00
- 09120 STP-US-226-09-18-90-11:00 08072 STP-WS-229-02-06-90-16:1d Co-60 Co-60 -2.9E-01 8.7E-Oi 2.8E+00 f 5.9E-01 1.9E+00 09121 ST P-WS-227 19-90-14 :Os 08075 STP-WS-227 02-12-90-13:Os Co-60 -2.6E-01 co-60 -3.3E-01 4.6E-01 1.4E+00
[
-2.6E-01 4.0E-01 1.3E*00 09122 S T P-US-227 19-90-14:Os 08076 STP-WS-227-02-12-90-13:Os Co-60 Co-60 1.5E+00 1.0E+00 3.9E+00 5.0E-02 4.1E-01 1.4E*00 09199 STP-US-237 09-28-90-13:29 08164 STP-WS-216-02-28-90-14:5d co-60 STP-US-226-10-18-90-12:25 Co-60 6.5E-01 9.4E-01 3.3E+00
-3.0E-01 2.9E-01 8.9E-01
- 09297 08165 STP-WS-216-02-28-93-14:5d Co-60 Co-60 -3.4E-01 7.7E-01 2.5E+00 1.4E-01 4.9E-01 1.6E+00 09333 STP-US-216-10-23-90-13:45
- 08166 S! P-WS-226-02-28-90-11:40 Co-60 Co-60 -1.9E+00 8.9E-01 2.2E+00 7.4E-01 4.6E-01 1.6E+00 09403 STP-WS-211-10-29-90-15:41 08267 STP-VS-216-03-21 90-15:17 Co-60 Co-60 8.8E-01 5.8E-01 2.2E+00 6.UE-01 1.9E+00 09404 STP-US-212-10-29-90-15:29
- 08268 STP WS-226-03-21-90-11:Os co 60 -2.3E-01 Co-60 -4.3E-01 6.3E-01 2.0E+00 4.2E-01 1.4E+00 09405 STP-WS-213-10-29-90-15:52
- 08269 STP-WS-226-03-21-90-11:0s Co-60 2.3E-01 Co-60 -2.0E-01 3.9E-01 1.2E+00 j 0.0E+00 3.4E-01 1.1E400 09406 STP-WS-229-10-29-90-16:28 08270 STP-WS-218-03-21-90-10:15 Co-60 Co-60 -2.7E-01 5.4E-01 1.7E+00
-8.0E-01 5.6E-01 1.6E+00 09407 STP-WS 237-10-29-90-15:5s 08413 STP-WS-216-04-27-90-10:57 Co-60 Co-60 3.8E-01 5.8E-01 2.0E+00
-2.8E-01 5.0F-01 1.6E+00 09408 STP-US-237-10-29-90-15:5s
- 08414 STP-WS-226-04-26-90-11:32 Co-(O Co-60 0.0E+00 1.1E+00 3.5E+00 1.8E-01 7.0E-01 2.3E+00 09410 STP-WS-219-10-29-90-16:09 08415 STP-US-218-04-26-90-10:2s Co-60 Co-60 0.0E+00 6.3E-01 2.1E+00 5.3E-01 2.0E+00 09459 STP-WS-216-11-13-90-14:50 08416 STP-WS-218-04-26-90-10:2s Co-60 1.2E+00 Co-60 1.2E +00 5.2E-01 9.0E-01 1.2E+00 8.8E-01 3.3E+00
- 09460 STP-WS-226-11-13-90-11:1d 08527 STP-WS-216-05-16-90-15:15 Co-60 Co-60 -1.5E-01 8.6E-01 2.8E+00 l 8.2E-01 4.8E-01 1.9E + 00
- 09461 STP-WS-226-11-13-90-11:1d 1.8E+00
- 08528 STP-US-226-05-16-90-10:3d Co-60 Co-60 -5.3E-01 5.9E-01 l
-9.9E-01 4.8E-01 1.3E+00 09546 STP-WS-219-11-26-90-14:45
- 08529 STP-US-226-05-16-90-10:3d Co-60 Co-60 -1.1E+00 1.1E+00 3.2E+00
-7.3E-01 4.8E-01 1.3E+00 09572 STP US-229-12-10-90-14:52 08532 STP-ut N 16-90-16:10 Co-60 Co-60 6.5E-01 8.9E-01 3.1E+00 9.2E-01 2.8E+00 09595 STP-WS-209-12-13-90-12:32 08533 STP-WS-211-05-16-90-13:4s Co-60 -9.2E-01 Co-60 1.1E+00 5.9E-01 2.3E+00 7.0E-01 5.5E-01 2.0E+00
- 09632 ST P-WS-226 18-90-10:45 08534 STP-WS-211-05-16-90-13:4s Co-60 Co-60 0.0E+00 8.9E-01 3.0E+00 2.5E-01 4.5E-01 1.5E*00 09633 STP-WS-227-12-19-90-11:20 08535 STP-WS-212-05-16-90-15:33 Co-60 Co-60 -3.9E-01 5.7E-01 1.8E+00 1.2E+00 1.1E+00 4.ct+00 09683 STP-WS-216-12-28-90-14:35 08536 STP-WS-213 05-16-90-15:57 Co-60 Co-60 -1.3E-01 3.8E-01 1.2E+00 0.0E+00 7.8E-01 2.6E+00 09684 STP-WS 240-12-28-90-13:40 08537 STP-WS-229-05-16-90-16:05 Co 60 2n-65 -4.9E+00 1.7E+00 4.8E+00 9.1E-01 2.7E+00 07955 ST P-WS -211 17-90-13:49 08570 STP-WS-227 05-23-90-14:15 Co-60 -8.1E-01 2n-65 -5.0E+00 1.4E+00 3.6E+00 co-60 -2.4E-01 6.9E-01 2.2E+00 07956 S TP-WS-212-01 90- 13 :38 2.3E+00 08634 ST P-VS-216-06-12-90-15:30 08036 STP-WS-216-01-31-90-15:0d 2n-65 -1.5E+00 7.9E-01 Co-60 -1.8E+00 9.4E-01 2.6E+00 1.7E+00 5.8E+00
- 08635 ST P-WS-225-06-12 11:00 08037 STP-WS-216-01-31-90-15:Od 2n-65 0.0E+00 Co-60 -6.7E-01 4.8E-01 1.5E+00 1.3E+00 4.0E+00 08668 STP WS-P T-06-14-90-12:20 08038 STP-WS-219-01-31-90-15:13 2r-65 -1.2E+00 Co-60 -2.2E-01 5.3E-01 1.7E+00 -2.5E+00 9.2E-01 2.7E+00
- 08828 ST P-WS-226-07-09-90-11:3s 1.1E+00
- 08039 STP-WS-221-01-31-90-12:3s 2n-65
- 08829 S T P-WS-226-07-09 11 :3s co-60 4.1E-0? 3.?E-01 2n-65 -3.1E-01 9.5E-01 3.0E+00 Co-60 2.0E-01 1.9E-01 6.M - 01
- 08040 STP-WS-221-01-31-90-12:3s 3.9E+00 08858 ST P-WS-216 13-90-11:30 2n-65 9.8E-01 1.1E+00 2.6E-01 4.5E-01 1.6E+00 08068 STP-VS-209-02-06-90-16:20 08919 STP-WS-233-07 11-90-13:30 Co-60 2n-65 -1.8E+00 1.6E+00 4.7E+00 7.8E-01 8.6E-01 3.1E+00 08069 STP-WS-213-02-06-90-16:Os 08914 STP-WS-210 L8-08-90-14:36 Co-60 2n-65 1.4E+00 1.1E+00 3.9E*00
-3.8E-01 5.8E-01 1.8E+00 08070 STP-WS-213-02-06-90-16:Os
- 08935 STP-WS-226-08-08-90-11:00 Co-60 2n-65 7.0E-01 1.6E+00 5.M + 00 0.0E+00 6.0E-01 2.OE+00 08071 STP-WS-229-02-06-90-16:1d 3.0E+00 08997 ST P-uS-227-08-17 13:3d Co-60 2n-65 -1.2E+00 9.9E-01 5.1E-01 1.6E+00 08072 STP-US-229-02-06-90-16:1d 08998 ST P-WS-227-08-17 13 :3d Co-60 - 1. 7E - 01 2n-65 -1.3E+00 1.2E+00 3.8E+00
-4.1E-01 5.7E-01 1.8E +00 08075 S T P- WS-227 12 13:Os 2.7E +00 09086 S T P-WS-209-09-05-90-14:21 Co-60 2n-65 8.VE-02 8.2E-01 Co-60 4.3E-01 8.0E-01 2.8E+00 08076 S T P-WS-227- 02-12 13:Os 2.9E+0" 09087 STP-US-211-09-05-90-13:48 STP-WS-216-02-28-90-14:5d 2n-65 -6.2E-01 9.0E-01 3.6E-01 1.2E
- 00 08164 09088 STP-WS-212-09-05-90-13:3d Co-60 1.0E-01 2n-65 6.5E-02 6.8E-01 2.2E+00 8.6E-01 2.9E*00 08165 STP-WS-216 @2-28-90-14:5d 09089 STP-WS-212-09-05-90-13:3d Co-60 0.0E *00 2n-65 3.6E-01 8.8E-01 3.0E+00 1
-7.2E-01 3.8E-01 1.0E+00
- 08166 STP-WS-226-02-28-90-11:40 2.9E+00 i
09090 STP-WS-213-09 05-90-13:57 Co-60 STP-WS-216-03 21-90-15:17 2n- 65 1.9E-01 8.6E-01
-1.5E+00 5.9E 01 1.6E+00 08267 09091 STP-WS-229-09-05-90-14:15 Co-60 2n-65 -4. 2E *00 1.3E+00 3.4E+00 5.4E-01 1.8E+00
- Da38 Sir'WS-226-03-21-90-11:Os 09119 STP-US-216-09-18-90-14:40 co-60 8.6E-02 i
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m W W m m m m m e m e m W m m e m mm ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 SHORELINE SEDIMENT SHORELINE BEDIMENT LAB SAMPLE RESULT 1 StGMA RESULT 1 SICMA LLD LAP SAMPLE NUMBER SAMPLE SUBMIS$10N CODE ANALYSIS pCf/Kg dry wt ERROR SAMPLE SUBMfSS10N CODE ANALYSIS pCi/Eg dry wt ERROR ttD NtARER STP-SS-213-06-26-90-12:1d Co-58 1.8E+00 3.8E+00 1.3E+01 Mn-54 9.6E+01 2.3E+00 8.9E+00 08754 09635 STP-SS-215-12-19-90-14:30 08755 STP-SS-229-O H 6-90-13:00 Co-58 5.0E+00 4.1E+00 1.4E+01 STP-SS-216-12-19-90-15:10 Mn-54 6.1E+00 2.9E+00 9.6E+00 2.0E+01 09636 09596 STP-SS-209-12-13-90-12:23 Co-58 9.2E-01 6.0E+00 Mn-54 -2.0E+00 3.6E+00 1.?E+01
- 09637 STP-SS-221-12-18-90-12:45 09597 S1P-SS-211-12-13-90-11:4s Co-58 -5.3E+00 5.6E+00 1.i3E+01 STP-SS-227-12-1940-11:25 Mn-54 1.4E+00 2.2E+00 7.3E+00 1.3E+01 09633 09598 STP-SS-211-12-13-90-11:4s Co-58 3.6E-01 3.9E+00 Mn-54 -8.4E+00 4.5E+00 1.4E+01 09639 STP-SS-230-12-19-90-11:44 09599 STP-SS-212-12-13-90-11:34 Co-58 -4.3E+00 4.3E+00 1.4E+01 STP-SS-233-12-19-90-11:34 Mn-54 .L1E+00 3.3E+00 1.1E+01 1.1E+01 09640 09600 STP-SS-213-12-13-90-12:01 Co-58 -4.6E+00 3.3E+00 STP-SS-221-06-14-90-15:47 Fe-59 -7.5E-01 5.0E+00 1.6E*01 2.4E+01 o 08664 00601 STP-SS-229-12-13-90-12:10 Co-58 -3.8E-01 7.2E+00 08665 STP-SS-227-06-14 90-12:35 Fe-59 -3.0E+01 1.0E+01 3.2E*0! 4.4E+00 8.0E+00 09635 STP-SS-215-12-19-90-14:30 Co-58 4.5E+02 08666 STP-SS-230-06-14-90-12:55 Fe-59 2.4E+00 7.2E+00 2.4E+01 1.4E+01 09536 STP-SS-216-12-19-90-15:10 Co-58 1.?E+02 5.6E+00 08667 STP-SS-233-06-14-90-12:45 Fe-59 -3.0E+01 1.3E+01 4.2r+01 4.1E+00 1.4E+01
- 09637 STP-SS-221-12 *8-90-12:45 Co-58 4.8E+00 STP-SS 215-06-19-90-14:10 Fe-59 1.9E-01 7.1E+00 2.3E+01 8.4E+00 08713 09638 STP- SS-227 1 J-90-11:25 Co-58 -2.7E-01 2.5E+00 STP-SS-215-06-19-90-14:25 Fe-59 1.2E*01 5.2E+00 1.8E+01 1.9E+01 08714 09639 STP-SS-230-12-19-90-11:44 Co-58 5.7E+00 5.5E+00 Fe-59 4.4E+00 4.2E+00 1.4E+01 1.3E+01 03715 STP-SS-216-06-19-90-13:35 09640 STP-SS-233 12-19-90-11:34 Co-58 3.2E+00 3.8E+00 STP-SS-209-06-26-90-13:10 Fe-59 7.6E+00 6.7E+00 2.3E+01 6.6E+00 08750
- 08664 $TP-SS-221-06-14-90-15:47 Co-60 -5.7E-01 2.0E+00 08751 STP-SS-211-06-26-90-11:54 Fe-59 - 2. 7E + 01 4.7E+00 T.5E*01 4.2E+00 1.4E*01 8.5E+00 08665 STP-SS-227-06-14-90-12:35 Co-60 -3.7E+00 08752 STP-SS-212-06-26 90-11:18 Fe-59 1.5E+00 2.6E+00 -3.3E*00 2.8E+00 9.0E+00 08666 STP-SS-230-06-14-90-12:55 Co-60 08753 STP-SS-213-06-26-90-12:1d Fe-59 1.1E+01 8.1E+00 2. 7E + 01
-3.1E+00 5.1E+00 1.7E+01 08667 STP-SS-233-06-14-90-12:45 Co-60 STP-SS-213-06-26-90-12:1d F+-59 5.1E+00 8.6E+00 2.9E+01 1.2E+01 08754 08713 STP-SS-215-06-19-90-14:10 Co-60 8.1E+01 5.0E+00 STP-SS-229-06-26-90-13:00 Fe-59 1.0E+01 8.9E+00 3.0E+01 3.0E+00 7.4E+00 08755 08714 STP-SS-215-06-19-90-14:25 Co-60 8.?E+01 STP-SS-209-12-13-90-12:23 Fe-59 2.2E+01 1.5E+01 5.3E+01 1.9E+00 6.1E+00 095 % 08715 STP-SS-216-06-19-90-13:35 Co-60 8.2E +00 Fe-59 1.6E+00 1.4E+01 4.6E+01 1.0E+01 09597 Sfo-SS-211-12-13-90-11:4s 08750 STP-SS-209 06-26-90-13:10 co-60 3.2E+00 2.9E+00 STP-SS-211-12-13-90-11:4s Fe-59 -4.7E-01 9.1E+00 3.0E+01 2.1E+00 6.7E+00 09598 08751 STP SS-211-06-26-90-11:54 00-60 -8.3E+00 Fe-59 -6.0E+00 1.1E+01 3.5E+01 3.7E+00 09599 STP-SS-212-12-13-90-11:34 08752 STP-SS-212-06-26-90-11:18 Co-60 1.6E+00 1.1E+00 STP-SS-213-12-13-90-12:01 Fe-59 7.8E+00 8.4E+00 2.8E+01 3.7E+00 1.2c+01 09600 08753 STP-SS-213-06-26-90-12:1d Co-60 -7.9E-01 STP-SS-229-12-13-90-12:10 fe-59 1.OE+01 1.8E+01 6.1E+01 3.$E+00 1.2E+01 09601 08754 STP-SS-213 06-26-90-12:1d Co-60 -1.3E+00 i Fe-59 1.3E+01 4.0E+00 1.3E+01 1.2E+01 I 09635 STP-SS-215-12-19-90-14:30 08755 STP-SS-229-06-26-90-13:00 Co-60 -1.5E+00 3.8E+00 Fe-59 3.6E+00 6.2E+00 2.1E+01 5.1E+00 1.7E+01 09636 STP-SS-216-12-19-90-15:10 09596 STP-SS-209-12-13-90-12:23 Co-60 3.8E+00 Fe-50 -1.4E+01 1.1E+01 3.4E+01 1.5E+01
- 09637 STP-SS-221-12-18-90-12:45 09597 STP-SS-211-12-13-90-11:4s Co-60 -2.2E+00 4. 7E +00 STP-SS-227-12-19-90-11:25 Fe-59 -9.0E+00 6.4E+00 2.1E+01 3.3E+00 1.1E+01 09638 09598 STP-SS-211-12-13-90-11:4s Co-60 1.3E+00 Fe-59 1.7E+01 1.4E*01 4.8E+01 1.2E+01 09639 STP-SS-230-12-19-90-11:44 09509 STP-SS-212-12-13-90-11:34 Co-60 -1.5E+00 3.8E+00 STP-SS-233-12-17-90-11:34 Fe-59 1.8E+01 9.4E+00 3.2E+01 2.7E+00 9.2E+00 09640 09600 STP-SS-213-12-13-90-12:01 Co-60 5.1E+00 STP-SS-221-06-14-90-15:47 Co-58 -1.5E+00 2.2E+00 7.2E+00 1.8E+01
- 08664 09601 STP-SS-229-12-13-90-12:10 Co-60 -7.5E+00 5.8E+00 Co-58 -1.4E+01 4.3E+00 1.4E+01 4.2E+00 6.1E+00 08665 STP-SS-227-06-14-90-12:35 09635 STP-SS-215-12-19-90-14:30 Co-60 4.1E*02 Co-58 - 3. 7E +00 3.0E+00 9.9E+00 1.0E+01 08666 STP-SS-230-06-14-90-12:55 09636 STP-SS-216-12-19-90-15:10 Co-60 5.1E+01 3.8E+00 Co-58 - 8.4E +00 5.6E+00 1.8E+01 1.2E+01 08667 STP-SS-233-06-14-90-12:45
- 09637 STP-SS-221-12-18-90-12:45 Co-60 3.4E+00 3.7E+00 co-58 5.1E+02 7.8E+00 1.4E*01 2.1E+00 7.0E+00 08713 STP-SS-215-Oe 19-90-14:10 09638 STP SS-227-12-19-90-11:25 Co-60 1.3E+00 Co-58 6.4E+02 6.?E+00 1.1E+01 4.5E+00 1.4E+01 08714 StP-SS-215-06-19-90-14:25 09639 STP-SS-230 12-19 90-11:44 Co-60 -5.7E+00 Co-58 1.4E+02 3.9E+00 8.3E+00 1.0E+01 08715 STP-SS-216-06-19-90-13:35 09660 STP-SS-233-12-19-90-11:34 Co-60 2.0E+00 3.0E +00 Co-58 2.8E+00 3.2E+00 1.1E+01 4.9E+00 1.6E+01 08750 STP-SS-209-06-26-90-13:10
- 08M4 STP-SS-221 06-14-90-15:47 Irr65 -2.7E+00 STP-SS-211-06-26-90-11:54 Co-58 -9.2E+00 2.2E+00 7.2E+00 1.2E+01 3.0E+01 08751 08665 STP- SS-227 14-90-12:35 2n-65 -2.4E+02 STP-SS-212-06-26-90-11:18 Co 58 2.8E+00 1.1E+00 3.8E+00 -1.8E+02 9.1E+00 2.2E+01 08752 1.3E+01 OP.666 STP-SS-230-06-14-90-12:55 In-65 08753 STP-SS-213-06-26-90-12:1d co-58 7.?E+00 3.8E+00
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ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 RESIDENT DABBLER DUCK MIGRATORY DABBLER DUCK LAB SAMPLE PESULT 1 SIGMA LAB SAMPLE RTSUtf 1 StGaa NUMBER SAM 9tE SUBMISSION CEDE AMAtYSIS pCi/Kg ERROR tto N&r8ER SAMPLE SURutSS104 CODE ANALYS*$ pCi/Kg wat vt EPPOR LLO 08932 STP-81-Z42-06-18-90-12:00 1-131 - 2. 7E +02 2.6E+02 8.4E+02 08108 STP-83-I52-01-27-90-12:00 1-131 -6.7E+00 4.5E+01 1.5E+02 08932 STP-81-Z42-06-18-90-12:00 Cs-1% -5.8E+00 3.4E400 1.1E*01 08110 STP-83-209-01-23-90-12:00 t-131 6.5E+01 5.1E+01 1.7E*02 08932 STF-81-242-06-18-90-12:00 Cs-137 3.1E+00 3.4E+00 1.1E+01 09765 STP-83-Z42-11-25-90-12:00 1-131 -1.5E +02 2.4E+C2 7.7E+02 08932 S!P-81-242-06-18-90-12:00 K-40 4.2E403 1.2E+02 1.2E+02 09766 STP-83-242-11-25-90-12:15 t-131 6.7E+01 2.2E +02 7.2E+02 08932 STP-81-Z42-06-18-90-12:00 Mn-54 -1.6E+00 3.6E+00 1.?E+01 08108 S TP-85-Z52-01 93-12:00 Cs-134 -7.8E*00 3.4E +00 1.1E+01 08932 STP-81-Z42-06-18-90-12:00 Fe-59 -2.2E+01 1.5E+01 4.6E*01 08110 STP-85-209-01-23-90-12:00 Cs- 1 % -7.0E+00 2.6E +00 7.9E+00 08932 STP-81-Z42-06-18-90-12:00 Co-58 3.3E+00 5.1E+00 1.7E+01 09765 STP-83-Z42-11-25-90-12:00 Cs-1% - 7.2E +00 3.0E+00 9.1E+00 08932 STP-81-Z42-06-18-90-12:00 Co-60 5.2E+00 3.5E*00 1.2E+01 09766 STP-83-242-11-25-90-12:15 Cs-1% -6.8E+00 2.5E+00 7.4E*00 08932 STP Z42-06-18-90-12:00 Im 65 - 1.4E +01 9.4E+00 3.0E+C1 08108 STP-83-Z52 01-27-90-12:00 Cs-137 2.6E-01 3.8E +00 1.3E+01 08932 STP-81-Z42-06-18-90-12:00 Zr-95 4.1E+00 9.3E+00 3.1E+01 08110 STP-83-209-01-23-90-12:00 Cs-137 9.0E-01 7.7E+00 9.1E+00 08932 STP-81-Z42-06-18-90-12:00 Nt>-95 -6.5E-01 5.4E*00 1.8E+01 09765 STP-85-242-11-25-90-12:00 Cr 137 1.5E *S 3.L.600 1.1E+01 08932 STP-81-242-06-18-90-12:00 Ba-140 2.2E+02 1.3E+02 4.6E*02 09766 STP-83-242-11-25-90-12:15 Cs-137 4.fr. + 00 2.5E 00 8.9E+00 03932 STP-81-Z42-06-18 90-12:00 in-140 6.fE +0 7 5.0E*01 1.Pr*02 08108 STP-83-Z52-01 90- 12:00 K-40 4.3E+03 1.4E*02 1.3E +02 08110 STP-83-209-01-23-90-12:00 E-40 3.7E+03 1.1E+02 1.1E+02 09765 Sfo-83-Z42-11-25-90-12:00 E-40 3.0E+03 1.2E+02 1.2E+02 09766 STP-23-242-11-25-90-12:15 E-40 2.4E+03 9.7E+01 9.0E+01 08108 S TP- 83 -Z52-01 90- 12:00 Mn-54 2.1E+00 3.9E+00 1.3E+01 08110 STP-83-209-01-23-90-12:00 mms 4 -2.6E+00 2.7E *00 8.5E*00 09765 STP-83-Z42-11-25-90-12:00 Mn-54 -8.9E-01 3.5E+00 1.2E+01 09766 STP-83-Z42-11-25-90-12:15 Mn-54 6.0E+00 2.9E+00 1.0E+01 "8105 ST P-85-Z52-01 90- 12:00 Fe-59 3.0E+00 1.1E+01 3.6E+01 08110 STP-83-209-01-23-90-12:00 Fe-59 - 8.8E +00 9.8E +00 3.tE*01 09765 STP-83-242-11-25-90-12:00 Fe-59 2. 7E +00 1.3E+01 4.5E+01 09766 STP-83-Z42-11-25-90-12:15 Fe-59 3.5E+00 1.3E +01 4.4E+01 08108 STP Z52- 01-27-90-12:00 Co-58 -1.1E+00 4.8E+00 1.6E+01 08110 STP-83-209-01-23-90-12:00 Co-58 -3.6E+00 3.5E+00 1.1E+01 09765 STP-83-Z42-11-25-90-12:00 Co-58 -9.0E+00 5.4E+00 1.7E +01 09766 STP-83-Z42-11-25 90-12:15 Co-58 3.6E+00 4.3E+00 1.5E+01 08108 STP-83-Z52-01-27-90-12:00 Co-60 1. 7E +00 3.8E*00 1.3E+01 08110 STP-83-209-01-23-90-12:00 Co-60 8.6E-01 2.6E+00 8.8E +00 09765 STP-83-Z42-11-25-90-12:00 Co-60 0.0E+00 3.1E+00 1.0E+01 09766 STP-83-Z42-11-25-90-12:15 Co-60 3.2E +00 2.9E+00 1.0E+01 08108 STP-83-Z52 01-27-90-12:00 Zm65 -6.1E+00 8.5E+00 2.7E+01 08110 S TP-8 3-209-01 90-12:00 Zn-65 - 3. 7E + 00 6.4E
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ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 PIGEON PISCIVOROUS FISH LAB SAMPLE RESULT 1 SICMA LAB SAMPLE RESULT 1 5108A N'JMBE R SAMPLE SUBMISSION CODE ANALYSTS g<i/Kg wet wt EPPOR LLD WUMBER SAMPtE SURMf SSION CTE ANALYSIS pCi/Kg wet wt ERPOR ttD 08928 STP-88-241-06-16-90-12:00 Mb-95 -4.4E+00 4.5E+00 1.4E+01 08716 STP-F1-Z52-06-19-90-15:3s I-131 -2.1E+00 5.4E+00 1.8E+01 09533 STP-88-Z51-10-03-90-12:00 Mb-95' -1.DE+01 6.9E+00 2.2E+01 08717 STP-F1-Z52-06-19-90-15:3s I-131 8.9E+00 6.4E+00 2.?E+01 08711 SY P-88-236-05-07-90-12:00 Ba-140 9.6E+01 9.3E+01 3.1E+02 08718 STP-F1-252-06-19-90-15:30 I-131 -3.9E-0^ 4.8E*00 1.6E+01 08712 STP-88-Z41-06-04-90-12:00 Ba-140 3.3E+01 2.3E+01 7.8E+01 09427 StP-F1-212-11-07-90-11:30 1-131 -6.1E+00 1.M + 01 5.2E+01 08928 STP-88-Z41-06-16-90-12:00 Ba-140 -8.4E+01 1.1E+02 3.5E+02 08716 STP-F1-Z52 06-19-90-15:3s Cs-134 -4.6E+00 2. 7E+00 8.3E+00 09533 STP-88-251-10-03-90-12:00 Es-140 5.6E+02 4.6E+02 1.6E + 03 08717 STP-F1-Z52-06-19-90-15:3s Cs-134 -4.4E+00 2.1E*00 6.6E+00 08711 STP-88-236-05-07-90-12:00 to-140 6.6E+01 4.4E+01 1.6E+02 08718 STP-F1-252-06-19-90-15:30 Cs-134 -1.9E+00 1.7E+00 5.3E+00 08712 SVP-88-241-06-04-90-12:00 to-140 3.9E+00 8.5E+00 2.9E+01 09427 S TP-F 1-212- 11 90-11 :30 Cs-134 -8.1E+00 4.9E+00 1.5E+01 08928 STP-BS-Z41-06-16-90-12:00 to-140 4.7E*01 5.1E+01 1.8F+02 08716 STP-F1-Z52-06-19-90-15:3s ts-137 T.4E+00 2.3E+00 7.0E+00 09533 STP- 88-Z51 03-90-12:00 to-140 -9.5E +01 1.9t+G2 4.1E+02 08717 $1P-F1-252-06-19-90-15:3s ts-137 1.0E+01 2.7E+00 7.8E+00 08718 STP-F1-Z52-06-19-90-15:30 Cs-137 9.4E+00 2.0E+00 5.8E+00 09427 51P- F1 -212-11 90-11 :30 Cs-137 -1.1E+01 5.4E+00 1.6E+01 08716 STP-F1-Z52 06-19-90-15:3s K-40 3.7t+03 1.3E+02 9.6E+01 08717 STP-F1-Z52-06-19-90-15:3s K-40 3.9E+03 1.0E+02 9.7E+01 08718 STP-F1-Z52-06-19-90-15:30 K-40 3.7E+03 8.1E+01 6.4E+01 09427 STP- F1 -212-11 90- 11:30 K-40 3.5E+03 1.9E+02 2.0E+02 08716 STP-F1-Z52-06-19-90-15:3s Mn-54 5.3E+00 2.8E+00 9.9E+00 0871T STP-F1-Z52-06-19-90-15:3s Mn-54 -2.2E+00 2.2E+00 6.9E+00 03718 STP-F1-Z52-06-19-90-15:30 Pn-54 2.3E+00 1.6E+00 5.6E+00 09427 STP-F1-212-11-07-90-11:30 Mn-54 -1.6E+01 6.0E+00 1.7E+01 08716 STP F1-Z52-06-19-90-15:3s Fe-59 -T.1E-01 6.4E+00 2.1E+01 08717 STP F1-Z52-06-19-90-15:3s Fe-59 -5.4E+00 5.8E+00 1.8E+01 08718 STP-F1-Z52-06-19-90-15:30 Fe-59 7.6E *00 4.4E+00 1.5E+01 09427 S TP- F1-212 07-90-11 :30 Fe-59 -1.6E+01 1.5E+01 4.5E+01 08716 STP-F1-Z52-06-19-90-15:3s Co-58 -2. m 00 2.7E+00 8.6E+00 08717 STP-F1-Z52-06-19-90-15:3s Co-58 -1.8E+00 2.5E*00 8.0E+00 08718 STP-F1-Z52-06-19-90-15:30 Eo-58 2.9E+00 1.8E+00 6.2E+00 09427 STP- F 1 -212- 11-07-90-11:30 Co-58 -1.9E*00 5.2E+00 1.7E+01 08716 STP-F1-252-06-19-90-15:3s Co-60 -3.7E+00 2.?E+00 8.8E+00 08717 STP-F1-Z52-06-19-90-15:3s Co-60 -4.5E-01 2.3E+00 7.6E+00 08718 STP-F1-252-06-19-90-15:30 Co-60 -1.4E+00 1.8E+00 5.7E+00 09427 51P F1-212-11-07-90-11:30 Co-60 8.0E+00 5.8E+00 2.1E+01 03716 STP-F1-752-06-19-90-15:3s In-65 4.?E*00 6.1E+00 2.1E+01 08717 StP-F1-Z52 06-19-90-15:3s 2n-65 -5.5E+00 5.6E+00 1.8E+01 08718 51P-F1-Z52-06-19-90-15:30 In-65 3.OE+00 4.1E+00 1.4E+01 09427 ST P - F 1 -212- 11 -0 7 11:30 In-65 -3.2E+01 1.5E +01 4.4E+01 08716 STP-F1-Z52-06-19-90-15:3s Ir-95 2.5E+00 5.3E +00 1.8E+01 08717 STP-F1-Z52-06-19-90-15:3s Zr-95 -2.9E+00 4.0E+00 1.3E +01 08718 STP-F1-252-06-19-90-15:30 Zr-95 8.1E-01 3.2E+00 1.1E+01 09427 51P-f t-212-11 90-11:30 Ir-95 -1.1E+01 1.1E+01 3.3E+01 09716 Str-F1 752.lW 19-90-15:3s wb-95 2.8E+00 3.0E+00 1.0E+01 OR717 STP-F1-Z52-06-19-90-15:3s wb-95 1.3E+00 2.4E+00 8.1E +00 Dmotes rnntrol locatiorn Pao
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ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 ARTfiROPODIVOROUS FISH PISCIVOROUS FISH RESuti 1 SIGMA RESULT 1 StGMA LAB SAMPtE LAB SAMPLE SAMPtE SUmstS104 CECE anatYSIS g<i/Fg wat wt Ett0R LLD tto WW9F R NUMBFR SAMPLE SUBMIS$104 CODE ANALYSIS gfi/tg wt wt Ett0R 1-131 -1.0E+01 8.8E+00 2.8E+01 Mb-95 -2.1E+00 1.8E+00 5.7E+00 0T787 STsF2-215-01 15-90-12:00 8.0E+00 08718 STP-F1-Z52-06-19-90-15:30 STP-F2-216 29 90-12:00 1-131 4.9E+00 2.3E+00 .
-2.4E+00 5.9E+00 1.9t+01 03'56 1.1E+02 l 09427 S TP- F 1 -212-11-07-90-11 :30 utr95 tM 26 STP-F2-216-10-<6-90-12:00 1-131 -1.1t+02 3.9E+01 9.M + 00 1.0E+01 3.4E+01 4.0E+01 08716 STP-F1-Z52-06-19-90-15:3s Ba-140 09428 STP-F2-214-11-07-90-13:3s t-131 -5.6E+00 1.2E+01
-9.9E+00 1.1E+01 3.5t+01 08717 STP-F1-Z52-06-19-90-15:3s 8s-140 09429 S T P- F2 -214- 11 90-13:35 t-131 -1.0E+01 7.M + 00 2.4E+01 STP-F1-Z52-06-19-90-15:30 an-140 6.8E+00 7.9E+00 2. 7E + 01 0.0E+00 2. 7E +00 9.1E+00 08718 8.1E*01 07?87 STP-FZ-215-01-15-90-12:00 Cs-134 STP-F1-212-11-07-90-11:30 Ba-140 -5.3E+01 2.7F+01 -1.3E*00 1.4E+00 4.5E+00 09427 1.4E+01 08756 STP-F2-216-06 29-90-12:00 CS-134 08716 STP-F1-252-06-19-90-15:3s ts-140 5.7E+00 3.M+00 Cs-134 -3.M*00 3.1E+00 9. M *00 3.9E+00 1.3E+01 09426 STP-F2-216-10-26-90-12:00 08717 STP-F1-Z52-06-19 90-15:3s ts-140 -5.7E-01 STP- F2-214 07-90-13:3s ts-134 - 1.M +01 4.3E +00 1.2E +01 to-140 3.2E+00 3.2E*00 1.1E *01 09428 8.1E+00 08718 STP-F1-Z52-06-19-90-15:30 STP-F 2-214- 11 90-13:3s Cs-134 -1.2E+01 2.8E+00
-2.4E+00 1.0E+01 3.3r +01 09429 09427 S T P- F 1-212- 11 90- 11 :30 to-140 STP-F2-215-01-15-90-12:00 Cs-137 1.3E +01 2.M +00 T.M+00 07987 5.6E+00 STP-F2-216-06-29-90-12:00 CS-137 2.3E *0C 1.6E+00 08756 1.1E+01 51P-F2-216-10-26-90-12:00 Cs-137 -3.2E 01 3.3E+00 09426 1.3E "f1 ts-137 -1.0E+00 4.1E+00 09428 STP-F2-214-11-07 90-13:3s Cs-137 2.4E+00 2.8E +00 9.4 *O 09429 STP- F 2-214-11-07-90-13:3s K-40 3.M+03 1.?t+02 1.4E 02 07987 STP-F2-215-01-15-90-12:00 E-40 3.3E+03 7.5E+01 6.0E % 1 08756 STP-F2-Z16-06-29-90-12:00 E-40 2.4E+03 1.2E+02 t .4E +( 2 09426 STP-F2-Z16-10-26-90-12:00 K-40 3.8E+03 1.5E+02 1.3E+02 09428 ST P- F 2-214- 11-07-90-13:3s K-40 3.4E +03 9. 8E +01 9.0E+01 09429 S T P-r2-214- 11-07-90-13 :3s 1.1E+01 STP-F2 215-01-15-90-12:00 Mn-54 8.0E+00 2.9E+00 07987 4.8E+00 STP-F2-216-06-29-90-12:00 Mn-54 -1.5E+00 1.5E+00 0S756 Mn-54 - 4. 3E +00 3.7E+00 1.1E+C1 09426 STP-F2-Z16-10-26-90-12:00 pn-54 1.8E+00 4.3E +00 1.5E+01 09423 ST P- F2-214 07-90-13:3s 9.2E+00 pn-54 -5.1E+00 2. -E *00 09429 S TP- F2-214 07-90-13:3s 2.3E+01 Fe-59 - 6.0E +00 7.2E+00 07987 STP-F2-215-01-15-90-12:00 STP-F2-216-06-29-90-12:00 Fe-59 3.M +00 3.ic+00 1.3E+01 08756 3.6E+01 Fe-59 -1.3E+01 1.2E+01 09426 STP-F2-216-10 26-90-12:00 Fe-59 -1.4E*01 9.6E+00 2.9E+01 09428 ST P- F 2-214-11 904 3:3s Fe-59 -8.8E+00 7.0E +00 2.2E+01 09429 STP-F2-214-11-07 90-13:3s Co-58 8.0E+00 3.2E +00 f.?E+01 77987 STP-F2-215-01-15-90-12:00 5.0E+00 0.0E+00 1.5E+00 08756 STP-F2-Z16-06-29-90-12:00 Co-58
-6.3E+00 4.2E+00 1.3E+01 09426 STP-F2-216-19-26-90-12:00 Co-58 1.3E+01
-8.8E+00 4.4E+00 n9426 STP-F2-214-11 07-90-13:3s Co 58 Co-58 -8.7E+00 3.0E *00 8.8E+00 09429 Sir- F2-214 - 1147-90-13 :3s 1.0E+01 Co-60 -2.5E+00 3.3E +00 07987 STP-F2-215-01-15-90-12:00 5.2E+00
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ADDENDUM 1 STPEGB REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAG SAMPLE RESULT 1 SIGMA LAB SAMPLE PESULT 1 SIGMA NLHRER SAMPLE SUBMISSION CCDE ANALYSIS g i/M'3 ERROR LLD MUMBER SAMPLE SURMISSION CODE mWALYSIS pCI/M'3 EDROR LLD 08593 STP-AP ***-05-30-90-15:Oc 1-131 2.2E-04 9.5E-05 3.4E-04 09370 STP-AP ***-10-24-90-15:Sc I-131 -1.6E-05 1.0E-04 3.3E-04 08632 STP-AP ***-06-06-90-14:Sc I-131 -3.PE-04 2.8E-04 8.9E-04 09402 STP-AP ***-10-29-90-15:2c t-131 0.0E+00 2.3E-04 7.5E-04 08661 STP- AP "*-06-12-90-16:1c t-131 2.0E-05 2.4E-04 7.8E-04 09454 STP-AP ***-11-06-90-15:1c t-131 - 7.1E-M 1.6E-04 5.2E-04 08704 STP-AP-015-06-20-90-13:59 I-131 -6.1E-04 7.0E-04 2.2E-03 09485 STP-AP ***-11-13-90-15:Oc t-131 1.2E-04 1.5E-04 5.1E-04 08710 STP-AP ***-06-20-90-14:3c I-131 1.4E-04 1.9E-04 6.4E-04 09509 STP- AP *" 1'i-90-16:2c t-131 -7.9E-04 3.SE-04 1.2E-03 08740 STP- AP *"-06-25-90-14:3c I-131 -3.5E-04 3.2E-04 1.0E-03 09531 STP-AP ***-11-26-90-14:2c I-131 -4.4E-04 1.5E-04 4.5E-04 08778 STP- AP "*-07-02-90-14:3c I-131 -B.0E-05 1.6E-04 5.3E-04 09568 STP- AP "*-12-03-90-17:Ic I-131 -8.7E-05 1.3E-04 4.3E 04 08804 $1P- AP *-07-09-90-15:4c I-131 8.4E-05 2.1E-04 7.0E-04 09594 Sib aP ***-12-10-90-10:1c t-131 5.2E-05 3.4E-04 1.1E-03 08805 STP-AP-035-06-25-90-10:1c t-131 1.3E-03 2.5E-03 8.5E-03 09627 STP-AP ***-12-18-90-15:4c I-131 -3.0E-04 2.0E-04 6.3E-04 03806 STP-AP-018-06-25-90-10:Sc t-131 -1.OE-03 3.0E-03 9. 7E -01 09682 STP-AP ***-12-28-90-14:Oc t-131 1.1E-04 2.1E-04 7.0E-04 08307 STP-AP-033-06-25-90-11:1c t-131 -1.4E-03 2.9E-03 9.4E-03 09701 STP-AP-035-12-28-90-10:Oc I-131 5.9E-04 1.1E-03 3.6E-03 08808 STP-AP 039-06-25-90-12:Oc t-131 -1.4E-03 2.6E-03 8.5E-03 09702 STP-AP-018-12-28-90-10:3c t-131 -6.0E-04 2.0E-03 6.6E-03
- 08809 STP- AP-037-06-25-90-14:3c I-131 -5.lE-03 4.1E-03 1.3E-02 09703 STP-AP-033-12-21-90-29:5c 1-131 1.0E-03 2.3E-03 7.7E-03 08810 STP-AP-015-06-25-90-12:2c 1-131 -2.5E-04 3.7E-03 1.2E-02 09704 STP-AP-039-12-28-90-12:3c I-131 1.4E-03 1.7E-03 5.8E-03 08811 STP-AP-016-06-25-90-12:2c 1-131 7.2E-04 3.5E-03 1.2E-02
- 09705 STP-AP-037-12-28-90-13:Oc t-131 -1.9E-04 1.3E-03 4.2E-03 08812 STP-AP-001-06-25-90-12:3c 1-131 3.3E-03 3.1E-03 1.0E-02 09706 STP-AP-015-12-28-90-13:1c t-131 1.8t-04 2.4E-03 8.1E-03 08813 STP-AP-006-06-25-90-13:dc t-131 2.6E-03 2.8E-03 9.5E 03 09707 STP-AP-016-12-28-90-13:2c t-131 6.1E-03 2. E-03 8.1E-03 08814 STP-AP-006-06-25-90-13:dc t-131 -3.1E-03 2.7E-03 8.5E-03 09708 STP-AP-001-12-28 90-13:2c t-131 -4.8E-03 2.6E-03 8.0E-03 08352 STP- AP *-07-18-90-15:Sc I-131 -1.2E-05 1.9E-04 6.4E-04 09709 STP-AP-006-12-28-90-14:cd 1-131 -2.2E-03 2.9E-03 9.3E-03 08896 STP-AP
- 23-90-13:3c I-131 1.7E-04 2.1E-04 7.2E-04 0?710 STP-AP-006-12-28-90-14:cd I-131 3.1E-03 4.0E-03 1.4E-02 08908 STP- AP ***-07-31 90-15:2c t-131 -2.8E-04 1.6E-04 5.2E-04 07922 STP- AP *"-01 90-13:3c Cs-134 -4.1E-04 1.2E-04 3.36 04 08968 STP- AP *"-08 90-14:Oc t-131 -6.8E-05 6.6E-05 2.1E-04 07?44 STP-AP ***-01-09-90-14:2c Cs-134 -4.0E-04 1.5E-04 4.2E-04 08996 STP-AP
- 14-90-16:0c I-131 2.5E-04 1.8E-04 6.1E-04 07978 STP- AP ***-01-17-90-15:Oc Cs-134 -2.9E-04 1.1E-04 3.3E-04 09021 STP-AP
- 22-90-13:1c I-131 -1.6E-04 1SE-04 6.2E-04 08n09 STD AP ***-01-24-90-16:Oc Cs-134 -2.5E-04 1.1E-04 3.3E-04 09033 STP-AP ***-08-28-90-15:5c I-131 -2.3E 04 2.6E-04 8.3E-04 08C35 STP-AP
- 31-90-14:2c Cs-134 -4.5E-04 1.2E-04 3.2E-04 09075 STP-AP ***-09-05-90-14:Oc t-131 1.3E-04 1.3E-04 4.3E 04 08065 STP-AP
- 06-90-16:4c Cs-134 -2.1E-04 1.4E-04 4.3E-04 09106 STP-AP
- 12-90-10:4c I-131 1.0E-04 1.4E-04 4.6E-04 08098 STP-AP ***-02-15-90-14:5c Cs-134 -2.7E-05 8.9E-05 2.9E-04 09146 STP-AP ***-09-18-90-10:4c I-131 -1.8E-04 2.7E-04 8.6E-04 08136 S19-AP ***-02-21-90-15:3c Cs-134 -7.4E-04 1.8E-04 4.3E04 09187 STP-AP ***-09-25-90 16:2c 1-131 2.0E-04 2.6E-04 8.8F-04 08163 STP-AP ***-02-28-90-14:3c Cs-134 -2.2E-04 1.1E-04 3.2E-04 09226 STP-AP ***-10-02-90-14:1c I-131 -7.2E-05 3.5E-04 1.1E-03 08191 STP-AP ***-03-07-90-14:3c Cs-134 -2.9E-04 1.2E-04 3.4E-04 09229 STP-AP-035-09-25-90-10:2c I-131 -2.7E-03 1.5E-03 4.6E 03 08244 STP-AP ***-03-15-90 13:1c Cs-134 -6.9E-04 1.2E-04 3.0E-04 09230 STP-AP-018-09-25-90-11:1c I-131 7.0E-05 1.3E-03 4.5E-03 08266 STP-AP ***-03-21-90-16:3c Cs-134 -2.5E-04 1.2E-04 3.6E-04 09231 STP-AP-033-09-25-90-12:1c t-131 4.4E-04 1.3E-03 4.4E-03 08298 STP-AP ***-03-28-90-13:2c Cs-134 -5.0E-34 1.1E-04 2.6E-04 09232 STP-AP-039-09-25-90-12:3c l-131 -4.1E-03 2.1E-03 6.5E 03 08324 STP-AP ***-04-03-90-14:4c Cs-134 -4.9E-04 1.3E-04 3.5E-04
- 09233 STP- AP-037-09-25 13:Oc I-131 -2.2E-03 2.1E-03 6.5E 03 08329 STP-AP-035-03-28-90-10:Oc Cs-134 -1.4E-04 9.9E-05 2.7E-04 09234 STP-AP-015-09-25-90-16:2c t-131 2.8E-04 1.8E-03 5.9E-03 08330 STP-AP-018-03-28-90-10:3c Cs 134 -8.5E-05 8.1E-05 2.6E-04 09235 STP-AP-016-09-25-90-16:2c I-131 -1.8E-03 1.5E-03 4.8E-03 08331 STP-AP-033-03-28-90-13:2c Cs-134 -2.3E 04 9.1E-05 2.7E-04 09236 STP-AP-001-09-25-90-16:2c t-131 -5.9E-04 1.2E-03 4.0E 03 08332 STP-AP-039-03-28-90-13:Oc Cs-134 -4.4E-04 9.0E-05 2.3E-04 09237 STP-AP-006-09-25-90-15:cd 1-131 1.4E-04 1.4E-03 4.8E-03
- 08333 STP-AP-037-03-28-90-12:4c Cs-134 -2.2E-04 9.3E-05 2.7E-04 09238 STP-AP-006-09-25-90-15:cd 1-131 -3.8E-03 2.00 03 6.1E-03 08334 STP-t>-015-03-28-90-12:1c Cs-134 -1.9E-04 8.bE-05 2.6E-04 09277 STP-AP ***-10-11-90-15:2c' l-131 -6.1E-06 1.3E-04 4,1E-04 08335 STP-AP-016-03-28-90-12:1c Cs-134 -3.2E-04 9.7E-05 2.7E-04 09329 STP-AP ***-10-18-90-16:4c t-131 -4.9E-04 1.5E-03 5.0E-03 08316 STP-AP-001-05-28-90-12:Oc Cs-134 -8.6E-05 8.3E-05 2.6E-04 l
- Denotes control locations Page t-58 I M M M M M M M M M M m M M
W W E E W W M M M M W. W W M M M W m ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 AIRDORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE REstET 1 SIGMA LAB SAMPLE RESULT 1 SIGMA NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M 3 ERROR ttD NtPRT R SA**PLE SUB4tSS10h CODE ANAtv515 r<i/M'3 ERPOR ttD 08337 STP-AP-006-03 28-90-11:dc Cs-134 -3.9E-04 9.1E-05 2.4E-04 09232 STP-AP-039-09-25-90-12:3c Cs-1% -4.0E-04 9.9E-05 2.6E-04 08338 STP-AP-006-03-28-90-11:dc Cs-134 -3.6E-04 9.5E-05 2.5E-04
- 09233 STP- AP-037-09-25-90-13:Oc Cs- 1% -2.4E-04 9.0E-05 2.6E-04 08369 STP- AP *"-04-10-90-14:4c Cs-134 5.7E-05 1.0E-04 3.5E-04 09234 STP-AP-015-09-25 90-16:2c Cs-1% +2.6E-04 8.3E-05 2.3E-04 08393 STP-AP ***-04-19-90-16:Oc Cs-134 -9.0E-05 8.2E-05 2.6E-04 09235 STP-AP-016-09-25-90-16:2c Cs-134 -2.3E-04 6.1E-05 1.7E-04 08446 STP-AP
- 26-90-14:2c Cs-1% -2.4E-04 1.1E-04 3.1E-04 OV236 STP-AP-001-09-25-90-16:2e Cs-134 -7.3E-05 5.3E-05 1.7E-04 08472 STP-AP ***-05-02-90-15:2e ts-134 -3.4E-04 1. 7E - 04 5.0E-04 09237 STP-AP-006-09-25-90 45:cd Cs-134 -2.4E-04 6.0E-05 1.7E-04 08498 STP-AP ***-05-08-90-13:2c Cs-134 -2.0E-04 1.3E-04 4.0E-04 09238 STP-A*-006-09-25-90-15:cd Cs-134 -2.8E-04 9.0E-05 2.5E-04 08526 STP-AP ***-05-16-90-14:5c Cs-134 -1.4E-04 9.4E-05 2.9F-04 09277 STP-AP
- 11-90-15:2c Cs-134 -2.3E-04 5.9E-05 1.7E-04 08569 STP-AP ***-05-24-90-14:4c Cs-134 -2.8E-04 1.2E-04 3.6E-04 09329 STP-AP
- 18-90-16:4c Cs-134 -3.5E-04 1.1E-04 3.1E-04 08593 STP-AP ~ 30-90-15:Oc Cs-134 -1.6E-04 6.8E-05 2.0E-04 09370 STP-AP " 24-90-15 Sc Cs-1% -2.1E-04 5.6E-05 1.6E-04 08632 STP-AP ***-06-06-90-14:5c Cs-134 -1.5E-04 1.2E-04 3.7E 04 09402 STP- AP '"-10 29-90-16:2c Cs-1% -5.0E-04 1.0E-04 2.8E-04 08661 STP-AP
- 12-90-16::c Cs-134 -3.6E-E4 1.2E-04 3.3E-04 09454 STP-AP ***-11-06-90-15:1c Cs-134 -3.8E-04 6.5E-05 1.7E-04 08704 STP-AP-015-06-20-90-13:59 Cs-134 -2.7E-03 5.7E-04 1.5E-03 09485 STP-AP 13-90-15:Oc Cs-1% -2.0E-04 7.1E-05 2.1E-04 08710 STP-AP
- 20-90-14:3c Cs-134 -1.3E-04 9.1E-05 2.8E-04 09509 STP-AP ***-11-19-90-14:2c Cs-134 -7.5E-04 1.6E-04 4.2E-04 08740 STP-AP ***-06-25-90-14:3c Cs-134 1.4E-04 1.8E-04 6.4E-04 09531 STP- AP "*- 11 90-14:2c Cs-134 -6.0E-04 8.3E-05 2.2E-04 08778 STP- AP ~-07-02-90-14:3c Cs-134 -4.0E-05 6.9E-05 2.2E-04 09568 STP-AP ***-12-03-90-17:1c Cs-134 -1.2E-04 6.2E-05 1.9E-04 08804 STP- AP "-07-09-90-15:4c Cs-134 -1.7E-04 7.6E-05 2.4E-04 09594 STP-AP ***-12-10-90-10:1c Cs-134 -3.1E-04 1.2E-04 3.3E-04 08805 STP-AP-035-06-25-90-10:1c Cs-134 -2.6E-04 8.6E-05 2.4E-04 09627 STP-AP ~ 18 90-15:4c Cs-134 -3.6E-04 1.1E-04 3.1E-04 08806 STP-AP-018-06-25-90-10:Sc Cs-1% -2.3E 8.9E-05 2.6E-04 09682 STP-AP
- 28-90-14:Oc Cs-134 -3.2E-04 8.7E-05 2.2E-04 08807 STP-AP-033-06-25-90-11:1c Cs-134 -2.3E-04 9.7E-05 2.9E-04 09701 STP-AP-035-12 28-90-10:Oc Cs-134 -2.0E-04 5.9E-05 1.8E-04 08808 STP-AP-039-06-25 90-12:Oc Cs-134 -1.7E-04 9.1E-05 2.8E-04 09702 STP-AP-018-12-28-90-10:3c Cs-134 -2.2E-04 8.7E-05 2.5E-04
- 08809 STP- AP-037-06-25 14:3c Cs-134 -1.6E-04 9.4E-05 2.9E-04 09703 STP-AP-033-12 21-90-09:Sc Cs-134 -2.5E-04 7.2E-05 2.1E-04 08810 STP-AP-015-06-25-90 12:2c Cs-134 7.0E-06 8.0E-05 2.6E-04 09704 STP-AP-039-12-28-90-12:3c Cs-134 -1.5E-04 8.0E-05 2.3E-04 08S11 STP-AP-016-06-25-90-12:2c C5-134 -5.5E-05 7.7E-05 2.5E-04
- 09705 STP-AP-037-12-28-90-13:Oc Cs-134 -1.5E-04 5.5E-05 1.6E-04 08812 STP-AP-001-06-25-90-12:3c Cs-134 -1.4E-04 5.7E-05 1.8E-04 09706 $1P-AP-015-12-28-90-13:1c Cs-134 -2.1E-04 S.0E-04 3.0E-34 08813 STP-AP-006-06-25-90-13:dc Cs-134 -1.9E-04 6.0E-05 1.8E-04 09707 STP-AP-016-12-28 ?O-13:2c Cs-134 -2.3E-04 8.8E-05 2.5E-04 08814 STP-AP-006-06-25-90-13:dc Cs-134 -1.8E-04 5.7E-05 1. 7E -04 09708 STP-AP-001-12-23-90-13:2c Cs-134 -1.3E-04 9,1E-05 2.8E-04 08852 STP-AP ***-07-18-90-15:5c Cs-134 -2.1E-04 8.7E-05 2.6E-04 09709 STP-AP-006-12-28-90-14:cd Cs-1% -2.1E-04 1.0E-04 3.0E-04 08896 STP-AP ***-07-23-90-13:3c Cs-134 -1.3E-04 1.0E-04 3.2E-04 09710 STP-AP-006-12-28-90-14:cd Cs-134 -1.8E-04 9.1E-05 2.6E-04 08908 STP- AP ***-07-31-90-15:2c Cs-134 -2.9E-04 6.9E-05 2.0E-04 07922 STP-AP ***-01 04-90-13:3c Cs-137 5.5E-05 1.3E-04 4.3E-04 08968 STP-AP ***-08-08-90-14:Oc Cs-134 -4.4E-05 3.0E-05 9.5E-05 07944 STP-AP ***-01-09-90-14:2c Cs-137 0.0E+00 1.6E-04 5.4E-04 08996 STP-AP ***-08-14-90-16:Oc Cs-134 -1.9E-04 7.8E-05 2.4E-04 07978 ST P- AP *** 17 15:Oc Cs-137 9.3E-05 1.1E-04 3.9E-04 09021 STP-AP
- 22-90-13:1c Cs-134 -3.5E-04 9.5E-05 2.6E-04 08009 STP-AP ***-01-24-90-16:00 Cs-137 -1.5E-04 1.3E-04 4.0E-04 09033 STP-AP ***-08-28-90-15:5c Cs-1 % -1.1E-04 1.1E-04 3.3E W. 08035 STP- AP "* 31 14:2c Cs-137 -1.5E-04 1.3E-04 4.0E-04 09975 STP-AP ***-09-05-90-14:Oc Cs-134 - 7.5E - 05 5.5E-05 1.7E-04 08065 STP-AP ***-02-06-90-16:4c Cs-137 -3.8E-04 1.5E-04 4.1E-04 09106 STP-AP ***-09-12-90-10:4e Es-134 -2.0E-04 6.5E-05 1.9E-04 08098 STP-s? ***-02-15 90-14:5c Cs-137 -1.1E 05 1.OE-04 3.3E-04 09146 STP-AP
- 1S-90-10:4c Cs-134 -5.0E-04 1.3r-04 3.6E-04 08156 STP-AP ***-02-21-90-15:3c Cs-137 -8.5E-05 2.0E-04 6.3E-04 09187 STP-AP ***-09-25-90-16:2c Cs" % -6.5E-04 1.41-04 3.6E-04 08163 STP-AP ***-02-28-90-14:3c Cs-137 2.GE-04 1.1E-04 3.9E-04 09226 STP-AP ***-10 02-90-14:1c Cs-134 -4.2E-04 1.3E-04 3.3E-04 03191 STP- AP *** 07-90-14 :3c Cs-137 -4.0E-05 1.2E-04 3.7E-04 09229 STP-AP-035-09-25-90-10:2c Cs-134 -2.2E-04 6.6E-05 1.9E-04 03244 STP-AP
- 15-90-13:1c Cs-137 -1.3E-04 1.1E-04 3.2E-04 09230 STP-AP-018-09-25-90-11:1c Cs-134 -1.3E-04 5.9E-05 1.8E-04 08266 STP-AP ***-03-21-90-16:3c Cs-137 9.5E-05 1.2E-04 4.3E-04 09231 STP-AP-033-09-25-90-12:1c Ce1% -2.0E-04 6.7E-05 1.PJ-04 0*??S STP- AP ***-OM8-00-13:2c Cs-137 9.8E-05 1.Or-14 3.6E-04
- Omtes cmtrot f orntims P m-n.-So
ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 AIRBORNE.. PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESULT 1 SICMA LAB SAMPLE RESULT 1 SIGMA NtMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M*3 ERROR LLD NtM9ER SAMPLE SUBMISSION CODE ANALYSIS pCl/M'3 Fer0R Lt0 08324 STP-AP ***-04-03-90-14:4c Cs-137 4.6E-05 1.3E-04 4.5E-04 09033 STP-AP ***-08-28-90-15:Sc Cs-137 - 7.1 E - 05 1.2E-04 3.8E-04 08329 STP-AP-035-03-28-90-10:Oc Cs-137 -6.2E-05 9.7E-05 3.1E-04 09075 STP-AP ***-09-05-90-14:0c Cs-137 -1.2E-04 5.9E-05 1.8E-04 08330 STP AP-018-03-28-90-10:3c Cs-137 9.3E-05 8.3E-05 2.9E-04 09106 STP-AP
- 12-90-10:4c Cs-137 1.6E-05 6.7E-05 2.2E-04 08331 STP-AP-033-03-28-90-13:2c Cs-137 -8.4E-05 7.8E-05 2.4E-04 09146 STP-AP ***-09-18-90-10:4c Cs-137 -6.8E-05 1.2E-04 3.8E-04 08332 Sip-AP-039-03-28-90-13:Oc Cs-137 -1.3E-04 8.0E-05 2.4E-04 09187 STP-AP
- 25-90-16:2c CS-137 0.0E+00 1.1E-04 3.7E-04
- 08333 STP-AP-037-03-28-90-12:4c Cs-137 -4.2E-05 9.5E-05 3.1E-04 09226 STP-AP
- 02-90-14:1c Cs-137 -3.6E-04 1.4E-04 3.9E 04 08334 STP-AP-015-03-28-90-12:1c Cs-137 -1.9E-05 8.4E 05 2.8E-04 09229 STP-AP-035-09-25-90-10:2c Cs-137 -1.6E-04 6.8E-05 2.0E-04 08335 STP-AP-016-03-28-90-12:1c Cs-137 -4.9E-05 8.4E-05 2.7E-04 09230 STP-AP-018-09-25-90-11:1c Cs-137 8.2E-05 6.4E-05 2.2E-06 08336 STP-AP-001-03-23-90-12:Oc Cs-137 8.3E-05 9.9E-05 3.4E-04 09231 STP-AP-033-09-25-90-12:1c Cs-137 9.7E-06 6.3E-05 2.1E-04 08337 STP-AP-006 03-28-90-11:dc Cs-137 1.1E-04 8.2E-05 2.9E-04 09232 STP-AP-039-09-25-90-12:3c Cs-137 1.0E-05 9.1E-05 3.0E-04 08338 STP-AP-006-03-28-90-11:dc Cs-137 -1.6E-04 8.7E-05 2.6E-04
- 09233 STP- AP-037-09 25-90-13:Oc Cs-137 2.8E-05 8.5E-05 2.9E-04 08369 STP-AP ***-04-10-90-14:4c Cs-137 1.1E-04 9.9E-05 3.5E-04 09234. STP-AP-015-09-25-90-16:2c Cs-137 -3.7E-05 7.9E-05 2.5E-04 08393 STP-AP
- 19-90-16:Oc Cs-137 5.6E-05 8.7E-05 3.0E-04 09235 STP-AP-016-09-25-90-16:2c Cs-137 -6.6E-05 6.5E-05 2.1E-04 08446 STP-AP * -04 26-90-14:2c Cs-137 1.2E-05 1.3E-04 4.2E-04 09236 STP-AP-001-09-2*-90-16:2c Cs-137 4.2E-05 5.2E-05 1.8E-04 08472 STP-AP ***-05-02-90-15:2c Cs-137 -4.7E-05 1.6E-04 5.1E-04 09237 STP-AP-006-09-25-90-15:ed Cs-137 0.0E+00 5.7E-05 1.9E-04 08498 STP-AP
- 08-90-13:2c Cs-137 -1.4E-04 1.5E-04 4.6E-04 09238 STP-AP-006-09-25-90-15:cd Cs-137 0.0E400 8.0E-05 2.6E-04 08526 STP-AP
- 16-90-14:5c Cs-137 7.8E-05 1.0E-04 3.5E-04 09277 STP-AP ***-10-11-90-15:2c Cs-137 9.3E-06 5.9E-05 2.0E-04 08569 STP-AP
- 24-90-14:4c Cs-137 1.8E-04 1.3E-04 4.5E-04 09329 STP-AP
- 18-90-16:4c Cs-137 -3.7E-05 1.1E-tw 4.5E-04 08593 STP-AP ***-05-30-90-15:Oc Cs-137 1.0E-04 7.0E-05 2.5E-04 09370 STP- AP "*-10-24-90-15:5c Cs-137 4.7t-06 5.3E-05 1.TE-04 08632 STP-AP 06-90-14:5c Cs-137 -5.3E-05 1.3E-04 4.1E-04 09402 STP- AP "*-10-29-90-16:2c Cs-137 1.5E-04 1.0E-04 3.7E-04 08661 STP-AP ***-06-12-90-16:1c Cs-137 1.4E-04 1.2E-04 4.4E-04 09454 STP- AP *"-11-06-90-15:1c Cs-137 -3.4E-05 6.3E-05 2.0E-04 08704 STP-AP-015-06-20-90-13:59 Cs-137 1.1E-03 5.6E-04 2.0E-03 09485 STP-AP
- 13-90-15:Oc Cs-137 8.5E-05 7.2E-05 2.5E-06 08710 STP-AP ***-06-20-90-14:3c Cs-137 2.1E-05 9.0E-05 3.0E-04 09509 STP-AP ***-11-19-90-14:2c Cs-137 1.8E-04 1.5E-04 5.1E-04 08740 STP- AP *"-06-25-90-14:3c Cs-137 -7.8E-05 2.2E-04 7.0E-04 09531 STP-AP- **-11-26-90-14:2c Cs-137 1.7E-04 7.8E-05 2.4E-04 08778 STP- AP ***-07-02-90-14:3c Cs-137 -8.2E-05 7.2E-05 2.3E-04 09568 STP- AP * **-12 03-90-17:1c Cs-137 -5.6E-05 6.2E-05 1.9E-04 08804 STP- AP *-07-09-90-15:4c Cs-137 -8.6E-05 8.6E-05 2.7E -04 09594 STP-AP ***-12-10-90-10:1c Cs-137 4.9E-05 1.3E-04 4.4E-04 08805 STP-AP-035-06-25-90-10:1c Cs-137 0.0E+00 9.1E-05 3.0E-04 09627 STP- AP "*-12-18-90-15:4c Cs-137 1.5E-04 1.0E-04 3.6E-04 08806 STP-AP-018-06-25-90-10:Sc Cs-137 -5.0E-05 8.9E-05 2.8E-04 09682 STP-AP
- 28-90-14:Oc Cs-137 3,5E-05 9.9E-05 3.3E-04 08807 STP-AP-033-06-25-90-11:1c Cs-137 5.8E-05 8.4E-05 2.9E-04 09701 STP-AP-035-12-28-90-10:Oc Cs-137 4.1E-06 5.9E-05 1.9E-04 08808 STP-AP-039-06-25-90-12:Oc Cs-137 2.7E-05 7.8E-05 2.6E-04 0?702 STP-AP-018-12-28-90-10:3c Cs-137 -2.0E-05 8.9E-05 2.9E-04
- 08809 STP-AP-037-06-25-90-14:3c Cs-137 1.8E-05 8. 7E -05 2.9E-04 09703 STP-AP-033-12 21-90-09:5c Cs-137 1.7E-05 6.6E-05 2.2E-04 08810 STP-AP-015-06-25-90-12:Ze Cs-137 4.1E-05 8.2E-05 2.8E-04 09704 STP-AP-039-12 28 90-12:3c Cs-137 6.9E-05 9.3E-05 3.2E-04 08811 STP-AP-016-06-25-90-12:2c Cs-137 1.5E-04 7.3E 05 2.7E -04
- 09705 STP AP-037-12-28-90-13:Oc Cs-137 4.1E-05 5.6E-05 1.9E-04 08812 STP-AP-001-06-25-90-12:3c Cs-137 -1.6E-05 5.5E-05 1.8E-04 09706 STP-AP-015-12-28-90-13:1c Cs-137 -7.5E-05 8.0E-05 2.5E-04 08813 STP-AP-006-06-25-90-13:dc Cs-137 2.6E-05 5.8E-05 2.0E-04 09707 STP-AP-016-12 28 90-13:2c Cs-137 5.2E-05 9.6E-05 3.3E-04 08814 STP-AP-006-06-25-90-13:dc Cs-137 1.4E-04 5.4E-05 2.0E-04 09708 STP-AP-001-12-28 90-13:2c Cs-137 1.2E-05 8.7E-05 2.9E-04 08852 STP-AP
- 13-90-15:Sc Cs-137 7.3E-05 8.9E-05 3.1E-04 09709 STP-AP-006-12-28-90-14:cd Cs-137 1.3E-04 9.3E-05 3.3E-04 08896 S1P-AP- 23-90-13:3c Cs-137 5.7E-05 9.9E-05 3.30-04 09710 STP-AP 006-12-28-90-14:cd Es-137 1.8E 04 9.6E-05 3.6E-04 08908 STP- AP ***-07-31-00-15:2c Cs-137 -1.2E-04 7.5E-05 2.3E-04 07922 STP- AP *"-01-04-90-13:3c K-40 9.4E-03 1.8E-03 4.0E-03 08968 STP-AP
- 08-90-14:Oc Cs-137 7.3E-M 3.3E-05 1.1E-04 07944 STP-AP ***-01-09-90-14:2c K-40 1.1E-02 2.2E-03 4.4E-03 08996 S1P- AP *"-08-14-90-16:Oc Cs-137 0.0E+00 8.7E-05 2.9E-04 07978 ST P- AP *" 17-90-15:3c K-40 6.9E-03 1.4E-03 2.2E-03 09021 STP-AP ***-08-22-90-13:1c Cs-137 -9.6E-06 8.6E-05 2.8r-04 08009 STP-AP "*-01-24-90-16:Oc K-40 9.9E-03 1.80-03 2.8E-03
- Denotes rmtrol tocations P m t-60
- -- M M m m M M -p W m m m m m wp e m m
7 y - - . ADDENDUM i STPEGS REMP RESULTS DATA - 1990 AIRDORNE PARTICULATE AIRDORNE PARTICULATE 1 SICMA REstn.T LAB SAMPLE LLD PESULY 1 S10MA SAMPLE SUBMISSION CODE ANALYSIS pCi/M'3 ERROR LAB SAMPLE tLD WUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M*3 ERROR NUMBER 2.1E-03 K-40 8.7E-03 1.0E-03 3.1E-03 08812 STP-AP-001-06-25-90-12:3c K-40 8.0E-03 1.7E-03 K-40 9.4E-03 1.0" 03 1.9E-03 08035 STP-AP
- 31-90-14:2c 2.0E-03 4.6E-03 08813 ST-)- AP-006 25 13:dc 1.0E-03 2.0E-03 08065 STP-AP ***-02-06-90-16:4c K-40 7.7E-03 STP-AP-006-06-25-90-13:dc K-40 8.6E-03 1.3E-03 2.7E-03 08814 1.0E-03 2.1E-03 d 08098 STP-AP
- 15-90-14:5c K-40 5.2E-03 08852 STP-AP
- 18-90-15:Sc K-40 4.3E-03 K-40 1.2E-02 2.9E-03 5.3E-03 K-40 1.1E-02 1.7E-03 3.8E-03 L 08136 STP-AP
- 21-90-15:3c 2.9E-03 08896 STP- AP *** 23-90-13:3c 2.4E-03 K-40 1.2E-02 1.8E-03 K-40 7.4E-03 1.1E-03 08163 STP-AP
- 28 90-14:3c 1.5E-03 2.8F-03 08908 STP- AP *-07-31-90-15:2c 5.1E-04 1.1E-03 08191 STP- AP ***-03 90- 14:3c K-40 6.7E-03 STP-AP " 08-90-14:Oc K-40 3.5E-03 1.6E-03 5.3E-03 08968 1.6~-03 3.0E-03 STP-AP ***-03-15-90-13:1c K-40 0.0E+00 STP-AP
- 08-14-90-16:Oc K-40 1.2E-02 08244 1.9E-03 3.2E-01 08?96 1.1E-03 4.7E-03 STP-AP
- 21-90-16:3c K-40 1.2E-02 STP AP " 22-90-13:1c K-40 1.9E-03 08266 1.5E-03 3.5E-03 09021 1.k-03 4.0E-03 08298 STP-AP
- 28-90-13:2c K-40 6.6E-03 STP-AP ***-08-28-90-15:Sc K-40 8.4E-03 1.9E-03 4.4E-03 09033 9.2E-04 2.0E-03 STP-AP
- 03-90-14:4c K-40 7.7E-03 STP-AP ***-09-05-90-14:Oc K 40 6.9E-03 08324 1.3E-03 2.2E-03 09075 1.3E 03 2.6E-03 STP-AP-035-03-28-90-10:Oc K-40 6.5E-03 STP-AP
- 12-90-10:4c K-40 1.0E-02 08329 1.?E-03 2.8E-03 09106 2.1E-03 4.2E-03 STP-AP-018-03-28-90-10:3c K-40 5.3E-03 STP-AP
- 18 90-10:4c K-40 1.2E-02 08330 1.4E-03 2.6E-03 09146 2.1E-03 3.7E-03 08331 STP-AP-033-03-28-90-13:2c K-40 8.7E-03 09187 STP-APa** 09-25-90-16:2c K 40 1.1E-02 K-40 7.2E-03 1.4E-03 3.0E-03 K-40 6.1E-03 1.7E-03 3.5E-03 08332 STP-AP-039-03-28-90-13:Oc 1.4E-03 3.?E-03 09226 STP-AP ***-10-02-90-14:1c 1.1E-03 2.0E-03
- 08333 STP- AP-037-03-28-90-12:4c K-40 6.2E-03 STP-AP-035-09 25-90-10:2c K-40 7.9E-03 1.3E-03 1.4E-03 09229 1.0E-03 2.?E-03 STP-AP-015-03-28-90-12:1c K-40 9.1E-03 STP-AP-018 09-25-90-11:1c K 40 6.9E-03 08334 1.3E-03 2.9E-03 09230 9.4E-04 1.9E-03 STP-AP-016-03-28-90-12:1c K-40 6.8E-03 STP-AP-033-09-25 90-12:1c K-40 7.3E-03 08335 1.4E-03 5.6E-03 09231 1.3E-03 2.2E-03 STP-AP-001-0!-28-90-12:0c K-40 5.1E-03 STP AP-039-09-25-90-12:3c K-40 6.9E-03 08336 1.4E-03 2.9E-05 09232 1.1E-03 2.6E-03 STP-AP-006-03-28-90-11:dc K-40 7.1E-03 STP-AP-037-09-25 90-13:Oc K-40 3.9E-03 08337 1.3E-03 2.8E-03
- 09233 1.2E-03 2.9E-03 08338 STP-AP-006-03-28-90-11:dc K-40 5.5E-03 09234 STP-AP-015-0?-25-90-16:2c K-40 4.7E-03 K-40 1.2E-02 2.1E-03 3.9E-03 K-40 7.5F-03 1.0E-03 2.0E-03 08369 STP-AP ***-04-10-90-14:4c 1.3E-03 2.5E-03 09235 S1P-AP-016-09-25-90-16:2c 8.6E-04 1.8E-03 STP-AP
- 19-90-16:Oc K-10 7.5E-03 STP-AP-001-09-25-90-16:2c K-40 6.4E-03 08393 1.5E-03 4. 7E -03 09236 9.0E-04 1.8E-03 08446 STP-AP ***-04-26-90-14:2c K-40 -1.6E-03 09237 STP AP-006-09-25-90-15:cd K-40 T.2E-03 K-40 6.4E-03 1.9E-03 3.2E-03 K-40 1.3E-02 1.7E-03 2.3E-03 08472 STP-AP ***-05-02-90-15:2c 4.9E-03 09238 STP-AP-006-09-25 90-15:cd 1.1E-03 2.2E-03 K-40 1.5E-02 2.6E-03 K-40 7.6E-03 08498 STP-AP
- 08 90-13:2c 1.6E-03 3.1E-03 09277 STP-AP ***-10-11-90-15:2c 1.6E-03 3.3E-03 STP-AP ***-05-16-90-14:Sc K 40 9.5E-03 K-40 6.8E-03 08526 3.CE-03 6.3E-03 09329 STP AP ***-10-18-90-16:4c 6.2E-03 8.6E-04 1.6E-03 STP-AP ***-05-24 90 14:4c K-40 1.4E-02 09370 STP-AP
- 24-90-15:Sc r-40 08569 1.7E-03 3. 7E - 03 1.5E-03 3.3E-03 STP-AP
- 30-90-15:Oc K-40 8.2E-03 STP-AP
- 29-90-16:2c K-40 9.2E-03 08593 1.7E-03 6.2E-03 09402 1.3E-03 3.0E-03 STP-AP " 06-90-14:5c K-40 2.4E-03 STP-AP
- 06-90-15:1c K-40 8.0E-03 08632 2.0E-03 4.5E-03 09454 1.3E-03 2.8E-03 STP-AP
- 12-90-16:1c K-40 8.9E-03 STP-AP
- 13-90-15:Oc K-40 9. 7E-03 08661 2.?E-02 3.?E-02 09485 2.0E-03 3.9E-03 K-40 3. 7E -01 STP-AP ***-11-19-90-14:2c K-40 1.2E-02 08704 STP-AP-015-06-20-90-13:59 1.5E-03 2.8E-03 09509 1.1E-03 2.3E-03 STP-AP
- 20-90-14:3c K-40 8.8E-03 STP-AP ***-11-26-90-14:2c K-40 8.2E-03 08710 2.7E 03 5.?E-03 09531 1.1E-03 2.4E-03 STP-AP
- 25-90-14:3c K-40 1.1E-02 STP-AP ***-12-03-90-17:1c K-40 6.1E-03 08740 1.2E-03 2. 7E - 03 09568 1.9E-03 4.0E-03 STP-AP ***-07-02-90-14:3c K-40 7.5E-03 Sip-AP ***-12-10 90-10:1c K-40 7.3E-03 08778 1.3E-03 3.1E-03 09594 1.6E-03 3.3E-03 K-40 7.9E-03 STP-AP
- 18-90-15:4c K-40 8.2E-03 08804 STP AP ***-07-09-90-15:4c 8.3E-03 1.5E-03 3.0E-03 09627 5.8E-03 1.5E-03 3.3E-03 08805 STP-AP-035-06-25-90-10:1c K-40 09682 STP-AP
- 28-90 14:Oc K-40 K-40 5.8E-03 1.3E-03 2.5E 03 K-40 7.9E-03 9.4E-04 1.9E-03 08806 STP-AP-018-06-25-90-10:Sc 2. PI. -03 09701 STP-AP-035-1?-28-90-10:Oc 1.3E-03 3.E-03 K-40 9.1E-03 1.5E-03 K-40 5.3E-03 08807 STP-AP-033-06-25-90-11:1c 2.7E-03 09702 STP-AP-018-12-28-90-10:3c 1.2E-03 2. 7E -03 K-40 7.9E-03 1.3E-03 K-40 6.7E-03 08808 STP-AP-039-06-25-90-12:Oc 3.0E -03 09703 STP-AP-033-12-21 90-09:Sc 1.3E-03 5.4E-03 K-40 4.5E-03 1.2E-03 K-40 4.4E-03 l
- 08809 STP-AP-037-06-25-90-14:3c 2.9E-03 09704 STP-AP-039-12-28-90-12:3c 8.5E-04 1.9E-03 K-40 9.3E-03 1.5E-03 STP-AP-037-12 28 00-13:Oc K-40 4. 7E-03 08810 STP-AP-015-06-25-90-12:2c 1.2E 03 2.3r-03
- 09705 STP-AP-016-06-25-90-12:2c K-40 7.3E-03 08811
- Denotes controt locatirm P w t-61
ADDENDUM 1 STPEGB REMP RESULTB DATA - 1990 AIRDORNE PARTICULATE AIRDORNE PARTICULATE LAB SAMPLE RESUt.T 1 SICMA LAB SAMPLE RESULT 1 SIGMA NtMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M'3 ERROR ttD NUMBER SAMPLE SUBMISSION CODE ANALYSIS pCi/M'3 ERROR LLD 09706 STP-AP-015-12-28-90-13:1c K-40 9.9E-03 2.3E-03 4.8E-03 08804 STP- AP *-07 09-90-15:4e se-7 1.6E-01 2.7E-03 2.6E-03 09707 STP-AP-016-12-28-90-13:2c K-40 6.9E-03 1.4E-03 3.1E-03 08805 STP-AP-035-06-25-90-10:1c Be-T 1.3E-01 4.3E-03 5.2E-03 09708 STP-AP-001-12-28-90-13:2c K-40 7.8E-03 1.7E-03 3.2E-03 08806 STP-AP 018-06-25-90-10:5c Be-7 1.4E-01 4.5E-03 5.1E-03 09709 STP-AP-006-12-28-90-14:cd K-40 7.0E-03 1.4E-03 2.9E-03 08807 STP-AP-033 06-25-90-11:1c Be-T 1.4E-01 4.4E-03 5.0E-03 09710 STP-AP-006-12-28-90-14:cd K-40 7.2E-03 1.7E-03 3.5E-03 08808 STP-AP-039-06-25-90-12:Oc Be-7 1.4E-01 4.4E-03 5.8E-03 07922 STP-AP ***-01-04-90-13:3c Be-7 1.1E-01 3.4E-03 3.9E-03
- 08809 STP- AP-037-06 25-90-14:3c Be-7 1.4E-01 4.4E-03 4.9E-03 07944 STP-AP ***-01-09-90-14:?c Be-7 1.0E-01 3.6E-03 4.5E-03 08810 STP-AP-015-06-25-90-12:2c Be-7 1.3E-01 4.2E-03 5.3E-03 07978 STP-AP ***-01-17-90-15:Oc Be-7 2.3E-01 4.3E-03 3.5E-03 08811 STP-AP-016-06-25-90-12:2c Be-T 1.4E-01 4.2E 03 5.1E-03 08009 STP-AP ***-01-24-90-16:Oc De-7 9.5E-02 3.0E-03 3.3E-03 08812 STP-AP-001-06-25-90-12:3c Be-T 1.3E-01 3.0E-03 3.9E-03 08035 STP-AP ***-01-31-90-14:2c Be-7 1.5E-01 3.8E-03 3.5E-03 08813 STP-AP-006-06-25-90-13:dc Be-7 1.4E-01 3.3E-03 4.3E-03 08065 STP-AP ***-02-06-90-16:4c Be-7 1.3E-01 3.9E-03 4.3E-03 08814 STP-AP-006-06-25-90-13:dc Be-7 1.4E-01 3.1E-03 3.9E-03 08098 STP-AP
- 15-90-14:5c Be-7 2.0E-01 4.0E-03 3.4E-01 08852 STP- AP *-07-18-90-15:5c Be-T 1.4E-01 3.1E-03 2.6E-03 08136 STP-AP
- 21-90-15:3c Be-7 2.0E-01 6.5E-03 6.6E-03 08896 STP- AP ***-07-23-90-13:3c Be-T 1.4E-01 2.8E-03 3.4E-03 08163 STP-AP ***-02-28-90-14:3c Be-7 1.9E-01 4.4E-03 3.8E-03 08908 STP- AP ***-07-31-90-15:2c Be-7 1.8E-01 2.6E-03 2.3E-03 08191 STP- AP *-03-07-90-14:3c Be-7 1.6E-01 3.8E-03 3.3E-03 08?68 STP-AP ***-08-08-90-14:Oc Be-T 9.5E-02 1.3E-03 1.1E-03 08244 STP-AP " 15-90-13:1c Be-7 1.8E-01 3.8E-03 3.2E-03 08996 $1 P- AP "* 1f 90-16:Oc Be-7 2.4E-01 3.3E-03 2.8E-03 08266 $1P-AP
- 21-90-16:3c 8e-7 2.1E-01 4.6E-03 4.3E-03 09021 STP-AP ***-08-2<-90-13:1c Be-7 1. 7E - 01 3.5E-03 3.2E-03 08298 STP-AP
- 28 90-13:2c 8e-7 2.6E-01 4.8E-03 3.8E-03 09033 STP-AP
- 28-90-15:Sc Be-7 1.6E-01 3.8E-03 3.8E-03 08324 STP-AP
- 03-90-14:4c Be-7 1.8E-01 4.5E-03 4.7E-05 09075 STP- AP *"-09-05-90-14:Oc Be-7 1.5E-01 2.1E-03 1.9E-03 08329 STP-AP-035-03-28-90-10:Oc Be-7 1.6E-01 4.8E-03 5.4E-03 09106 STP-AP
- 12-90-10:4c Be-T 1.3E-01 2.3E-03 2.4E-03 08330 STP-AP-018-03-28-90-10:3c Be-7 1.6E-01 4.5E-03 4.5E-03 09146 STP-AP ***-09-18 90-10:4c Be-7 7.7E-02 2.9E-03 3.8E-03 08331 STP-AP-033-03-28-90-13:2c 8e-7 1.5E-01 4.8E-03 6.5E-03 09187 STP-AP ***-09-25-90-16:2c Be-7 1.5E-01 4.1E-03 4.2E-03 08332 STP-AP-039-03-28-90-13:Oc Be-7 1.5E-01 4.5E-03 5.0E-03 09226 STP-AP ***-10-02-90-14:1c Be-7 2.7E-01 5.6E-03 4.8E-03
- 08333 STP-AP-037-03-28 90-12:4c Be-T 1.7E-01 4.8E-03 5.1E-03 09229 STP AP-035-09-25-90-10:2c Be-T 1.4E-01 3.2E-03 3.6E-03 08334 STP AP-015-03-28-90-12:1c Be-7 1.6E-01 4.5E-03 4.7E-03 09230 STP-AP-018-09-25-90-11:1c Be-7 1.5E-01 3.1E-03 3.1E-03 08335 STP-AP-016-03-28-90-12:1c Be-7 1.6E-01 4.7E-03 5.4E-03 09231 STP-AP-033-09-25-90-12:1c Be-T 1.2E-01 2.9E-03 3.8E-03 08336 STP-AP-001-03-28-90-12:Oc Be-7 1.6E-01 4.9E-03 5.0E-03 09232 STP-AP-039-09-25-90-12:3c Be-7 1.3E-01 4.3E-03 5.OE-03 08337 STP-AP-006-03-28-90-11:dc Be-7 1.7E-01 4.8E-03 5.1E-03
- 09233 STP- AP-037-09-25-90-13 :Oc Be-7 1.4E-01 4.4E-03 5.0E-03 08338 STP-AP-006-03-28-90-11:dc Be-7 1.6E-01 4.9E-03 5.4E-03 09234 STP-AP-015-09-25-90-16:2c Be-T 1.3E-01 4.1E-03 4.8E-03 08369 STP-AP
- 10-90-14:4c Be-T 2.2E-01 4.3E-03 3.5E-01 09235 STP-AP-016-09-25-90-16:2c se-T 1.4E-01 3.0E-03 3.0E-03 08393 STP-AP ***-04-19-90-16:Oc Be-7 1.8E-01 3.5E-03 2.8E-03 09236 STP-AP-001-09-25-90-16:2c Be-7 1.3E-01 2.8E-03 3.0E 03 08446 STP-AP
- 26-90-14:2c 8e-7 2.2E-01 4.4E-03 3.4E-03 09237 STP-AP-006-09-25-90-15:cd Be-T 1.3E-01 3.0E-03 3.8E-03 08472 STP-AP
- 02-90-15:2c Be-7 1.4E-01 4.8E-03 4.9E-03 09238 STP-AP-006-09-25-90-15:cd Be-T 1.3E-01 4.3E-03 5.6E-03 08498 STP-AP
- 08-90-13:2c Be-7 1.4E-01 3.9E-03 4.4E-03 09277 STP-AP
- 11-90-15:2c Be-7 1.2E-01 2.1E-03 2.1E-03 08526 STP AP
- 16-90-14:5c Be-7 1.2E-01 3.1E-03 3.1E 01 09329 STP-AP " *-10-18-90-16:4c Be-T 2.2E-01 5.1E-03 4.9E-03 08569 STP-AP ***-05-24-90-14:4c Be-7 1.4E-01 3.9E-03 4.6E-05 09370 STP-AP
- 24-90-15:5c Be-7 7.1E-02 1.6E-03 1.9E-03 08593 STP-AP
- 30-90-15:Oc Be-7 7.8E-02 2.1E-03 2.5E-03 09402 STP-AP "*-10 29-90-16:2c Be-7 2.1E-01 3.7E-03 3.5E-03 08632 STP-AP
- 06-90-14:5c Be-7 1.2E-01 3.5E-03 4.0E-03 09454 STP-AP
- 06-90-15:1c Be-T 1.8E-01 2.5E-03 2.1E-03 08661 STP-AP
- 12-90-16:1c Be-7 1.4E-01 4.0E-03 4.3E-03 09485 STP-AP
- 13-90-15:Oc Be-T 1.8E-01 2.8E-03 2.7E-03 08710 StP-AP ***-06-20 90-14:3c Be-7 1. 7E -01 3.6E-03 3.2E-03 09509 STP-AP
- 19-90-14:2c Be-T 1.3E-01 3.9E-03 4.8E-03 08740 STP-AP ***-06-25-90-14:3c Be-7 1.5E-01 5.4E-03 6.1E-03 09531 STP-AP ***-11-26-90-14:2c Ba-7 1.9E-01 2.6E-03 2.4E-03 08778 STP- AP *-07-02-90-14:3c Be-7 1. 7E -01 2.6F-03 2.6E-03 ON STP- AP "* 03-90-17:1c Be-7 1.2E-01 2.5E-03 2.3E-03
- Dmotes contret locations rao* t 62
mumanum
- = = == == - - == - == = = -
ADDENDUM 1 STPECB REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRBORNE PARTICULATE RESULT 1 SIGMA RESUti 1 $1GMA LAB SAMPLE LAB SAMPLE *JMBER SAMPLE SUPMISSION ET E ANALYSi$ pCi/M'3 ERROR LLD NUM9Est SAMPLE SUBMISSION CTE AttALYSIS pCi/M'3 EPPOR tto STP-AP ***-05-08-90-13:2c Mn-54 2.4E-04 1.5E-04 5.3E-04 5.0E-03 4. 7E- 03 08498 09594 STP-AP ***-12-10-90-10:1c Be-7 2.1E -01 Mn-54 2.4E-05 9.9E-05 3.3E-04 1.9E-01 4.OE-03 3.7E-03 08526 STP-AP ***-05-16-90-14:Sc 09627 STP-AP ***-12-18-90-15:4c Be-7 Mn-54 1.2E-04 1.1E-04 3.8E-04 3.5E-03 3.1E-03 08569 STP-AP ***-05-24-90-14:4c 09682 STP-AP "*-12-28-90-14:Oc Be-7 1.4E-01 Mn-54 6.8005 6.1E-05 2.2E-04 1.9E-01 3.2E-03 3.2E- 03 08593 STP-AP ***-05-30-90-15:Oc 09701 STP-AP-035-12-28-90-10:Oc Be-7 Mn-54 -1.3E-04 1.2E-04 3. 7E-04 1.7E 01 5.1E-03 5.8E-03 08632 STP- AP *"-06-06-90-14:5c 09702 STP-AP-018-12-28-90-10:3c Be-7 Mn-54 0.0E+00 1.4E-04 4.6E-04 1.7E-01 3.7E-03 4.0E-03 08661 STP-AP "*-06-12-90-16:1c 1.8E-03 09703 STP-AP-033-12-21-90-09:5c Be-T Mn-54 4.3E-04 5.3E-04 5.1E-03 5.4E-03 08704 STP-AP-015-06-20-90-13:59 09704 STP-AP-039-12-28 90-12:3c Be-7 1.7E-01 Mn 54 -1.1E-05 8.8F05 2.9E-04 1.9E-01 3.4E-03 3.4E-03 08710 STP- AP "C06-20-90-14:3c
- 09705 STP-AP-037-12-28-90-13:Oc Be-T Mn-54 -1.1E-04 2.0E 04 6.3E-04 1.9E-01 5.5E-03 5.4E-03 08740 STP- AP *"-06-25-90-14:3c 2.0E-04 09706 STP-AP-015-12-28-90-13:1c Be-7 STP- AP *" 07-02 90-14:3c Mn-54 -5.4E-05 6.4E-05 1.7E-01 5.1E-03 5.8E 03 08778 2.8E-04 09707 STP-AP-016-12-28-90-13:2c Be-7 Mn-54 -4.8E-05 8.7E 05 1.9E-01 5.5E-03 5.5E-03 08804 STP- AP *"-07 09-90-15:4c 09708 STP-AP-001-12-28-90-13:2c Be-7 Mn-54 -4.5E-05 9.3E-05 3.0E-04 1.9E 01 5.5E-03 5.5E-03 08805 STP-AP-035-06-25-90-10:1c 09708 STP-AP-001-12-28-90-13:2c Be-7 Mn-54 -6.2E-05 1.1E-04 3.3E-04 Be-7 1.7E-01 5.2E-03 5.3E-03 08806 STP AP-018-06-25-90-10:5c 8.1E-05 3.00 04 09709 STP-AP-006-12-28-90-14:cd 08807 STP-AP-033-06 25-90-11:1c Mn-54 1.3E-04 Be-7 1.8E-01 6.1E-03 6.?E-03 1.1E-05 8.1E -05 2.7E-04 09710 STP-AP-006-12-28-90-14:cd 08808 STP-AP-039-06-25-90-12:Oc Mn-54 Mn-54 7.4E-05 1.2E 04 4.0E-04 0.0E +00 9.8E-05 3.2E-04 07922 STP- AP "*-01-04-90-13:3c 4.9E-04
- 08809 STP-AP-037-06-25-90-14:3c Mn-54 STP-AP ***-01-09-90-14:2c Mn-54 7.1E-05 1.5E-04 Mn-54 2.0E-05 8.6E-05 2.9E-04 07944 08810 STP-AP-015-06-25-90-12:2c Mn-54 0.0E+00 9.8E-05 3.2E-04 -7.1E-05 8.0E-05 2.5E-04 07978 STP- AP "*-01-17-90-15:Oc 4.1E-04 08811 STP-AP-016 06-25-90-12:2c Mn-54 STP-AP
- 24-90-16:0c Mn-54 -1.3E-04 1.3E-04 Mn-54 -3.0E-05 6.0E-05 1.9E-04 08009 3.6E-04 0*.812 STP-AP-001-06-25-90-12:3c STP-AP ***-01-31-90-14:2c Mn-54 -1.9E-04 1.2E-04 Mn-54 -2.7E-05 5.9E-05 1.9E-04 08035 5.?E-04 08813 STP-AP-006-06-25-90-13:e STP-AP
- 06-90-16:4c Mn-54 7.3E-05 1.5E-04 Mn-54 5.4E-06 5.8E-05 1.9E-04 08065 3.3E-04 0*814 STP-AP-006 06-25-90-13:dc 08098 STP-AP " 15-90-14:Sc Mn-54 -1.0' 04 1.0E-04 STP- AP ***-07-18-90-15:5c Mn-54 -3.1E-05 7.1E-05 2.3E-04
-6.!E-05 2.1E-04 6.8E-04 08852 2.9E-04 08136 STP-AP ***-02-21-90-15:3c Mn-54 STP- AP ***-07-23-90-13:3c Mn-54 -2.8E-04 9.9E-05
-7.1E-05 9.tE-05 2.9E-04 08896 2.3E-04 08163 STP-AP **o 02-28-90-14:3c Mn-54 STP- AP ***-07-31 15:2c Mn-54 -1.8E-05 6.9E-05 1.2E-04 3.5E-04 08908 08191 STP-AP
- 07-90-14:3c Mn-54 - 2. AE - 04 Mn-54 -5.1E-05 3.1E-05 9.5E-05
-2.3E-04 9.2E-05 2.4E 04 08968 STP-AP * -08 08 90-14:Oc 2.6E-04 08244 STP-AP
- 15-90-13:1c Mn-54 STP- AP "* 08-14-90-16:Oc Mn-54 -4.2E-05 7.9E-05 1.0E-04 1.3E-04 4.5E-04 08996 2.3E-04 08266 STP-AP
- 21-90-16:3c Mn-54 STP-AP ***-08 22-90-13:1c Mn-54 -4.2E-05 7.3E-05 v.9E-05 3.1E-04 09021 08298 51P-AP
- 28-90-13:2c Mn-54 -6.6E-05 Mn-54 -9.0E-05 1.0E-04 3.2E-04
-8.5E-05 1.3E-04 4.1E-04 09033 STP- AP *"-08-28 90-15:Sc 1.8E-04 08324 STP-AP ***-04-03-90-14:4c Mn-54 STP AP
- 05 90-14:Oc Mn-54 4.4E-05 5.2E-05
-5.1E-05 9.8E-05 3.1E 04 09075 2.2E-04 08329 STP-AP-035-03-28-90-10:Oc Mn-54 STP-AP
- 12-90-10:4c Mn-54 4.5E-05 6.6E-05 8.2E-05 2.8E-04 09106 0833J STP-AP-018-03-2C-90-10:3c Mn-54 5.6E-05 Mn-54 1.2E-04 1.1E-04 3.8E-04 1.6E-04 9.1E-05 3.3E-04 09146 STP- AP *"-09-18-90-10:4c 4.1E-04 08331 STP-AP-033-03-28-90-13:2c Mn-54 STP-AP "*-09-25-90 16:2c Mn-54 1.6E-04 1.1E-04 4.5E-05 9.7E-05 3.3E-04 09187 4.4E 04 08332 STP-AP-039-03-28-90-13:Oc Mn-54 STP-AP ***-10 02 90-14:1c Mn-54 -1.1E-04 1.4E-04
-1.4E-04 1.1E-04 3.3E-04 09226 2.0E-04
- 08333 STP-AP-037-03-28-90-12:4c Mn-54 STP-AP-035-09-25-90-10:2c Mn-54 -1.1E-04 6.7E-05 5.7E-05 8.4E-05 2.9E-04 09229 2.1E-04 08334 STP-AP-015-03-28-90-12:1c Mn-54 S?P-AP-018-09-25-90-11:1c Mn-54 2.3E-05 6.3E-05 2.3E-04 1.0E-04 3.6E 04 09239 2.0E-04 08335 STP-AP-016-03-28-90-12:1c Mn-54 STP-AP-033-09-25-90 12:1c Mo-54 -2.9E-05 6.3E-05 9.8E-05 3.4E-04 09231 3.2E-04 08336 STP AP-001-03-28-90-12:Oc Mn-54 7.7E-05 Mn-54 -6.5E-05 1.0E-04 8.8E-05 2.PE-04 09232 STP-AP-039-09 25-90-12:3c 3.2E-04 08337 STP-AP-006-03-28-90-11:dc Mn-54 -4.6E-05 Mn-54 -6.7E-05 1.0E-04 1.10 04 3.6E-04
- 09233 STP-AP-037-09 25-90-13:0c 2.9E-04 08338 STP-AP-006-03-28-90-11:dc Mn-54 1.3E-05 Mn-54 -4.5E-05 9.2E-05 1.OE-04 3.?E -04 09234 STP-AP-015-09 25-90-16:2c 2.4E-04 08369 STP-AP ***-04-10-90-14:4c Mn-54 -9.1E-05 STP-AP-016-09-25-90-16:2c Mn-54 -5.8E-05 T.6E-05 .
8.4E-05 3.?E-04 09235 1.9E-04 I 08393 STP-AP *** 04-19-90-16:Oc Mn-54 2.2E-04 STP-AP-001-09-25-90-16:2c Mn-54 3.6E-05 5.5E-05 1.1E 04 3.5E-04 09236 1.9E-04 08446 STP-AP **C 04-26-90-14:2c Mn-54 -1.0E-04 Sir-AP-006-00 75 90-15:cd Mn-54 5.3E -06 5.9E-05
- 1. 7E -04 U f-04 P??37 08472 STP- AP "*-05-02-90-15:2c Mn-54 0.or+00
- Denotes control locations Page 1-63 i
ADDENDUM 1 STPEGB REMP RESULTil DATA - 1990 AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESuti 1 SICMA L AB SAppe r RESULT 1 SIGMA CJM8ER SAMPLE SUSMISSION CODE ANALYSIS pCi/M'3 ERROR LLD 4FRE R SAMotE SURMISSION CODE ANALYSIS pCi/M 3 ERROR LLD 09238 STP-AP-006-09-25-90-15:cd Mn-54 -3.4E-05 7.6E-05 2.4E-04 08334 STP-AP-015-03-28-90-12:1c Fe-59 -2.7E-04 3.6E-04 1.1E-03 09277 STP-AP
- 11-90-15:2c Mn-54 2.0E-05 5.9E-05 2.0E-04 08335 STP-AP-016-03-28-90-12:1c F e-f 9 0.0E+00 3.6E-04 1.2E-03 09329 STP-AP
- 18-90-16:4c Mn-54 -1.4E-05 1.3E-04 4.1E-04 08356 STP-AP-001-03-28-90-12:Oc Fe-99 -6.7E-04 4.7E-04 1.4E-03 09370 STP-AP " 24-90-15:5c Mn-54 -3.1E-05 5.5E-05 1.8E-04 08337 STP-AP-006-03-28-90-11:dc Fe-59 -2.3E-04 3.4E-04 1.1E-03 69402 STP-AP " 29-90-16:2c Mn-54 1.1E-04 9.6E-05 3.3E-04 08338 STP-AP-006 03-28-90-11:d- Fe-59 6.7E-05 4.3E-04 1.4E-03 69454 STP-AP ~ 06-90 15:1c Mn-54 -1.6E-05 5.9E-05 1.9E-04 08369 STP-AP ~ 10-90-14:4c Fe-59 2.1E-04 2.4E-04 8.5E-04 09485 STP-AP " 13-90-15:Oc Mn-54 4.0E-05 7.0E-05 2.4E-04 08393 STP-AP ~ 19-90-16:Oc Fe-59 3.6E-04 1.7E-04 6.6E-04 09509 STP-AP
- 19-90-14:2c Mn-54 -6.1E-05 1.4E-04 4.6E-04 08446 STP-AP
- 26-90-14:2c Fe-59 -2.3E-04 2.0E-04 6.1E-04 09531 STP-AP
- 26-90-14:2c Mn-54 -1.0E-04 7.1E-05 2.2E-04 08472 STP-AP ***-05-02-90-15:2c Fe-59 -2.0E-04 3.6E-04 1.1E-03 09568 STP-AP ***-12-03-90-17:1c Mn-54 7.7E-06 5.1E-05 1. 7E -04 08498 STP-AP
- 08-90-13:2c Fe-59 -8.8E-05 3.4E-04 1.1E-03 09594 STP-AP- 10-90-10:1c Mn-54 -9.2E-05 1.2E-04 3. 7E -04 08526 STP- AP *" 16-90-14 :5c Fe-59 2.8E-04 2.1E-04 7.7E-04 09627 STP- AP "*- 12-18-90-15:4c Mn 8. 7E - 05 1.0E-04 3.1E-04 08569 STP-AP ~ 24-90-14:4c Fe-59 7.2E-05 2.2E-04 7.4E-04 09682 STP- AP *"-12-28-90-14:Oc Mn-54 -9.1E-05 8.3E-05 2.5E-04 08593 STP-AP
- 30-90-15:Oc Fe-59 4.2E-05 1.3E-04 4.3E-04 09701 STP-AP-035-12-28-90-10:Oc Mn-54 -6.4E-05 5.8E-05 1.BE-04 08632 STP-AP ***-06-06-90-14:5c Fe-59 -3.7E-04 2.6E-04 7.6E-04 09702 STP-AP-018-12-28-90-10:3c Mn-54 -6.2E-05 9.0E-05 2.8E-04 08661 STP-AP
- 12-90-16:1c Fe-59 -1.4E-04 2.9E-04 9.3E-04 09703 STP-AP-033-12-21-90-09:Sc Mn-54 7.9E-05 7.1E-05 2.5E-04 08704 STP-AP-015-06-20-90-13:59 Fe-59 -1.1E-03 1.3E-03 3.9E-03 09704 STP-AP-039-12-28-90-12:3c Mn-54 0.0E+00 1.0E-04 3.3E-04 08710 STP-AP *"-06-20-90-14:3c Fe-59 3.0E-05 1.8E-04 6.0E-04 09705 STP-AP-037-12-28-90-13:Oc Mn-54 -1.7E-05 6.2E-05 2.0E-04 08740 STP- AP "*-M-25-90-14:3c Fe-59 -4.5E-04 4.2E-04 1.3E-03 09706 STP-AP-015-12-28-90-13:1c Mn-54 -3.1E-05 9.5E-05 3.1E-04 08778 STP- AP "*-07-02-90-14:3c Fe-59 -0.7E-05 1.6E-04 5.0E-04 09707 STP-AP-016-12-28-90-13:2c Mn-54 7.5E-05 8.4E-05 3.0E-04 08804 STP- AP ***-07-09 90-15:4c Fe-59 -2.1E-04 1.BE-04 5.4E-04 09708 STP-AP-001-12-28-90-13:2c Mn-54 2.9E-05 8.9E-05 3.0E-04 08805 STP-AP-035-06-25-90-10:1c Fe-59 4.4E-04 3.6E-04 1.3E-03 09709 STP-AP-006-12-28-90-14:cd Mn-54 1.3E-05 9.5E-05 3.2E-04 08806 STP-AP-018-06-25-90-10:Sc Fe-59 -1.3E-04 4.0E-04 1.3E-03 09710 STP-AP-006-12-28-90-14:cd Mn-54 -1.6E-04 1.1E-04 3.2E-04 08807 STP-AP-033-06-25-90-11:1c Fe-59 -5.3E-04 3.4E-04 9.5E-04 07922 STP-AP
- 04-90-13:3c Fe-59 0.0E+00 2.2E-04 7.2E-04 08808 STP-AP-039-06-25-90-12:Oc Fe-59 -5.9E-04 4.1E-04 1.2E-03 07944 $1P- AP "*-01-09-90-14:2c Fe-59 7.5E-04 3.1E-04 1.2E-03
- 06809 STP-AP-037-06-25-90-14:3c Fe-59 -3.1E-04 3.7E-04 1.1E-03 07978 STP-AP
- 17-90-15:Oc Fe-59 -3.8E-04 2.3E-04 6.7E-04 08810 STP-AP-015-06-25-90-12:2c Fe-59 -2.6E-04 3.2E-04 1.0E-03 08009 STP-AP ~ 24-90-16:Oc Fe 2.8E-04 2.5E-04 7.4E - 04 08811 STP-AP-016-06 25-90-12:2c Fe-59 -2.7E-04 3.4E-04 1.1E-03 08035 STP- AP *"-01-31-90-14:2c Fe-59 -3.2E-04 2.7E-04 8.1E-04 08812 STP-AP-001-06-25-90-12:3c Fe-59 - 7.9E - 05 2.5E-04 8.1E-04 08065 STP-AP ***-02-06-90-16:4c Fe-59 -1.5E-04 2.9E-04 9.1E-04 08813 STP-AP-006-06-25-90-13:dc Fe-59 3.9E-04 2.5E-04 9.1E-04 08098 STP-AP ***-02-15-90-14:5c Fe-59 0.0E+00 2.3E-04 7.5E 04 08814 STP-AP-006-06-25-90-13:dc Fe-59 2.6E-04 2.8E-04 9.7E-04 08136 STP-AP- 21-90-15:3c Fe-59 -5.1E-04 4.0E-04 1.1E-03 08352 STP- AP *"-07-18-90-15:Sc Fe-59 -6.1E 04 1.8E-04 4.1E-04 08163 STP-AP ***-02-28-90-14:3c Fe-59 1.1E-04 2.?E-04 7.6E-04 08896 STP- AP "*-07-23 90-13:3c Fe-59 2.0E-04 2.1E-04 7.4E-04 08191 STP- AP ***-03-07-90-14:3c Fe-59 -2.3E-04 2.3E-04 6.8E-04 08?08 STP- AP ~-07-31-90-15:2c Fe-59 -6.6E-05 1.7E-04 5.5E-04 08244 STP-AP " *-03-15-90-13:1c Fe 59 -1.0E-04 2.?E-04 6.8E-04 08968 STP-AP ***-08-08-90-14:Oc Fe-59 -1.3E-04 7.1E-05 2.1E-04 08266 STP-AP
- 21-90-16:3c Fe-59 -1.9E-04 2.5E-04 7.8E-04 08996 STP-AP ***-08-14-90-16:Oc Fe-59 3.2E-04 1.6E-04 5.8E-04 08298 STP-AP
- 28-90-13:2c Fe-59 1.7E-04 2.3E-04 7.9E 04 09021 STP-AP ***-08-22-90-?3:1c Fe-59 -1.1E-04 1.8E-04 5.6E-04 08324 STP-AP
- 03-90-14:4c Fe-59 -2.8E-04 3.0E-04 9.3E 04 09033 STP-AP ~ *-08-28-90-15:Sc Fe-59 -4.4E-04 2.6E-04 7.5E-04 08329 STP-AP-035-03-28-90-10:Oc Fe-59 -1.2E-04 3.6E-04 1.2E-03 09075 STP-AP ***-09-05-90-14:Oc Fe-5" -7.1E-05 1.2E-04 3.8E-04 08330 S19-AP-018-03-28-90-10:3c Fe-59 -1.1E-04 3.4E-04 1.1E-03 09106 STP-AP
- 12-90-10:4c Fe-59 1.7E-04 1.7E-04 5.8E-04 08331 STP-AP-033-03-28-90-13:2c Fe 59 -2.6E-04 3.2E-04 9.8E-04 09146 STP-AP ***-09-18-90-10:4c Fe-59 3.6E-04 2.4E-04 8.9E-04 08332 STP-AP-039-03-28-90-13:Oc Fe-59 2.1E-04 3.4E-04 1.2E-03 09187 STP-AP 25-90-16:2c Fe-59 -2.2E-04 2.5E-04 7.6E-04
- 08333 STP-AP-037-03-28-90-12:4c Fe-59 -6.3E-04 3.9E-04 1.1F-03 09226 STP-AP ~ 02-90-14:1c Fe-59 1.0E-04 3.1E-04 1.0E-03
- Denotes controt locations Page t.-64 M M O
ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 AIRDORNE PARTICULATE AIRBORNE PARTICULATE RESULT 1 SIGMA RESULT 1 SICMA L AR SAMPLE LAB SAMPLE Pci/M'3 EePOR tto ERROR ttD NUNRER SAMPLE SUBalSSION CODE ANALYSIS NUM8ER SAMPLE SUBMISSION CODE ANALYSIS PCi/M'3 STP-AP ***-03-15-90-13:1c Co- 58 -1.8E-04 1.0E-04 2.9E-04
-6.5E-05 2.8E-04 9.2E-04 08244 09229 STP-AP-035-09-25-90-10:2c Fe-59 Co-58 3.0E-05 1.2E-04 4.1E-04 1.7E-04 2.4E-04 8.1E-04 08266 STP- AP *"-03-21-90-16:3c 09230 STP-AP-018-09-25-90-11:1c Fe-59 Co-58 -1.7E-04 1.2E-04 3.6E-04 1.6E-04 2.6E-04 8.9E-04 08298 STP-AP
- 28-90-13:2c 09231 STP-AP-033 09-25-90-12:1c Fe-59 STP- AP *"-04-03-90-14:4c Co-58 -1.6E-04 1.4E-04 4.2E-04 6.9E-04 3.7E-04 1.4E-03 08324 09232 STP-AP-039-09-25-90-12:3c Fe-59 STP-AP-035-03-28-90-10:Oc Co-58 - 3.M - 04 1.5E-04 4.2E-04 1.6E-04 3.8E-04 1.3E-03 08329
- 09233 STP- AP-037-09-25-90-13:Oc Fe-59 STP-AP-018-03-28-90-10:3c Co-58 -1.5E-04 1.4E-04 4.3E-04 Fe-59 -2.7E-04 3.5E-04 1.1E-03 08330 09234 STP-AP-015-09-25-90-16:2c STP-AP-033-03-28 90-13:2c Co-58 1.7E-04 1.5E-04 4.5E-04 1.1E-04 3.0E-04 1.0E-03 08331 09235 STP-AP-016-09-25-90-16:2c Fe-59 Co-58 -6.6E-05 1.4E-04 4.4E-04
-9.8E-05 2.0E-04 6.3E-04 08332 STP-AP-039-03-28 90-13-Oc 09236 STP-AP-001-09-25-90-16:2c Fe-59 STP-AP-037-03-28-90-12:4c Co-58 3.8E-05 1.6E-04 5.3E-04 Fe-59 -6.7E-04 2.6E-04 7.3E-04
- 08333 3.9E-04 09237 STP-AP-006-09-25-90-15:cd STP-AD-015-03-28 90-12:1c Co-58 -1.2E-04 1.3E-04
-1.6E-04 3.4E-04 1.1E-03 08334 09238 STP-AP-006-09-25-90-15:cd F e-59 Co-58 -1.9E-04 1.5E-04 4.5E-04 2.7E-05' 1.2E-04 4.1E-04 08335 STP-AP-016-03-28-90-12:1c 09277 STP-AP
- 11-90-15:2c Fe-59 STP-AP-001-03-28-90-12:Oc Co-58 -2.2E-04 1.7E-04 5.0E-04 Fe-59 3.1E-04 3.5E-04 1.2F-03 08336 3.9E-04 09329 STP-AP
- 18-90-16:4c STP-AP-006-03-28-90-11:dc Co-58 -7.0E-05 1.?E-04 1.1E-04 1.1E-04 4.0E-04 08337 4.8E-04 09370 STP- AP *"-10-24-90-15:5c F e-59 STP-AP-006-03-28-90-11:dc Co-58 -3.0E-04 1.7E-04 Fe-59 -1.3E-04 2.3E-04 7.5E-04 08338 4.3E-04 09402 STP-AP ***-10-29-90-16:2c STP-AP ***-04-10-90-16:4c Co-58 3.0E-04 1.1E-04
-2.3E-04 1.4E-04 4.?E-04 08369 2.7E-04 09454 STP-AP ***-11-06-90-15:1c Fe-59 STP-AP ***-04-19-90-16:Oc Co-58 -4.2E-05 8.5E-05 1.6E-04 1.4E-04 5.1E-04 08393 09485 STP-AP
- 13-90-15:Oc F e-59 Co-58 1.1E-04 1.1E-04 3.9E-04
-5.3E-04 3.0E-04 8.6E-04 08446 STP-AP
- 26-90-14:2c 5.4E-04 09509 STP-AP
- 19-90-14:2c Fe-59 STP-AP ***-05-02-90-15:2c Co-58 -1.3E-04 1.7E-04 5.1E 05 1.5E-04 5.1E-04 08472 09531 STP-AP ***-11-26-90-14:2c Fe-59 Co-58 -5.3E-05 1.5E-04 4.8E-04 4.1E-05 1.3E-04 4.4E-04 08498 STP-AP ***-05-08-90-13:2c 3.YE-04 09568 STP-AP
- 03-90-17:1c F e-59 08526 STP-AP ***-05-16-90-14:Sc Co-58 -7.6E-05 9.9E-05 re-59 -1.5E-04 2.9E-04 9.0E-04 1.2E-04 3.1E-04 09594 STP-AP ***-12-10-90-10:1c 08569 STP-AP ***-05-24-90-14:4c Co-58 -3.3E-04 Fe-59 9.3E-05 2.2E-04 7.6E-04 -1.9E-04 6.6E-05 1.7E-04 09627 STP-AP
- 18-90-15:4c 7.5E -04 08593 STP- AP "*-05-30-90-15:Oc Co-58 09682 STP- AP "*-12-28-90-14:0c re-59 1.8E-04 2.1E-04 Co-58 -1.9E-04 1.2E-04 3.4E-04 3.1E-04 2.2E-04 7.8E-04 08632 STP-AP ***-06-06-90-14:5c 4.6E-04 09701 STP-AP-035-12-28-90-10:Oc Fe-59 STP-AP
- 12-90-16:1c Co-58 1.8E-05 1.4E-04 1.2E-04 2.6E-04 8.9E-04 08661 09702 STP-AP-018-12-28-90-10:3c Fe-59 Co-58 -4.4E-04 5.6E-04 1.8E-03 2.9E-04 1.1E-03 08704 STP-AP-015-06-20-90-13:59 09703 STP-AP-033-12-21-90 09:Sc Fe-59 5.2E 04 Co-58 7.2E-05 8.8E-05 3.1E-04 6.9E-05 3.6E-04 1.2E-03 08710 STP- AP *"-06-20 14:3c 09704 STP-AP-039-12-28-90-12:3c Fe-59 Co-58 -1.5E-04 2.1E-04 6.5E-04 1.7E-04 2.5E-04 8.4E-04 08740 STP-AP
- 06-25-90-14:3c 2.2E-04
- 09705 STP AP-037-12-28-90-13:Oc Fe-59 STP- AP "*-07-02-90-14:3c Co-58 -7.7E-05 7.1E-05 1.5E-04 3.9E-04 1.3E-03 08778 09706 STP-AP-015-12-28-90-13:1c Fe-59 Co-58 2.9E-05 8.5E-05 2.9E-04 6.5E-04 3.9E-04 1.4E-03 08804 STP-AP *** 07-09-90-15:4c 5.1E-04 09707 STP-AP 016-12-28-90-13:2c Fe-59 Co-58 1.9E-04 1.4E-04 3.7E-04 3.0E-04 1.1E-03 08805 STP-AP-035-06-25-90-10:1c 09708 STP-AP-001-12-28-90-13:2c Fe-59 Co-58 -9.5E-05 1.5E-04 4.9E-04
-1.3E-04 3.8E-04 1.2E 03 08806 STP-AP-018 06-25-90-10:Sc 09709 STP-AP-006-12-28-90-14-cd Fe-59 Co-58 -1.6E-04 1.4E-04 4.2E-04 5.0E-04 1.6F 03 08807 STP-AP-033 06-25-90-11:1c 09710 STP-AP-006-12-28-90-14:cd Fe-59 0.OE+00 Co-58 5.0E-05 1.3E-04 4.4E-04 1.2E-04 3.8E-04 08808 STP-AP-039-06-25-90-12:Oc 07922 STP- AP *"-01-04-90-13:3c Co-58 -3.1E-05 Co-58 -2.3E-04 1.5E-04 4.4E-04 1.6E-04 6.0E-04
- 08809 STP-AP-037-06-25-90-14:3c 07944 STP- AP "*-01-09-90-14:2c Co-58 3.7E-04 Co-58 1.4E-04 1.4E- 04 4.9E-04 1.2E-04 1.2E-04 4.3E-04 08810 STP-AP-015-06-25-90-12:2c 4.4E-04 07978 $1P- AP "*-01-17-90-15:Oc Co-58 STP-AP-016 06-25-90-12:2c Co-58 0.0E*00 1.3E-04 1.3E-04 4.0E-04 08311 08009 STP-AP
- 24-90-16:Oc Co-58 -1.5E-04 Co-58 -4.0E-05 9.1E-05 3.0E-04 1.2E-04 3.7E-04 08812 STP-AP-001-06-25-90-12:3c 08035 STP- AP "*-01-31-90-14:2c Co-58 -1.9E-04 Co-58 -1.4E-04 1.0E-04 3.1E-04 1.5E-04 4.8E 04 OA813 STP-AP-006 06-25-90-13:dc 08065 STP-AP
- 06-90-16:4c Co-58 0.0E+00 Co-58 2.6E-05 9.4E-05 3.1E-04 1.1E 04 3.7E 04 08814 STP-AP-006-06-25-90-13:dc 3.0E-04 08098 STP-AP ***-02-15-90-14:Sc Co-58 -1.3E-05 STP-AP ***-07-18-90-15:5c Co-58 -1.4E-04 9.9E-05
-3.0E-04 2.2E-04 6.6E-04 0*E52 3.3E-04 08136 STP-AP
- 21-90-15:3c Co-58 STP- AP "* 23-90-13:3c Co-58 -8.1E-05 1.0E-04
-4.6E-05 1.1E-04 3.6F-04 0*??6 2.5E-04 08163 STP-AP " *-02-28-90-14:3c Co-58 099M ST P- AP *** -0 7- 31 15:2c Co-58 -1.0F-04 8.0E-05 Co-58 -1.1E-04 1.2E-04 3.Ar 04 08191 STP- AP ***-03-07-90-14:3c i
- Denom rentrol locations P W t-6%
ADDENDUM 1 BTPEGB REMP RESULTG DATA - 1990 AIREORNE PARTICULATE AIRBORNE PARTICULATE RESULT 1 SIGMA RESUtf 1 SIGMA LAB SAMPLE LAB SA*PLE NUMtE R SAMPLE SURMTSSION CODE ANALYSIS pCi/M'3 EPROR LLD pCi/M 3 ERROR LtD NUMRER SAMPtE SUBMISSION CODE ANALYSIS Co-60 -2.7E-05 1.7E-04 5.4E-04
-4.2E-05 3.3E-05 1.0E-04 07944 STP-AP ***-01-09-90-14:2c 08968 STP-AP
- 08-90-14:Oc Co-58 Co-60 -2.3E-04 1.2E-04 3.4E-04
-7.4E-06 8.2E-05 2.7E-04 07978 STP- AP *-01-17-90-15:Oc 08996 STP-AP
- 14-90-16:Oc Co-58 Co-60 -3.6E-04 1.5E-04 3.9E-04 l
-3.3E-05 8.9E-05 2.9E-04 08009 STP-AP ***-01-24-90-16:0c 09021 STP-AP ***-08-22-93-13:1c Co-58 Co-60 -2.4E-04 1.0E-04 2.3E-04 I
-6.M -05 1.1E-04 3.M - 04 08035 STP-AP ***-01-31-90-14:2c 4.6E-04 09033 STP-AP
- 28-90-15:5c Co-58 Co-60 -2.9E-05 1.4E-04 l
8.5E-05 5.5E-05 1.9E-04 08065 STP-AP ***-02-06-90-16:4c 09075 STP-AP ***-09-05-90-14:Oc Co-58 Co-60 -6.1E-05 1.?E-04 3.9E-04 1.2E-04 7.3E-05 2.6E-04 08098 STP-AP ***-02-15-90-14:5c 09106 STP-AP ***-09-12-90-10:4c Co-58 Co-60 -3.1E-04 2.3E-04 6.3E-04
-1.8E-04 1.3E-04 3.M -04 08136 STP-AP ***-02-21-90-15:3c 09146 STP-AP
- 18-90-10:4c Co-58 Co-60 -2.8E-04 1.0E-04 2.3E-04 i
6.9E-05 1.30-04 4.3E-04 08163 STP-AP ***-02-28-90-14:3c 09187 STP-AP
- 25-90-16:2c Co-58 Co-60 1.2E-04 1.1E-04 3.9E-04
-1.4E-04 1.4E-04 4.30-04 08191 STP- AP *** 07-90-14:3c 09226 STP-AP ***-10-02-90-14:1c Co-58 Co-60 8.4E-05 1.2E-04 4.0E-04 Co-58 -1.5E-04 9.7E-05 2.9E-04 03244 STP- AP *-03-15-90-13:1c 4.4E-04 09229 STP-AP 035-09-25-90-10:2c 08266 STP-AP ***-03 21-90-16:3c Co-60 -1.1E-04 1.4E-04 Co-58 7.0E-05 9.6E-05 3.3E-04 8.0E-05 1.1E-04 3.7E-04 09230 STP-AP 018-09-25-90-11:1c 08298 STP-AP ***-03-28-90-13:2c Co-60 09231 STP-AP-033-09-25-90-12:1c Co-58 1.7E-04 9.4E-05 3.4E - 04 Co-60 8.3E-05 1.6E-04 5.6E-04
-1.90-04 1.4E-04 4.3E-04 08324 STP-AP
- 03-90-14:4c 09232 STP-AP 039-09-25-90-12:3e Co-58 STP- AP-035-03-2849-10:0c Co-60 -1.9E-05 1.1E-04 3.5E-04
-3.0E-04 1.3E-04 3.7E-04 08329
- 09233 STP- AP 037-09-25-90-13:Oc Co-58 Co-60 0.0E*00 7.5E-05 2.5E-04 1.2E-04 1.1E-04 3.8E-04 08330 STP-AP-018-03 28-VD-10:3c 09234 STP-AP-015-09-25-90-16:2c Co-58 Co 4. 7E -05 7.8E-05 2.4E-04 1.7E-05 9.6E-05 3.2E-04 08331 STP-AP-033-03-28-90-13:2c 09235 STP-AP-016-09-25-90-16:2c Co-58 Co-60 -1.1E-04 7.7E-05 2.2E-04 5.3E-05 8.1E-05 2. 7E - 04 08332 STP-AP-039-03 28-90-13:Oc 09236 STP-AP 001-09-25-90-16:2c Co-58 Co-60 -5.7E-05 9.9E-05 3.1E-04 ,
-2.1E-04 9.9E-05 3.0E-04
- 08333 STP-AP-037-03-28-90-12:4c '
09237 STP-AP-006-09-25-90-15:cd Co-58 Co-60 1.6E-05 8.7E-05 2.9E-04 5.1E-05 1.2E- 04 4.2E-04 08334 STP-AP-015-03-28-90-12:1c 09238 STP-AP-006-09-25-90-15:cd Co-58 Co-60 1.6E-05 7.8E-05 2.6E-04 4.3E-05 5.9E-05 2.0E-04 08335 STP-AP-016 03-28-90-12:1c 09277 STP-AP ***-10-11-90-15:2c Co-58 Co-60 -1.1E-04 1.0E-04 2.9E-04
-1.BE-05 1.5E-04 4.9E-04 08336 STP-AP-001-03 28-90-12:Oc 09329 S1P-AP ***-10-18-90-16:4c Co-58 Co-60 -6.5E-05 9.4E-05 2.9E-04 0.0E+00 5.6E-05 1.8E-04 08337 STP-AP-006-03-28 90-11:dc 09370 STP-AP ***-10-24-90-15:5c Co-58 Co-60 -7.6E-05 9 . 35 - 0 5 2.8E-04 1.1E-04 1.1E-04 3. 7E - 04 08338 STP-AP-006-03-28-90-11:dc C9402 STP-AP
- 29-90-16:2c Co-58 Co-60 8.2E-05 1.1E-04 3.9E-04 8.5E-05 ' 6.5E-05 2.3E 04 08369 STP-AP
- 10-90-14:4c 3.3E-04 09454 STP-AP
- 06-90-15:1c Co-58 08393 STP-AP
- 19 90-16:Oc Co-60 1.8E-04 8.6E-05 Co-58 -9.1E-05 7.6E-05 2.4E-04 -1.4E-04 9.4E-05 2.6E-04 09485 STP- AP *-11-13-90-15:Oc 08446 STP-AP ***-04-26-90-14:2c Co-60 Co-58 -2.1E-04 1.5E-04 4.5E-04 -2.6E-04 2.1E-04 6.0E-04 09509 STP-AP ***-11-19-90-14:2e 08472 STP-AP
- 02 90-15:2c Co-60 Co-58 -1.7E 04 7.4E-05 2.2E-04 -3.7E-04 1.7E-04 4.4E-04 09531 STP-AP ***-11-26-90-14:2c 08498 STP-AP * -05+08 90-13:2c Co-60 Co-58 8.1E-06 5.9E-05 2.0E-04 -1.3E-04 9.4E-05 2.7E-04 09568 STP- AP *-12-03-90-17:1c 4.1E-04 08526 STP-AP ***-05-16-90-14:5c Co-60 09594 STP-AP
- 10-90-10:1c Co-58 2.0E-05 1.2E-04 Co-60 -1.6E-04 1.1E-04 3.2E-04
-1.3E-05 1.1E-04 3.6E-04 08569 STP-AP
- 24-90-14:4c 1.9E-04 09627 STP-AP ***-12-18-90-15:4c Co-58 STP-AP ***-05-30-90-15:Oc Co-60 -9.4E-05 6.7E-05
-5.5E-05 9.7E-05 3.1E-04 08593 09682 STP-AP ***-12-28-90-14:Oc Co-58 Co-60 1.7E-04 1.3E-04 4.BE-04 Co-58 1.7E-04 8.7E-05 3.1E-04 08632 STP-AP
- 06-90-14:Sc 4.8E-04 09701 STP-AP-035-12-28-90-10:Oc Co-60 2. 7E - 05 1.4E-04 7.3E-05 1.3E-04 4.6E-04 08661 STP-AP
- 12-90-16:1c 2.4E-03 09702 STP-AP-018-12-28-90-10:3c Co-58 Co-60 1.5E-03 6.1E-04 2.2E-05 1.2E-04 3.9E-04 08704 StP-AP-015-06-20 90-13:59 3.3E-04 09703 STP-AP-033-12-21-90-09:Sc Co-58 STP-AP
- 20-90-14:3c Co-60 3.6E-05 9.8E-05
-8.4E-05 1.4E-04 s.3E-04 08770 5.3E-04 09704 STP-AP-039-12-28-90-12:3c Co-58 Co-60 -1.4E-04 1.8E-04
-9.3E-05 8.4E-05 2.6E-04 08740 STP-AP ***-06-25-90-14:3c 2.4E-04
- 09705 STP-AP-037-12-28 90-13:Oc Co-58 STP- AP *** 02 14:3c Co-60 9.4E 06 7.2E-05
-2.5E-04 1.7E-04 5.2E - 04 08778 3.1E-04 09706 STP-AP-015-12-28-90-13:1c Co-58 Co-60 4.4E-05 9.3E-05 1.1E-04 1.4E-04 4.8E-04 08804 STP-AP *** 07-09-90-15:4c 2.3E-04 09707 STP-AP-016-12-28-90-13:2c Co-58 STP-AP-035-06-25-90-10:1c Co-60 -1.1E-04 8.1E-05 1.3E-04 4.2E-04 OS*AS 09708 S1P-AP-001-12-28-90-13:2c Co-58 -4.4E-05 Co-60 -1.8E-05 1.1E-04 3.4E-04 1.5E-04 4.9E-04 08806 STP-AP-018-06-25 90-10:Sc 3.3E-04 09709 SIP-AP 006-12-28-90-14:cd Co-58 -2.0E-05 STP-AP-033-06-2C 90-11:1c Co-60 1.7E-05 9.9E-05 1.6E-04 4.(E 04 0*.807 09710 STP-AP On6-12-28-90-14:cd Co-58 -2.2E-04 Co-60 -6.0E-05 9.0E-05 2.8E-04 6.BE-05 1.2E-04 4.2r-04 0**M S 4-AP-039-00 25 90-12:Oc 07922 STP-AP
- 04-90-13:3c Co-60
- Denotes control t ocat iorn Page L-(4 E E E N M N
M M W W M M M M M M M W W M M M M M M ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRDORNE PARTICULATE LLB SAMPtE RESUti 1 SIGMA t.48 SAMPLE RESULT 1 $!CMA NUMRfp SAMPLE SUBMISSION CODE ANALYSIS pCi/M'3 ERPOR tto MMBER SA"PtE SUBMISSION CtX'E ANALYSIS pci/C 3 Ene0R LLD
- 08809 STP-AP-037-06-25-90-14:3c Co-60 -2.0E-04 1.1E-04 3.2E-04 09703 STP-AP-033-12-21-90-09:Sc Co-60 4.2E-05 6.5E-05 2.3E-04 08810 STP-AP-015-06-25-90-12:2c Co-60 0.0E+00 7.8E-05 2.6E-04 09704 STP-AP-039-12-28-90-12:3c Co-60 8.4E-05 1.1E-04 3.8E-04 08811 STP-AP-016-06-25-90-12:2c Co-60 8.5E-05 8.5E-05 3.0E-04
- 09705 STP-AP-037-12-28-90-13:Oc Co-60 5.0E-05 6.3E-05 2.2E-04 08812 STP-AP-001-06-25-90-12:3c Co-60 4.1E-05 5.6E-05 1.9E-04 09706 31P-AP-015-12-28-90-13:1c Co-60 -4.5E-05 8.5E-05 2.6E-04 08813 STP-AP-006-06-25-90-13:dc Co-60 -1.1E-04 5.3E-05 1.5E-04 09707 STP-AP-016-12-28-90-13:2c Co-60 5.2E-05 7.5E-05 2.7E-04 08814 STP-AP-006-06-25-90-13:dc Co-60 -3.OE-05 6.9E-05 2.2E-04 09708 STP-AP-001-12-28-90-13:2c Co-60 1.3E-04 1.1E-04 3.9E-04 08852 STP- AP "-07-18-90-15:Sc Co-60 -4.9E-05 8.6E-05 2.7E 04 09709 STP-AP 006-12-28-90-14:cd Co-60 -1.8E-05 8.0E-05 2.6E-04 08896 STP- AP *-07-23-90-13:3c Co-60 -1.0E-04 1.1E-04 3.4E-04 09710 STP-AP 006-12-28-90-14:cd Co-60 -5.1E-05 9.6E-05 2.9E-04 08908 STP- AP ***-07-31-90-15:2c Co-60 -9.7E-06 8.0E-05 2.6F-04 07922 STP- AP *"-01-04-90-13:3c Zn-65 1.1E-04 2.3E-04 7.8E-04 08968 STP-AP ~ 08-90-14:Oc Co-60 -4.3E-05 3.5E-05 1.1E-04 07944 STP-AP ***-01-09-90-14:2c Zn-65 1.4E-04 2.8E-04 9.6E-04 08996 STP-AP
- it.-90-16:Oc Co-60 5.4E 05 8.6E-05 2.9E-04 07978 STP- AP *** 17-90-15:Oc Zn-65 -3.5E-04 2.7E-04 8.0E-04 09021 STP-AP ***-08-22-90-13:1c Co-60 -9.5E-05 9.2E-05 2,8E 04 08009 STP- AP "* 01 90-16:Oc Zn-65 -3.2E-04 2.7E-04 8.1E-04 009 3 STP-AP ***-08-28-90-15:Sc Co-60 -9.7E-05 1.1E-04 3.4E-04 08035 SYP-AP
- 31-90-14:2c Zn-65 -4.0E-05 2.5E-04 8.2E-04 0?n75 STP-AP ***-09-05-90-14:Oc Co-60 4.8E-05 6.2E-05 2.1E-04 08065 STP-AP ***-02-06-90-16:4c 2n-65 -2.9E-04 3.3E-04 1.0E-03 09 D6 STP-AP " *-09-12-90-10 4c Co-60 -8.0E-05 7.2E-05 2.2E-04 08095 STP-AP ***-02-15-90-14:Sc Zn-65 -4.1E-04 2.1E-04 5.7E-04 09146 S1P- AP *" 18 10:4c Co 7.0E -05 1.3E-04 4.2E 04 08136 STP AP ***-02-21-90-15:3c 2n-65 1.7E-04 4.5E-04 1.5E-03 09187 Sip-AP ***-09-25-90-16:2c Co-60 0.0E+00 1.3E-04 4.3E-04 08163 STP-AP ***-02-28-90-14:3c Zn-65 -3.3E-04 2 1E-04 6.0E-04 C9226 STP-AP ***-10-02-90-14:1c Co-60 8.9E-05 1.4E-04 5.0E-04 08191 STP- AP 07-90-14:3r 2n-65 -3.2E-04 2.8E-04 8.5E-04 09229 STP-AP-035-09-25-90-10:2c Co-60 -1.1E-04 7.3E-05 2.2E-04 08244 STP- AP *"-03-15-90-13:1c 2n-65 - 1. 7E - 04 2.2E-04 6.7E-04 09230 STP-AP-018-09-25-90-11:1c Co-60 5.OE-05 6.5E-05 2.2E-04 08266 STP-AP ***-03-21-90-16:3e 2n-65 0.0E+00 2. 7E-04 8.8E-04 09231 STP-AP-033-09-25-90-12:1c Co-60 0.0E+00 6.1E-05 2.0E-04 08298 STP-AP
- 28-90-13:2c In-65 -6.8E-05 2.4E-04 7.8E-04 09232 STP-AP-039-09-25-90-12:3c Ci-60 -5.7E-05 9.9E-05 3.1E-04 08324 Sir-AP ***-04-03-90-14:4c 2n-65 -2.3E-04 3.0E-04 9.4E-04
- 09233 STP- AP-037-09-25-90-13:Oc Co-60 3.1E-05 7.6E-05 2.6E-04 08329 STP-AP-035-03-28-90-10:Oc Zn-65 -1.8E-04 2.0E-04 6.2E-04 09234 STP-AP-015-09-25-90-16:2c Co-60 6.4E-05 8.2E-05 2.9E-04 08330 STP-AP-018-03-28-90-10:3c Zn-65 6.1E-05 2.1E-04 7.1E-04 09235 STP-AP-016-09-25-90-16:2c Co-60 -9.4E-05 6. 7E -05 2.0E-04 08331 STP-AP-033-03-28-90-13:2c Zn-65 1.8E-04 1.9E-04 6.8E-04 09236 STP-AP-001-09-25-90-16:2c Co-60 1.4E-05 5.9E-05 2.0E-04 08332 STP-AP-039-03-28-90-13:Oc Zn-65 -3.0E-05 2.OE-04 6.4E-04 09237 STP-AP-006-09-25-90-15:cd Co 60 2.2E-05 6.1E-05 2.1E-04
- 08333 STP-AP-037-03-28-90-12:4c Zn-65 -3.9E-04 2.1E-04 5.8E-04 09238 STP-AP-006-09-25-90-15:cd Co-60 -8.0E-05 9.2E-05 2.8E-04 08334 STP-AP 015-03-28-90-12:1c Zn-65 -1.9E-04 2.0E-04 6.1E-04 09277 STP-AP ***-10-11-90-15:2c Co-60 -9.5E-05 6.4E-05 1.9E-04 08335 STP-AP-016-05 28-90-12:1c Zn-65 -5.3E-04 2.3E-04 6.2E-04 09329 STP-AP ***-10-18-90-16:4c Co-60 -2.?E-05 1.2E-04 3.9E-04 08336 STP-AP-001-03-28-90-12:Oc Zn-65 -2.2E-04 2.4E-04 7.5E-04 09370 STP-AP- 24-90-15:Sc Co-60 8.9E-05 5.8E-05 2.1E-04 08337 STP-AP-006-03-28-90-11:dc Zn-65 -1.9E-04 1.7E-04 5.0E-06 09402 STP-AP- 29-90-16:2c Co-60 0.0E+00 1.1E-04 3.8E-04 08338 STP-AP-006-03-28-90-11:dc In-65 -3.2E-04 2.3E-04 6.7E-04 09454 STP-AP
- 06-90-15:1c Co-60 2.5E-05 5.9E-05 2.0E-04 08369 STP AP "* 10-90-14:4c Zn-os -4.1E-04 2.5E-04 7.2E-04 09485 STP-AP
- 13-90-15:Oc Co-60 5.2E-05 8.7E-05 3.0E-04 08393 STP- AP "*-04-19-90-16:Oc Zn-65 5.2E-05 1.7E-04 5.8E-04 09509 STP- AP *"-11-19-90-14:2c Co-60 4.3E-04 1.7E-04 4.0E-04 08446 STP-AP ***-04-26-90-14:2c 2n 65 3.3E-05 2.0E-04 6.8E-04 09531 STP-AP ***-11-26-90-14:2c Co-60 3.0E-05 8.1E-05 2. 7E -04 08472 STP-AP ***-05-02-90-15:2c Zn-65 -9.2E-04 3.9E-04 9.9E-04 09568 STP- AP "-12-03-90-17:1c Co-60 -6.0E-05 6.2E-05 1.9E-04 08498 STP-AP "*-05-08-90-13:2c 2n-65 -4.7E-04 3.2E-04 9.2E-04 09594 STP-AP *"-12-10-90 10:1c Co-60 3.0E-05 1.2E-04 4.1E-04 08526 ST P- AP *** 16-90-14 :5c Zn-65 3.1E-05 1.9E-04 6.3E-04 09627 STP- AP "*-12-18-90-15:4c Co-60 1.9E-05 1.0E-04 3.4E 04 08569 STP-AP
- 24-90-14:4c 2n-65 0.0E+00 2.5E-04 8.4E-04 09682 STP- AP "*-12-28 14:Oc Co-60 2.1E-05 1.1E-04 3.8E-04 0 % 93 STP- AP "*-05-30 90-15:Oc Zn-65 0.0E+00 1.5E-04 4.9E-04 09701 STP-AP-035-12-28-90-10:Oc Co-60 5.5E-05 5.9E-05 2.1f-04 08632 STP-AP ***-06-06-90-14:5c Zn-65 -6.8E-04 2.6E-04 6.7E-04 09702 STP-AP-018-12-28-90-10:3c Co-60 2.6r-04 8.9E-05 3.+ 04 0.*A61 SYP-AP
- 12-90-16:1c Zn-65 -6.OE-04 2.9E-04 8.0E-04
- Demtn control locatims Pac 1 -67
ADDENDUM 1 BTPEGff REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRDORNE PARTICULATE 1 S1GP8A [A9 SAMptE RESULT 1 SICPeA LAB SAMPLE RESULT pCi/M'3 EePOR ttD ePJMMER SA**PLE SURMISSION E00E ANALYSIS pCi/M'3 EPece LLD NUP89ER SAMPLE SUBMISSION CG)E ANALYSIS Zn-?5 -2.8E-03 1.4E-03 4.2E-03 09485 STP- AP *" 11-13-90-15:Oc Zn-65 -8.9E-05 1.6E-04 5.2E-04 08704 STP-AP-015-06 W 13:59 9.5E-04 Zn-65 -1.?E-04 1.9E-04 6.0E-04 09509 STP-AP " * .1-19-90-14:2c Zn-65 -3.2E-04 3.1E-04 08710 STP-AP
- 20-00-14:3c 1.7E-04 5.0E-04 08740 STP-AP ***-06-25-90-14:3c Zn-65 -6.2E-04 5.0E-04 1.5E-03 09531 STP AP
- 26-90-14:2c Zn-65 -4.6E-04 6.4E-05 1.5E-04 09568 STP-AP ***-12-03-90-17:1c Zn-65 -8.2E-05 1.5E-04 4.8E-04 08778 STP- AP *-07-02-90-14:3c 2n-65 5 . 0E - O'.
1.8E-04 5.2E-04 09594 STP-AP
- 10-90-10:1c Zn-65 1.0E-04 3.1E-04 1.0E-03 08804 STP- AP ***-07-09-90-15:4c. In-65 -4.BE-04 7.6E-04 Zn-65 -3.9E-04 2.2E-04 6.3E-04 09627 STP-AP
- 18-90-15:4c Zn-65 -2.9E-04 2.5E-04 08805 STP-AP-035-06-25-90-10:1c 2.0E-04 6.4E-04 08806 STP-AP-018-06-25-90-10:5c Zn-65 -4.5E-04 2.0E-04 5.1E-04 0?682 STP-AP
- 28-90-14:0c Zn-65 -1.1E-04
-2.9E-04 2.2E-04 6.6E-04 09701 STP-AP-(35-12-28-90-10:Oc In-65 -5.1E-04 1.4E-04 3.7E-04 OG807 STP-AP-033-06-25-90-11:1c Zn-65 1.8E-04 4. 7E -04 09702 STP-AP-018-12-28-90-10:3c Zn-65 3.0E-04 2.1E-04 7.8E-04 08808 STP-AP-039-06-25-90-12:Oc In-65 -4.4E-04 5.4E-04 2n-65 -4.5E-04 2.5E-04 7.1E-04 09703 STP-AP-033-12-21-90-09:Sc Zn-65 -1.6E-04 1.7E-04 o 00809 STP-AP-037-06-25-90-14:3c 2.5E-04 7.7E-04 In-65 0.0E+00 1.9E-04 6.3E-04 09704 STP-AP-039-12-28-90-12:3c Zn-65 -2.0E-04 OG810 STP-AP-015-06-25-90-12:2c 1.4E-04 4.0E-04 2n-65 -1.9E-04 2.0E-04 6.2E-04
- 09705 STP- AP-037-12-28-90-13 :Oc Zn-65 -2.9E-04 OG811 STP-AP-016-06-25-90-12:2c 2.2E-04 7.9E-04 In-65 -1.9E-04 1.4E-04 4.5E-04 09706 STP-AP-015-12-28-90-13:1c In-65 2.2E 04 08812 STP-AP-001-06-25-90-12:3c 5.7E-04 Zn-65 7.2E-05 1.4E-04 4.6E-04 09707 STP-AP-016-12-28-90-13:2c In-65 -2.7E-04 2.0E-04 OG813 STP-AP-006-06-25-90-13:dc 2.3E-04 8.5E-06 STP-AP-006-06-25-90-13:dc Zn-65 -2.1E-04 1.4E-04 4.1E-04 09708 STP-AP-001-12-28-90-13:2c Zn-65 3.3E-04 OG814 Zn-65 -5.5E-05 2.1E-04 6.8E-04 09709 STP-AP-006-12-28-90-14:cd Zn-65 -3.5E-05 2.0E-04 6.7E-04 08852 STP- AP *-07-1S-90-15:Sc 3.5E-04 2.9E-04 1.0E-03 Zn-65 -1.8E-04 2 X 04 6.4E-04 09710 STP-AP-006-12-28-90-14:cd 2n-65 OG896 STP- AP ***-07-23-90-13:3c 1.9E-04 7.1E-04 In-65 -2.6E-04 1.5E-04 4.5E-04 07922 STP-AP ***-01-04-90-13:3c Zr-95 3.2E-04 08908 STP-AP
- 11-90-15:2c 2.5E-04 8.5E-04 STP-AP ***-08-08-90-14:Oc In-65 -1.4E-04 6.4E-05 1.8E-04 07944 STP-A7 ***-01-09-90-14:2c Zr-95 6.2E-05 08968 1.9E-04 6.3E-04 STP-AP ***-08-14-90-16:Oc 2n-65 -1.8E-04 1.9E-04 5.8E-04 07978 STP-AP ***-01-17-90-15:0c Zr-95 2.3E-05 08996 2.2E-64 7.3E-04 STP-AP
- 22-90-13:1c Zn-65 -5.4E-05 1.8E-04 5.9E-04 08009 STP-AP
- 24-90-16:Oc Zr-95 2.6E-05 09021 2.0E-04 6.4E-04 STP-AP ***-05-28-90-15:Sc Zn-65 -1.7E-04 2.6E-04 8.1E-04 08035 STP-AP
- 31-90-14:2c Zr-95 - 7.9E - 05 09033 2.8E-04 7.6E-04 STP-AP ***-09-05-90-14:Oc Zn-65 -2.3E-05 1.?E-04 4.1E-04 08065 STP-AP
- 06-90-16:4c Zr-95 -7.8E-04 09075 1.9E-04 6.0E-04 STP-AP
- 12-90-10:4c Zn-65 0.0E
- 00 1.5E-04 4.8E-04 08098 STP-AP
- 15-90-14:Sc Zr-95 -9.0E-05 09106 4.0E-04 1.4E-03 Zn-65 -6.4E-04 2. 7E -04 7.0E-04 08136 STP-AP ***-02-21-90-15:3c Zr-95 1.7E-04 09146 STP-AP ***-09-18-90-10:4c 1.8E-04 5.8E-04 In-65 2.4E-04 7.0E-04 08163 STP-AP ***-02-28-90-14:3c Zr-95 -7.9E-05 09187 STP-AP
- 25-90-16:2c - 3.0E - 04
-2.3E-04 2.2E-04 6.9E-04 09226 STP-AP
- 02-90-14:1c In-65 1.0E-04 3.2E 04 1.1E-03 08191 STP AP ***-03-07-90-14:3c Ir-95 5.5E-04 08244 STP-AP
- 15-90-13:1c Zr-95 1.8E-04 1.9E-04 6.8E-04 09229 STP-AP-035-09-25-90-10:2c Zn-65 -9.4E-05 1. 7E-04 7.0E-04
-1.8E-04 1.5E-04 4.8E-04 08266 STP- AP "*-03-21-90-16:3c Zr-95 -2.1E-04 2.2E-04 09230 STP-AP-018-09-25-90-11:1c Zn-65 1.4E-04 4.4E-04 08298 STP-AP ***-03-28-90-13:2e Ir-95 4. 7E-05 2.0E-04 6.7E-04 09231 STP-AP-033-09-25-90-12:1c Zn-65 -2.1E 04 7.5E-04
-2.2E-04 2.?E-04 6.8E-04 08324 STP-AP
- 03-90-14:4c Zr-95 -2.4E-04 2 4E-04 09232 STP-AP-039-09-25-90-12:3c In-65 ' 9.2E-04 In-65 -3.0E-04 2.0E-04 5.9E-04 08329 STP-AP-035-03-28-90-10:Oc Zr-95 2.0E-04 2.7E-04 o 09233 STP- AP-037- 09-25-90-13 :Oc Zr-95 2.7E-04 2.4E-04 8.4E-04 09234 STP-AP-015-09-?5-90-16:2c Zer 65 3.1E-05 2.?E-04 7.3E 04 08330 STP-AP-018-03-28-90-10:3c 1.6E-04 5.?E 04 08311 STP AP-033-03-28 90-13:2c Zr-95 3.0E-05 2.6E-04 8.7E-04 09235 STP-AP-016-09-6 16:2c In- 65 -3.3E-05 7.8E-04
-2.8E-04 1.2E-04 3.4E-04 08332 STP-AP-039-03-28-90-13:0c Zr-95 0.0E+00 2.4E-04 09236 STP-AP-001-09-25 90-16:2c Zn-65 9.3E-04 1.4E-04 4.6E-04
- 08333 STP- AP-037-03 28-90-12:4c Zr-95 0.0E+00 2.8E-04 09237 STP-AP-006-09-25-90-15:cd 2n-65 7.1E-05 7.3E-04 1.9E-04 5.4E-04 08334 STP-AP-015-03-28-90-12:1c Zr-95 3.0E-05 2.2E-04 09238 STP-AP-006-09 25-90-15:cd 2n-65 -3.4E-04 7.5E-04 1.2E-04 3.9E-04 08335 STP-AP-016-03 28-90-12:1c Zr-95 -9.3D 05 2.3E-04 09277 STP-AP ***-10-31-90-15:2c Zn-65 -4.1E-05 7.9E-04 2.5E-04 7.8E-04 08336 STP-AP-001-03 28 90-12:Oc Zr-95 -8.4E-04 2.9E-04 09329 STP-AP ***-10-18-90-16:4c Zn-65 -1.2E-04 6.5E-04 1.3E-04 4.3E-04 08337 STP-AP-006-03 28-90-11:dc Zr-95 -1.6E-04 2.1E-04 09370 STP-AP ***-10-24-90-15:5c In-65 -2.'! 05 2.9E-04 1.0E-03 Zn-65 -5.2E-05 2.2E-04 7.?f-04 08338 STP-AP-006-03-28-90-11:dc Zr-95 2.8E-04 09402 STP-AP ***-10-29-90-16:2c Zr-95 -1.4E-04 1.9E-04 5.9E-04 09454 STP-AP
- 06-90-15:1c In-65 -3.1E-04 1.4E-04 4.1F-04 083A9 STP-AP
- 10-90-14:4c
- Denotn enntrol tocations Page t-68 Y M S % M E $ E
M M M W W W W m W W m m m ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 AIRDORNE PARTICULATE AIRDORNE PARTICULATE RESULT 1 SitMA 1 SICMA LAB SAMPLE LLD
. RESULT PCi/M'3 ERROR LAS SAMPLE LLD wtD*BE R SAMPLE SURMISSION CODE ANALYSIS PCi/M"3 ERROR NUMRTR SAMPLE SUBMISSION CODE ANALYSIS Zr-95 -3.2E-04 1.7E-04 5.3E-04 1.4E-04 4.7E-04 09235 STP-AP-016-09-25-90-16:2c 5.9E-04 08393 STP-AP "*-04-19-90-16:Oc Zr-95 -1.8E 05 Zr-95 2.8E-04 1.7E-04 1.8E-04 5.8E-04 09236 STP-AP-001-09-25-90-16:2c 08446 STP-AP
- 26-90-14:2c Zr-95 -1.1E-04 Zr-95 -9.8E-05 1.8E-04 5.8E-04 4.5E-04 3.2E-04 1.2E- 03 09237 S T P- A P-006 25-90-15:cd 8.4E-04 08472 STP-AP
- 02-90-15:2c Zr-95 STP-AP-006-09-25-90-15:~t Ir-95 3.6E-04 2.3E-04
-4.5E-04 2.5E-04 7.5E-04 09238 3.3E-04 08498 STP-AP- 08-90-13:2c Zr-95 STP- AP "*-10-11-00-15:2c Zr-95 -5.5E-05 1.0E-04
-3.2E-04 1.8E-04 5.3E-04 0927? 8.2E-04 08526 STP-AP ***-05-16-90-14:5c Zr-95 STP-AP
- 18-90-16:4c 7r-95 -1.2E-04 2.6E-04 2.3E-04 6.9E 04 09329 3.5E04 08569 STP-AP
- 24-90-14:4c Zr-95 -3.3E-04 Zr-v5 8.?E-05 1.0E-04
-1.9E-04 1.3E-04 3.9E-04 09370 STP-AP ***-10 24-90-15:Sc 6.0E 04 STP-AP * -05 30 90-15:Oc Zr-95 Zr-95 -1.6E-04 1.9E-04 08593 2.0E-04 6.0E-04 09402 $1P-AP ***-10-27-90-16:2c 3.9E-04 08632 STP-AP
- 06-90-14:5c Zr-95 -2.1E-04 STP- AP *"-11 90-15:1c Zr-95 7.7E-05 1.2E-04
-1.9E-04 2.3E 04 7.30 04 09454 4.0E-04 STP-AP * -06 ^2 90-16:1c Zr-95 Zr-95 -1.3E-04 1.3E-04 08661 1.1E-05 3.4E-03 09485 STP-AP
- 13-90-15:Oc 8.5E-04 STP-AP-015-06-20-00-13:59 Zr-95 -7.5E-04 Zr-95 2.2E-04 2.5E-04 08704 1.7E-04 5.4E-04 09509 STP-AP
- 19-90-14:2c 3.8E-04 08710 STP-AP ***-06-20-90-14:3c Zr-75 - 1.6E -04 Zr-95 -3.4E-04 1.3E-04 1.0E-04 3. 7E -04 T.2E-03 09531 STP-AP ***-11-26-90-14:2c 3.4E-04 08740 STP-AP- 25-90-14:3c Zr 95 STP-AP *" -1" 03-90-17:1c 2r-95 -1.8E-04 1.2E-04
-3.3E-05 1.3E-04 4.1E-04 095N' 6.5E-04 08778 STP-AP
- 02-90-14:3c Zr-95 STP-AP
- 10 90-10:1c Zr-95 -1.3E-04 2.1E-04
-1.4E-04 1.4E-04 4.3E-04 094 6.0E-04 08804 STP-AP- 09-90-15:4c 2r-95 09627 STP-AP
- 18 90-15:4c Zr-95 2.4E-04 1.7E-04 2r-95 1.8E-04 2. 7E-04 9.4E-04 Zr-95 -4. 7E -05 1.8E-04 5.9E-04 08805 STP-AP-035-06-25-90-10:1c 7.8E 04 09682 STP AP
- 28-90-14:Oc 08806 STP-AP-018-06-25-90-10:5c Zr-95 7.4E-04 2.9E-04 Zr-95 -1.0E-04 1.6E-04 5.fE-04 2.7E-04 8.?E-04 09701 STP-AP-035-12-28-90-10:Oc 7.9E-04 08807 STP-AP-033-06-25-90-11:1c Zr-95 -3.5E-04 STP-AP-018-12-28-90-10:3c Zr-95 -9.8E-05 2.5E-04 2.4E-04 8.1E 04 09702 7.5E-04 08808 STP-AP-039-06-25-90-12:Oc Zr-95 0.0E+00 Zr-95 2.7E-04 2.1E 04 2.8E-04 8.90 04 09703 STP-AP-033-12-21-90-09:Sc 9.0E 04
- 08809 STP-AP-037-06-25-90-14:3c Zr-95 -1.9f-04 STP-AP-039-12-28-90-12:3c Zr-95 3.3E-04 2.5E-04 2.6E-04 8.00-04 09704 4.9E-04 08810 STP-AP-015-06-25-90-12:2c Zr-95 -2.5E-04 Zr-95 -7.5E-05 1.5E-04 2.80 04 2.00 04 7.1E-04
- 09705 STP- AP -037-12-28 13:Oc 7.8E-04 08811 STP-AP-016-06-25-90-12:2c Zr-95 STP-AP-015-12-28-90-13:1c Zr-95 - 7. 7E - 04 3.0E-O' 1.8E-04 6.1E 04 09706 9.6E-04 08812 STP-AP-001-06-25-90-12:3c Zr-95 1.4E-04 Zr-95 4.0E-04 ?.7E-04 1.8E-04 5.6E-04 09707 STP-AP-016-12-28-90-13:2c 7.7E-04 08813 STP-AP-006-06-25-90-13:dc Zr-95 -2.0E-04 STP-AP-001-12-28 90-13:2c Zr-95 -7.8E-05 2.4E-04 1.8E-04 5.8E 04 09708 9.2E-04 08814 STP-AP-006-06-25-90-13:dc Zr-95 -3.0E-05 STP-AP-006-12-28-90-14:cd Ir-95 3.5E-6 2.8E 04 1.4E-04 5.1E-04 09709 1.2E-03 08852 STP-AP " 18-90-15:5c Zr-95 1.5E-04 STP-AP-006-12-28-90-14:cd Zr-95 9.8E-05 3.5E-04 1.9E-04 6. 7E- 04 09710 4.0E-04 STP- AP *-07-23-90-13:3c Zr-95 3.9E-04 wb-95 -5.9E 05 1.2E-04 08896 1.3E-04 3.9E 04 07922 STP-AP
- 04-90-13:3c 4. 7E-04 089b8 STP- AP *"-07-31-90-15:2c Zr-95 -1.7E-04 ST P- AP *"- 01 90- 14:2c 'fb-95 -1.6E-04 1.5E-04 5.5E-05 1. 7E -04 07944 3.5E-04 08968 S1P-AP ***-08 08-90-14:Oc Zr-95 -8.2E-05 STP- AP
- 17-90-15:Oc wb-95 -6.4E 05 1.1E-04 1.3E-04 L 1E-04 07978 1.1E-04 3.2E-04 08996 STP-AP
- 14-90 16:Oc Zr-95 -1.1E-04 S1P-AP
- 24-90-16:Oc ab-95 -2.0E-04 1.8E-04 5.9E 04 08009 4.2E-04 STP-AP ***-08 22-90-13:1c Zr-95 7.5E-J5 wb-95 3.0E-05 1.3E-04 09021 2.1E-04 7.?E - 04 08035 STP-AP
- 31-90-14:2c 1.6E-04 4.2E-04 09033 STP-AP ***-08 28-90-15:Sc Zr-95 1.4E-04 S)P- AP " *-02 06-90-16:4c wb-95 -4.3E 04 9.6E-05 2.9E-04 08065 2.9E-04 STP-AP
- 05-90-14:Oc Zr-95 -1.9E-04 mb-95 -1.5E-04 9.7E -05 09075 1.0E 05 1.2E 04 4.0E-04 08098 STP AP "* 15-90-14:Sc 2.1E 04 6.4E-04 09106 STP-AP ***-09-12-90-10:4c Zr-95 08136 STP- AP *"-02-21-90-15:3c wb-95 -2.50 04 Zr-95 -2.?E-04 2.0E-04 6.1E-04 wb-95 -2.3E-04 1.?E-04 3.4E-04 09146 STP-AP ***-09-18-90-10:4c 8.2E 04 08163 STP- AP *"-02^ 28-90-14:3c Zr-95 3.2E-04 2.3E-04 wb-95 -2.6E-04 1.3E-04 3.8E-04 09187 STP-AP ***-09-25-90-16:2c 8.1F-04 08191 STP- AP *"- 03 -0 7-90-14 :3c Zr-95 -6.*f-05 2.5E-04 wb-95 -1.8E-C4 9.9E-05 2.9E-04 09226 STP-AP ***-10-02-90-14:1c 6.4E 04 08244 STP-AP
- 15-90-13:1c 4.3E-04 Zr-95 -1.1E-04 2.0E-04 P&95 -1.5E-05 1.3E-04 09229 STP-AP-035-09-25-90-10:2c 5.6E-04 08266 STP-AP ***-03 21-90-16:3c Zr-95 1.2E-04 1.7E-04 wb-95 -2.6E-04 1.2E-04 3.4E-04 09230 STP-AP-018-09-25-90-11:1c 5.5E 04 08298 STP-AP * -03 28-90-13:2c 4.4E-04 Zr-95 -1.5E-05 1.7E 04 ub-95 -3.6E-04 1.5E-04 09231 STP-AP-033 09-25-90-12:1c 2.9E-04 8.1E-04 08324 STP- AP *-04 03-90-14:4c 1.5E-04 5.4E-04 09232 STP-AP-039-09-25-90-12:3c Zr-95 -6.8E-04 STP-AP-035-03-23-90-10:Oc Nb-95 2.2E-04 2.4E-04 7.9E-04 05329 1.3E 04 4.60 04
- 09233 STP-AP 037-09-25-90-13:Oc Zr-95 -8.9E-05 STP-AP-OtS 03-?M-90-10:3c wb-95 4.9E-05 2.3E-D4 P.M n4 08330 09234 STP-AP-015-09-25 90-16:2c Zr-95 5.1E-04
- Demtes cmtrol t oratims Pw t 49 !
l __ 4
ADDENDUM 1 STPEGS REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPtf RESUti 1 SIGMA LAR SAMPLE RESULT 1 STGMA NUMBER SAMPLE SURMISSION C N E ANALYSIS pCi/M'3 ERPOR LtD NUMBE R SAMPLE SURMISSION CODE ANALYS!$ pCi/M'3 ERPOR LLD 08331 STP-AP-033-03-28-90-13:2c Nb-95 1.3E-04 1.5E-04 5.1E-04 09146 STP-AP
- 18-90-10:4c Nb-95 -9.1E-05 1.3E-04 4.0E-04 08332 STP-AP-039-03-28-90-13:Oc Nb-95 -4.9E-05 1.3E-04 4.3E-04 0918T STP-AP ***-09-25-90-16:2c Nb-95 -9.9E-05 1.3E-04 4.1E-04
- 08333 STP- AP-037-03-28-90-12:4c Nb-95 -9.4E-05 1.7E-04 5.3E-04 09226 STP-AP ***-10-02-90-14:1c Nb-95 -2.6E-04 1.5E-04 4.5E-04 08334 STP-AP-015-03-28-90-12:1c Nb-95 -3.4E-05 1.3E-04 4.1E-04 09229 STP-AP-035-09-25-90-10:2c Nb-95 -6.8E-05 1.1E-04 3.4E-04 08335 STP-AP-016-03-28-90-12:1c Nb-95 -8.7E-05 1.5E-04 4.9E-04 09230 S*P-AP-018 09-25-90-11:1c ab-95 3.5E-05 9.2E-05 3.1E-04 08336 STP-AP-001 03-28-90-12:Oc Nb-95 7.9E-05 1.8E-04 6.2E-04 09231 STP-AP-033-09-25-90-12:1c Nb-95 -3.4E-05 1.0E-04 3.4E-04 08337 STP-AP-006-03-28-90-11:dc Nb-95 1.2E-04 1.5E-04 5.3E-04 09232 STP-AP-039-09-25-90-12:3c ab-95 -1.9E-05 1.6E-04 5.2E-04 08333 STP-AP-006-03-28-90-11:dc kb-95 -1.4E-04 1.7E-04 5.4E-04
- 09233 STP- AP-037-09-25-90-13:Oc Nb- 95 -1.7E-05 1.4E-04 4.5E-04 08369 STP- AP "*-04-10-90-14:4c Nb-95 -6.6E-05 1.1E-04 3.4E 04 09234 STP-AP-015-09-25-90-16:2c Nb-95 ~3.3E-05 1.3E-04 4.1E-04 08393 STP-AP
- 19-90-16:Oc Nb-95 4.0E-05 8.8E-05 3.0E -04 09235 STP-AP-016-09-25-90-16:2c Nb-95 -1.9E-04 1.1E-04 3.4E-04 08446 STP-AP *** 04-26-90-14:2c 'Nb-95 -5.1E-05 1.1E-04 3.5E-04 09236 STP-AP-001-09-25-90-16:2c ab-95 -7.50-05 9.2E-05 2.9E-04 08472 STP-AP
- 02-90-15:2c Nb-95 - 7.5 E - 05 1.6E-04 5.0E-04 09237 STP-AP-006-09-25-90-15:cd Nb-95 - 4. 7E - 05 1.1E-04 3.5E-04 08498 STP-AP ***-05-08-90-13:2c Nb-95 1.3E-04 1.5E-04 5.?E 04 09238 STP-AP-006-09-25-90-15:cd Nb-95 6.7E-05 1.3E-04 4.4E-04 08526 STP-AP ***-05-16-90-14:5c kb-95 -1.2E-05 9.9E-05 3.2E 04 09277 STP-AP' * -10 11-90-15:2c Nb-95 2.0E-05 6.2E-05 2.1E-04 08569 STP- AP *"-05-24-90-14:4c Nb-95 - 1. 7E - 04 1.2E-04 3. 7E -04 09329 STP-AP * "-10-18-90-16:4c Nb-95 -1.4E-04 1.5E-04 4.8E-04 08593 STP-AP ***-05-30-90-15:0c Nb-95 -9. 7E - 05 7.0E-05 2.1E-04 09370 STP-AP "*-10-24-90-15:5c ab-95 -1.3E-04 5.7E-05 1.7E-04 08632 STP-AP ***-06-06-90-14:Sc Nb-95 -4.5E-05 1.2E-04 3.8E 04 09402 STP-AP "*-10-29-90-16:2c Nb-95 -6.8E-05 1.1E-04 3.6E-04 08661 STP-AP " 12-90-16:1c Nb-95 1.4E-04 1.3E-04 4.5E-04 09454 STP- AP *"-11-06 90-15:1c Nb-95 4.3E-05 6.2E-05 2.1E-04 08704 STP-AP-015-06-20-90-13:59 Nb-95 -1.8E-04 6.2E-04 2.0E-03 09485 STP- AP "*-11-13-90-15:Oc Mb-95 4.0E-05 8.0E-05 2.7E-04 08710 STP-AP
- 20-90-14:3c Nb-95 2.5E-04 8.9E-05 2.4E -04 0?509 ST P- AP "* 19 14:2c Nb-95 -1.6E-05 1.4E-04 4.7E-04 08740 STP-AP
- 25-90-14:3c Nb-95 -2.8E 2.0E-04 6.6E-04 09531 STP-AP ***-11-26-90-14:2c Nb-95 -6.9E-05 8.0E-05 2.6E-04 08778 STP- AP *"-07-02-90-14:3e Nb-95 3.1E-05 7.1E-05 2.4E-04 09568 STP- AP *-12-03-90-17:1c ab-95 -1.5E-04 6.4E-05 1.8E-04 08804 STP- AP ***-07-09-90-15:4c Nb-95 1.4E-05 8.8E-05 2.9E-04 09594 STP- AP *"-12-10-90-10:1c Nb-95 1.1E-04 1.3E-04 4.6E-04 08305 STP-AP-035-06-25-90-10:1c Nb-95 -1.2E-04 1.4E-04 4.4E-04 09627 STP-AP
- 18-90-15:4c ab-95 8.5E-05 1.1E-04 3.8E-04 08806 STP-AP-018-06-25-90-10:5c Nb-95 -1.3E-04 1.8E-04 5.6E-04 09682 STP- AP "C 12-28-90-14:Oc Mb-95 2.6E-05 8.9E-05 3.0E-04 08807 STP-AP-033-06-25-90-11:1c Nb-95 -3.6E-05 1.5E-04 5.0E-04 09701 STP AP-035-12-28-90-10:Oc N6-95 -2.1E-05 9.0E-05 2.9E-04 08808 STP AP-039-06-25-90-12:Oc Nb-95 -3 OE-04 1.4E-04 4.1E-04 09702 STP-AP-018-12-28-90-10:3c Nb-95 -1.8E-05 1.4E-04 4.5E-04
- 08809 ST P- AP-037-06-25 14:3c Nb-95 -3.8E-04 1.6E-04 4.6E-04 09703 STP-AP-033-12-21-90-09:Sc Nb-95 1.1E-05 1.1E-04 3.6E-04 08810 STP-AP-015-06-25-90-12:2c Mb-95 -9.4E-05 1.5E-04 4.8E 04 09704 STP-AP-039-12-28-90-12:3c Nb-95 -1.2E-04 1.6E-04 4.9E-04 08811 STP-AP-016-06-25-90-12:2c Nb-95 1.9E-04 1.3E-04 4.5E-04
- 09705 STP-AP-037-12-28-90-13:Oc Nb-95 - 7.5E - 05 9.4E-05 3.0E-04 08812 STP-AP-001-06-25-90-12:3c Nb-95 -1.7E-04 1.1E-04 3.4E-04 09706 STP-AP-015-12-28-90-13:1c Nb-95 2.3E-05 1.6E-04 5.4E-04 08813 STP-AP-006-06-25-90-13:dc Nb-95 -9.3E-05 1.1E-04 3.7E-04 09707 STP-AP-016-12-28-90-13:2c Nb-95 -1.3E-04 1.5E-04 4.6E-04 08814 STP-AP-006-06-25-90-13:dc Nb-95 -1.1E-04 9.6E-05 3.0E-04 09708 STP-AP-001-12-28-90-13:2c Nb-95 1.3E-04 1. 7E -04 5. 7E-04 08852 STP-AP " *-07-18-90-15:5c Nb-95 -1.1E-04 7.9E-05 2.3E-04 09709 STP-AP-006-12-28-90-14:cd ab-95 1.?E-04 1.6E-04 5.5E-04 08896 STP- AP *"-07-23 13:3c kb-95 1.3E-04 1.0E-04 3.5E-04 09710 STP AP 006-12-28-90-14:cd Nb-95 1.1E-04 1.6E-04 5.6E-04 08908 ST P- AP *-07-31-90-15:2c Nb-95 -6.6E-05 7.3E-05 2.3E-04 ON22 STP- AP "* 04-90-13:3c so-140 5.5E-04 4.2E-04 1.5E-03 08968 STP-AP ***-08-08-90-14:Oc Nb-95 1.1E-05 3.4E-05 1.1E-04 O M44 STP- AP "* 01 09-90-14:2c Be-140 4.6E-05 5.1E-04 1.7E-03 08996 STP-AP ***-08-14-90-16:Oc Nb-95 1.3E-04 7.9E-05 2.8E-04 07978 STP- AP *" 17-90-15:Oc Ba-140 -5.6E-04 3.7E-04 1.1E-03 09021 STP- AP *"-08-22-90-13:1c Nb-95 2.1E-05 9.9E-05 3.3E-04 08009 STP-AP ***-01-24-90-16:Oc Sa-140 -2.1E-04 4.4E-04 1.4E-03 09033 STP-AP
- 28-90-15:5c Nb-95 5.2E-05 1.2E-04 4. 2E - 04 08035 STP-AP
- 01-31-90 14:2c Ba-140 -3.0E-04 4.4E-04 1.4E-03 09075 STP-AP
- 05-90-14:0c Nb-95 -1.8E-05 6.0E-05 1.9F - 04 08n65 STP- AP "* 06-90-16:4c Ba-140 -1.6E-04 5.7E-04 1.BE-01 00106 STP-AP
- 12-90-10:4c NS-95 -3.4E-05 7.6E-05 2.5F'04 Oas?9 STP AP "*-02-15-90-14:Sc Ba-140 -7.1E-04 3.7E-04 1.1E-03
- Oemtes emtrol locatims Paga t - 70 EM M M W W M M M M M M M m m W m m e e
M & M & W S ' 5 O & S & W S Y Yb O &. -S ADDENDUM 1 STPEGB REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESULT 1 S!CMA LAB SAMPLE RESULT 1 SICMA WUMBER SAMPLE SUBMISSION CODE ANALYSIS. pci/M'3 ERROR LtD NUMBER SAMPLE SURMISSION CODE ANALYSIS pCi/M'3 ERROR 11 0 08136 STP-AP ***-02-21-90-15:le Ba-140 3.9E-04 7.6E-04 2.6E-03 08852 STP-AP ***-07-18-90-15:Sc Be-140 -5.7E-04 3.6E-04 1.1E-03 08163 STP-AP
- 28-90-14:3e so-140 1.5E-04 4.5E-04 1.5E-03 03896 STP- AP "*-07-23-90-13:3c so-140 4.7E-04 4.0E-04 1.'.E-03 08191 STP- AP "-03-07-90-14:3c so-140 -2.7F-04 4.0E-04 1.3E-03 Ew908 STP-AP ***-07-31-90-15:2c so-140 - 7.5E - 05 2.8E-04 9.3E-04 08244 STP-AP
- 15-90-13:1c Ba-140 -6.2E-04 4.0E-04 1.2E-03 08968 STP-AP
- 08-90-14:Oc so-140 -1.6E-05 1.2E-04 3.8E-04 08266 STP-AP
- 21-90-16:3c Ba-140 0.0E+00 4.4E-04 1.5E-03 08996 STP- AP *"-08-14-90-16:Oc B e - 1 '.0 -1.1E-04 3.3E-04 1.1E-03
'08298 STP-AP
- 28-90-13:2c Ba-140 4.4E-04 4.2E-04 1.4E-03 09021 STP-AP ***-08-22-90-13:1c Ba-140 -3.2E-04 3.6E-04 1.1E-03 08324 STP-AP
- 03-90-14:4c Ba-140 -3.0E-04 5.1E-04 1.6E-05 09033 STP-AP
- 28-90-15:Sc so-140 0.0E*00 4.?E-04 1.4E-03 08329 STP-AP-035-03-28-90-10:0c Ba-140 -3.9E-03 2.3E-03 6.8E-03 09075 STP- AP "*-09-05-90-14:Oc so-140 8.6E-05 2.1E-04 7.2E-04 08330 STP-AP-018-03-28-90-10:3e Ba-140 2.0E-03 1.9E-03 6.5E-03 09106 STP- AP *" 12 10:4c Ba-140 9.1E-05 2.6E-04 8.6E-04 08331 STP-AP-033-03-28-90-13:2e Ba-140 1.4E-03 1.PE-03 6.2E-03 09146 STP-AP
- 18-90-10:4c sa-140 -4.0E-04 4.9E-04 1.5E-03 08332 STP-AP-039-01-28-90-13:Oc Ba-140 -1.8E-03 2.2E-03 7.1E-03 09187 STP- AP
- 09-25-90-16:2c so-140 -2.1E-04 4.9E-04 1.6E-03
- 08335 Si?- AP-037-03-28-90-12:4c Ba-140 2.3E-04 2.3E-03 7.7E 03 09226 STP AP
- 02-00-14:1c Be-140 -6.1E-04 5.6E-04 1.7E-03 08334 STP AP '7-03-28-90-12:1c Ba-140 -4.2E-04 1.8E-03 6.0E 03 09229 STP AP-035-09-25-90-10:2c Ba-140 -1.2E-03 1.5E-03 4.7E-03 08335 STP-AP-016-03-28-90-12:1c Ba-140 4.4E-04 2.1E-03 6.9E-G3 09230 STP AP-018-09-25-90-11:1c Ba-140 -6.1E-04 1.4E-03 4.6E-03 08336 STP-AP-001-03-28-90-12:Oc Ba-140- 4.0E-03 2.7E-03 9.7E-03 09231 STP-AP 033-09-25-90-12:1c so-140 -2.1E-04 1.5E-03 4.8E-03 08337 STP-AP-006-03-28-90-11:dc Ba-140 5.0E-03 2.6E-03 9.4E-03 09232 STP-AP-039-09-25-90-12:3c Ba-140 -3.8E-03 2.2E-03 6.5E-03 08338 STP-AP-006-03-28-90-11:dc Ba-140 2.3E-03 3.0E-03 1.0E-02
- 09233 STP- AP-037-09-25-90-13:Oc Be-140 -8.?E 04 2.0E-03 6.6E-03 08369 STP-AP ***-04-10-90-14:4c Be-140 - 2.4E - 04 3.8E-04 1.2E-03 09234 STP-AP-015-09-25-90-16:2c Ba-140 4.2E-03 1.9E-03 7.1E-03 08393 STP-AP ***-04-19-90-16:Oc Ba-140 6.0E-05 3.7E-04 1.0E-03 09235 STP-AP-016-09-25-90-16:2c Ba-140 -1.1E-03 1.5E-03 4.7E-03 0S446 STP-AP ***-04-26-90-14:2c Ba-140 -7.50-05 3.8E-04 1.?E-03 09236 STP-AP-001-09-25-90-16:2c Ba-140 5.5E-04 1.3E-03 4.5E-03 08472 STP-AP
- 02-90-15:2c 8s-140 -3.7E-04 5.4E-04 1.7E-03 09237 STP-AP-006-09-25-90-15:cd Ba-140 2.4E-03 1.3E-03 4.7E-03 08498 STP-AP ***-05-08-90-13:2c Ba-140 -5.0E-04 4.7E-04 1.5E-03 09238 STP-AP-006-09-25-90-15:cd Be-140 1.9E-03 2.0E-03 6.9E-03 08526 STP- AP "*-05-16-90-14:5c Ba-140 3.4E-04 3.7E-04 1.3E-03 09277 STP-AP * -10 11-90-15:2c Ba-140 9.6E-05 2.3E-04 7.7E-04 08569 STP-AP " 24-90-14:4c Ba-140 5.1E-04 3.4E-04 1.2E-03 09329 STP-AP
- 18-90-16:4c Be-140 4.0E-04 1.5E-03 4.9E-03 08593 STP-AP ***-05-30-90-15:Oc Ba-140 2.8E-04 1.9E-04 6.6E-04 09370 STP-AP
- 24-90-15:Sc Be-140 -1.8E-04 1.8E-04 5.9E-04 08632 STP-AP
- 06-90-14:5c Ba-140 3.4E-04 5.0E-04 1.7E-03 09402 STP-AP
- 29-90-16:2c Ba-140 4.9E-04 4.3E-04 1.5E-03 l 0*L61 STP-AP ***-06-12 90-16:1c so-140 -1.1E-04 5.1E-04 1. 7E -03 09454 STP-AP
- 06-90-15:1c sa-140 2.1E-04 2.4E-04 8.1E-04
! 08704 STP-AP-015-06-20-90-13:59 Ba-140 -4.6E-04 1.6E-03 5.3E-03 09485 STP-AP ***-11-13-90-15:Oc sa-140 -1.0E-04 2.9E-04 9.3E-04 l 08710 STP-AP
- 20-90-14:3c Ba-140 3.4E-04 3.5E-04 1.2E-03 09509 STP AP *"-11-19-90-14:2c sa-140 -4.4E-04 6.2E-04 2.0E-03 l 08740 STP-AP
- 25-90-14:3c 8a-140 7.4E-05 6.6E-04 2.2E-03 09531 STP-AP
- 26-90-14:2c sa-140 -5.5E-04 2.8E-04 8.8E-04 08778 STP- AP *-07-02-90-14:3c Ba-140 2.4E-04 2.9E-04 9.7E-04 09568 STP-AP
- 03-90-17:1c Ba-140 -3.7E-04 2.6E-04 7.9E-04 08804 STP- AP "-07-09-90-15:4c Ba-140 -1.6E-04 3.4E-04 1.1E-03 09594 iTP-AP ***-12-10-90-10:1c so-140 -2.6E-04 5.1E-04 1.6E-03 08805 STP-AP-035-06-25-90-10:1c 8s-140 2.4E-03 2.3E-03 8.0E-03 09627 STP-AP ***-12-18-90-15:4c sa-140 7.3E-04 3. 7E-04 1.3F-03 08806 STP-AP-018-06-25-90-10:5c Ba-140 -7.8E-04 2.7E-03 8.8E-03 09682 STP-AP " *-12-28-90-14:Oc sa-140 4.?E-05 3.3E-04 1.1E-03 OFA07 STP-AP-033-06-25-90-11:1c Ba-140 2.3E-03 2.3E-03 7.9E-03 09701 STP-AP-035-12-28-90-10:0c Sa-140 1.2E-03 1.?E-03 4.0E-03 08808 STP-AP-039-06-25-90-12:Oc sa-140 3.8E-03 2.5E-03 9.0E-05 09702 STP-AP-018-12-28-90-10:3c Ba-140 8.7E-04 2.1E-03 6.8E-03
- 08809 ST P- AP-037-06-25-90-14:3c sa-140 -5.8E-03 3.1E-03 9.2E-01 09703 STP-AP-033-12-21-90-09:5c Be-140 2.7E-03 2.2E-03 7.4E-03 08810 STP-AP-015-06-25-90-12:2c Ba-140 4.3E-03 3.0E-03 1.0E-02 09704 STP-AP-039-12-28-90-12:3c 8a-140 4.7E-04 2.0E-03 6.8E-03 08811 STP-AP-016-06-25-90-12:2c Ba-140 1.1E-03 2. 7E -03 9.0E-03
- 09705 ST P - AP-037 28-90-13:Oc Be-140 1.2E-03 1.3E-03 4.3E-03 08812 STP-AP-001-06-25-90-12:3c Ba-140 3.8E-03 2.3E-03 7.9E-03 09706 STP-AP-015-12-?d-90-13:1c Ba-140 1.9E-03 2.3E-03 7.9E-03 08813 STP-AP-006-06-25-90-13:dc Ba-140 2.7E -03 2.3E-03 7.8F-03 09707 STr-AP-016-12-28-90-13:2c sa-140 3.0E -03 2.1E-03 7.5E-03 03814 STP-AP-006-06-25-90-13:dc Ba-140 -5.8F-04 2.0E 03 6.5F-03 09708 STP-AP-001-12-28-90-13:2c sa-140 2.9E-03 2.4F-03 8.6E-03
- Omom toctrot locatiom Pam 1-71 i
ADDENDUM 1 STPEGB REMP RESULTS DATA - 1990 AIRBORNE PARTICULATE AIRBORNE PARTICULATE LAB SAMPLE RESUtT 1 SICMA TAB SAMLE RESULT 1 SIGMA NtNSER SAMPLE StmMISSION CODE ANALYSl$ pCi/M'3 ERROR ILD tlUMBER SAMPt1E SUBMISSION CODE ANAtTS!S pCi/M*3 EPROR LLD 09709 STP-AP-006-12-28-90-14:cd es-140 1.9E-03 2.5E-03 8.7E-03 08806 STP-AP-018-06-25-90-10:Sc to-140 2.4E-03 1.3E-03 5.1E-03 09710 STP-AP-006-12-28-90-14:cd Ba-140 4.'*E-04 2.8E-03 9.2E-03 08807 STP-AP 033-06 25-90-11:1c La-140 -1.9E-03 1.3E-03 3.5E-03 07922 STP- AP *"-01 90-13:3c in-140 -4.2E-05 2.0E-04 6.4E-04 08808 STP-AP-039-06-25-90-12:Oc ta-140 1.2E-03 1.3E-03 4.8E-03 07944 STP-AP
- 09-90-14:2c to-140 1.8E-04 1.9E-04 7.00-04
- 08809 STP-AP-037-06-25-90-14:3c to-140 -6.7E-04 1.6E-03 4.9E-03 07978 STP- AP ***-01-17-90-15:Oc ta-140 -4.3E-04 2.0E-04 4.9E-04 08810 $1P-AP-015-%-25-90-12:2c La-140 -T.1E-03 8.4E-04 2.2E-03 08009 STP-AP ***-01-24-90-16:Oc ta-140 -9.5E-05 2.3E-04 7.4E-04 08811 STP-AP-016-06-25-90-12:2c la-140 - 1. 7E - 03 1.5E-03 4.3E-03 08035 STP-AP *'*-01-31-90-14:2c ta-140 -1.5E-04 2.2E-04 6.9E-04 08812 STP-AP-001-06-25-90-12:3c ta-140 2.1E-03 1.1E-03 4.1E-03 08065 STP-AP *"-02-06-90-16:4c La-140 -6.1E-05 3.1E-04 9.9E-04 08813 STP-AP-006-06-25-90-13:dc ta-140 1.0E-03 9.7E-04 3.5E-03 08098 STP-AP ***-02-15-90-14:5c La-140 4.5E-05 1.7E-04 5.9E-04 08814 SIP-AP-006-06-25-90-13:dc ta-140 -2.0E-03 9.5E-04 2.6E-03 08136 STP- AP *"-02-21-90-15:3c ta-140 -6.6E-04 4.1E-04 1.0E-03 08852 STP- AP "* 18-90-15:Sc La-140 1.5E-04 1,8E-04 6.3E-04 08163 STP- AP "*-02-28-90-14:3c La-140 -1.5E-04 2.2E-04 6.5E-04 08896 STP- AP ***-07 23-90-13:3c to-140 -9.8E-05 1.7E-04 5.4E-04 08191 STP- AP ***-03-07-90-14:3c La-140 -5. 7E - 04 2.0E-04 4.1E-04 08908 ST P- AP *"-07-31 15 :2c La-140 -3.6E-04 1.6E-04 4.2E-04 08244 SfP-AP " *-03-15-90-13:1c to-140 4.20-05 1.8E-04 6.1E-04 08968 STP- AP "*-08-08-90-14:0c to-140 3.6E-05 6.6E-05 2.2E-04 08266 STP-AP "*-03-21-90-16:3c to-140 8.5E-05 2.0E-04 6.9E-04 08996 STP-AP ***-08-14-90-16:0c te-140 0.0E*00 1.6E-04 5.2E-04 08298 STP- AP "*-03-28-90-13:2c La-140 1.6E-04 1.9E-04 6.9E-04 09021 STP- AP *"-08-22-90-13:1c te-140 2.5E-04 1.8E-04 6.6E-04 08324 STP- AP *"-04-03-90-14:4c ta-140 -5.7E 05 2.8E-34 9.2E-04 09033 STP- AP *"-08-28-90-15:5c ta 140 -3.7E-04 2.4E-04 6.6E-04 08329 STP-AP-035-03-28-90-10:Oc ta-140 -1.2E-03 1.3E-03 3.BE-03 09075 STP- AP *"-09-05-90-14:Oc ta-140 6.0E-05 1.0E-04 3.6E-04 08330 STP-AP-018-03-28-90-10:3c to-140 6.2E-04 8.5E 04 3.1E-03 09106 STP- AP *" 12-90-10:4c La-140 -3.8E-05 f.4E-04 4.4E-04 08331 STP-AP-033-03-28-90-13:2c La-140 1.2E-03 1.1E-03 4.lE-03 09146 SfP-AP ***-09-18-90-10:4c La-140 1.6E-04 2.5E-04 8.9E-04 08332 STP-AP-039-03-28-90-13:0c to-140 3.4E-03 1.4E-03 2.9E 03 09187 STP-AP ***-09-25-90-16:2c La-140 2.8E-04 2.1E-04 8.1E-04 o 08333 STP-AP-037-03-28-90-12:4c ta-140 -1.8E-03 1.1E-03 3.0E-03 09226 STP AP "*-10 02-90-14:1c ta-140 0.0E*00 2.9E-04 9.7E-04 08334 STP-AP-015-03-28-90-12:1c ta-140 1.1E-03 7.2E-04 2.9E-03 09229 $1P-AP-035-09-25-90-10:2c to-140 - 7. 7E - 04 7.5E-04 2.2E-03 08335 STP-AP-016-03-28-90-12:1c ta-140 1.3E-03 1.1E-03 4.0E-03 09230 STP-AP-018 09 25-90-11:1c ta-140 - 7. 5E - 04 6.5E-04 1.9E-03 08336 STP-AP-001-03-28-90-12:Oc ta-140 0.0E+00 1.6E-03 5.3E-03 09231 STP-AP-033-09-25-90-12:1c to-140 0.0E+00 6.BE-04 2.2E-03 08337 STP-AP-006-03-28-90-11:dc ta-140 1.4E-03 1.2E-03 4.5E-03 09232 51P-AP-039-09-25-90-12:3c ta-140 -1.5E-03 1.2E-03 3.3E-03 08338 STP-AP-006-03-28-90-11:dc to-140 3.2E-04 1.7E-03 5. 7E - 03
- 09233 $1P- AP-037 25-90-13:Oc to-140 6.0E-04 9.6E-04 3.4E-03 08369 STP-AP ***-04-10-90-14:4c La-140 1.3E-04 2.CE-04 7.1E-04 09234 STP-AP-015-09-25-90-16:2c ta-140 8.4E-04 8.4E-04 3.1E-03 08393 STP- AP "*-04-19-90-16:Oc to-140 -5.9E-05 1.5E-04 4.8E-04 09235 STP-AP-016 09-25-90-16:2c ta-140 -1.6E-03 8.4E-04 2.4E-J3 08446 STP- AP *"-04-26 14:2c La-140 1.5E-04 2.1E-04 7.4E-04 09236 STP AP-001-09-25-90-16:2c te-140 1.9E-04 5.5E-04 1.9E-03 08472 STP-AP ***-05-02-90-15:2c to-140 1.4E-04 2.7E-04 9.4E-04 09237 STP-AP-006-09 25-90-15:cd te-1@ 1.2E-03 7.3E-04 2.7E-03 08498 STP-AP ***-05-08-90-13:2c ta-140 4. 7E-04 3.4E-04 1.2E-03 09238 STP-AP-006-09-25-90-15:cd ta-140 1.3E-03 1.1E-03 4.OE-03 08526 STP-AP ***-05-16-90-14:Sc to-140 7.4E -05 1.9E-04 6.4E-04 09277 ST P- AP *** 11 15 :2c to-140 2.3E 04 1.2E-04 4.4E-04 08569 STP-AP ***-05-24-90-14:4c La-140 3.6E-05 1.5E-04 5.0E-04 09329 STP- AP "*-10-18-90-16:4c La-140 -1.5E-04 7.3E-04 2.3E-03 08593 STP- AP "*-05-30-90-15:Oc La-140 2.1E-05 8.7E-05 3.0E-04 09370 STP-AP
- 24-90-15:5c to-140 6.3E-05 8.4E-05 3.0E-04 08632 STP-AP ***-06-06-90-14:5c La-140 3.9E-04 2.9E-04 1.1E-03 09402 STP-AP ***-10-29 90-16:2c La-140 -1.3E-04 2.0E-04 6.4E-04 08661 STP-AP ***-06-12-90-16:1c ta-140 -1.1E-04 2.6E-04 8.1E-04 09454 SYP-AP ***-11-06-90-15:1c to-140 1.1E-04 1.4E-04 4.9E-04 08704 STP-AP-015-06-20-90-13:59 ta-140 1. 7E -04 8.3E-04 2.8E-03 09485 STP - AP "* 13-90-15:0c in-140 -2.2E-05 1.3E-04 4.4E-04 08710 STP-AP ***-06-20-90-14:3c to-140 1.8E-04 1.7E-04 6.1E-04 09509 STP- AP "* 11 90- 14:2c ta-140 -3.2E-04 3.2E-04 9.8E-04 08740 STP-AP " *-06-25-90-14:3c to-140 -2.5E-04 3.5E-04 1.0E-03 09531 STP-AP ~ -11 26-90-14:2c to-140 -2.1E-04 1.4E-04 4.1E-04 08778 STP- AP "*-07-02-90-14:3c to-140 1. 7E- 04 1.5E-04 5. 3E -04 09568 STP AP *"-12-03-90-17:1c to-140 -1.1E-04 1.2E-04 3.5E-04 08804 S1P- AP ***-07-09 15 :4c La-140 0.OE+00 1.PE-04 6.1E-04 09594 Sir- A? *" 10-90-10:1c La-140 8.0E-04 3.2E-04 1.3E-03 OMOS STP-AP-035-06-25-90-10:1c ta-140 -1.7E-03 1.3E-03 3.7E-03 0 % 27 ST P - AP "* 18 15:4c ta-140 5.2E-04 1.9E-04 7.6E-04
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ADDENDUM 1 STPEGS REMP RESULTS DATA 1990 AIR IODINE AIR IODINE LAB SAMPLE RESULT 1 S10MA RESUtf 1 StGMA L49 SAMPLE tto MUMBER SAMPLE StmMISSION ETE ANALYSIS pCi/M'3 E##0e LLD WUMBER SAMPLE StieMISS104 EmE ANALYSIS PCi/M 3 ERROR
- 08146 ST P- A t -037-02-28-90-13:34 t-131 -1.1E-02 3.8E-03 1.2E-02 08016 STP-At-033-01-31-90-11:47 .1-131 - 7. 0E - 03 3.7E-03 1.1E-02 08147 STP-Al-015-02-28 90-13:53 1-131 4.4E-03 2.6E-03 8.9E-03 08017 STP-Al-039-01-31-90-12:53 1-131 -6.7E-03 3.5E-03 1.1E-02 8.7E-03 08148 STP-Al-016-02-28 90-13:59 I-131 4.3E-03 2.5E-03
- 08018 STP-At-037-01-31-90-13:24 t-131 -6.9E-03 3.6E-03 1.1E-02 08149 STP-AI-001-02-28-90-14:05 I-131 4.3E-03 2.5E-03 8.7E-03 08019 STP-Al-015-01-31-90-13:49 t-131 1.1E 03 2.0E-03 6.6E-05 8.7E-03 G8150 STP-At-006-02-73 90-14:3d 1-131 4.3E-03 2.5E-03 08020 STP-Al-016-01-31-90-14:00 1-131 1.?E-03 2.2E-03 7.5E -03 08151 STP-Al-006-02-28 90-14:3d t-131 4.2E-03 2.5E-03 8.4E-03 08021 STP-At-001-01-31-90-14:14 1-131 1.1E-03 2.0E-03 6.6E-03 1.3E-02 08170 STP-Al-035-03-07-90-10:06 I-131 3.6E-03 3.9E-03 08022 STP-Al-006-01-31-90-14:2d 1-131 1.00-03 1.9E-03 6.4E-03 1.3E-02 08171 STP- A l-018-03 90- 10:37 I-131 3.6E-03 3.9E-03 08023 STP-Al-006 01-31-90-14:2d 1-131 1.1E-03 2.0E -03 6.6E-03 1.4E-02 08172 STP-Al-033-03-07-90-11:06 t-131 3.7E-03 4.0E-03 08044 STP-Al-035-02 06-90-10:01 1-131 -1.6E-03 2.1E-03 6.8E-03 1.3E-02 08173 STP- Al-039-03-07-90-11:43 1-131 3.6E-03 3.9E-03 08045 STP-Al-018-02-06-90-10:30 I-131 -1.6E-03 2.1E-03 6.8E-03 3.9E-03 f.3E-02 6.6E-03
- 08174 S T P- Al -037-03-07-00-12:11 1-131 3.6E-03 08046 STP-Al-033-02-06-90-10:58 I-131 -1.5E-03 2.1E-03 7.5E-03 2.9E-03 1.0E-02 6.6E-03 08175 Sio- A l-015-03-07 12:31 1-131 08047 STP-Al-039-02-06-90-11:51 1-131 -1.5E-03 2.1E-03 7.5E-03 2.9E-03 1.0E-02 6.6E-03 08176 STP-Al-016-03-07-90-12:36 1-131
- 08048 STP-Al-037-02-06-90-12:16 t-131 -1.5E-03 2.1E-03 7.3E-03 2.BE-03 1.0E-02 1.4E-02 08177 STP- Al-001 07-90-12:39 I-131 08049 STP-Al-015-02-06-90-12:36 1-131 -6.4E-05 4.5E-03 7.5E-03 2.9E-03 1.0E-02 1.0E-02 3.?E 02 C8178 STP-AI-006-03-07-90-12:5d I-131 08050 STP-At-016-02-06-90-12:41 1-131 -1.4E-02 1-131 7.5E-03 2.9E-03 1.0E-02 I-131 -6.?E-03 4.3E-03 1.4E-02 08179 STP Al-006-03-07-00-12:5d 08051 STP-Al-001-02-06-90-16:47 08223 STP-Al-035-03-15-90-13:18 t-131 -1.3E-03 3.?E-03 1.0E-02 08052 STP-Al-006 02-06-90-15:3d I-131 -6.4E-05 4.5E-03 1.4E-02 1.0E-02 08224 STP-Al-018-03-15-90-12:50 1-131 -1.3E-03 3.?E-03 08053 STP-Al 006-02-06-00-15:3d 1-131 -6.2E-03 4.4E-03 1.4E-02 1.0E-02 08225 STP-Al-033-03-15-90-12:24 1-131 -1.3E-03 3.2E-03 08077 STP-Al-035-02-15-90-10:09 I-131 -3.4r-05 3.4E-03 1.1E-02 1.1E-02 08226 STP-Al-039-03-15-90-12:03 1-131 -1.3E-03 3.2E-03 08078 STP-Al-018-02-15 90-10:38 1-131 -3.4E-03 3.5E-03 1.1E-02 1.1E-02
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- 08249 STP-AI-037-03-21-90-16:20 1-131 0.0E + 00 08117 STP-Al-033-02-21-90-11:03 1-131 -8.8E-03 7.1E-03 8.0E-04 3.1E-03 1.0E-02 2.?E-02 02250 STP-Al-015-03-21-90-16:02 1-131 08118 STP-Al-039-02-21-90-11:45 1-131 -8.6E-03 6.9E-03 t-131 7.BE-04 3.0E-03 1.0E-02 1-131 -8.BE-03 7.0E-03 2.2E-02 08251 STP-At-016-03-21-90-15:55
- 08119 STP-Al-037-02-21-90-12:13 08252 STP-Al-001-03-21-90-15:44 t-131 8.0E-04 3.1E-03 1.0E-02 STP-Al 015-02-21-90-15:14 1-131 -4.4E-03 3.TE-03 1.2E-02 1.0E 08120 08253 STP-Al-006-03-21-90-14:2d 1-131 7.9E - 04 3.1E-03 STP- Al-016-02-21-90-15:22 1-131 -4.4E-03 3.6E-03 1.2E-02 1.0E-02 08121 08254 STP-Al-006-03-21-90-14:2d -131 7.9E-04 3.1E-03 08122 STP-Al-001-02-21-90-15:34 I-131 -4.5E-03 3. 7E-03 1.2E-02 3.6E-03 1.2E-02 1.2E-02 08277 STP-At-035-03-28-90-10:05 l-131 -3.3E-03 08123 STP-At-006-02-21-90-14:1d t-131 -4.5E-03 3.8E-03 -3.2E-03 3.5E-03 1.1E-02 1.2E 02 08278 STP Al-018-03-28-90-10:30 1-131 08124 STP- Al- 006-02-21 14:2d 1-131 -4.5E-03 3.8E-03 t-131 -3.1E-03 3.4E-03 1.1E-02 1-131 -1.1E-02 3.8E-03 1.2E-02 08279 STP-Al-033-03-28-90-13:29 08142 STP-Al-035-02-28-90-10:20 08280 STP-Al-039-03 28-90-13:06 1-131 -3.2E-03 3.5E-03 1.1E-02 STP-Al-018-02-28-90-11:47 1-131 -1.1E-02 3.8E-03 1.2E-02 1.2E-02 08143
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