ML20073D001

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Annual Radiological Environ Operating Rept 1990
ML20073D001
Person / Time
Site: LaSalle  Constellation icon.png
Issue date: 12/31/1990
From: Diederich G
COMMONWEALTH EDISON CO.
To: Davis A
NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III)
References
NUDOCS 9104260109
Download: ML20073D001 (131)


Text

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mm:nw alth Edison:-- .

!yr = ' : LaSalle County Nuclear Station * * *

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{ i' - A Rural Route #1, Box 220 s f - Marseilles,ll!inois 61341'-

_ /zfTelephone 815/B57 6761 -

i April 1, 1991 Mr.-Bert Davis '

Administrato'r'-

Nuclear Regulatory Connission. Region III 799-Roosevelt-Road- -

Glen-Ellyn, Illinois 60137

Dear Mr. Davis:

1 Enclosed -is the 1990: Annual : Radiological Environmental  :

Operating. Report--for LaSalle ' County Nuclear Power- Station, 3 Docket -Numbers 373 Eand 374. ' This ' report contains the results of L the- Radiological Environmental: and Meteorologica1' Moni to-1 ng - Programs .- 3
Two. copies of ~ the a eport - are - provided for your -use. .Two

,  ;; copies---wil1 be forwarded - to, the' Document Control Desk .and one

' <4 -copy.to-the Resident Inspector.

Sincerely; 1

3- ,

l, j0mk
  • G. J. Clederich- -i

' Station Manager.

LaSalle County Stationi GJD/KFK/djf' enclosure-Ecc: Station File

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01 373 PDR [

I e LAS ALLE COUNTY STATION ANNUAL R ADIOLOGIC AL ENVIRONMENT AL OPER ATIN G REPORT 1990 i

M A R C H 19 91

TABLE OF CONTENTS Page INTRODUCTION .......................... 1

SUMMARY

. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 1.0 EFFLUENTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 1.1 Gaseous .......................... 3 1.2 Liquid . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 2.0 SOLID RADI0 ACTIVE WASTE , , . . . . . . . . . . . . . . . . . . . 3 3.0 00SE TO MAN . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 3.1 Gaseous Ef fluent Pathways ................. 3 3.2 Liquid Ef fl uent Pathways . . . . . . . . . . . . . . . . . . 5 3.3 Di rect R ad i a ti on . . . . . . . . . . . . . . . . . . . . . . 5 4.0 SITE METEOROLOGY ........................ 6

.5.0 ENVIRONMENTAL MONITORING .................... 6 5.1 Gamma Radiation ...................... 6 5.2 Airborne 1-131 and Particulate Radioactivity . . . . . . . . 7 5.3 Terrestrial Radioactivity ................. 7 5.4 Aquatic Radioactivity ................... 7 5.5 Milk............................ 8 5.6 Sample Collections .................... 8 5.7 Prog ram Mod i fi ca t i on . . . . . . . . . . . . . . . . . . . . 8 6,0- ANALYTICAL PROCEDURES . . . . . . . . . . . . . . . . . . . . . . 8 7.0 MILCH ANIMALS AND NEAREST CATTLE CENSU3ES . . . . . . . . . . . . 8 8.0 NEAREST RESIDENCES CE NSUS . . . . . . . . . . . . . . . . . . . . 9 9 ,0 INTERLABORA'ORY COMPARIS0N PROGR AM RESULTS ........... 9 t

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l TABLE OF CONTENTS (continued)

Page APPENDIX 1 - DATA TABLES AND FIGURES . . . . . . . . . . . . . . . . . . 10 Station Releases Tabl e 1.1-1 Gaseous Effluents .................. 11 Table 1.2-1 Li qui d Ef fl ue nt s . . . . . . . . . . . . . . . . . . . 13 Table 2.0-1 Solid Waste Shipments ................ 17 Figure 3.1 Figure 3.1-4.

Isodose and Concentration Contours ......... 25 Table 3.1-1 Maximum Doses Resulting f rom Airborne Releases . . . - . 29 Table 3.2-1 Maximum Doses Resulting from Liquid Discharges . . . . 31 Environmental Monitoring Figure 5.0 Figure 5.0-4 Locations of Environmental Radiological Stations . . . 33 Table 5.0-1 Environmental Radiological Monitoring Sampling Sites ................. 37 Table 5.0-2 Environmental Radiological Monitoring Program . ... 38 Table 5.0 Table 5.0-6 Environmental Summary Tables . . . . . . . . . . . . . 44 Table 5.1-1 Gamma Radiation Measurements (TLD) . . . . . . . . . . 50 APPENDIX 11 - METEOROLOGICAL DATA ................... 54 APPENDIX 111 - LISTING 0F MISSED S AMPLES . . . . . . . . . . . . . . . . 83 APPENDIX IV - MILCH ANIMALS, NEAREST CATTLE, AND NEAREST RESIDENCES CENSUS .................... 85 APPENDIX V - INTERLABORATORY COMPARIS0N PROGRAM RESULTS. . . . . . . . . 90 i

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INTRODUCTION LaSalle Station, a two-unit BWR plant is located near Marseilles, Illinois, in LaSalle County, 3.5 miles south of the Illinois River. Each reactor is designed to have a capacity of 1078 MW net. Unit No. 1 loaded fuel in March 1982. Unit No. 2 loaded fuel in late December 1983. The plant has been designed to keep releases to the environment at levels below those specified in the regulations.

Liquid ef fl uents from LaSalle County Station are released to the Illinois River in controlled batches after radioassay of each batch. Gaseous effluents are released to the atmosphere af ter delay to pennit decay of short half-life gases. Releases to the atmosphere are calculated on the basis of analyses of routine grab samples of noble gases and continuously collected composite samples of iodine and particulate matter. The results of effluent analyses are sumarized on a monthly basis and reported to the Nuclear Regulatory Commission as required per Technical Specifications. Airborne concentrations of noble gases, 1-131 and particulate radioactivity in offsite areas are calculated using effluent and meteorological data.

Environmental monitoring is conducted by sampling at indicator and reference (control). locations in the vicinity of the LaSalle County Station to measure changes in radiation or radioactivity levels that may be attributable to plant operations. _ If significant changes attributable to LaSalle County Station are measured, these changes are correlated with effluent releases. External ganna radiation exposure from noble gases and 1-131 in milk are the most critical pathways at this site; however, an environmental monitoring program is conducted which includes other pathways of less importance.

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SUMMARY

Gaseous and liquid effluents for the period remained at a fraction of the Technical Specification limits. Calculations of environmental concentrations based on effluent, Illinois River flow, and meteorological data for the period indicate that consumption by the public of radionuclides attributable to the plant are well below the regulatory limits. Radiation exposure from radio-nuclides released to the atmosphere represented the critical pathway for the period with a maximum individual dose estimated to be 2.15E-04 mrem for the year, when a shielding- and occupancy f actor of 0.7 is assumed. The assessment of radiation doses is performed in accordance with the Offsite Dose Calcula-tion Manual (00CM). The results of analysis confirm that the station is operating in compliance with 100FR50 and 40CFR190.

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i 1.0 EFFLUENTS 1.1 Gaseous Effluents to the Atmosphere Measured concentrations of noble gases, radioiodine, and particulate radioactivity released to the atmosphere during the year, are listed in Table 1.1-1. A total of 6.87E+02 curies of fission and activa-tion gases was released with an average release rate of 7.55E+01 pCi/ sec .

A total of 2.17E-03 curies of 1-131 was released during the year, with an average release rate of 1.75E-04 pCi/sec for all iodines.

A total of 1.27E-03 curies of beta-gamma emitters were released as airborne particulate matter, with an average release rate of 2.11E-04 pCi/sec. Alpha emitting radionuclides were not measurable.

A total of 1.70E-01 curies of tritium was released, with an average release rate of 8.37E-03 pCi/sec.

1.2 Liquids _ Released to the Illinois River A total of 4.07E+05 liters of radioactive liquid waste (prior to dilution) containing 2.46-02 curies (excluding tritium, gases, and al pha) were discharged after dilution wi th a total of 3.12E+08 liters of water. These wastes were released at a quarterly average concentration of 2.05E-06 pCi/ml, discharged on an unidentified nuclide basis. A total of 2.08E-01 curies of alpha radioactivity and - 3.74E-01 curies of tritium were released. Quarterly release estimates in liquid effluents are given in Table 1,2-1.

2.0 SOLID RADI0 ACTIVE WASTE Solid radioactive wastes were shipped by truck to Oak Ridge, Tennessee; Beatty, Nevada; Waltz Mill, Pennsylvania; Barnwell Nuclear Center, South Carolina; and Channahon, Illinois. The record of waste shipments is sunnarized in Table 2.0-1.

3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways Gamma Dose Rates Gamma air and whole body dose rates offsite were calculated based on measured release rates, isotopic composition of the noble gases, and meterological data for the period (Table 3.1-1). Isodose contours of whole body dose are shown in Figure 3.1-1 for the year.

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- . - - - . . _ - -~__--. --._-_ - ___ _ - ___

I Based on measured ef fl uents and meteorological data, the maximum dose to an individual would be 2.15E-04 mrem for the year, with an occupancy or shielding factor of 0.7 included. The maximum gamma air dose was 4.08E-04 mrad.

Beta Air and Skin Rates The range of beta particles in air is relatively small (on the order of a few meters or less); consequently, plumes of gaseous effluents may be considered " infinite" for purpose of calculating the dose from beta radiation incident on the skin. However, the actual dose to sensitive skin tissues is difficult to calculate because this depends on the beta particle energies, thickness of inert skin, and clothino covering sensitive tissues. For purposes of this report the skin is taken to have a thickness of 7 mg/cm2 and an occupancy factor of 1.0 is used. The skin dose from beta and gamma radiation for the year was 1.25E-03 mrem. The maximum of fsite beta air dose for the year was 1.41E-03 mrad.

The air concentrations of radioactive noble gases at the offsite receptor locations are given in Figure 3.1-2.

Radioactive Iodine The human thyroid exhibits a significant capacity to concentrate ingested or inhaled iodine, and the radioiodine , 1-131, released during routine operation of the plant, may be made available to man thus resulting in a dose to the thyroid. The principal pathway of interest for this radionuclide is ingestion of radioiodine in milk by an infant.

Iodine-131 Concentrations in Air The calculated concentration contours for 1-131 in air are shown in Figure 3.1-3. Included in these calculations is an iodine cloud depletion factor which accounts for the phenomenon of el emental iodine deposition cn the ground. The maximum offsite concentration is estimated to be 3.43E-04 pCi/m3 for the year.

Dose to Infant's Thyroid The hypothetical thyroid dose to an inf ant living near the plant via ingestion of milk was calculated. The radionuclide considered was 1-131 and the source of milk was taken to be the nearest dairy farm with the cows pastured from May to October. The maximum inf ant's thyroid dose was 3.64E-03 mrem during the year (Table 3.1-1).

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Concentrations of Particulates in Air Concentration contours of radioactive ai rborne particulates are shown in Figure 3.1-4. The maximum offsite level is estimated to be 1.44E-05 pCi/m3 Summary of Doses Table 3.1-1 sumarizes the doses resulting from releases of airborne radioactivity via the different exposure pathways.

3.2 Liquid Effluent Pathways _

The three principal pathways through the aquatic environment for potential doses to man from liquid waste are ingestion of potable water, eating aquatic foods, and exposure while walking on the

,norel i ne . Not all of these pathways are applicable at a given time or statien but a reasonable approximation of the dose can be made by adjusting the dose formula for season of the year or type and degree of use of the aquatic environment. NRC* developed equations were used to calculate the doses to the whole body, lower G1 tract, thyroid, bone and skin; specific parameters for use in the equations are given in the Commonwealth Edison Offsite Dose Calcu-lation Manual. The maximum whole body dose for the year was 4.18E-05 mrem and no organ dose exceeded 3.24E-05 mrem.

3.3. Direct Radiation In section 3/4.11 of the LaSalle Technical Specifications, 40CFR190 calculations of total dose due to the Uranium fuel Cycle are required only when calculated doses from liquid or gaseous releases of radio-activity exceed certain levels. These levels are twice the following limits :

o The RETS limits on dose or dose commitment to an individual due to radioactive materials in liquid ef fluents f rom each reactor unit (1.5 mrems to the whole body or 5 mrem to any organ during any calendar quarter; 3 mrem to the whole body or 10 mrem to any organ during any calendar year).

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i a The RETS-limits on air dose in noble gases released in gaseous ef fluents to a member of the public f rom each reactor unit (5 mrad for gamma radiation or 10 mrads -

for beta radiation during any calendar quarter; 10 mrads for gamma radiation or 20 mrad for beta radiation during any calendar year).

o The RETS limits on dose to any individual due to iodine-131, iodine-133, tritium, and radionuclides in particulate form with half-lives greater than eight days in gaseous effluents released from each reactor unit (7.5 mrems to any organ during any calendar quarter; 15 mrems to any organ during any calendar year).

During the period January-to December,1990, LaSalle County Station did not exceed these criteria, and members of the public (occasional visitors to the site) did not exceed these criteria either when onsite.

4.0 SITE METEOROLOGY A sumary of the site meteorological measurements taken during each quarter of the year is given in Appendix 11. The data are presented as cumulative joint frequency distributions of 375' and 33' levels. Data recovery for these measurements was about 98.9%.

5.0 ENVIRONMENTAL MONITORING Table 5.0-1 provides an outline of _the Radiological Environmental Moni-toring Prooram as required in the Technical Specifications. _ Tables 5.0-3 to 5.0-6 summarize data for the year. Except for tables of special interest, tables listing all data are no longer included in the annual repo rt . All data tables are available for inspection at the. Station or in the Corporate offices.

Specific findings for various environmental media are discussed below.

5.1 Gamma Radiation External radiation dose from onsite sources and noble gases released to the atmosphere was measured at ten indicator and four reference (background) -locations using CaSO4 :0y thermoluminescent dosimeters (TL0s). A comparison of the TLD results for reference stations with' onsite and offsite indicator stations is included in Table 5.1-1. A total of forty-eight additional TL0s were installed on June 1,1980 such that each sector was covered at both five miles and the site boundary. Six (6) TLD locations were added to the monitoring program on July 1,1985.

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l Quarterly external radiation dose at fourteen air sampling locations averaged 17.8 mR) and was similar to levels measured in 1986 (17.1 mR),1987 (17.8 mR),1988 (16.5 mR), and 1989 (17.6 mR) . The differences are not statistically significant.

5.2 Airborne 1-131 and Particulate Radioactivity Locations of the samplers are shown in Ngure 5.0-1. Airborne 1-131 remained below the LLD of 0.10 pCi/m4 throughout the year.

Gross beta concentrations ranged from 0.010 to 0.079 pCi/m3 and averaged 0.024 pCi/m3 and was slightly lower than in 1985 -(0.025 pCi/m3), 1986 (0.027, except for the period from May 16 through June 6 when it was influenced by the nuclear reactor accident at 1987 (0.027 pCi/m3), 1988 (0.031 pCi/m3), and 1989 Chernobyl),3 (0.028 pCi/m .

Gamma-emitting isotopes were blow the LLO level of 0.01 pCi/m3 in all quarterly composites.

No radioactivity attributable to plant operation was detected in any s ample .

5.3 Terrestrial Radioactivity Well- water was collected quarterly from one onsite well and five offsite wells and analyzed for tritium and gamma-emitting isotopes.

All results were below the limits of detection, indicating that there was no measurable amount of radioactivity due to the Station's releases.

5.4 Aquatic Radioactivity Weekly surface water samples from the Illinois River at Seneca and LSCS Cooling Lake were composited monthly and analyzed for gamma-emitting isotopes. Weekly samples from the sane locations were composited quarterly and analyzed for tritium. None of the com-posited samples indicated the presence of gamma-emitting isotopes above their respective LLD levels. Tritium was detected in five samples and ranged from 226 to 294 pCi/L. Similar results were obtained in 1988 and 1989.

Sediment samples were coll ected twice a year from one indicator location (downstream _ at Cooling Lake) and analyzed for gamma-emitters. Gamma-emitters were below their respective detection limits in all samples.

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f Levels of gamma radioactivity in fish were measured and found in all samples to be below the lower limits of detection for the program.

5.5 Milk Milk samples were collected monthly from November through April and weekly from May through October and analyzed for iodine-131 and gamma-emitting isotopes.

1-131 remained below the detection limit of 0.5 pC1/L.

Cs-134 and Cs-137 were below the LLD level of 5 pCi/L. All other gamma-enitting isotopes, except naturally-occurring K-40, were below their respective LLDs. There was no indication of the effect on the environment due to station operation.

5.6 Sample Collections All samples were collected as scheduled except those listed in the Listing of Missed Samples, Appendix 111.

5.7 Program Modifications Boldt Dairy (L-18) was replaced by Flatness Dairy. Gass Farm (L-20) was added to the program in November,1990; the additional dairy was not required by the ODCM but was added to the program to ensure that the program included at least four dairies.

6.0 ANALYTICAL PROCEDURES A sunnary of the procedures used for analyzing radioactivity in environ-mental samples is given in Appendix V of - the report for the period January - December 1988. Procedures used during the period covered by this report remained essentially unchanged.

7.0 - MILCH ANIMALS AND NEAREST CATTLE CENSUSES A census of milch animals was conducted within five miles of the station.

The survey was conducted by a " door-to-door" canvas and by information from Illinois Agricultural Agents. The census was conducted by A. Lewis on June 13 and 14, 1990. The nearest cattle census was conducted by A.

Lewis on July 10,11, and 12,1990.

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8.0 NEAREST RESIDENCES CENSUS A census of the nearest residences within a five (5) mile radius was conducted by A. Lewis on June 27, 1990.

Results of milch animals, nearest cattle, and nearest residence censuses are presented in Appendix IV.

9.0 INTERLABORATORY COMPARISON PROGRAM RESULTS Interlaboratory Comparison Program Results are presented in Appendix V.

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e APPENDIX 1 DATA ~ TABLES AND FIGURES 1

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TABLE 1.1-1 LASALLE COUNTY NUCLEAR POWER STATION UNITS ONE AND TWO DOCKET NUMBERS 50-373 AND $0-374 ETTLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

GASEOUS ErrLUENTS-SUMMATION Or ALL RELEASES First Second Quarter Quarter A. rission and Activation Gases

1. Total release ci 4.36E+00 4.20E-02
2. Average release rate for period uCi/see 1.85E+00 8.23E-02 B. Iodines
1. Total iodine-131 Ci 7.65E-04 5.64E-04
2. Average release este for period uCi/sec 3.12E-04 1.71E-04 O. Particulates
1. Particulates with T1/2 >8 days Ci 8.34E-04 1.80E-04
2. Average release rate for period uC1/sec 3.13E-04 2.20E-04
3. Gross alpha radioactivity

. Ci <1.00E-11 <1.00E-11 D. Tritium

1. Total release C1 0.00E+00 8.45E-03
2. Average release rate for period uC1/see <1.00E-06 1.07E-03

"<" indicates activity of sample is less than LLD given in uci/mi 11

TABLE 1.1-1(continued)

LASALLE COUNTY NUCLEAR POWER STATION UNITS ONE AND TWO DOCKET NUMBERS 50-373 AND 50-374 EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

GASEQUS EFFLUENTS-SUMMATION OF ALL RELEASES Third Fourth  :

Quarter Quarter A. Fission and Activation Gases

1. Total release Ci 6.74E+02 8.39E+00
2. Average release rate. for period uCi/sec 2.96E+02 4.23E+00 B. Iodines
1. Total iodine-131 C1 -3.21E 5.24E-04
2. Average release rate for period uC1/sec- 1.13E-04 1.02E C. Particulates
1. Particulates with T1/2 >8 days Ci 2.38E-04 1.70E-05 2.-Average release rate for period uCi/sec 2.54E-04 5.70E 3. Gross alpha radioactivity.

Ci <1.00E-11 <1.00E-11 D. Tritium

1. Total release Ci 8.85E-02 7.32E-02 2.. Average release rate for period uCi/sec 1.80E-02 1.44E-02

'<' indicates' activity of sample is less than LLD given in uci/mi r

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TABLE 1,2-1 ErrLUENT AND WASTE DISPOSAL SCHI ANNUAL REPORT (1990)

UNIT ONE LIQUID.ErrLUENTS-SUMMATION Or ALL RELEASES rirst Second Quarter Quarter A.-Fission and Activation Products 1, Total release ' (not including Ci 0.00E+00 0.00E+00

. tritium,. gases, alpha)-

2. Average concentration released uC1/ml N/A N/A 3.-Maximum concentration released uCi/ml N/A N/A

- 5. Tritium-

1. Total release ci 0.00E+00 0.00E+00
2. Average concentration released uC1/ml N/A N/A C.JDissolved Noble' Gases
1. Total release ci- 0.00E+00 0.00E+00 ,

2.' Average concentration released uCi/ml N/A N/A D. Gross Alpha Radioactivity 1.' Total release - . Ci 0.00E+00 0.00E+00 2.' Average concentration released uC1/ml N/A N/A E. Volume of Waste Released liters- 0.00E+00 0.00E+00 nr. Volume of. Dilution Water liters 0.00E+00 0.00E+00

"<". indicates activity of sample is less than LLD given in uCi/ml 13

s; - . . . . ~. . - . . - - . . - - , - - - - - -

TABLE 1.2-l'(continued)

EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

UNIT ONE LIQUID EFFLUENTS-SUMMATION OF ALL RELEASES Third Fourth Quarter Quarter A.' Fission and Activation Products 1._ Total release (not including C1 0.00E+00 5.97E-03 trittua, gases, alpha)

2. Average concentration released uCi/e1 N/A 4.30E-06
3. Maximus concentration released uCi/mi N/A 2.10E-05 B. Tritium
1. Total' release Ci 0.00E+00 1.83E-01 2.-Average concentration released uCi/ml N/A 9.20E-04

'-C.

Dissolved Noble Gases '

1. Total release -Ci 0.00E+00 <1.00E-05
2. Average concentration released uC1/a1 N/A N/A D. Gross Alpha Radioactivity

-1.' Total release C1' O.00E+00 5.98E-07.

2. Average concentration _ released uCi/e1 N/A 3.00E-09 E. Volume of Waste Released liters 0.00E+00 1.99E+05 F.-Volume of Dilution Water liters- 0.00E+00 1.73E+08

'<+ indicates activity of sample is less-than LLD given in uCi/ml l

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TABLE 1.2-1 (continued)

EFTLUENT AND WASTE DISPOSAL SEMIANNUAL P2 PORT (1990)

UNIT TWO LIQUID ETTLUENTS-SUMMATION OF ALL RELEASES First Second Quarter Quarter A. rission and Activation Products

1. Total release (not including Ci 0.00E+00 0.00E+00 tritium, gases, alpha)
2. Average concentration released uCi/ml N/A N/A
3. Maximum concentration released uCi/mi N/A N/A
3. Tritium
1. Total release Ci 0.00E+00 0.00E+00
2. Average concentration released uCi/mi N/A N/A C. Dissolved Noble Gases
1. Total release Ci 0.00E+00 0.00E+00
2. Average concentration released uCi/mi N/A N/A D. Gross Alpha Radioactivity
1. Total release ci 0.00E+00 0.00E+00
2. Average concentration released uCi/ml N/A N/A E. Volume of waste Released liters 0.00t+00 0.00E+00
r. Volume of Dilution Water liters 0.00E+00 0.00E+00

<" indicates activity of sample is less than LLD given in uC1/mi l

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4 1 TABLE 1.2-1 (continued)

EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

UNIT TWO LIQUID EFFLUENTS-SUMMATION OF ALL RELEASES Third Fourth Quarter Quarter A. Fission and Activation Products

1. Total release (not including Ci 0.00E+00 1.86E-02 tritium, gaeve, alpha)
2. Average concentration released uC1/ml N/A 1.21E-05
3. Maximum concentration released uCi/ml N/A 5.48E-05 B. Tritium
1. Total release Ci 0.00E+00 1.91E-01
2. Average concentration released uCi/ml N/A 9.20E-04 C. Dissolved Noble Gases
1. Total release Ci 0.00E+00 <1.00E-05
2. Average concentration released uCi/ml N/A N/A D. Gross Alpha Radioactivity
1. Total release Ci 0.00E+00 2.08E-01
2. Average concentration released uCi/mi N/A 1.00E-09 E. Volume of Waste Released liters 0.00E+00 2.08E+05 F. Volume of Dilution Water liters 0.00E+00 1.39E+08

'<' indicates activity of sample is less than LLD given in uC1/ml i

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TABLE 2.0-1 ErrLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL Jan. Feb. March First-Quarter

1. Spent resins, filter sludges,

- evaporator bottoms,letc.

a. Quantity shipped- cu.m. 3.97E+01 1.86E+01 1.29E+01- '7.12E'01
b. Total activity 1 Ci 4.51E+02 6.50E+02 1.12E+02 1.21E+03
c. Major nuclides (e stimat e) .
Co  % 22 25 36 Jre-55 4 64 58 35-

,Mn  % 05 13 21 ,

d. Container type LSA LSA LSA

-e.. Container volume

' cu.m. 2.12E-01 2.12E-01 3.94E+00 3.85E+00 3.85E+00 5.07E+00 3.94E+00 3.94E+00 5.07E+00 4

.f; Solidification agent Cament . Cement Cement-

2. Dry. compressible waste, contaminated equipment,-etc.

a.-Quantity; shipped . cu . m .~ -5.70E+01: 5.43E+01 2 . 21 E + 01 -- 1.33E+02

-b. Total activity Ci 2.182+00 1.43E+00 _7.04E 4.31E+00

c. Major nuclides (estimate)

-Co-60:  % 36 36 36 Mn-54' 4 21 21 211 Cr-51  % 32 32 32

-d. Container' type" LSA .LSA LSA

e. Container volume cu.m. 2.12E-01 2.12E-01 2.12E-01 2.72E+00 2.72E+00 2.72E+00 3.51E+01 I

f 17

TABLE 2.0-1 (cor.tinued)

ErrLUENT AND WASTE DISPOSAL SD'IANNUAL REPORT (1990)

SOLID WASTE SHIPPED CrrSITE FOR BURIAL OR DISPOSAL 3 Jan. Feb. March First Quarter

3. Solid wasta Disposition
a. Number of Shipments 14 07 04 25
b. Mode of Transportation Hittman Hittman Hittman Number 14 07 04 l'
c. Destination Barnwell, SC Barnwell, SC Barnwell, SC Humber 03 01 01 Beatty, NV Boatty, NV Beatty. NV Number 08 04 02 Oak Ridge, TN Oak Ridge, TN Oak Ridge, TN Number 03 01 01 Waltz Mill, PA Humber 01 18

TABLE 2.0-1 (continued)

ErrLUENT AND WASTE DISPOSAL SEMIANNUAL REPOP,T (1990)

, SOLID WASTE SHIPPED OTTSITE TOP. BURIAL Oh DISPOSAL April Ma.y June  ?,econd Quarte r

1. Spent resins, filter sludges, evaporator bottoms, etc.
a. Quantity shipped cu.m. 1.56E+01 1.47E+01 2.10E+01 5.13E+01
b. Total activity Ci 9.43r+01 5.4BE+01 1.13E+02 2.62E+02
c. Major nuclides (e stinate)

Co-60  % 70 79 79 re-55  % 0.1 01 01 Mn-54  % IS 1B 18

d. Container type ISA LSA LSA
6. Container volume cu.m. 2 125-01 2,122-01 2.12E-01 3.94E+00 3.:34t&OO 3.94E+00

<. 5,07t+00 5.07E+00

f. Solidification agent Can.e nt Cettent Coment:
2. Dry compressible -wiste, contaminated equipinent,- etc.
a. Quantity shipped cu.m. 1.21.tt 01 2.aD E+M 3.12r+D1 9.61E+01
b. Total activity C1 4 A5M&00 1.041+C0 7 . 4 4:*,+01 3.19r.+01
c. Major nuclides (estimate) re-59  % 30 30 30 Mn-54  % 2% 28 28 Cr-51 4 25 25 25
d. Container type LEA LNt LSA
e. Container volume cu.a. :2.128-01 2 .12r:-Crt 2.125-01 2.721400 2.72E+04 4.05t&OO 19

]

9 t TABLE 2.0-1 (continued)

F.TTLUtHT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

SOLID WASTL SHIPPED OTT31TE FOR BURIAL OR DISPOSAL April May June Second Quarter

3. Solid Naste Disposition
a. Number of Shipments 07 05 08 20
b. Mode of Transportation Hittman M.i ttman Mittman Number 06 04- 06 Kindrick Kindrick Kindrick Humber 01 01 0 ?.
c. Destination Barnwell, SC Beatty, NV Barnwell, SC Humber 01 04 02 Beatty, NV Cak Ridge, TN Beatty. NV Number 04 01 04 Cak Ridge, TH Cak Ridge, TN Humber 02 02 20

5 i

' TABLE 2.0-1 (continued)

EFFLUEWT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL

. July August September Third Quarter 1.-Spent resins,: filter sludges, evaporator bottoma,_etc.

s. Quantity shipped cu. a. 1.91E+01 1.35E+01 1.55E+01 4.81E+01 b.' Tote) activity--

C1 4.04E+02 5.68E+02-- 3.35E*02 .1.31E+03

c. Major nuclides (estimate).

Mn-54  %. 09 08 10

-Fe-55  % 62 69 65 Co-50  % 22 20 23 cd. Container type- LSA LSA LSA t

.e. Container volume cu. a.'- 3.94E+00 2.08E-01 2.08E-01 5.07E+00 3.94E+00 3.14E-01 3.94E+00-f.1So11dification ager.t Cement ~ Cement ' Cement 4

~ 2. Dry. compressible waste r

.contesinated-equipment, etc.

a.- Quentity, shipped cu. a. S.10E+0i S.68E+01 7.18E+01 1.80E+02'

, . .b. Total activAty Ci 7.53E-03 6.03E+00 3.35E*00 9.39E+00

c. Hajor nuclidee (estimate)

'Cr-51  % 14 14 14 Mn-54 .% 13 15 ~15

.Fe-55  %. 45 45- 45 ._

Fe-59  % 16 16 16

'd. Container type LSA LSA LSA <

e. Container volume cu. e. 2.08E-01 2.08E-01 2.0dE-01 ~

2.72E+00 21 4

.N-* + + . ._,-_________._m_.___._____._ m__ _ _ _ . _ _

1. -

l TABLE 2.0-1(continued)

EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1990)

SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL July Auguct Sept. Third Quarter

3. Solid Waste Disposition
h. Number of Shipmente 08 07 10 25
b. Mode of Transportation Truck Truck Truck Number 06 07 10
c. Destination Barnwell, SC Barnwell, SC Barnwell, SC Humber 03 00 00 Beatty, NV Beatty, NY Beatty, NV Number 01 04 05 .

1 Oak Ridge, TN Oak Ridge, TN Oak Ridge, TN i Number 04 03 05 22

,_ m _ ,. m. -- - '

I?BLE 2.0-1 (continued)

EFFLUENT AND WASTE bl5POSAL SEMIANNUAL REPORT (1990)

SOLID WASTE SHIPPED OFFSITE FOR DURIAL OR DIEPOSAL -

October November December Fourth Qecrter

1. Spent resins, 211 tor si'idges, e9eporator bottoss, etc.
m. C:sttity at:1pped cu. a. 0.00E+00 1.17E+01 7 32L+00 1.9',t+01
b. Total activity Ci 0.00E*00 5. 85E >01 4.980s01 i.08E+02
c. Nascr nuclices (estinkte n Mn*54 1 h/A 74 24 Fa 55 1 NiA 02 02 Co-60  % N/A 70 71 '
d. Container type N/A LSA LSA
e. Cantainsi volume cu. a. H/A 5.83E+45  ?.08E-01 5.B3E+00
f. Solidification agent N/A Cement c'escr:t
2. Dry cospress)hle vaste, contaminated equipment, etc.
s. Quantity snippad cu. w. 8.99E+pi 1.30E+02 S.49E+01 3.05E+02
b. Total activity C1 2.15E+00 3.94E+00 4.87E+00 1.10E+01
c. Ma;or nuclides (estimate)

Cr 51 1 14 14 14 m Mn-54  % in 15 15 Fe-55  % 45 45 45 Fe-59 1 16 16 16 f=

d. Container type LSA LSA LSA i
e. Container vclume cu. a. 2.08E-01 -2.08E 01 2.08E-01 2.72E+00 2.72E+00  ?.*/2E+00

=L 5'-

23 E L

.s._.._ __ .. . . _ . . _ . _ .-_._._ _ . . . _ . _ _ . . ~ - . . . _ _ _ _ _ _ . _ . . _ _

o  !

a

'iABLE 2.0-1 (continued) t EtrLUENT AND WASTE DISPOSAL SEMIANNUAL REPOST (1990)

SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSat i

October Novesber Dec. Fourth Quarter

1. Solid Waste Dispositic%
e. Number of S'nipaants 06 10 06 22 ,

b.- Rod? of ,tansport-ation Truck Truck Truck NurWr Os 10 06 ,

> Destination 0)try111, SC Barnve11,1+d Darnvoll. SC ,

Npaber 00 02 01 Beatty, NV Beatty, N/ Beatty, NV Number . 00 00 01 p Channshon, li Channshon, IL Channahon, IL N.ater 00 01 00 Oak Ridge, TN Oak Ridge, TN Oak Ridge, TN  !

Number 06 CJ Cl Waltz Mill, .'A Wrltz Mill, PA Waltz Mill, PA Mueher 00 01 00 i 24

. - . . - _ _ . . . . . . . . ~ . - - . . . . ___- . _ - . -

FIGURE 3.1-1 Estimated Cumulative Gama Dose (in mrom) from the t,asalle l',e.ti'.1 for the period January-December 1990

/ @#j#

,'f.

L5HJA. th L ebe ? s ) j 200 g Smal' figure - multiply by 10-e  ; 30 Large figure - Avitiply by 10-e -

(_ (DJ ses\ ,

t b0 V

( wmom,. m um. *m' I f s d@i. ..... a.

4 g 100 "

y r

"~

. J

^

D. ' *, 25

/

Oflowo Morris i m, . .m.. -

l gnet 0 ir,o o 10 1 A 8

  • 10 hpc . " ""_ ,

c  %.... .....4 ;% w .. .

i ov.....

ts

' n ]l 1

i.

b **I

06

,, J v k

Amewe

/

55

/

odell

. o

-t4 - ,

25 0 $ IC 15 7)mi bud =%ddi d '- ~ '&

FIGURE 3.1-2 Estimated Total concentrations (in pCi/tr3) of Noble Gases from the Lasalle Station y 6gs# N N for the period January *becomber 1990 /

Isopleth_La 113 100 Small figure - multioly by 10 1 Large figure - multiply by 10'1 p _

III///t/MI/>

{ }h '/////////h

$0, ,,,,,,,,,,,

).

.... ne

)

~ %- \ /

0

! I*i

- s: -

j

.....o , l 10 25

\

/ O '

o.,, , ) 80 ortis f s 3 ,,, '

lHeno s D *' N e 10 0 h '

I 8 inn a J

s,... . .

(f e e v.....

15' ,, . .]

} ..... .

..  %;;,SO rx / /

/- ,

Dwight

- 55 Odell

' t3 - ,

s 26 0 5 10 15 20mi ut=%d=%d '

m

FIGURE 3.1-3 Estimated Total Concentrations (in pCi/m8) f

~

  • 'p' w of Iodine from the Lasalle Station for ,,

the period January-December 1990 -"*._

lasnisih_Leeb 10 0 Small figure - multiply by 10 s Large figure - multiply by 10 s ~~"" \

T t

} \

, e ,. .sm wwum x f.. ,

Y?-

l i w.4, .

N f f ,

n.,iw

/

]' )

4 r

e m N

j

[ *""

~

\

l fi y \ aw j A e

s...e re y l \

200 .1 Q ,....

3 # no '

4r

'o n....

streetor w /

/

\\ "

T SO Dwight

n. _Y

\ hwa 55 0d'"

.* "" 25 ,

27 o s 10 15 20 mi

= =%L_ w 3

FIGURE 3.1-4 Estimated Total Concentrations (in pCi/m3) of #.y w Particulate Matter from the Lasalle Station /

for the period January-December 1990 , g 1Eqplq1h Labe1$

Small figure - multiply by 10-7 {

_y"w"

\

~ 00 # 1 Large figure - multiply by 10 7 )

N n 25 E , ,

,, Viaiai,iisi,v 4,,, td ... 7

o. + r

/

O oi. T f So

/ ..,,,e y g ua...m.

,,,,-. ~ .-

ye j 10 0 i J e t,

7....

( 5,

,,, 3 * **'

~

is 100 l j ,

/

g T

) 25 &

- -w ,,

odell r e -- ,

28 o j _

10 15 to mi

. . - . . . - - . - . . - - . . - . . - . ~ . - . ~ . - . . . - _ . . ~ _ . - . - . . . _ . - - - -

TABLE 3.1-1 LASALLE UNIT ON! j 1990 ANNUAL REPORT  !

KAX1 MUM DOSES RESULT!MG FROM AIP60RNE RELEASES '

PERIOD OF RELEAst - 01/01/90 70 12/31/90 CALCULATED 03/06/91 I INrANT RECEPTCR ]

1 IST 2ND 3RD 4TH TYPE QUARTER QUARTER QUARTth OUARTER ANNUAL JAN*P'R APR=JUN JUL SEP OCT-DEC CAMKA A!R '2.548-06 1.61t-09 5.89t 06 3.232-04 4.088-04 (MAAD) (ESE ) (ESE ) (ESE ) (ESt )

DETA AIR 8.88t-06 (E8E )

4.$3t.10 1.38t-03 2.79t-05 1.41t 03

- ( MRAD ) (t 1 (E I (t I 707. 90DY (t ) (E 1 1.05t-05 6.35t-10 2.73E-06 1.77t-04 2.16t 04 (MREM) I

$RIN (tst ) .

2.60t-06 Itst ) (tst ) (Est ) (tSt ) '

1.50t 09 9.662-04 -2.73t.04 1.252-03 (MREM) (tst 1 (tst 1 (t 1 (tSt 1 ORGAN (tSt )

1.15E-04 1.16E 03 1.04t-03 7.34t 04 3.64t 03 (MREM) (Est ) (tSt ) (Est ) (E ) (tSt )

THYR 0!D THYROID THYROID THYROID THYROID THIS IS A REPORT FOR THE CALENDAR YEAR 1990 COMPLIANCE STATUS . 10 CFR 50 APP. !

!HTANT RECEPTOR

............ g Or APP t. ............

OTRLY 1.17 QTR 2ND OTR .3RD OTR 4TH QTR YRLY  % or OBJ JAN-MAR APR-JUN JUL-8tP OCT NOV CBJ APP.!

canna AIR (MkAD) $.0 0.00 0.00 (~ . 0 0 0.01 10.0 0.00 BtfA.LIR (MKAD) 10.0 0.00 0.00 .A C1 0.00 30.0 0.01

. TOT. 90DY (MREM) 2.5 0.00. 0.00 0.00 0.01 5.0 0.00 SKIN (MatM) 7.6 0.00 0.00 ).C1 0.00 15.0

. ORGAN (MREM) 7.5 0.01 0.01 0.02 6.01 0.01  !$,0 0.02 THYRCID THYR 010 THif.01D THYR 0!D THYROID RESULTS BAstD VPON ,

ODCM ANNEX REVISION 0 MARCH 1989 s

I i

i 1

)

TABLE 3.1 1 (continued)

LASALLE UNIT ONS 1990 ANHUAL RtPORT MAXIMUM 00828 RtSULTING PROM AIR 80RNE RELEAsts PERIOD OF RELEASE - 01/01/90 70 12/31/90 CALCULAftD 03/06/91 '

ADULT BtCEPTOR 18T 2ND 3RD 4TH TYPE QUARTtR QUARTER- QUARTER QUARTER ANNUAL JAN. MAR APR=JUN JUL.StP OCT.DEC CAMMA AIR 2.648-06 1.51t-09 6.89t.05 3.2 3t.0 4 4.08t-04 (MRAD) (Est ) (Est ) (E8E ) (tSt ) (tst )

8tTA AIR 8.88t-06 4.53t.10 1.30t-03 2.19t.06' 3.41t-0)

( MRAD) (E ) (t I (t ) (t 1 (t )

TOT. 90DY 1.06t.06 6.168 10 2.13t.06 1.77t 04 2.15t.04 (MRtM) (Est ) (Est ) (tst ) (tst ) (tSt )

BRIN- 2.602 05 1.50r-09 9 66t.04 2.13t.04 (MPEM) (E$t ) 1.25t.03 (E82 ) (t I (Est ) (tSt )

ORGAN 1.012 04 8.24t-04 7.?lt-04 4.922 04 2.80t.03 (MREM)- (28t ) (Est ) (tSt ) (ESt ) '(185 1 THYROID- THYROID THYR 01D THYROID THYR 010 j

THIS IS A REPORT FOR THE CALENDAR YEAR 1990  ?

COMPLIANCE STATUS . 10 CPR 50 APP.1 ADULT RECEPTOR

[

-........... % CP AFP !. .---.--.. ..

OTRLY 18T QTR 2ND OTR 3RD OTR 4TH OTR VRLY  % 0F 08J JAN. MAR- APR=JUN JUL.StP OCT.NOV OBJ APP.I.

CAMMA AIR (MRADI- 6.0 0.00 0.00 0.00 0.01 10.0 0.00 SETA AIR (MRAD) 10.0 0.00 0.00 0.01 0.00 20.0 0.01 TOT. D0DY (MREM) 2.5 0.00 0.00 0.00 0.01 6.0 0.00 SRIN (MatM) - 1.5 0.00 0.00 0.01 0.00 ~16.0 0.01 ORGAN (MREM) 1.$- 0.01 0.01 0.01 0.01 15.0- 0.02 r THYR 0!D THYROID THYR 0!D THYROID THYROID Rt8ULTS RASED UPON ODCM ANNEX REVISION 0 MARCH 1989 i

l 30

l

.l l

l l

i I

l TABLE 3.2 1 l

LA$ALLC UNIT ONS ADULT DECEPTOR 1990 ANNUAL REPORT RAK! MUM D0$t$ (MREM) RESULTING PROM LIQUID EPPLUENTS PERIOD CP RELP,ASE . 01/01/90 70 12/31/90 CALCULAftD 01/06/91 1 15T 2ND 3RD 4TH D058 TYPE QUARTER . _ QUARTER QUARTER QUARTth ANNUAL JAN. MAR APR.JUN JUL.$tP OCT.DEC

. TOTAL 0.00t+00 0.00t+00 800) 0.00t+00 1.012 05 1.418 05 .

INTFRNAL- 0 00t+00 0.00t+00 0.00t+00 ORGAN- 2.42t.05 2.42t.05 LIVER LIVER

-THIS 18 A REPORT POR THE CALENDAR YEAR 1990-COMFL1 ANCE STATUS

  • 10 CPR 50 APP. I

............ % CP APP 1. ............

OTRLY 18T QTR 2ND OTR 3RD QTR 4TH QTR YRLY l OP OBJ- JAN.nAR APR.JUN JUL*8tP OCT.NOV CBJ APP.!

n TOTAL RODY (MREMI- 1.5 0.00 0.00 0.00 0.00 3.0 0.00 CRIT. ORGAN (MREM) 5.0 0.00 0.00 0.00 0.00 10.0 0.00 LIVER LivtR RESULTS BASED UPON ODCM ANNEX REVISION 0 KARCH 1989 s

k-

-h

-f 31

. . 3 l

TABLE 3.2-1(continued)  ;

P LASALLE UNIT TWO ADULT RECtPTOR 1990 ANNUAL REPORT MARtMUM D0st$ (MREM) htSULTING FROM Ll0VfD EFFLUENTS t R100 0F RELtAst - 01/01/90 to 12/31/90 CALCVLATED 03/06/91' 187 2ND )RD 4TH Dost TYPt 00ARTER QUARTER- QUARTER OUARTth ANHVAL JAH+ MAR APR*JUN JUL*SEP OCT=DEC TOTAt, 0.00t+00 0.00t*00 0.00t+00 2.372 05 2.375 05 RODV ,

INTERNAL 0.00t+00 0.00t*00-- 0.00t+00 3.24t-05 3.24t.06 ORGAN .

LIVER -LIVER THIS !$ A REPORT POR THt CALENDAR YEAR 1940- I 4

'COMPL1ANCE STATUS 10 CrA $0 APP. I

............ I or APP !. *...........

CTRLY. 187 QTR 2ND OTR 3RD OTR._ 4TH OTR YRLY  % or ORJ JAN MAR APR.JUN JUL.SEP OTT.NOV ,

ORJ APP.!

, TOTAL 60DY (HREM) 1.5 0.00 0.00 0.00 ~0.00 3.0 0.00 CRIT. ORGAN (MREM) 5.0 0.00 0.00' '0.00 0.00 10.0 4 00-Ltyth L1Vta RESULTS SAst0.CP0A ODCM ANNEX REVISION 0 MARCH 1989 i

b 32

FIGURE 5.0-1 otte.o p,t ,

^

i t_14 3d FMatsedies South Ottaaa \,,,% **',

ss S. n- . ,

$ 2' e

b

  • 6 6

I ant Pl f

Este Property #13

Orand Ridge Verona e

Kinsman 11eRansom ett '

, Kernaq Sitestor 10' Orundy La Salle County ,

County Livingston County i= 4 i e e t es*** L A S ALLE COUNf y ST Af ton

=

e

_t _a _e _t J see=we FlX(D AIR SAMPLING AND TLD $1TE$

L48 Neareise #1 L43 Nearmes f a L 43 Omene #3 -

L es Neermes M L es Onse as -

L46 Nemrene M L47 Senese L48 Mengas L 48 Grand Itadge L te transar L Il Rameeus L 13 Karman L 13 Reves 4 m Conroe llaed L 14 Osame

1 FIGURE 5.0-2 A  ;,

p af . . .

e ies a e 'p '  !

N x

N 22 '8 li-A$

ea -, s -

9

. , , . N (. , w .mi.iw e j,

% gue\\

~~

l 'lit "'

/E. '

w x

f ,

/ '

E flJ 4 8 til t

, ;ii... gu- , ;i*i ,; i i.,j , y c,u m ,,,,3 :*{

. . .. , 7 '..7,. , .... ,

=- e a. a. is i. se .

L A S ALLE COUNTY ST ATION INNER R!% f LD LOCAf!ONS 34 I

I FIGURE 5.0-3 osia.o

,***' r w ar.eiii.. d South

~

Sen.c. .

._i

.ib i ..

eit e.;..

_ ii , gegia . =p lie.1 e l lie. a e jos.;

3:53 sibi I e8*8 g Plant j e mi siz e sia i I

  • M8 Site Property j orand niege *** verona alit:1 .11:1 Nil alii:1 ,

" w* *i 8

Kintman Ransom

, Kernan Streator

- s Grundy La Salle. County . .

County

.m Uvingston County e . s  : a t eaae.

8. A Sa LLE COUN T Y ST ATION

' ~ ~-~ ~ ~ . .

. . . . . . ~ ,

Out[R RING t'DL LOCATIONS 35

FIGURE % 0-4 V

6....

.... + i.

on .

!.n verwn uae i.,i lot,ee .,

'4. M genegg 4.s '#

...s. -

L 10 RL t3 r

4 11 t*

L* . S 6s- d.n A

Al.170 e

P.sn.esa '

l L 19 e t

' ' ' ' ' ' ' 8"**' LA SALLE COUNTY ST ATION

_8 _ _

' a e

_. a u ,

i L.16 Lowery Dairy INGl5HM M0 WAf[RBORN[ [1PO$@[

eATHwAf $ W L[ L g An g s L 17 Mayer Patterson Dairy L 18 Flatness Dairy -

L.19 Dettenhausen Dairy L 20 Gass Farm L 21 Illinois River at Seneca L 24 LSCS Cooling Lake near Recreation Area

.L-27 L$CS Onsite Well L 28 Marseilles Well Water L 29 Seneca Well Water-L.30 Ransom Well water

'L-32 Illinois $ tate Park Well~

L*34 Cooling Lake 015 charge Structure Downstream L 35 N rseilles Pool of Illinois River 36

.g'c.--r, yy.w-pg w-

. . l 1

4 1

l TABLE 5.0 1 l i

l I

L LaSalle Station u e  ;

Radiological Environmental Monitoring l

  • t Locations .a , i 2, M

- 2 ,

R

  • a 2 . .

E D 3

  • w 2 4 M C @ .0 N

@ C 3 U W G v e  %

n .a .a .a c e -t e

~ ,C @ .at ~ .D + %

L 23 o - .0 3

.M

.ar .D T 4. O o

.a s o a .a 3 s e- v u. aw r o.

e e 3 cc o o >

e s.

c L 01 Nearsite #1 00. . . . . . . . , , .

L 02 Nearsite #2

00. ... . . . . .......

L 03 Onsite #3 00... . . . . .. . . .

L-04 Nearsite #4 00.. . . . . ....

L 05 Onsite #5 00.. . , . . ..

L 06 Nearsite #6 00.. . . . . . . . . . . .

L 07 Seneca 00. ... . .. . . . . . . . . ,

L 05 Marseilles 00........ . ..... . . . . .

L 09 Grand Ridge 00. ... . . .. . . . . . .

L 10 Streatcr 00.. . . . . . .......

L il Ransom 00.. ..... .

L.12 Kernan OO............. .......

L 13 Route 6 at Gonnam Road 00..... . . . .. . . . ....

L.14 Ottawa 00.... ,.................

L 16 Lowery Farm ... .. . O.....,.........

L 17 Hayer Petterson 04try L 18 toict Dalry

.. , ,. . O.... . . .,,.. .

L 19 Dettenhausen Dairy

.,, , . . . O.... . . .......

L*20 Gass Farn .......O....... .......

L 21 filinois River at Seneca

.. .... . O... . . . .......

L 24 LSCS Cooling Lake near Recreation Area .................O.......

L 27 LSCS Onsite Well .....O...........O.......

L 28 Marseilles Well Water .......................O.

L 29 Seneca Well Water .......................O.

L.30 Ransom Well Water .......................O.

L.31 Ottawa Well Water ......................O.

L 32 Illinois State Park Well .......................O.

L*34 Cooling Lake Discharge Structure Downstreani

....... . . . . ...........O.

L.35 Marseilles Pool of Illinois River

. O........,,..

. . . . ...O.........

CENSUS D:iry ResidInce 37

Table 5.0-2 i

i LA SALLE COUNTY STATION ENVIRONMENTAL RA0105.0GICAL MONITORING PROGRAM, SAMPLING LOCATIONS

1. AIR SAMPLERS Distance Direction Site Codea location Jmiles) _ ,(*) _

L-01 Near-site No. 1 0.5 326 L-02 On-site Station No. 2 0.6 11 L-03 On-site Station No. 3 0.2 56 L-04 Near-site No. 4 1.5 90 L-05 On-site Station No. 5 0.3 145 L 06 . Near-site No. 6 0.4 270 L-07 Seneca 5.2 18 L-08 Marseilles 7.0 326 L-09 (C) Grand Ridge 10.4 260 L-10 (C) Streator 13.5 220 L-11 Ransom 6.0 191 L-12 (C) Kernan 5.0 214 L-13 Route 6 at Gonnam Road 7.0 100 L-14 (C) Ottawa 12.0 315

2. Ilus
a. Same as No. 1.
b. Special TLD Samplers Distance Direction Site Code imile_sl _h, , ,

inner Ring L-101-1,2 0.5 359 L-102-1,2 0.6 17 L-103-1,2 0.7 46 L-105-1,2 0.7 91 L-106-1,2 1.4 110 L-107-1,2 0.8 128 L-109-1,2 0.6 178 L-110-1,2 0.6 205 L-111a-1,2 0.7 217 L-111b-1,2 0.8 230 L-112-1,2 0.9 244 L-113a-1,2 0.8 262 L-113b-1,2 0.8 273 L-114-1,2 0.9 288 a

Control (reference) locations are cenoted by a "C" after site code. All other locations are indicators.

38

1 l

TABLE 5.0-2 (continued)

LA SALLE COUNTY STATION ENVIRONMENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS

2. TLDs
b. Special TLD Samplers (continued) ,

Distance Direction Site Code (tailes) (') ,

Outer Ring L-201-1,2 2.0 15 L-202-1,2 2.3 33 L-203-1,2 4.0 56 L-204-1,2 3.5 78 L-205-1,2 3.5 102 L-206-1,2 4.3 123 ^

L 207-1,2 4.5 146 L-208-1,2 4.5 170 L-209-1,2 4.0 192 ,

L-210-1,2 3.3 216 L-211-1,2 4.5 240 L-212-1,2 4.0 261 L-213-1,2 3.8 283 L-214-1,2 2.0 303 L-215-1,2 2.0 330 L-216-1,2 1.5 350

3. MILK

~

Distance Direction Site Codea Location (miles) (*)

L-16 Lowery Dairy Farm 8.2 120 L-17 (C) Hayer-Patterson Dairy Farm 12.3 18 -

L-18(C) Flatness Dairy Farm 12 .5 10 L-19 Bettenhousen Dairy Farm 8.5 180 L-20 Gass Farmb 4.6 34 8 a Control (reference) locations are denoted by a "C" af ter site code. - All- .

other locations are indicators, b

Additional- f arm was not required by the 00CM but was includad to ensure that the program has at least four milking stations. This is not a commercial

~

dairy but a farm having milking co'<s for personal use.

V

'39

Table 5.0-2 (continued)

LA SALLE COUNTY STATION ENVIRONMENTAL PAD 10 LOGICAL MONITORING PROGRAM, SAMPLING LOCATIONS

4. GR_0VND/_WELL WATER Distance Direction Site _Codea L o_c a tj_o_n_

.imile_sl ,_l' )_ ,

L-27 Onsite Well L-28 Harseilles Well 7.0 326 L-29(C) Seneca Well 5.1 18 L-30 Ranson Well 6.0 191

< L-31 Ottawa Well 12.8 304 L-32 1111nois State Park 6.5 326

5. SilRFACE WATER Distance- Direction Site Codea Locat_ ion ,1 miles) _,(*)_

L-21 (C) 1111nois River at 4.0 22-Seneca L-24 LSCS Ccoling Lake 0.3 112

6. FISH Distance Direction Site Codea location (mjles]

e _,l' L L-24. LSCS Cooling Lake 0.3 112

-near Recreation Area L-35 . Marseilles Pool of 6.5~ 326 1111nois River

, 7. SHORELINE SEDIMENTS Distance Direction Site Code 8 Location _

_1milesl , _ _( ' ), _

L-34 Downstream of cooling At Station lake discharge structure a

Control (reference) locations are denoted by a "C" after site code. All l other lochtlons are indicators.

40

-. n. .,#l-y 4

.i TABLE 5.0-21(contir.aed)- --.-

I L

LA SALLE COUlfff STAffolt' ENVIR0leIEllTAL RADIOLOSICAL 710mlTORinG PROGR#f. $44PLE COLLECT!0'l AND AftRLY$($

tocetfoe Collectson Type of Frequency Sample Hedte_ Code"

}

5fte Fregmency Analysis of Analysts Wernert s 1

{'

i'

.1. Airborne- . 'e. .Onsite and hear Field Continuous Gross bete Weekly - Om all sanytes,

.Particulates coeretten .. Gaune Isot b arterly One guerteely cervos etes f raza each locat een.

. L-1 Ineersite tio. I, for a w=ek L-2 fleersite let. 2 Gemne isot Weekly it gross bete in a sample esteeds IOR the L-3 Onstte fio. 3 3

,L-4 yeerly mean of the control smoles j

.feeersite ho. 4 Filter Weetly

' L-5 Onstte tie. 5 ' Enchange l-6 IIeersite leo. 6 b.'For Field L-F Seeece L-8 . Pierseille L-9 (C) Grand Ridge t-10 (C) ..Streetor i $ L-Il Rensem a

L-12 (C) rernen L-13 Route 6 et Gonaan Rd.

, L-14 (C) Ottawe i

2. Airborne Same es 1. keetly 1-131 j Iodine Weekly On all ss=ples,
3. Air sempting Sene es 1. Test eas Trata Weekly On all samplers.

tie tatenance

4. TLD Some es 1. Quarterly Geruse Quarterly Tme sets at all M Iocettons. One set L-101-1.2 laner Ring read quarterly. Second set rees of 302-1.2 required by Commmeameettee fossen. At other 103-1.2 lecettoes. eli sets read quarterly.

105-1.2 Mintesa of twe TLDs per set.

106-1.2 l.

107-1.2

'108-1.2 109-I.2

'.I10-1.2

} lite-l.2 Ilib-1.2 i: 112-1.26 Il3e-l.2

.Il3b-1.2 .

114-I.2b-i b* Coateel (reference) locettens are deaeted t*y a *C* fn this colossi. All other locettons are tadicators.

hew special TLD site for this Spec ' ,

i

TABLE 5.0-2 (continued) 1.A SALLE COUNTY 5iAT10m EMY1ROf#1RTAL RA010 LOGICAL Mom 1TORING PROGP AN, 5A." rte COLLECTIOM AND A%tLYSC5 tocation Collection Type of Frequency Frequency Analysis of Analysis Femarks

$ ample Media tode' 56te

4. TLD (continued) L -201-1,2 Outer Ring 202-1,2 203-1,2 204-1,2 205-1,2 206-1 ,2 207-1,2 208-1,2 209-1,2 210-1,2 T.1-1,2 212-1,2 213-1,2 214-1 ,2 215-1,2 3 216-1,2 rv B 1-*erk ly: 1-131 st-weekly on alt saeples. LLD: 0.5 pC1/L.
5. Milk L-16 Lowry Dairy 81-Ecekly On all samples.

Hauer-Patterson Dalry May thrcwgh Ga wa Isot.

L-17(C)

L-18 (C) Flatness Dairy October L-19 Bettenhousen Detry Ori all samples- LLD: 0.5 pC1/L.

Monthly: 1-'31 Nonthl y L-20 Gass Farmb On all samples.

hovember Garma Isot Monthly through April Quarterly Garw a Isot Quarterly On all samples.

Ground /:Jel l L-27 Onsite well rfaarterly On all saeples.

6.

L-28 Marsettles Well Tritium Water L-29 (C) Seneca Well L-30 Ransom idell L-31 Ottawa kell L-32 Illinois State Park Well

' Weekly Garuna Isot Monthly On ee-thly carposttes frtus eacts location.

7. Surface Water L-21 (C) Illinois River at Trit tura Quarterly On quarterly (wposites from each Ottawa loc ation.

L-24 L5CS Cooling Lake Sest-eneual Garw.a Isot Sect-annual On edible perticas only. Teo species.

8. Fish L-24 LSCS Cooling take L-35 Marsettles root a Control (referenr.e) locations are denoted by a "C" after site code. All other locations are indicators.

b An additional dairy was not required by the G)Cff tut was incit:ded to ensure that the progrant has at least four datries. .

+

-.1 TABLE 500-2 (contirmed). " -

LA SALLE COUNTf STAf ton -

Dett#0setENT4 9A010L9GIC4 ft0WITORIME PROGIMt. 54FLE COLLECTI0s An0 AnRYSES Lecetten Collection Type of Sanple tiedte Code' fregaency site Fregeency ' Aralysts of Analysis - neueres

9. Shereltne ' t.34- Downstrean of Sed tment s - Serif.amamal . Gamme Isot Seet. annu al coollag late..
20. Detry Census. a. Site boundeep to 2 miles -
a. Enumerettes Amavally During grattag seesea.

by a deer.te--

deer or egelua-.

lent covating techalgee.

b. . miles to 5 etles -

_ b. Eaumeret ten Aanvally Berlag gearing sessen.

by estag referenced information free cemety agriceitoral A ageets or other W reliable sources.

c.. At defrfes Itsted to Itein 4 -- c. Ingetre as Jbweally Omrf ag vrartag seesen.

to feedtag practices:

1. Festore only.
r. reed a c w eniy,
3. Postere aad feed; f f both, asa famer to estimete fruttaa of feed fran pastwre:

<251,25-50E 50-151 or 1751.

II. Meerest in all 16 sectors up to 5 miles

  1. esidence Ceases.. Annually.

W

_., ~ - , . , -- - ,-. ,, , ,. , . . . , , .- -. _. ~. __ - _ _ - . _ _ _ _ .

TABLE 5.0-3 RADIOLOGICAL ENVIRf7tMIMTAL POMIT021frG PROGRAM OcARTERLY Stre'ARY Occhet %. 50-373, 50-374 Mame of Facility taSall* thsciear Foner station Locatfon of Facility Parse 111es, Illinois Reportleg Feriod 1st Quarter 1990 (Corrty, State)

Indicator location with Highest Control Locations Quarterly Paan tocations W of Sanle Type and ,,. gegens an.-roottee Type fair 6*r of Meana Reage %selts Analyses LLD Range tocation Reage (Units) _J t-04, fecer.stte no. 4 0.024 (13/13)' me.e 0 Air Particulates Gross Beta 78 0.01 0.C22 (78/78)

(pC1/m3) (0.011-0.038) 1.5 mi 900* (0.016-6.031) acae O Gama spec. 6 0.01 (LD _

- <tLO O Airborne ledtee 1-131 78 0.10 4t0 -

(pct /m3) y t-CS, On-Site me. 5 l 19.2 (1/1) 15.7 (4/4) 0 Game Backcround Cama Dese is 3.0 17.7 (10/10)

(15.1 19.2) 0.3 et # 1a5* ' -

(15.3-16.9) g (TLDs) (mRICtr.)

4t0 0 Milk 1-131 12 0.5 4LD - -

(pC1/1)

Ga m a Sp*c. 12 4LD - <tto O Cs-134 5 -

4LD - - 4LD 0 Cs-137 5 4tD - - <tLD 0 Other Gam es 10 Surface Water Gama Spec. 6 (pCf/1) 4t0 0 Cs-134 10 <tLD ,

i 4tD - - <tLD 0 Cs-137 10

<tLD 0 Other Games 20 4LD - -

4tD - <tt0 0 Tritfun 2 700 -

4

'Well Water Gama Spac- E (pC1/1) <tD 0 Cs-134 10 4LD - -

<ttD 4LD 0 Cs-137 to - -

20 <tt0 - - <tt 0 1 0 Other Games 4tD - <tLD ,1 0 Tritfum 6 200 -

a Pean and range based og detectabte messer m ts oniv. Fraction fadicated in parenthesis.

M

TABLE 5.0-4 RADIOLOGICAL Ent!RonMcMTAL m0MITORItiG PROGRAM QIfARTEttY 5tF'UtRT Mame cf Feclitty LaSalle Maclear Fwr Station Dociet No. 50-373. 50-374 Location of Facf11ty Marse 111es. 111tm is Reporti g Period 2nd Ovarter 1990 (County State)

Indfcator totat1on wIth Highest Cont rol Sample Type and tocations Quarterly Mean Locations mireer of Type Muncer of Mean8 Mean Meana Wea-routine Rance tocation Fange kaage tesults (Units) Analyses LLD 0.01 0.018 (78/78) L-01I Neer-site Station 0.018 (13/13) Mene 0 l Air Part fculates Grass Beta 78

'oCf/m3) (c.c10-0.031) no. 1 0.5 mi e 326* (0.011-0.030)  !

Gamma Spec. 6 0.01 *LLD - - Seae 0 ,

l 0.10 4LD - Mone 0 Airborne lodine I-131 78 -

(PCf/m3)

Gama Background Game Dese 14 3.0 If.9 (10/10) L-06. **er-s tte me. 6 19.2 (1/1) 15.8 (4/4) 0 (TLDs) (mR/Qtr.) (14.4 19.7) 0.4 el ,270* -

(14.9-16.4) 3 m

0.5 4LD - - 4tD 0 Milk 1-131 20 (pCf/L)

Gama ' opec. 20 4LS - 4t0 0 r s-134 5 -

4LD - - 4LD 0 Cs-137 5 4LD - 4 10 0 Other Games 10 -

i Sarface Water Gams Spec. 6 (pCf/t) 0 Cs-134 10 4LD - - 4t0 10 ALD - - 4t0 0 Cs-137 4t0 - 4LD 0 Other Games 20 -

L-21 1111 nots River at 272 (1/1) 272 (1/1) 0 Trf tf um 2 200 280 G/1)

Seneca 4.P ml ,22*

a Mean and range based on detectable measurements only. Fractions indicated fr pareetheses. .

b Locations L-01. L-02. L-03. L-OS. and L-06 all had identical means of 0.018 pCf/m3

y , _

xa s TABLt- 5.0-4 (continued)

RADIOLOGICAL (WVIPO!c(NTAL MONITORING PRCraAM QUARitPLY 5tPTt927 kame of factifty tasalle tbclear Power Station. Dociet me. 2-173.50-374 location of Facility Marselltes. Illinois Reporting iteric.- - Fed Qsart e 1900 (County. State) m.

Indicator tocri .Hi@y' Cont roi totattoaa Qo.4tet.y N ew . Locaticas i* We af Sample Type and pgena him$er of Meana 'Q roetfac Type Analyses LLD Range tocatton henge Range l W8ess1ts (Units)

Well Water Garena Spec. 6 4 (p'1/L) 4LD 0 Cs-134 10 <ttD -- -

<tt0 C Cs-131 ID 4LD - -

- 4tD 0 Other Ganvies 20 <tLD -

- 4tD 0 Tritium 6 200 <tLD -

Bottom Sediments Gama Spec. 1 (pCf/m3 ) <ttD 0 Cs-134 0.1 4tD - -

cn - 4t0 0 Cs-131 0.1 4LD -

<t tD 0 Other Gamas 0.2 <ttD - -

r1sh Gaara Spec. 9 (PCf/g et) 4tD 0 Cs-134 0.1 <ttD - -

4tD 0 Cs-137 0.1 <tt0 - -

<tLD 0 Other Ga-etas '5. ? <ttD - -

a I

a Mean and range 5:,# on detectable measureets only. Fractio *s indicated in parentheses.

$df ,

TABLE 5.0-5 RADIOLOGICAL ENVIROSLRTAL MONITOAING Pitor.JtAM QUARTERLY SL9FiARY W of Factitty La$slie huclear Power Station Docket he. 50-373. 50-1/t Location of Facility Marseil les ,111 t net s Reporting Perted 3rd Essarter 19W (Loanty. State)

Location with Highest Opifroi Inditetor Locations Quarterly Mean ~ tocat te% Siust ee of lype and 5 ample Type m

'uster of Meane Nean rwe hon-routine ,

Range Location 4tasvyt aange Fesults i (Units) Analyses LLD L-06. Near-5fte #6 hk 0 Air Particulates Gross Beta 78 0.01 0.025 (78/78) j 4.027 (13/13)

(pC1/n3) (0.011-0.e79) 0.4 at # 270*

I (C 415-0.079.i p *?

Gacuna Spec. 6 0.01 <tLD -

l I <tt b l 0 Airborne lodtr.e 1-131 78 0.10 <LLD -

l -

(pCi/m3) t l t 4-w w Ganssa Background Ganima Dose 14 3.0 18.5 (10/10) L-05, onsite Station { 5 .4 (1/1) R 4 (4/4)  ! 0 (15.2-20.4)

( H .3-17.21- j ho. 5. 0.3 et 9 1456l _

24 I 0.S <tLD - I -

i <1Lu v 3 Mik 1-131 t  ;

uu.M i l g Ce na Spec. 24

<tLD l - <tLD 0 Cs-134 5 y l , ,

l 3

-i

<tt 0 - - 4tu  ! O '

C5-137 5 ' l

  • I

<LL9 - <tt V  ! llt  ;

Other Ommes 10 I

4

-

  • i f' f

Surface Water Gama Spec. 6 -

(pCi/t) e f j 4:t - j - 3 <tED -

U e  !

Cs-134 lu I I Cs-137 10 <Lto - I uD 0

{. j

, l

.l- (LL&  ! G Other Games 20 . ALD - -

t-24. Recreatt pal i 2?6 (1/1) <tLD 0 Tritium 3 200 226 (1/1)

  • j Area Cosling Late.

i 0.3 mi V 112'  ; J 1

I l t Well Water Gampa 1.ec 4 6 i' (pCi/L) f l {

<lLD - - 4tt, '

O  ;

(s434 10 ) l

]

10 <tL D -

- i *LLD u Cs.137 20 <ttD - -  : 4LD t t,

. Other Gammas l I u 6 200 <LLD - -

f <tt b

{ Tritium f a Mean en4 range $ased on detectable messerements only. Fractiees inalcated in parentheses.

.-c TABLE 5.0-6 a RADIOLOGICAL ENy!RONtiMTAL MOh!TORifG FPOGF.AM QUAMLRLY

SUMMARY

I.

hane of Facility LaSalle Nclear Fower Station Doctet No. 50-373, 50-374 Location sf Facility Marseilles, Illincts Reporting Period 4th Quarter 1990 (County, Mate)

Indicator location with Highest Contret Locattoes ')sarterly Mean Locations hustrer of Sample Type end _

Mean8 hon-rovtIne ;

Meena Nean Type Amtecr of Range Range Result s Arulyses LLD Range Location (Units )

?

I 0 Air Part culates Gross Beta 18 l 0,.Cl , 0.029(78/18f L-02, f: car Site fio. 2 0.0M (13/13) None

{0.076-0.G42f 0.6 as a 11* (0.019 0.042)

(PC1/m ) l

,LLD - Sone O 0.01

! Gama Spec. 6

<tLD - hoce 0 Atrt>orne lodtne I-131 78 0.10b -

(pC1/m3)

L-05, on $tte No. 5 22.8 (1/1) 17.9 (4/4) 0 3.0 20.2 (10/10)

$ Game Pac 69 round Gaeuna Dose 14 (16.0-22.8) 0.3 at # 145* (11.1-18.4) 0.5 <tLD - - 4LO O Milk 1-131 18 (PCf/L)

Gama Spec. 16

- <tL C 0 i Cs-134 5 <tLD -

l

< l - - ALD 0 Cs-137 5 <L LD j

4LD 0 Other Gaavas 10 4LD - -

I Surface kater Gamma Spec. 6 (pct /L) - A LD 0 Cs-134 10 <tLD -

- 4LD 0 Cs-137 10 4LD -

l i

20 ALD - - 4LC G

! Other Gunnes 294 (1/2) 238 (1/1) 0 9 1 Tritiva 2 200 254 (1/l) L-24. Mecreattonel

. Area Cooling ta6e, 0.3 at 9 112*

j i .

k i 'I *rll l! t

. ~

, i f n e _

ot s tt r

emt e O 0 0 O O 0 0 0 U 0 erse anR a t

S e

!l s

l n ooa e O e em e e n ne e D D O ring L L L L n n n tt en L t t L io o o io u e nae h h R M ecMlie t r C=

L

( c 0

9 9 _

1 4

7 r e 3 e 0

t r

n

.m-aa ea - - - - - - - - - - -

5 a t mR u s 3

. Q e e

7 h lgn 3 t ia v - 4 A

A 5 0 Hv h 3

,I t y s d il e W i o

r wre et _

h s

e f e or t n

i P i a n R o I

t Ibg i r

t u aQ i t - - - - - - - - - -

e r

-a t

Ai f w a c p t t t Q

J e r o n .

k c L i )

c

) m A

oe DR

- dm 3

d t e G t8 e O a6 c(

u R n P n o Il4 1i~

i de nm

- 1' ,! {

i t M i t

iu l

n I a s so R rs nv o O S t i o on e c T I r n )

e t,o8i en; D D D D D D D

_ t w

( N e t

1 t ct em L 0 L L L D O D __ to L L L L macl O w a iaea M o 1

1 dcMR t

1 t 4 4 t t t L t 6

< < < . F ryre t

- L P ,

5 no IL A r s .

0 T N

a e y e l t jl. ,

.v yf 5 E l l n l o M e i u n E

k 0 h se L(o r oe s

L R e a C 1 1 2 1 1 7 su B

I L ta V l M L G G 0 0 0 0 0 0 G 0 nc A N E

l a

1 I 2 0 2 ee T S mb L a e A L r)

C 6 u4 I y 6 0 1 t1 G t 1 a O e0 L

i l s< (

O yi f e I t c d os s s s D D t a n e e a e l

bL A

R i F ars ,

m . n . n aL t ey r. c u e s cf e,lc e n e a e  :

a t

cd F

a o n

pon y

Tf A a

p N.

7 3

E r

a n 5 p

4 1 G

r

!c 4 7 G ee td f o a e e

a 3 3 e e 3 3 r ee oi m 1

1

- h t

t s 1

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h cec a s s  :

s s ea t e T C t

O i

r w e C C t

O m

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C s t O ax ce m c a o S T L G N L d1 e3 s1 a -

bI s

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_ e s t e t r a

l et r rt w dd i

- ppi e) - e d c mfn tL 9 S9 ns a7U s/ / l aer

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  • b

4 g LASALLE Table 5.1-1 GAMMA RADIATION, AS MEASURED BY THERMOLUMINESCENT 005tMETERS (TLDs)

STANDARD RADIOLOGICAL MONITORING PROGRAM lst Quarter 2nd Quarte,r. 3rd Quarter 4th Quarter Date Placed: 12-29-89 03-30-90 06-29-90 09-29-90 Date Removed: 03-30-90 06-29-90 09-29-90 12-28-90 Days in the Field: 91 91 92 90 Location Averaga mR/ Quarter On-Site and Near-Site Indicator Locations, L-01 Near Site No. 1 18.621.3 15.721.0 18.0 1.4 21.5 0.9 L-02 On-Site No. 2 18.5 1.2 16.520.9 18.721.3 20.1 1.3 L-03 On-Site No. 3 17.811.0 16.320.6 17.821.2 19.921.2 i L-04 Near-Site No. 4 18.121.7 17.921.1 19,721.6 21.521.8 L-05 On-Site No. 5 19.221.3 17,921.1 20.421 .7 22.8 1.4 L-06 Near-Site No. 6 17.811.6 19.210.7 20.3 1.6 22.lil.4 Mean s.d. 18.3 0.5 17.221.3 19.2 1.1 21.321,1

_0ff-Site Indicator Locations L-07 SeneJa 18.6t0.9 17.821.2 19.411.2 20.5 1.5 L-08 Marseilles 18.021.3 16.720.6 18.9 1.2 19.911.7 L-11 Ransom 15.121.1 14.420.8 15.221.2 16.020.8 L-13 Rt. 6/Gonnam Road 15.2 1.1 16.220.8 15.921.2 17.5 1.1 .

.Mean 2 s.d. 16.721.8 16.3 1.4. 17.422.1 18.512.1 Background Locations L-09 Grano Ridge 16,911.5 15.710.8 17.221.7 18.121.0 L-10 Streator 15.321.5 14.920.8 15.321.4 17.110.7 L-12 Kernan 15.321.4 16.020.7 16.3 1.3 17.920.8 L-14 Ottawa 15.321.5 16.420.7 16.6 1.3 18.4 1.1 Mean s.d. 15.720.8 15.8 0.6 16.4 0.8 17.9 0.6 l

50

LASALLE Table 5.1-1 (continued)

GAMMA RADI ATION. AS MEASURED BY THERMOLUMINESCENT 00SIMETERS (TLDs)

SPECIAL PROGRAM Inner Ring, Near Site Boundary, Indicator locations 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 12-29-89 03-30-90 06-29-90 09-29-90 Date Removed: 03-30-90 06-29-90 09-29-90 12-28-90 Days in the Field: 91 91 92 90 Locatior, Average mR/ Quarter Code L-101-1 16.521.5 15.620.6 17.421.2 18.621.0 L-101-2 16.120.7 16.621.0 17.420.8 18.821.3 L-102-1 19.321.5 19.720.8 20.421.8 22.121.3 L-102-2 18.121.0 19.6i0.9 19.520.9 20.721.0 L-103-1 17.821.5 17.111.2 19.3tl.3 19.721.6 L-103-2 17.921.2 20.010.8 18.821.1 21.5 1.0 L-105-1 17.5 1.0 18.221.0 19.221.1 21.6 1.1 L-105-2 18.021.4 17.721.0 19.1 1.4 19.0 1.5 L-106-1 16.621.4 17.320.7 18.3 1.1 19.4 0.8 L-106-2 15.621.0 15.520.9 17.221.6 16.021.5 L-107-1 17.121.1 19.121.4 19.821.4 21,4 1.6 L-107-2 16.5 0.8 17.020.7 17.721 .2 17.721.0 L-108-1 16.921.1 19.121.0 18.721.2 20.921.0 L-108-2 14.721.1 15.120.7 15.4 1.1 16.321.3 L-109-1 17.411.0 18.220.8 20.021.2 20.321.1 L-109-2 16.8 1.3 17.920.9 18.521.5 18.721.2 L-110-1 17.211.1 17.2 0.7 19.320.8 19.120 8 L-110-2 16.8!1.1 17.420.8 18.221.5 18.821.0 L-111a-1 16.420.7 18.120.7 18.7 1.2 20.021.0 L-111a-2 16.52'.1 19.3 1.3 18.021.1 21.021.7 L-111b-1 16.721.2 18.110.7 19.822.0 20.720.7 L-111b-2 17.621.4 17.421.3 18.7 1.2 19.620.9 L-112-1 15.6 1.6 17.1 0.9 15.6 1.0 18.911.4 L-112-2 16.7 1.2 18.4 1.1 18.6!1.3 19.421.2 L-113a-1 15.520.9 19.221.2 16.321.6 20.221.4 L-113a-2 17.1 1.0 20.321.4 18.721.1 21.421.4 L-113b-1 14.811.1 18.820.9 16.0 1.5 20.0!1.0 L-113b-2 17.221.1 18.621.1 19.421.3 20.0 1.0 L-114-1 14.721.3 17.8t0.7 16.921.4 19.321.3 L-114-2 17.3 1.3 18.3 0.9 19.3 1.1 19.5 1.2 Mean 2 s.d. 16.821.0 18.021.2 18.3 1.3 19.721.4 i

51

LASALLE 4 e Table 5,1-1 (continued)

GAMMA RADIATION, AS MEASURED BY THERM 0 LUMINESCENT DO5! METERS (TLDs)

SPECIAL PROGRAM Outer Ring, Hear 5 Miles Radius, Indic6 tor Locations 1st Quarter 2nd Quarter 3rd Quarter ,4th Quarter Date Placed: 12-29-89 03-30-90 06-29-90 09-29-90 Date Removed: 03-30-90 06-29-90 09-29-90 12-28-90 Days in the Field: 91 91 92 90 location Average mR/Qtr.

L-201-1 15.321.1 17.421.0 16.621.2 18.921.2 L-201-2 17.421.2 17.920.8 19.121.5 18.6!0.8 L-202-1 15.5t1.5 17.220.9 16.621.1 17.9 1.0 L-202-2 17.220.9 17.821.0 18.121.0 19.621.8 L-203-1 14.6 1.1 15.6 1.0 15.111.2 15.921.5 L-203-2 17.421.2 19.021.3 18.421.5 20.221.9 L-204-1 15.121.5 17.420.6 16.921.2 18.721.0 L-204-2 15.6 1.0 17.020.7 16,821.6 17.820,9 L-205-1 15.921.3 19.431.0 16.921.2 21.321.8 L-205-2 15.220.8 17.120.9 16.921.0 18.321.3 L-206-1 15.421.4 17.421.0 16.721.1 19.621,4 L-206-2 16.321.3 16.6 0.9 17.621.6 17.2 0.9 L-207-1 16.720.8 19.120.7 17.5 0.9 P0.720.8 L-207-2 15.520.9 15,220.8 16.8 0.9 16.421.3 L-208-1 18.121.5 19.420.6 20.521.6 21.020.8 L-208-2 16.111.0 17.820.7 17.021.3 19.121.4 L-209-1 19.020.5 18.8 1.2 20.421.0 21.221.1 L-209-2 15.8 1.0 18.0 0.8 16.7 1.4 18.121.2 L-210-1 16.920.9 19.8 0.7 19.2 0.9 21.420.9 L-210-2 17.7 1.0 18.320.7 19.6 1.2 17.7 0.8 L-211-1 19.421.3 19.9 0.8 21.111.6 21 .2 1.1 L-211-2 17.411.2 17.920.8 19.521.5 19.020.8 L-212-l' 15.821.1 17.8 0.7 17.3 1.1 19.021.0 L-212-2 17.311.4 17.920.9 20.621.7 19.6 1.0 L-213-1 17.3 1.2 15.521.1 18.621.0 18.321.3 L-213-2 16.3 1.4 19.420.8 19.221.9 22.621.1 L-214-1 18.6!1.0 19.620.8 20.3 1.2 20.521.6 L-214-2 18.4 1.1 19.8 0.8 21.1 1.8 23.111.1 L-215-1 17.320.9 19.220.6 19.4 1.1 20.4 1.5 L-215-2 18.020.9 20.5 0.7 20.5 1.2 23.521.2 L-216-1 16.5 1.0 18.3 0.9 17.7 1.2 19.521.2 L-216-2 16.721.1 18.420.6 18.7 1.8 20,620.9 Mean i s.d. 16.7 1.2 18.221.4 18.421.6 19.621.8 52

LASALLE

! Table 5.1-1 (continued)

GAMMA RADIATION, AS MEASURED BY THERM 0 LUMINESCENT DO5! METERS (TL0s)

RESTRICTED AREA MONITORING PROGRAM 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter

- Date Placed: 12-29-89 03-30-90 06-29-90 09-29-90 Date Removed: 03-30-90 06'29-90 09-29-90 12-28-90 Days in the Field: 91 91 92 90 Locationa Average mR/Qtr.

lettial Pro 9t am:

L-304-1 18.71*. 5 20.0 1.3 21.0 1.7 22.621.4 L-305-1 17.921.4 18.326.8 19.729.9 20.521.2 L-308-1 13.3 1.0 15.2i0.8 14.811.1 17.0 0.8 1-310-1 25.2 1.4 29.610.9 40.413 7D 25.111.1 L-316-1 18.911.7 19.8 1.0 21.8 1.7 22.821.1 a

Description of locations:

L-304-1 Leased Farmland L-305-1 Boat Ramp L-308-1 Proposed Site of Relocated Meteorolo9 1cal Tower L-310-1 NGET Building L-316-1 Leased Farmland b

Spare No.1 placed at Location L-310-1 on 09-02-90. Results are prorated to 91 days.

1 53

t b 4

APPENDIX 11 METEOROLOGICAL DATA 1

54

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE- 0 0 0 0 0 0 0 NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 Hours of calm in this stability class: 0 Hour's of missing wind measurements in this stability class: 0 Hours-of missing stability measurements in all stability classes: 13 55

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 ,

STA31LITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 375-33 FT)

WINOS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-16 19-24 GT 24 TOTAL Y

N O O O O O O O NNE O O O O O O O

NE O O O O O O O ENE O O O O O O O 6 0 0 0 0 0 0 0 ESE O O O O O O O SE O O O O O 0- 0

-SSE O O O O O O O S 0 1 0 0 0 0 1 SSW 0 2 0 0 0 0 2 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 -0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 3 0 0. 0 0 3 Hours of calm in this stability class: 0 Hours'of missing wind measurements in this st' ability class: 0 Hours of missing stability measurements in all stability classes: 13 56

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O 1 0 0 1 NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O 0 0 0 0 0 0 SE O O O O O O O SSE O O O O O O O

~

S 0 0 0 0 0 0 0 SSW 0 1 0 1 4 2 8 SW 0 0 0 0 0 0 0 WSW 0 0 0 1 3 0 4 W 0 0 0 0 0 3 3 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 1 1 NNW 0 0 0 2 1 0 3 VARIABLE O O O O O O O TOTAL 0 1 0 5 8 6 20 iours of calm in this stability class: 0 iours of missing wind measurements in this stability class: O lours of missing stability measurements in all stability classes: 13 i

57

LASALLE NUCLEAR POWER STAT 80N PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - NEUTRAL (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 6 15 19 10 5 56 NNE 1 6 11 19 9 9 55 NE 2 5 29 30 17 2 85 ENE O 2 4 20 11 16 53 E 2 3 3 10 17 15 50 ESE O O 2 6 3 0 11 SE 1 3 2 7 4 1 18 SSE O 4 4 6 13 0 27 S 0 3 7 19 14 16 59 SSW 1 4 17 11 9 38 80 SW 1 7 20 9 12 21 70 WSW- 2 2 18 7 11 9 49 1

W 2 5 5 13 18 30 73 WNW 1 12 5 8 24 66 116 NW 1 4 13 15 39 44 116 NNW 1 5 20 43 10 13 92 VARIABLE O O O O O O O TOTAL 16 71 175 242 221 285 1010 Hours of calm in this stability class: 0

' Hours of missin9 wind measurements in this stability class: 75 Hours of missing stability measurements in all stability classes: 13 58

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 1 0 4 6 0 11 NNE 2 0 2 7 2 0 13 NE 1 2 6 1 2 0 12 ENE 2 1 3 0 1 1 8 E O 6 7 2 5 5 25 ESE O 6 4 4 6 6 26 SE O 3 3 6 4 13 29 SSE 1 0 2 5 5 24 37 S 0 0 10 5 10 100 125 SSW 1 3 3 6 19 105 137 SW 0 2 4 10 10 34 60 WSW 0 5 4 9 9 14 41 W 1 1 5 13 12 26 58 WNW 0 2 8 17 14 19 60 NW 0 3 4 12 12 12 43 NNW 0 1 2 9 6 2 20 VARIABLE O O O O O O O TOTAL 8 36 67 110 123 361 705 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 51 Hours of missing stability measurements in all stability classes: 13 i

59

LASALLE NUCLEAR POWER STATZOM PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE' O O O O O O O NE O O O O O O O ENE O 1 0 0 0 0 1 E O O O O 1 1 2 ESE O O O 3 1 0 4 SE- 0 0 2 3 2 1 8 SSE O O O 6 3 5 14 S 0 2 2 10 7 22 43 SSW 1' 3 1 8 7 17 37 SW O 1 3 6 9 29 48 WSW 0 2 1 5 2 21 31 W 0 0 3 7 6 6 22 WNW 0 1 1 6 4 1 13

- NW- 0 2 6 1 2 1 12

-NNW. 0 0 0 0' O O O VARIABLE O O O O O O O L

L TOTAL 1 12 19 55 44 104 235 l

l Hours.of calm in this stability class: 0-Hours of missin9 wind measurements in this stability class: 3 Hours of. missing stability measurements in all stability classes: 13 l

l'-

60

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O 1 0 1 SE O O O 1 1 0 2 SSE O O 1 1 3 2 7 S 0 0 0 3 3 8 14 SSW 0 0 0 0 2 7 9 SW 0 0 0 0 0 1 1 WSW 0 0 0 0 1 5 6 W 0 0 0 1 2 0 3 WNW 0 0 t 0 0 1 2 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 2 6 13 24 45

=iours of calm in this stability class: 0 iours of missing wind measurements in this stability class: 0 iours of missing stability measurements in all stability classes: 13 61

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

.) DIRECTION

.7-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O

] NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW . O O O O O O O NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours'of missing stability measurements in all stability classes: 35 I

62

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - MODERATELY UNSTABLE- (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET

! WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O 6 0 0 0 6 NE O O O 1 0 0 1 ENE O O O 1 0 0 1 E O O O O O O- 0 ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 1 0 0 1 2 SSW 0 0 5 1 8 11 25 SW 0 1 0 4 3 0 8 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 2 2 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 1 1 VARIABLE O O O O O O O TOTAL 0 1 12 7 11 15 46 Hours of calm in this stability class
0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 35 63

LASALLE NUCLEAR POWER STATZON PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 5 0 0 0 5 NNE O O 7 3 0 0 10 NE O O 2 5 0 0 7 ENE O O 1 0 0 0 1 E O O 1 1 0 0 2 ESE O O O O O O O SE 0- 0 0 0 0 0 0

-SSE O O O O 2 0 2 S O O 5 0 3 6 14 SSW 0 0 8 2 6 8 24 SW 0 2 3 3 2 0 10

~WSW 0 0 0 0 0 0 0 W~ 0 0 0 0 0 3 3 WNW 0 0 0 0 1 5 6 NW 0 0 0 0 0 2 2 NNW. 0 0 0 0 6 1 7 VARIABLE O O O O O O O I

TOTAL 0 2 32 14 20 25 93 Hours of calm in-this stability class: 0 Hours -of missing. wind measurements in this stabili ty class: 1 Hours'of missing stability measurements in all stability classes: 35 64

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - NEUTRAL (DIFF TEMP 375-33 FT) l WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 8 13 16 14 2 53 NNE O 8 9 16 15 2 50 NE O 16 33 32 3 0 84 ENE O 7 12 19 7 1 46 E O O 15 9 4 17 45 ESE 1 3 6 6 5 7 28 SE O 4 2 8 9 0 23 SSE O 5 16 16 12 6 55 S 1 6 14 15 25 22 83 SSW 0 5 5 14 23 31 78 SW 0 4 9 14 20 20 67 WSW 1 7 8 8 13 7 44 W 0 4 12 28 11 11 66 WNW 1 4 14 34 18 39 110 NW 0 3 19 31 50 26 129 NNW 0 7 11 12 34 8 72 VARIABLE O O O O O O O TOTAL. 4 91 198 278 263 199 1033 Hours of calm in this stability class: 0 Hours of missin9 wind measurements in this stability class: 0 Hours of missin9 stability measurements in all stability classes: 35 l

65

i LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 1 8 6 6 0 22

-NNE 1 4 3 8 5 0 21 NE O 2 14 16 3 0 35 ENE 1 2 4 8 3 0 18 E 1 3 16 9 5 0 34 ESE O 2 5 7 9 2 25 SE O 1 2 3 14 4 24 SSE 2 1 3 11 13 9 39 S 0 2 5 6 18 24 55 SSW 0 2 13 8 13 62 98 SW O 2 11 12 11 9 45 WSW 0 6 11 8 2 9 36 W 0 3 11 13 6 5 38 WNW 0 0 11 16 10 17 54 NW 0 3 5 11 12 3 34 NNW 0 4 5 8 2 0 19 VARIABLE O O O O O O O TOTAL 6 30 127 150 132 144 597 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 35 66

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS -~ MODERATELY STABLE (DIFF TEMP S75-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O 3 0 0 3 NNE O 1 2 2 0 0 5 NE O O 1 2 0 0 3 ENE O O O 1 2 0 3 E 1 0 4 6 2 0 13 ESE O 1 1 4 2 0 8 SE O 3 2 1 6 0 12 SSE O O 3 4 6 10 23 S 0 1 3 6 5 18 33 SSW- 0 2 2 7 5 41 57 SW 0 2 4 5 6 9 26 l

l WSW 0 2 8 9 7 0 26 W 0 0 7 7 12 3 29 WNW 0 0 5 9 24 9' 47 NW 0 0 2 10 7 2 21 NNW 0 3 3 2 2 0 10 VARIABLE O O O O O O O l TOTAL 1 15 47 78 86 92 319 l

(Nours of calm in this stability class: 0 Mouro of missing wind measurements in this stability class: 0 Mours.of missing stability measurements in all stebility classes: 35 67

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 0 0 0 0 0 1 NNE O 3 0 0 0 0 0 NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O 2 1 0 3 SE 1 0 0 3 1 1 6 SSE O O 2 2 5 8 17 S O O 3 4 5 2 14 SSW 0 0 1 0 0 0 1 SW 0 0 2 4 2 4 12 WSW 0 0 0 2 0 2 4 W 0 0 0 0 1 0 1 WNW 0 0 0 0 1 0 1 l NW 0 0 0 0 0 0 0 i

NNW 0 0 0 0 0 0 0 VARIABLE- 0 0 0 0 0 0 0 l

TOTAL 2 0 8 17 16 17 60 Hours of cal:a in this stability class: O Hours of missing wind measurements in this stability class: 0 Hours.of missing etability measurements in all stability classes: 35 l

l l

l l

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JULY -SEPTEMBER 1990 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED Al 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O

-SSE O O O O O O O S 0 0 0 1 0 0 1 SSW O O O O O O O SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW O O O O O O O NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 1 0 0 1 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stabilit/ measurements in all stability classes: 11 69

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 l STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 3 0 5 0 8 NNE O O 4 0 0 0 4 NE O O 4 2 0 0 6 ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 1 1 0 0 0 2 SSW 0 3 7 5 0 0 15 SW 0 0 3 7 2 3 15 WSW 0 0 0 1 0 0 1 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 1 0 0 1 VARIABLE O O O O O O O TOTAL 0 4 22 16 7 3 52 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 11 70

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 I

STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 5 4 0 0 9 NNE O O 4 2 0 0 6 NE O O 5 3 0 0 8 ENE O O 3 0 0 0 3 E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O 5 1 7 0 0 13 S 0 3 10 1 3 0 17 SSW O 2 7 4 3 2 18 SW 0 5 12 8 1 0 26 WSW 0 5 2 11 3 0 21 W 0 0 0 0 1 0 1 WNW 0 0 0 0 0 0 0 NW O O O O O O O NNW 0 0 1 4 1 0 6 VARIABLE O O O O O O O TOTAL 0 20 50 44 12 2 128 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 11 71

LASALLE NUCLEAR POWER STATf0N PERIOD OF RECORD - JULY-SEPTEMBER 1990 STABILITY CLASS - NEUTRAL (DIFF TEMP 375-33 FT)

WINDS ~ MEASURED AT 375 FEET WIND _

WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL

......... ..... ..... ..... ..... ..... ..... .n...

N 2 8 15 23 4 0 52 NNE 1 15 24 58 8 0 106 NE 1 20 53 63 5 0 142 ENE 2 8 25 29 3 0 67 E 3 9 19 19 1 0 51 ESE 1 7 17 3 1 0 29 SE 2 6 13 2 1 0 24 SSE O 5 22 19 6 0 52 S 1 8 21 22 5 0 57-SSW 3 8 8 15 16 3 53 SW 2 10 10 22 13 5 62 WSW O 8 10' 17 18 0 53 l

W 2 13 15 2 2 2 36 WNW- 3 24 7 13 5 4 56 NW 0 12 22 10 13 14 71

.NNW' 2 7 16 16 14 1 56 VARIABLE O O O O O O O

-TOTAL- 25 168 297 333 115 29 967-

--Hours of calm in this stability class: 0 Hours of. missing wind measurements in this stability class: 4

- Hours of' missing stability measurements.in all stability classes: 11 72 l

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 375-33 FT) l WINOS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 2 3 6 4 4 0 19 NNE O 5 7 20 10 0 42 NE O 11 29 12 1 0 53 ENE 1 12 13 7 0 0 33 E 5 4 13 17 3 2 44 ESE 1 3 8 6 2 0 20 SE O 7 7 8 6 0 28 SSE 1 3 5 4 3 1 17 S O 3 3 12 7 6 31 SSW 0 1 10 20 20 15 66 SW 1 6 6 7 18 23 61 WSW 2 5 13 5 7 4 36 W 0 7 8 1 2 1 19 WNW 2 5 2 4 1 0 14 NW 0 0 5 6 3 2 16 NNW 1 2 2 5 5 1 16 VARIABLE O O O O O O O TOTAL 16 77 137 138 92 55 515 iours of calm in this stability class: 0 iours of missing wind measurements in this stability class: 1 iours of missing stability measurements in all stability classes: 11 i

73

LASALLE NUCLEAR POWER STATION-

' PERIOD OF RECORD - JULY-SEPTEMBER- 1990 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 375-33 FT)

WINDS HEASURED AT 375. FEET WINO WIND SPEED (IN MPH)

DIRECTION .7-3 4-  ? 8-12 13-18 19-24 GT 24 TOTAL N- 0 1 1 3 2 0 7 NNE 1 0 1 0 0 0 2 NE 1 1 0 0 0 0 2 ENE O O 2 0 0 0 2 E 1 1 4 2 2 0 10 ESE O O 2 7 1 3 13 SE O O 7 9 7 4 27 SSE O 1 3 14 4 8 30 S 0- 2 3 15 13 16 49 SSW 0- 6 6 15 11 16 54 SW 2 4 16 12 21 42 97 WSW O 7 7 11 11 17 53 W 1 6 9 3 5 0 24 WNW 1 1 4 5 1 0 12 NW 1 2 4 8 3 0 18 NNW 0 0 4 5 2 0 11 VARIABLE O O O O O O O TOTAL- 8 32 73 109 83 106 411 Houro.of calm in_this-stability-class: 0

-Nours_of missin9 wind measurements in this stability class: O LHours of missing. stability measurements in all stability classes: 11 l

o l

74 L

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN HPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O 2 0 2 NNE O O O 1 1 0 2 NE 1 0 0 0 0 0 1 ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O 2 3 1 6 SSE O O 1 5 5 3 14 S 0 0 3 10 5 3 21 SSW 0 0 4 2 6 3 15 SW 0 2 0 1 6 14 23 WSW 0 0 0 3 1 2 6 W 0 0 0 3 3 3 9 WNW 0 0 0 6 5 2 13 NW 1 0 0 2 2 0 5 NNW O O O 1 0 0 1 VARIABLE O O O O O O O TOTAL 2 2 8 36 39 31 118 ours of calm in this stability class: 0 ours of missing wind measuremente in this stability class: O ours of missing stability measuremente in all stability classes: 11 75

+ .

LASALLE NUCLEAR DCWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 c STABILITY CLA3S - EXTREMELY UNSTABLE (DIFF TEMP 375-33 FT)

WINOS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O o SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3 76

l

\

! LASALLE NUCLEAR POWER STATION PERIOD OF RECCRD - OCTOBER-DECEMBER 1990 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET W.IND WIND SPEED (IN HPH)

DIRECTION .7-3 4- 7 8-12 13-18 ;9-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW J 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW O O O O O O O NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 12 Hours of missing stability measurements in all stability classes: 3 77

~ .. .-. . - . - . - . - . . - . - . . - -._ _ - . - .. - - - . .. - - _ ~ - - .

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN HPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S O O O O O O O SSW 0- 0 1 1 0 1 3 SW 0 0 1 0 0 2 3 WSW. O O O O O O O W 0 0 0 0 0 0 0 WNW 0 0 0- 0 0 0 0

, NW 0 0 0 0 1 1 2' NNW 0 0 0 0 0 0 0 VARIABLE. 0 0 0 0- 0 0 0 TOTAL. 0 0 2 1 _4 8 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 14 g Houro of missing stability measurements in all stability classes: 3' g

u e

78

LASALLE NUCLEAR POWER STATION i

PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - NEUTRAL (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 1 3 16 19 4 44 NNE O 1 2 9 28 4 44 NE O 3 5 19 11 1 39 ENE O O 3 5 4 6 18 E O 5 4 1 5 5 20 ESE O 4 7 12 8 4 35 SE 2 1 12 16 5 0 36 SSE 1 3 12 29 11 2 58 S 2 6 3 15 12 17 55 SSW 3 3 19 19 11 34 89 SW 2 2 12 29 18 34 97 WSW 1 5 5 7 9 to 37 W 3 6 6 22 9 37 83 WNW 0 9 14 29 34 35 121 NW 0 5 12 26 18 54 115 NNW 0 9 12 23 14 4 62 VARIABLE O O O O O O O TOTAL 15 63 131 277 216 251 953 lours of calm in this stability class: 0 iours of missin9 wind measurements in this stability class: 69 iours of missing stability measurements in all stability classes: 3 79

9 e LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 l STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 3 10 8 4 1 26 NNE O 4 4 11 8 0 27 NE O 1 3 6 1 0 11 ENE O O 2 3 4 0 9 E O 4 1 2 8 2 17 ESE O 2 2 2 8 0 14 SE O O 5 3 7 8 23 SSE 2 3 2 9 13 11 40 S 0 1 7 11 8 47 74 SSW 0 0 7 7 11 114 139 SW 0 2 5 2 16 55 80 WSW 0 2 3 3 2 3 13 W 0 1 7 7 12 10 37 WNW 3 3 3 7 14 16 46 NW 0 3 9 11 5 7 35 NNW 1 3 5 8 14 4 35 VARIABLE O O O O O O O TOTAL 6 32 75 100 135 278 626 Hours of calm in this stability class; o Hours of missing wind measurements in this stchility class: 17 Hours of missing stability measurements in all ctability classes: 3 80 m.m._.__ m_. _ _ _ _ . _ ____

LASALLE NUCLEAR POWER STAT 80N PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL t

N O 1 3 8 9 0 21 NNE O O 2 5 0 0 7 NE O 1 2 2 0 0 5 ENE O 4 0 0 0 0 4 E O 1 2 0 0 0 3 ESE O 2 2 1 0 1 6 SE 3 9 6 2 9 4 33 SSE 1 5 9 0 2 10 27 S 2 0 4 8 1 11 26 SSW 1 1 1 8 7 42 60 SW 1 0 5 3 4 50 63 WSW 0 2 2 3 3 14 24 W 0 2 1 5 8 10 26 WNW 0 1 4 7 15 8 35 NW 1 1 1 5 9 8 25 NNW 0 1 2 14 6 0 23 VARIABLE O O O O O O O TOTAL 9 31- 46 71 73 158 388 Hourb of calm-in this stability class: 0 Hours of missin0 wind measurements in.this stability class: 0 Hours of missin9 stability measurements in all stability classes: 3 81

LASALLE NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECF.MBER 1990 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 375-33 FT)

WINDS MEASURED AT 375 FEET WIND WIND SPEED (IN MPH)

DIRECTION .7-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O 1 0 0 0 0 1 ENE O O O O O O O E O 1 0 0 0 0 1 ESE O O O 1 0 0 1 SE O 1 2 3 5 4 15 SSE O O 2 4 3 6 15 S 0 0 0 2 8 8 18 SSW 0 0 0 0 0 9 9 SW 0 0 0 0 1 17 18 WSW 0 1 1 2 7 15 26 W 0 0 1 3 0 3 7 WNW 0 0 0 2 0 1 3 NW 0 0 0 0 3 0 3 NNW 0 0 0 1 0 0 1 VARIABLE O O O O O O O TOTAL 0 4 6 18 27 63 118 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 3 82

APPENDlx 111 LISTING OF MISSED SAMPLES 83

LASALLE e

LISTING OF MISSED SAMPLES .

Expected Collection Sample Type Location Dates Reason t

i There were no missed samples in 1990. ,

1 i

i 84

m.. _ _

l- -

q ,

l i

l 3

l n

1 i

4 i-i t

l' l l APPENDIX IV ,

i.

i MILCH ANIMALS, NEAREST CATTLE, AND NEAREST RESIDENCES CENSUSES j-i 6

.~l

^

4 4

d 4

J e

M

= hh 2

. . _ _ . - - . . . ~ . _ _ . . , . . . . . . . . . . --,_ _. .._._-_. __-,,m._,_._

- . - _ . . .- - -_ - . .~ - _ - . . - . - . -

t

)

LASALLE ,

MILCH ANIMALS CENSUS, 1990 a .

There are no commercial dairy farms within a five mile radius of LaSalle County Station.

Sarpl,ing Locations L-19 Robert Bettenhausen Farm 8.5 miles 0180' Nunber of cows - 76 Number of fresh cows - 60 Diet consists of the following:

Ground feed

  • 10 lbs. per day Ground corn mix ** 10 lbs, per day
  • Ground feed consists of:

Hay 10 lbs.

Silage 70 lbs.

    • Ground corn mix consists of:

Corn 2000 lbs.

Oats 400 lbs.

Soybeans 400 lbs.

Minerals 50 lbs.

Sal t- 50 lbs. ,

1 L-16 Lowery Dairy Farms 8.2 miles 0120' Number of cows - 102 Number of fresh cows - 76 Diet-consists of the following: I Ground feed

  • 20 lbs. per day Corn and oats silage Free choice j Alfalfa hay Free choice
  • Ground feed mix consists of:

Ground corn 2000 lbs. i l Soybean meal 600 lbs.

l Pre-mix 300 lbs.-  ;

Salt 50 lbs.

i

~

a Supplemental search; one private residence, Loretta Gass, L-20; two milk

- cows , 4.6 miles at 3a8*.

66  !

i

i LASALLE

- MILCH ANIMALS CENSUS 1990 (continued)

L-17 Earl Hayer - Andrew Patterson 12.3 miles @ 18' tbmber of cows - 37 Number of fresh cows - 28 Diet consists of the following:

Ground corn mix

  • 15 lbs, per day Silege 20 lbs, per day Ha! Free choice
  • Ground corn mix consists of:

Corn 2000 lbs.

Oats 1000 lbs.

Protein 700 lbs.

Minerals 50 lbs.

Salt 50 lbs.

L-18 Flatness Dairy Farm 12.5 miles @ 10' Number e f cows - 50 Number of fresh cows - 39 Diet consists of the following:

Ground feed mix

  • 20 lbs per day Silage 20 lbs. per oay Hay Free choice
  • Ground feed mix consists of:

Corn 1,500 lbs.

Soybean meal 750 lbs.

Oats 750 lbs.

Linseed meal 100 lbs.

Minerals 50 lbs.

Census conducted by A. Lewis on June 13 cnd 14, 1990.

87

LASALLE f4EAREST RESIDENCE CENSUS,1990 tiearest resident of the laSalle Station within a five (5) mile radius.

D_irection Distance N 2.2 miles NNE 1.4 miles

, NE 1.8 miles ENE 3.4 miles E 3.1 miles ESE 1.6 miles SE 1.5 miles SSE 1.1 miles S 2.2 miles SSW 2.0 miles SW 0.7 miles WSW 1.3 miles W 0.9 miles WNW 1.0 miles NW 2.6 miles NNW 1.2 miles (new house)

Census conducted by A. Lewis on June 7, 1990.

88

LASALLE NEAREST CATTLE CENSUS, 1990 Nearest cattle of the LaSalle Station within a five (S) mile radius.

Direction pistance N 4.2 miles NNE 3.0 miles NE No cattle ENE 3.2 miles E No cattle j l

ESE No cattle 1

SE 4.8 miles l i

SSE 4.5 miles S No cattle SSW No cattle SW No cattle WSW No cattle W 3.4 miles WNW 1.0 miles NW No cattle NNW S.0 miles Census conducted by A. Lewis on July 10, 11 and 12,'1990.

89

e 8 l

APPENDIX V INTERLABOR ATORY COMPARISON PROGR AM RESULTS 90

i Appendix V Interlabor0 tory Comparison Program Results Teledyne Isotopes Midwest Laboratory (formerly Hazleton Environmental Sciences) has participated in interlaboratory comparison (crosscheck) programs since the formulation of its. quality control program in December 1971. These-programs are operated by agencies which supply environmentel-type samples (e.g., milk or

~ water) -containing concentrations of radionuclides known to the issuing agency but not to participant laboratories. The. pu

- provide an independent check on the laboratory,rpose s analyticalof such a program procedures and is to to

' alert it to any possible problems.

Participant laboratories measure the concentrations of specified radionuclides- <

and report them to the issuing agency. Several months later. the agency

~

' reports:the known values to the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits. indicate a need to check -the instruments or procedures used.

The results in Table A-1 were obtained through participation in the environ.

mental sample crosscheck program for mil k,- water,- air- filters, and food samples

- during the~ period January 1986 through December,1990. This program has been  ;

(. conducted by the U.S. Environmental Protection Agency Intercomparison and  ;

Calibration St:ction - Quality Assurance Branch, Environmental Monitoring and Support Labort. tory, Las Vegas, Nevada.  ;

.Th'e- results. in Table ' A-2 were obtained for thermoluminescent dosimeters - (TLDs) during the teriod.1976,1977,1979,1980,1984, and .1985-1986 through partici-

..pation in-. tne 1Second, Third, Fourth, Fif th, Seventh, and Eighth International Intercomparison -of Environmental Dosimeters under the sponsorships listed in Table A-2.. Also Teledyne testing results are listed.

Table A-3 lists results of the analyses on in-house spiked samples.

Table Ai 4 lists results of the analyses on in-house " blank" samples.

' Attachment B lists acceptance-criteria for " spiked" samples.-

Addendum.to . Appendix A provides explanation for out-of-limit results.

91

Table A-1. U.S. Environmental Protection Agency's crosscheck program, comparison of EPA and Teledyne Isotopes Midwest Laboratory results for milk, water, air filters, and food samples,1986 through 1990.a Concentration in pCi/Lb epa Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 120C 1s, N=1 Limits STF-447 Food Jan 1986 Sr 89 24.312.5 25.015.0 16.3-33.7 Sr 90 17.310.6 10.011.5 7.4-12.6 1-131 22.712.3 20.010.6 9.6-30.4 Cs 137 16.310.6 15.015.0 6.3-23.7 K 927146 9502144 701-1199 STW-448 Water Feb 1986 Cr-51 45.023.6 38.015.0 29.3-46.7 Co-60 19.711.5 18.015.0 9.3-26.7 Zn-65 44.013.5 40.015.0 31.3-48.7 Ru-106 <9.0 0.015.0 0.0-8.7 Cs-134 28.312.3 30.0 5.0 21.3-38.7 Cs-137 23.710.6 22.015.0 13.3-30.7 STW-449 Water Feb 1986 H-3 5176248 52271525 4317-6137 STW-450 Water Feb 1986 V total 8.010.0 9.016.0 0.0-19.4 STM-451 Mil k Feb 1986 1-131 7.010.0 9.016.0 0.0-19.4

$TF-452 Water Mar 1986 Ra-226 3.8 0.1 4.110.6 3.0-5.2 Ra-228 11.010.5 12.411.8 9.2-15.5 STW-453 Water Mar 1986 Gr. alpha 6.710.6 15.015.0 6.3-23.7 Gr. beta 7.310.6 8.015.0 0.0-16.7 STW-454 Water Apr 1986 1-131 7.010.0 9.016.0 0.0-19.4 STW-455 Water Apr 1986 456 (Blind)

Sample A Gr. alpha 15.021.0 17.015.0 8.3-25.7 Ra-226 3.110.1 2.910.4 2.1-3.7 Ra-228 1.520.2 2.020.3 1.5-2.5 Uranium 4.710.6 5.016.0 0.0-15.4-Sample B Gr. beta 28.711.2 35.0 5.0 26.3-43.7 Sr-89 5.720.6 7.0 5.0 0.0-15.7 Sr-90 7.0 0.0 7.011.5 4.4-9.6 Co-60 10.711.5 10.015.0 1.3-18.7 Cs-134 4.0 1.7 5.015.0 0.0-13.7 L

C s-137 5,310.6 5.015.0 0.0-13.7 l 92

Table A-1. (continued)

Concentration in pC1/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 12ec 15 N=1 Limits STAF-457 Air Apr 1986 Gr. alpha 13.710.6 15.015.0 6.3-23.7 Filter Gr. beta 46.320.6 47.015.0 38.3-55.7 Sr-90 14.710.6 18.011.5 15.4-20.6 Cs-137 10.710.6 10.015.0 1.3-18.7 STV-458 Vrine Apr 1986 Tritium 4313170 44231189 4096-4750 STW-459 Water May 1986 Sr-89 4.310.6 5.015.0 0.0-13.7 Sr-90 5.020.0 5.011.5 2.4-7.6 STW-460 Water May 1986 Gr. alpha 5,310.6 8.015.0 0.0-16.7 Gr. beta 11.311.2 15.015.0 6.3-23.7 STW-461 Water Jun 1986 Cr-51 <9.0 0.015.0 0.0-8.7 Co-60 66.011.0 66.015.0 57.3-74.7 Zn-65 87.321.5 86.015.0 77.3-94 .7 Ru-106 39.712.5 50.025.0 41.3-58.7 Cs-134 49.322.5 49.015.0 40.3-57.7 Cs-137 10.321.5 10.015.0 1.3-18.7 STW-462 Water Jun 1986 Tritium 3427125 31251361 2499-3751 STM-464 Mil k Jun 1986 Sr-89 <1.0 0.015.0 0.0-8.7 Sr-90 15.310.6 16.011.5 13.4-18.6 1-131 48.312.3 41.016.0 30.6-51.4 Cs-137 43.721.5 31.025.0 22.3-39.7 K 15671114 1600280 1461-1739 STW-465 Water Jul 1986 Gr. alpha 4.710.6 6.015.0 0.0-14.7 Gr. beta 18.711.2 18.015.0 9.3-26.7 STW-467 Water Aug 1986 1-131 30.310.6 45.016.0 34.4-55.4 STW-468 Water Au9 1986 Pu-239 11.310.6 10.111.0 8.3-11.9 STW-469 Water Aug 1986 Vranium 4.020.0 4.0 6.0 0.0-14.4 STAF-470 Air Sep 1986 Gr. alpha 19.311.5 22.015.0 13.3-30.7 471 Filter Gr. beta 64.012.6 66.025.0 57.3-74.7 472 Sr-90 22.0 1.0 22.015.0 19.4-24.6 Cs-137 25.711.5 22.015.0 13.3-30.7 STW-473 Water Sep 1986 Ra-226 6.010.1 6.1 0.9 4.5-7.7 Ra-228 8.711.1 9.121.4 6.7-11.5 93

I Table Aol. (continued)

Concentration in pCi/Lb EPA Resultd Lab Sample Oate TIML Result Cont rol Code Type Collected Analysis t2cc 15, N=1 Limits STW-474 Water Sep 1986 Gr. alpha 16.313.2 15.025.0 6.3-23.7 Gr. beta 9.021.0 8.015.0 0.0-16.7 STW-475 Water Oct 1986 Cr-51 63.325.5 59.015.0 50.3-67.7 Co-60 31.012.0 31.015.0 22.3 39.7 Zn-657 87.325.9 85.025.0 76.3-93.7 Ru-106 74.717.4 74.025.0 65.3-82.7 Cs-134 25.710.6 28.015.0 19.3-36.7 Cs-137 46.321.5 44.015.0 35.3-52.7 STW-476 Water Oct 1986 H-3 5918260 59731597 4938-7008 SPW-477 Water Oct 1986 (Blind)

Sample A Gr. alpha 34.016.0 40.015.0 31.3-48.7 Ra-226 5.810.2 6.010.9 4.4-7.6 Ra 228 2.7tl.0 5.010.8 3.7-6.3 Uranium 11.010.0 10.016.0 0.0 20.4 Sample B Gr. beta 38.721.2 51.015.0 42.3-59.7 Sr-89 5.0t0.0 10.0t5.0 1.3-18.7 Sr-90 3.010.0 4.011.5 1.4-6.6 Co-60 24.711.2 24.015.0 15.3 32.7 Cs-134 11.022.0 12.025.0 3.3-20.7 Cs-137 9.321.2 8.015.0 0.0-20.4 STM-479 Milk Nov 1986 Sr-89 7.711.2 9.025.0 0.3-17.7 Sr-90 1.010.0 0.021.5 0.0-2.6 1-131 52.3t3.1 49.016.0 38.6-59.4 Cs-137 45.713.1 39.015.0 30.3-47.7 K 14891104 1565t78 1430-1700

STU-480 Urine Nov 1986 H-3 5540126 52572912 4345-6169 L

l- STW-481 Water Nov 1986 Gr. alpha 12.014.0 20.015.0 11.3-28.7 Gr. beta 20.023.5 20.0t5.0 11.3-28.7 STW-482 Water Dec 1986 Ra-226 6.720.2 6.8tl.0 5.0-8.6 Ra-228 5.210.2 11.121.7 8.2-14.0 STW-483 Water Jan 1987 Sr-89 19.725.0 25.0 5.0 16.3-33.7 L Sr-90 21.0i2.0 25.0tl.5 22.4-27.6

l Table A 1. (continued) i Concentration in pCi/Lb EPA Resultd Lab Sample Date ilML Result Control Code Type Collected Analysi s 22cc 15, N=1 Limits STW-484 Water Jan 1987 Pu-239 17.022.3 16.711.7 13.8-19.6 STF-486 Food Jan 1987 Sr-90 36.024.0 49.0210.0 31.7-66.3 1-131 78.023.4 78.028.0 64.1-91.9 Cs-137 89.723.0 84.015.0 75.3-92.7 K 942156 980149 895-1065 STF-487 Food Jan 1987 Sr-90 2.010.0 ---

(Blank) 1-131 <3 ---

Cs-137 <2 ---

K 9932102 ---

STW-488 Water Feb 1987 C0 60 49.020.0 50.015.0 41.3-58.7 Zn-65 96.017.2 91.015.0 82.3-99.7 Ru-106 92.0120.2 100.015.0 91.3-108.7 Cs-134 53.023.4 59.015.0 50.3-67.7 Cs-137 89.324.6 87.015.0 78.3-95.7 ST W-489 Water Feb 1987 H-3 41302140 42091420 3479-4939 STW-490 Water Feb 1987 Uranium 8.321.2 8.026.0 0.0-18.4 STM-491 Mil k Feb 1987 1-131 10.010.0 9.010.9 7.4-10.6 STW-492 Water Mar 1937 Gr. alpha 3.721.2 3.015.0 0.0-11.7 Gr. beta 11.321.2 13.015.0 4.3-21.7 STW-493 Water Mar 1987 Ra-226 7.010.1 7.3 1.1 5.4-9.2 Ra-228 7.112.3 7.521.1 5.5-9.5 SN-494 Water Apr 1987 l-131 8.020.0 7.010.7 5.8-8.2 STAF-495 Air Apr.1987 Gr. alpha 15.020.0 14.015.0 5.3-22.7 Filter Gr. beta 41.022.0 43.015.0 34.3-51.7 Sr-90 16.311.2 17.011.5 14.4-19.6 Cs-137 7.010.0 8.025.0 0.0-16.7 STW-496 Water Apr 1987 497 (Blind)

Sample A Gr. alpha 30.7 1.2 30.018.0 16.1-43.9 Ra-226 3.910.2 3.920.6 2.9-4.9 Ra-228 4.920.9 4.0 0.6 3.0-5.0 Uranium 5.010.0 5.0 6.0 0.0-15.4 95

l l

Table A-1. (continued)

Concentration in pCi/Lb EPA Resultd Lab Sample Date ilHL Result Control Code Type Collected Analysis 12cc 15, N=1 Limits STW-496 Water Apr 1987 497 (Blind)

Sample B Gr. beta 69.319.4 66.015.0 57.3-74.7 Sr-89 16.323.0 19.015.0 10.3-27.7 Sr-90 10.020.0 10.021.5 7.4-12.6 Co-60 8.323.0 8.025.0 0.0-16.7 Cs 134 19.022.0 20.015.0 11.3-28.7 Cs-137 14.721.2 15.015.0 6.3 23.7 STU-498 Urine Apr 1987 H-3 60171494 56202795 4647-6593 STW-499 Water May 1987 S r-89 38.016.0 41.015.0 32.3-49.7 S r-00 21.012.0 20.011.5 17.4-22.6 STW-500 Water May 1987 Gr. alpha 9.023.4 11.015.0 2.3-19.7 Gr. beta 10.321.2 7.025.0 0.0-15.7 STW-501 Water Jun 1987 Cr-51 40.018.0 41.015.0 32.3-49.7 Co-60 60.323.0 64.015.0 55. 3- 7 2 .;'

Zn-65 11.325.0 10.015.0 1.3-18.7 Ru-106 78.316.4 75.015.0 66.3-83.7 Cs-134 36.713.0 40.015.0 31.3-48.7 Cs-137 80.314.2 80.015.0 71.3-88.7 STW-502 Water Jun 1987 H-3 2906286 28951357 2277-3513 STW-503 Water Jun 1987 Ra-226 6.920.1 7.311.1 5.4-9.2 Ra-228 13.311.0 15.212.3 11.2-19.2 STM-504 Milk Jun 1987 Sr-89 57.024.3 69.015.0 60.3-77.7 Sr-90 32.011.0 35.025.0 32.4-37.6 1-131 64.012.0 59.016.0 48.6-69.4 Cs-137 77.710.6 74.015.0 65.3-82.7 K 1383117 1525276 1393-1657 STW-505 Water Jul 1987 Gr. alpha 2.310.7 5.015.0 0.0-13.7 Gr. beta 4.021.0 5.015.0 0.0-13.7 STF-506 Food Jul 1987 1-131 82.714.6 80.028.0 66.1-93.9 Cs-137 53.713.0 50.015.0 41.3-58.7 K 1548257 16802B4 1534-1826 STW-507 Water Aug 1987 1-131 45.724.2 48.016.0 37.6-58.4 96

e 8 l Table A-1. (continued)

Concentration in PCi/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Coll ected Analysi s 22cc is, N=1 Limits STW-508 Water Aug 1987 Pu 239 5.820.2 5.320.5 4.4-6.2 STW-509 Water Aug 1987 Uranium 13.310.3 13.026.0 2.6-23.4 STAF-510 Air Aug 1987 Gr. alpha 9.720.4 10.015.0 1.3-18.7 Filter Gr. beta 28.310.6 30.025.0 21.3-38.7 Sr-90 10.020.9 10.021.5 7.4-12.6 Cs-137 10.011.0 10.025.0 1,3-18.7 STW-511 Water Sep 1987 Ra-226 9.910.1 9.721.5 7.2-12.2 Ra-228 8.111.4 6.311.0 4.6 8.0 STW-512 Water Sep 1987 Gr. alpha 2.010.6 4.015.0 0.0-12.7 Gr. beta 11.311.3 12.015.0 3.3-20.7 STW-513 Water Sep 1987 H-3 44731100 a4921449 3714-5270 STW-514 Water Oct 1987 (Blind)

Sample A Gr. alpha 29.322.6 28.027.0 15.9-40.1 Ra-226 4.920.1 4.810.7 3.6-6.1 Ra-228 4.211.0 3.620.5 2.7-4.5 Uranium 3.010.1 3.0 6.0 0.0-13.4 Sample B Sr-89 14.321.3 16.025.0 7.3-24.7 Sr-90 9.710.4 10.0*1.5 7.4-12.6 Co-60 16.723.0 16.025.0 7.3-24.7 Cs-134 16.722.3 16.015.0 7.3-24.7 Cs-137 24.313.3 24.025.0 15.3-32.7 STW-516 Water Oct 1987 Cr-51 80.3 17.5 70.015.0 61.3-78.7 Co-60 16.012.3 15.015.0 6.3-23.7 Sample A Zn-65 46.315.6 46.025.0 37.3-54.7 Ru-106 57.3215.4 61.025.0 52.3-69.7 Cs-134 23.722.5 25.025.0 16.3-33.7 Cs-137 51.7 3.2 51.015.0 42.3-59.7 STU-517 Urine Nov 1987 H-3 72672100 74322743 6145-8719 STW-518 Water Nov 1987 Gr. alpha 3.0t2.0 7.025.0 0.0-15.7 Gr. beta 15.712.3 19.015.0 10.3-27.7 STW-519 Water Dec 1987 1-131 26.023.0 25.016.0 15.6-36.4 1

97

_ _ _ _ _ _ - - _ - - _ - - - _ _ - - = - . - - - - - - - - -

Table A 1. (continued)

Concentration in pC1/Lb EPA Resultd Lab Sample Date T!ML Result Control Code Type Collected Analysis 120C ls, N=1 Limits '

STW-520 Water Dec 1987 Ra-226 5.120.8 4.820.7- 3.6-6.0 <

Ra 228 3.410.1 5.320.8 3.9-6.7 STW-521 Water Jan 1988 Sr-89 27.325.0 30.015.0 21.3-38.7 Sr-90 15.321.2 15.021.5 12.4 17.6 STW-523 - Water Jan-1988 Gr. alpha 2.311.2 4.015.0 0.0-12.7 Gr. beta 7.721.2 8.025.0 0.0 16.7

-STF 524- Food Jan 1988 Sr 44.014.0 46.025.0 37.3-54.7 Sr 90 53.022.0 55.022.8 50.2 59.8  !

l-131 102.324.2 102.0210.2 84.3-119.7 Cs-137 95.716.4 91.015.0 82.3-99.7 K 10111158 1230262 1124 1336 STW-525 Water Feb 1988 Co-60 69.312.3 69.025.0 60.3-77.7 3 Zn-65 99.023.4 94.019.4 77.7-110.3 Ru-106 92.7114.4 105.0210.5 86.8-123.2 Cs-134 61.728.0 64.025.0 55.3-72.7-Cs-137 99.723.0 94.0t5.0 85.3-102.7

-STW 526 Water Feb 1988 H-3 34532103 33272362 2700-3954 l

STW-527- Water- .Feb 1988 -Vranium 3.020.0 3.026.0 0.0-13.4-STM-528 Mil k Feb 1988 131 4.711.2 4.020.4 3.3-4.7  :

STW-529 Water- Mar 1988 Ra-226 7.110.6 7.621.1 5.6-9.6 Ra-228- nae 7.7tl.2' 5.7 9.7 STW-530 Water- Mar 1988 Gr. alpha -4.311.2- 6.015.0 0.0-14.7 Gr.' beta 13.321.3 13.015.0. 4.3-21.7 STAF-!i31 Air' Mar 1988 Gr. alpha - 21.022 =.0 20.025.0 11'.3-28.7 Filter- Gr. beta 48.010.0 '50.015.0 41.3-58.7- '

S r-90 16.711.2 17.021.5 14.4-19.6; Cs-137 18.711.3 16.0!5.0 -7.3<24.7-

-STW-532 Water. Apr 1988 ~1-131 9.022.0 7.510.8 _6.2-8.8 ,

f I

98

Table A-1. (contiaved)

Concentration in pC1/Lb EPA Resultd Lab Sample Date T!!!L Result Cont rol Code Type Collected Analysis 22cc Is, N=1 Limits STW-533 Water Apr 1988 534 (Blind)

Sample A Gr. alpha NDf 46.0111.0 27.0-65.0 Ra-226 to 6.411.0 4.7-8.1 Ra-228 to 5.610.8 4.2-7.0 Uranium 6.020.0 6.026.0 0.0-16.4 Sample B Gr. beta ND 57.015.0 48.3-65.7 S r-89 3.311.2 5.015.0 0.0-13.7 Sr-90 5.311.2 5.0*1.5 2.4-7.6 Co-60 63.311.3 50.015.0 41.3-58.7 Cs-134 7.721.2 7.015.0 0.0-15.7 Cs-137 8.321.2 7.025.0 0.0-15.7 STU-535 Urine Apr 1988 H-3 64832155 62021620 5128-7276 STW-536 Water Apr 1988 Sr-F9 14.721.3 20.025.0 11.3-28.7 Sr-90 20.0 2.0 20.0 1.5 17.4-22.6 STW-538 Water Jun 1988 Cr-51 331.7213.0 302.0230.0 250.0-354.0 Co-60 16.012.0 15.025.0 6.3-23.7 Zn-65 107.7211.4 101.0110.0 83.7-118.3 Ru-106 191.3111.0 195.0120.0 160.4-229.6 Cs-134 18.324.6 20.025.0 11.3-28.7 Cs-137 26.321.2 25.015.0 16.3-33.7 STW-539 Water Jun 1988 H-3 5586192 55651557 4600-6530 STM-541 Mil k Jun 1988 Sr-89 33.7111.4 40.015.0 31.3-48.7 Sr-90 55.325.8 60.023.0 54.8-65.2 1-131 103.713.1 94.019.0 78.4-109.6 Cs-137 52.723.1 51.015.0 42.3-59.7 K 1587123 1600180 1461-1739 STW-542 Water Jul 1988 Gr. alpha 8.714.2 15.025.0 6.3-23.7 Gr. beta 5.321.2 4.015.0 0.0-12.7 STF-543 Food Jul 1988 Sr-89 NDf 33.015.0 24.3-41.7 Sr-90 ND 34.022.0 30.5-37'.5 1-131 115.025.3 107.0111.0 88.0-126.0 Cs-137 52.716.4 49.025.0 40.3-57.7 K 1190166 1240 62 1133-1347 1

99

i Table A-1. (continued) 1 -

Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Cont rol Code Type Collected Analysi s 22cc 15, N=1 Limits STW 544 Water Aug 1988 1-131 80.020.0 76.018.0 62.1 89.9 STW-545 Water Au9 1988 Pu-239 11.010.2 10.211.0 8.5-11.9 STW-5d6 Water Aug 1988 Uranium 6.010.0 6.026.0 0.0-16.4 STAF-547 Air Aug 1988 Gr. alpha 8.010.0 8.015.0 0.0-16.7 Filter Gr. beta 26.321.2 29.015.0 20.3-37.7 Sr-90 8.012.0 8.011.5 5.4-10.6 Cs-137 13.012.0 12.015.0 3.3-20.7 STW-548 Water Sep 1988 Ra-226 9.320.5 8.412.6, 6.2-10.6 Ra-228 5.810.4 5.421.6 4.0-6.8 STW-549 Water Sep 1988 Gr. alpha 7.022.0 8.025.0 0.0-16.7 Gr. beta 11.311.2 10.025.0 1.3-18.7 ,

STW-550 Water Oct 1988 Cr-51 252.0114.0 251.0125.0 207.7-294.3 Co-60 26.012.0 25.015.0 16.3-33.7 Zn-65 158.3110.2 151.0115.0 125.0-177.0 Ru-106 153.029.2 152.0115.0 126.0-178.0 Cs-134 28.715.0 25.015.0 16.3-33.7 Cs-137 16.321.2 15.015.0 6.3-23.7 STW-551 Water Oct 1988 H-3 23331127 2316:350 1710-2927 STW-552 Water Oct 1988 553 (Blind)

Sample A Gr. alpha 38.318.0 41.0110.0 23.7-58.3 Ra-226 4.510.5 5.010.8 3.6 6.4 Ra-228 4.410.6 5.220.8 3.6-6.4 Uranium 4.721.2 5.026.0 0.0-15.4 Sample B Gr. beta 51 .323.0 54.015.0 45.3-62.7 Sr-89 3.721.2 11.025.0 2.3-19.7 Sr-90 10.7il.2 10.021.5 7.4-12.6 Cs-134 15.322.3 15.015.0 6.3-23.7 Cs-137 16.721.2 15.025.0 6.3-23.7 100

Table A-1. (continued)

Concentration in PCi/lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 22cC 15, N=1 Limits S1M-554 Mil k Oct 1988 Sr-89 40.3t7.0 40.015.0 31.3-48.7 Sr-90 51.022.0 60.013.0 54.8-65.2 1-131 94.013.4 91.019.0 75.4-106.6 Cs-137 45.014.0 50.015.0 41.3-58.7 K 1500145 1600180 1461-1739 STV-555 Urine Nov 1988 H-3 30301209 30252359 2403-3647 STW-556 Water Nov 1988 Gr. alpha 9.013.5 9.025.0 0.3-17.7 Gr. beta 9.7 1.2 9.015.0 0.3-17.7 STW-557 Water Dec 1988 1-131 108.713.0 115.0112.0 94.2-135.8 STW-559 Water Jan 1989 Sr-89 40.018.7 40.015.0 31 .3-48 .7 Sr-90 24.313.1 25.011.5 2a.4-27.6 STW-560 Water Jan 1989 Pu-239 5.811.1 4.220.4 3.5-4.9 STW-561 Water Jan 1989 Gr. alpha 7.311.2 8.015.0 0.0-16.7 Gr. beta 5.321.2 4.015.0 0.0-12.7 STW-562 Water Feb 1989 C r-51 245146 235124 193.4-276.6 Co-60 10.012.0 10.015.0 1.3-18.7 2n-65 170110 159216 139.2-186.7 Ru-106 18117.6 178118 146.8-209.2 Cs-134 9.713.0 10.015.0 1.3-18.7 Cs-137 11.711.2 10.015.0 1.3-18.7 STW-563 Water Feb 1989 1-131 109.014.0 106.0111.0 86.9-125.1 STW-564 Water Feb 1989 H-3 2820220 27541356 2137-3371 STW-565 Water Mar 1989 Ra-226 4.220.3 4.920.7 3.7-6.1 Ra-228 1.911.0 1.710.3 1.2-2.2 STW-566 Water Mar 1989 U 5.010.0 5.016.0 0.0-15.4 STW-567 Air Mar 1989 Gr. al pha 21.711.2 21.015.0 12.3-29.7 Filter Gr. beta 68.324.2 62.015.0 53.3470.7 Sr-90 20.012.0 20.021.5 17.4-22.6 Cs-137 21.3 1.2 20.025.0 11 .3-2 8 .7 1

101

Table A-1. (continued)

Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 22 cC 15, N=1 Limits STW 568 Water Apr 1989 569 (Blind)

Sample A Gr. alpha 22.712.3 29.027.0 16.9-41.2 Ra-226 3.610.6 3.510.5 2.6-4.4 Ra-228 2.621.0 3.6t0.5 2.7-4.5 V 3.020.0 3.026.0 0.0-13.4 Sample B Gr. beta 52.316.1 57.015.0 43.3-65.7 Sr-89 9.315.4 8.025.0 0.0-16.7 Sr-90 7.020.0 8.021.5 5.4-10.6 C s-134 21.015.2 20.015.0 11.3-28.7 Cs-137 23.012.0 20.015.0 11.3-28.7 STW-570 Mil k Apr 1989 Sr-89 26.0210.0 39.015.0 30.3-47.7 Sr-90 45.724.2 55.013.0 49.8-60.2 Cs-137 54.026.9 50.015.0 41.3-58.7 K-40 15211208 1600180 1461-1739 STW-5719 Water May 1989 Sr-89 <0.7 6.015.0 0.0-14.7 Sr-90 5.021.0 6.011 .5 3.4-8.6 STW-572 Water May 1989 Gr. al pha 24.022.0 30.018.0 16.1-43.9 -

Gr. beta 49.3115.6 50.015.0 41.3-58.7 STW-573 Water Jun 1989 Ba-133 50.721.2 49.015.0. 40.3-57.7 Co-60 31 .312 .3 31.025.0 22.3-39.7 Zn-65 167110 165t17 135.6-194.4 Ru-106 12329.2 128213 105.5-150.5 i Cs-134 40.311.2 3915 30.3-47.7 Cs-137 22.321.2 2015 11.3-28.7 STW-574 Water Jun 1989 H-3 45131136 45032450 3724-5282 STW-575 Water Jul 1989 Ra-226 16.823.1 17.722.7 13.0-22.4 Ra-228 13.823.7 18.322.7 13.6-23.0 STW-576 Water Jul 1989 0 40.311.2 41.016.0 30.6-51.4 STW-577 Water Aug 1989 l-131 84.715.8 83.0 8.0 69.1-96.9 STAF-579 Air Aug 1989 Gr. alpha 6.010.0 6.0:5.0 0.0-14.7 Filter Cs-137 10.3 2.3 10.0i5.0 1,3-18.7 102

Table A-1. (continued) l -

Concentration in pCi/lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis $2cc 15, N=1 Limits STW-580 Water Sep 1989 Sr-89 14.721.2 14.015.0 5.3-22.7 Sr-90 9.721.2 10.021.5 7.4-12.6 STW-581 Water Sep 1989 Gr. alpha 5.010.0 4.015.0 0.0-12.7 Gr. Beta 8.722.3 6.025.0 0.0-14.7 STW-583 Water Oct 1989 Ba-133 60.3210.0 59.026.0 48.6-69.4 Co-60 29.014.0 30.025.0 21.1-38.7 Zn-65 132.316.0 129.0213.0 106.5-151.5 Ru-106 155.326.1 161.0116.0 133.3-188.7 Cs-134 - 30.716.1 29.015.0 20.3-37.7 Cs-137 66.314.6 59.015.0 50.3-67.7 STW-584 Water Oct 1989 H-3 34071150 34961364 2866-4126 STW-585 Water Oct 1989 586 (Blind)

Sample A Gr. Alpha 41.729.4 49.0112.0 28.2-69.8 Ra-226 7.920.4 8.4 1.3 6.2-10.6 Ra-228 4.410.8 4.120.6 3.1-5.1 V 12.020.0 12.026.0 1.5-22.4 Sample B Gr. Beta 31 .7 2 .3 32.0 5.0 23.3-40.7 Sr-89 13.324.2 15.015.0 6.3-23.7 Sr-90 7.0 2.0 7.013.0 4.4-9.6 Cs-134 5.020.0 5.015.0 0.0-13.7 Cs-137 7.0t0.0 5.015.0 0.0-13.7 STW-587 Water Nov 1989 Ra-226 7.910.4 8.711.3 6.4 11.0 Ra-228 8.911.2 9.311.2 6.9-11.7 STW-588 Water Nov 1989 V 15.010.09 15.016.0 4.6-25.4 STW-589 Water Jan 1990 Sr-89 22.7i5.0 25.015.0 16.3-33.7 Sr-90 17.3 1.2 20.011.5 17.4-22.6 STW-591 Water Jan 1990 Gr. Alpha 10.313.0 12.015.0 3.3-20.7 Gr. Beta 12.3 1.2 12.015.0 3.3-20.7 1

1

}

103

Table A.I. (continued)

Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Cont rol Code Type Collected Analysis 22cC 1s, N 1 Limi ts S1W-592 Water Jan 1990 Co-60 14.712.3 1515.0 6.3-23.7 2n-65 135.026.9 139.0214.0 114.8 163.2 Ru-106 133.3113.4 139.0114.0 114.8-163.2 Cs-134 17.321.2 18.025.0 9.3-26.7 Cs-137 19.311.2 18.015.0 9.3-26.7 Ba-133 78.010.0 74.017.0 61.9-86.1 STW-593 Water feb 1990 H-3 4827183 49761498 4113-5839 STW-594 Water Har 1990 Ra 226 5.020.2 4.910.7 4.1-5.7 Ra-228 13.520.7 12.711.9 9.4-16.0 STW-595 Water Mar 1990 V 4.020.0 4.016.0 0.0-14.4 STW-596 Air Mar 1990 Gr. Alpha 7.321.2 5.025.0 0.0-13.7 Filter Gr. Beta 34.010.0 31.015.0 22.3-39.7 Sr-90 10.020.0 10.011.5 7.4-12.6 Ct-137 9.321.2 10.015.0 1.3-18.7 STW-597 Water Apr 1990 598 (Blind)

Gr. Alpha Sample A 81.013.5 90.0123.0 50.1-129.9 Ra-226 4.920.4 5.010.8 3.6-6.4 Ra-228 10.610.3 10.211.5 7.6-12.8 U 18.723.0 20.016.0 9.6-30.4 Sample B Gr. Beta 51.0210.1 52.015.0 43.3-60.7 Sr-89 9.321.2 10.015.0 1.3-18.7 Sr-90 10.313.1 10.011.5 8.3-11.7 Cs-134 16.020.0 15.015.0 6.3-23.7 Cs-137 19.022.0 15.015.0 6.3-23.7 STM-599 Mil k Apr 1990 Sr-89 21.723.1 23.015.0 14.3-31.7 Sr-90 21.027.0 23.025.0 14.3-31.7 1-131 98.711.2 99.0110.0 81.7-116.3 Cs-137 26.016.0 24.025.0 15.3-32.7 K 1300.0169.2 1550.0178.0 1414.7-1685.3 STW-600 Water May 1990 Sr-89 6.022.0 7.025.0 0.0-15.7 Sr-90 6.721.2 7.015.0 0.0-15.7 STW-601 Water May 1990 Gr. Alpha 11.022.0 22.026.0 11.6-32.4 Gr. Beta 12.3 1.2 15.015.0 6.3-23.7 104

s Table A 1. (contir.ued)

-, _ Concentration in pCi/Lb EPA Resultd ,

Lab Sample Date TIML Result Control Code Type Collected Analysis 22eC 15, N=1 Limits STW-602 Water Jun 1990 Co-60 25.312.3 24.015.0 15.3-32.7 _

Zn-65 155.0210.6 148.0215.0 130.6-165.4 Ru 106 202.7217.2 210.0121.0 173.6-246.4  ;

, Cs 134 23.711.2 24.015.0 18.2-29.8 1 Cs-137 27.723.1 25.025.0 16.3-33.7 1 Ba-133 100.718.1 -99.0210.0 81.7 116.3 i STW-603 Water Jun 1990 H-3 29272300 29331358 2312-3554  !

STW-604 Water Jul 1990 Ra 226 11.820.9 12.1 1.8 9.0-15.2 4 Ra-228 4.121.4 5.111.3 2.8-7.4 i l

STW-605 Water Jul 1990 0 20.311.7 20.813.0 15.6-26.0 1 STW-606 Water Aug-1990 1-131 43.021.2 39.016.0 28.6-49.4 i STW 607 Water - Aug 1990 Pu-239 10.011.7 9.lt0.9 7.5-10.7 l STW-608 Air 'Au9 1990 Gr. alpha 14.0t0.0 10.025.0 1.3-18.7'  !

Fil ter Gr. beta 65.321.2 62.015.0' 53.3-70.7 Sr-90 19.016.9 20.015.0 11.3-28.7 Cs-137 19.022.0 20.015.0 11.3-28.7 1 STW-609 Water Sep 1990 S r-89 9.022.0 10.025.0 1.3-18.7 Sr-90 9.022.0 9.015.0 0.3-17.7 j STM-610 Water Sep 1990- Gr. alpha 8.311.2-- 10.015.0 1.3-18.7 Gr. beta 10.311.2 10.015.0 1.3-18.7 ..

1 STM-611 _ Mil k Sep 1990- _Sr-89 11.713.1 16.015.0 7.3-24.7 Sr-90 15.020.0 20.025.0. 11.3-28.7 1-131 63.016.0 58.016.0 47.6-68.4 i Cs-137 20.022.0 20.025.0 11.3-28.7  :

K 1673.3170.2 1700.0185.0 1552.5-1847.5 q STW-612 Water Oct 1990 Co-60 20.323.1 20.015.0 11.3-28.7 in-65 115.3212.2 115.0212.0 94.2-135.8-Ru-106 152.028.0 151.0115.0 125.0-177.0-Cs-134 11.010.0 12.015.0 3.3-20.7 Cs-137 14.0 2.0 12.025.0 3.3-20.7 Ba-133 116.729.9 110.0111.0 '90.9-129.1 STW-613 Water Oct 1990 H-3 71672330 72032720 5954-8452 105 l.

b Liable A-1. -(' continued) i Concentration in pCi/Lb l

EPA Resultd I

, 'L ab Sample Date TIML Result- Control Code Type Collected Analysis- 12 cC 15, N=1 Limits-STW-614 Water ~ Oct'.1990 615-SamplelA- Gr. -alpha 68.717.2 62.0t16.0 34.2-89.8 Ra-226 12.910.3 13.6t2.0 10.1-17.1

- Ra-228 4.210.6 5.011.3 2.7-7.3 0 10.410.6 '10.213.0 5.0-15.4:

Sample: B Gr. beta 55.028.71 ~53.015.0 44.3-61.7 o S r-89 15.712.9 20.015.0 11.3-28.7 4 Sr-90 12.012.0 15.015.0 6.3a23.7 J Cs-134 9.011.7 7.025.0 0.0-15.7

- Cs-137 - 7.721.2 5.015.0 0.0-13.7

-STW-616 Water. Nov 1990 Ra-226 6.811.0 7.411.1 5.5-9.3- ,

._.Ra-228 5.311.7 ' 7.711.9 4.4-11.0- 'i STW-6179 Water- Nov 1990- U 35.010.4- 35.5t3.6 29.3-41.7 a Results obtained by Teledyne~ Isotopes-Midwest Laboratory as a participant in -

the environmental . sample-crosscheck program-operated by the Intercomparison and' )

Calibration Section, Quality Assurance Branch, Environmental Monitoring and j j

' Support Llaboratory, U.S. . Environmental Protection Agency (EPA), Las Vegas, Nevada.- -

l. .

Lbi All results are in _the pCi/1, except, for ' elemental potessium (K) data in Emilk, which are Lin-mg/1; air- filter samples, which are in -pCi/ filter; and food. -

which :is in mg/kg.

c- Unless otherwise indicated, the TIML results:are given as the mean i 2 9 standard . deviations ~ for three- determinations.

d -USEPA results- are presented as the known_ values- and expected laboratory precision'(1s,1 determination) _ and control limits as defined by EPA.

8 NA = Not; analyzed.

f ND,= No data -not.-analyzed due to -relocation df the lab.

9l Sample was.an;alyzed but the results -not submitted to-EPA because deadline w

' as missed -(all dataLon: file).. -

E t

106 l

l

Table A 2. Crosscheck program results, thermoluminescent dosimeters (TLDs).

mR Teledyne Average 22cd Lab Result Known (All Code TLD Type Measurement 22o8 Valuec Participants)

..~- w . ,=

2nd International Intercomparisonb 115-2 CaF2:Mn Field 17.021.9 17.1 16.427.7 Bulb

' Lab 20.824.1 21.3 18 827.6 3rd Internalional Intercomparisone 115-3 CaF2:Mn Field 30.723,2 34 . 9 t 4 .8 31.523.0 e Bulb -

Lab 89.626.4 91.7214.6 8( 2214 .5 4th International Intercompariscaf 115-4 CaFp:Mn Field 14.121.1 14.121.4 16.029.0 Bulb Lab (Low) 9.321.3 12.222.4 1?.027.4 Lab (High) 40.411.4 E5.829.2 43.9 13.2 Sth International Intercomparison9 -

115- 3 A CaF2 :Mn field 31.421.8 30.026.0 30.2214.6 Bulb ,

Lab at begir.ning 77.425.8 75.227.6 75.8 40.4 Lab at the eno 96.625.8 88.428.8 90.7231.2 ,

115-5B Lif-100 Field 30,314.8 30.026.0 30.2214.6 ,

Chips Lab at beginnin9 81.127.4 ft4:/.6 75.8240.4 Lab at the end 85.4t11.7 88.428.8 90 ./231 .3 7th Intcrnational Interccmparisonh 115-7A LiF-100 Field 75.422.6 75.826.0 7511elv.8 Chips Lab (Co-60) 80.023.5 79.92d.0 77.9227.6 Lab (Cs-137) 66.6 2.5 75.023.8 73.0222.2 107

Table A-2. (continued) mR Teledyne Average 12cd 1.4D Result Known (All Code  ?LO Type Measurement 12ca Valuec Participants)

, iib-To CaF :Mn Field 71.522.6 75.816.0 75.1129.8 Aults Lob (Co-60) 84.816.4 79.924.0 77.9127.6 Lab (Cs-137) 78.8 1.6 75.023.8 73.0222.2 11f,-7C CaSO4 :Dy Field 76.822.7 75.816.0 75.1 29.8 Cards Lab (Co-60) 82.523.7 79.9 4.0 77.9227.6 Lab (C5-137) 79.013.2 75.023.8 73.0222.2 Byh Internati,onal Intercomps,risoni 115-8A LiF-100 Fi'ld e Site 1 29.521.4 29.711.5 ?8.9212.4 Chips Field Site 2 11 .3 0.8 10.420.5 10.119.06

'ab (C?-137)

. 13.720.9 17.220.9 16.226.8 s

115-8B CaF2 ;Mn Field Site i 32.3 1.2 29.711.5 28.9 12.4 Bulbs Fia!d Site 2

. 9.021.0 10.410.5 10.1 9.0 Lab (Cs-137) 15.8 0,9 17.220.9 16.226.8 115-8CL CaSO4 :0y Field-Site 1 32.3 0.7 29.721.5 28.9212.4 Cards Field Site 2 10.620.6 10.420.5 10.119.0 Lab (Cs-137) 18.120.8 17.2 0.9 16.226.8 Teledyne Testingd 89-1 LiF-100 Lab 21.0 0.4 22.4 --

Chips 89-2 Tel edynt Lab 20.9 1.0 20.3 --

CaSO4 :Dy Cards 108 ,

l Table A-2. (continued) r.R Teledyne Average 22od Lab Result Known (All Code TLD Type Measurement 200 Valuec Participants)

_Teledyne Testingj 90-1k Teledyne Lab 20,621.4 19.6 --

Ca904 :Dy Cards 90-l l Teledyne Lab 100.8 4.3 100.0 --

CaSO4 :Dy Cards a Lab result given is the mean 12 standard deviations of three determinations, b Second International Intercomparison of Environmental Desimeters conducted in April of 1976 by the Health and Safety Laboratory (GASL), New York, New York, and the School of Public Health of the University of Texas, Houston, Texas, c Value determined by sponsor of the intercomparison using continuously operated pressurized ion chamber.

d Mean 12 standard deviations of results obtained by all laboratories parti-cipating in the program.

e Third International Intercomparison of Environmental Dosimeters conducted in sumer of 1977 by Oak Ridge National Laboratory and the School of Public Health of the University of Texas, Houston, Texas.

f Fourth International Intercomparison of Environmental Dosimeters conducted in sumer of 1979 by the School of Public Health of the University of Texas, Houston, Texas.

9 Fif th International Intercomparison of Environmental Dosimeter conducted in fall of 1980 at Idaho Falls, Idaho and sponsored by the School of Public Health of the University of Texas, Houston, Texas and Environmental Measure-ments Laboratory, New York, New York, U.S. Department of Energy.

h Seventh International Intercomparison of Environmental Dosimeters conducted in the spring and sumer of 1984 at Las Vegas, Nevada, and sponsored by the U.S. Department of Energy, the U.S. Nuclear Regulatory Commission, and the U.S. Environmental Protection Agency.

1 Eighth International Intercomparison of Environmental Desimeters conducted in the fall and winter of 1985-1986 at New York, New Yor n, and sponsored by the U.S. Department of Energy.

d Chips were submitted in September 1989 and cards were submitted in November 1989 to Teledyne Isotopes, Inc., Westwood, NJ for irradiation, k Cards were irradiated by Teledyne Isotopes, Inc., Westwood, NJ on June 19, 1990.

I Cards were irradiated by Dosimetry Associates, Inc., Northville, MI on October 30, 1990, 109

Table A-3. In-house spiked samples.

_ Concentration (pCi/L)

Lab Sample Date  !!ML Expected Code Type Collected Analysis Retult Known Precision n=3 Activity 15, n=3a QC-MI-6 Mil k Feb 1986 Sr-89 6.021.9 6.43.0 8.7 Sr-90 14.211.7 12.9 2.0 5.2 1-131 34.213.8 35.213.5 10.4 Cs-134 32.021.8 27.315.0 8.7 Cs-137 35.812.1 35.0 5.0 8.7 QC-W-14 Water Mar 1986 Sr-89 1.610.4 1.611.0 7.1 Sr-90 2.4 0.2 2.422.0 4.2 QC-W-15 Water Apr 1966 I-131 44.922.4 41.517.0 10.6 Co-60 10.6tl.7 12.115.0 7.lb Cs-134 30.212.4 25.818.0 7.lb Cs-137 21.911.9 19,915.0 7.lb QC-MI-7 Mil k Apr 1936 1-101. 39.713.3 41.517.0 10.4 Cs-134 28.7 2.8 25.8 8.0 8.7 Cs-137 21.222.8 19.915.0 8.7 SPW-1 Water liay 1986 Gr. alpha 15.821.8 18.025.0 Sc QC-W-16 Water Jur,1986 Gr. alpha 16c220.7 16.912.5 8.7 G' . beta 38.413-5 30.2 5.0 8.7

-QC-M1-9 Mil k Jun 1986 Sr-89 <1.0 0.0 7.lb Sr-90 12.61'.8 13.323.0 4.2b I-131 38.917.0 34.817.0 10.4 Cs-134 33.013.4 36.125.0 8.7 Cs-137 38.Si2.8 39.025.0 8.7 SPW-2 Water Jun 1986 Gr. alpha 16.8 1.8 18.025.0 Sc SPW-3 Water Jun 1986 Gr. alpha 17.710.8 18.015.0 Sc QC-W-18 -Water Sep 1986 Cs-134 34.715.6 31.325.0 8.7 Cs-137 51.1 7.0 43.328.0 8.7 QC-W-19 Water Sep 1986 Sr-89 13.624.1 15.623.5 7.lb Sr-90 6.421.6 6.222.0 4.2b 110

1 Table A-3. in-house spiked samples-(continued)  :

Concent ration '(pci/L)

Lab Sampl'e Date TIML Expected '

Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-W-21 Water Oct 1986 Co-60 19.212.2 18.513.0 8.7 Cs-134 31.725.2 25.628.0 8.7 Cs-137 23.821.0 21.625.0 8.7 QC-NI-11 Mil k Oct-1986 Sr-89 12.321.8 14.323.0 8. 7-  !

QC-W-20 ' Water Nov 1986- H-3 38551180 39602350 520b

_QC-W-22 Water Dec 1986- Gr. alpha 9.811.4 11.224.0 8.7 Gr. beta 21.7 2.0 23.815.0 8.7 ,

-QC-W Water. .Jan 1987 .1-131 -29.822.5 27.913.0 10.4

_ QC-MI-12. Mil k Jan 1987 ' I-131~ 36.511.3 -32.6 5.0 '10.4 l Cs-137 32.614.2 27.418.0 8.7

.QC-MI-13 ~ Mil k Jan 1987 Sr-89 10.422.1 -12.2 4.0 8.7 Sr-90 14.621.6 12.623.0 5.2 L I-131 -49.521.2 54.918.0 10.4 L Cs-134 .. < l . 6 0.0, 8.7 Cs-137- '33.3 0.6 27.418.0 8.7 QC-Wa24- Water: Mar 1987 Sr 89- 24.723.6- 25.925.0- 8.7 Sr 23.923.8 22.818.0 5.2 QC-W Water- Apr.1987_ _ .I-131 28.021.9 29.325'.0 10.6.

JQC-MI-14 -Mil k Apr 1987 1-131 25.022.2 23.925.0 10.4 Cs-134 <2.1-- 0.0 8.7. t Cs-137- 34.222.0. 27.217.0 '8.7 4 QC-W-262 Water Jun 1987 -H-3 34222100 3362 300 .520- >

Co _24.811.4 26.527.0 8.7- '

Cs-134- <2.0 0.0 8. 7. -

.Cs-137 21.2 0 5- 21 .6 7.0 8.7-

~QC-W-27 c LWater Jun 1987 Gr. alphL S.521.9 10.114.0 8.7 Gr. beta !2.6 1.9 21.2 5.0 8.7

~ QC-W-28' Water Jun 1987 Gr. alphs 8.721.3 10.124.0 8.7

.Gr beta 12.2:5.2 9.423.0 8.7

~111

l Table A-3. In-house spiked samples (continued)

Concentration (pCi/L)

Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-W-29 Water Jun 1987 Gr. alpha 16.411.3 18.915.0 8.7 Gr. beta 15.914.0 11.814.0 8.7 QC-MI-15 Mil k Jul 1987 Sr-90 19.421.6 18.813.5 5.2 1-131 43.520.7 45.3 7.0 10.4 Cs-134 17,912.2 16.015.3 8.7 Cs-137 25.421.8 22.715.0 8.7 QC- W-30 Water Sep 1987 Sr-89 17.523.0 14.315.0 8.7 Sr-90 18.412.2 17.522.2 5.2 QC-W-31 Water Oct 1987 H-3 20531939 20592306 520 QC-W-32 Water Dec 1987 Gr. alpha 8.621.0 10.1 5.0 8.7 Gr. beta 15.210.1 13.113.0 8.7 QC-W-33 . Water Dec 1987 Gr. alpha 7.721.4 10.1 5.0 8.7 Gr. beta 10.921.0 7.9 3.0 8.7 =

QC-W-34 Water Dec 1987 Gr. alpha 4.020.9 5.123.0 8.7 Gr. beta 9.420.9 7.923.0 8.7 QC-MI-16 Mil k Feb 1988 Sr-89 31.824.7 31.716.0 8.7 Sr-90 25.5 2.7 27.823.5 5.2 1-131 26.420.5 23.225.0 10.4 Cs-134 23.822.3 24.2 6.0 8.7 Cs-137 26.5 0.8 25.1 6.0 8.7 QC-MI-17 Mil k Feb 1988 1-131 10.621.2 14.3 1.6 10.4 QC-W-35 Water Feb 1988 1-131 9.721.1 11.621.1 10.4 QC-W-36 Water Feb 1988 1-131 10.5 1.3 11.6 1.0 10.4

'QC-W-37 Water Mar 1988 Sr-89 17.122.0 19.828.0 8.7 Sr-90 18.720.9 17.315.0 5.2 QC-MI-18 Milk Mar 1988 1-131 33.212.3 26.7 5.0 10.4 Cs-134 31.322.1 30.225.0 8.7 Cs-137 29.921.4 26.2 5.0 8.7 112

3;  :. -

Table A 3. 'In-house spiked samples (continued)

L Concentration (pCi/L)

Lab - Sampl e 'Date TIML Expected

, Code  : Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-W Water Apr 1988 1-131 17.111.1 14.215.0 10.4 r QC-W Water Apr~1988 H-3 4439231 41761500 724 I i

QC-W-40~ Water Apr 19885 Co-60 23.710.5 26.16.0 8.7 Cs-134 25.422.6 29.?:4.5 8.7 Cs-137 26.622.3 26.224.0 8.7

-QC-W-41 Wat'er Jun 1988~ Gr.. alpha 12.320.4 13.115.0 8.7 Gr. beta- 22.r.tl.0 20.115.0 8.7

. QC-MI Mil k Jul 1988- .Sr-89 '15.1 1.6 16.425.0 8.7 Sr-90 18.010.6 18.325.0 5.2 I-131. 88.424.9 86.628.0 10.4 .

Cs-137 22.710.8 20.816.0 8.7 1 QC-W-42 Water! Sep 1988 Sr-89 48.5t3.3- 50.828.0 8.7 Sr-90 10.921.0 11.423.5 5.2 0 -QC-W-43' Water Oct 1988 -Co-60 20.9 3.2 21.423.5 8.7 Cs-134 .'38.711.6 38.016.0 8. 7 -

Cs-137 19.022.4. 21.023.5 8.7 QC-W-44 Water Oct 1988' E

-l-131 -22.2 0.6 23.323.5 10.4 fQC-W-45 Water 1 Oct 1988 H-3 4109243 4153 500 724 ,

.-QC-MI-20 Mil k ' Oct 1988 I-131 59.8 0.9 60.6 9.0- 10.4 Cs-134- 49.6tl.8f 48.617.5- 8. 7--

Os-137 25.8 4.6- 24.724.0 8.7 j

~

' QC-W-46. Water Dec 1988 Gr. a1pha 11 ' 5t2.3

. 15.225.0 8.7 Gr. beta 26.522.0 25.7 5.0 8.7

QC-MI - Mil k dan 1989 Sr 25.5 10.3 34.0 10.0 8.7 1 Sr-90~ 28.313.'2 27.-1 3.0 . 5.2 I-131- 540 13 550220 10.4 -i Cs-134 24.522.6= 22.625.5 8.7 Cs-137 24.010.6 20.525.0- 8.7 113

Table A-3. In-house spiked samples (continued)

Concentration (pCi/L)

Lab Sample Date TIML Expect ed Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-W-47 Water Mar 1989 Sr-89 15.223.8 16.115.0 8.7 Sr-90 16.4 1.7 16,913.0 5.2 QC-MI-22 Mil k Apr 1989 l-131 36.321.1 37.225.0 10.4 Cs-134 20.822.8 20.718.0 8.7 Cs-137 22.222.4 20.428.0 8.7 QC-W-48 Water Apr.1089 Co-60 23.522.0 25.1 8.0 8.7 Cs-134 24.221.1 25.928.0 8.7 Cs-137 23.6 1.2 23.028.0 8.7 QC-W-49 Water Apr 1989 l-131 37.2 3.7 37.2 5.0 10.4 QC-W-50 Water Apr 1989 H-3 3011 59 30892500 724 QC-W-51 Water Jun 1989 Gr. alpha 13.021.8 15.025.0 8.7 Gr. beta 26.021.2 25.528.0 8.7

-QC-MI-23 Mil k Jul 1989 Sr-89 19.426.5 22.0210.0 8.7 Sr-90 27.6 3.5 28.623.0 5.2 1-131 46.823.2 43.4 5.0 10.4 Cs-134 27.4 1.8 28.326.0 8.7 Cs-137 24.121.8 20.826.0 8.7 QC-MI-24 Mil k Aug 1989 Sr-89 25.4 2.7 27.2 10.0 8.7 Sr-90 46.021.1 47.829.6 8.3 QC-W-52 Water Sep 1989 1-131 9.6 0.3 9.7 1.9 10.4 QC-W-53 Water Sep 1989 l-131 19.020.2 20.924.2 10.4 QC-W-54 Water Sep 1989 Sr-89 25.8 4.6 24.7 4.0 8.7 Sr-90 26.5 5.3 29.725.0 5.2 QC-MI-25 Mil k Oct 1989 l-131 70.0 3.3 73.5220.0 10.4 Cs-134 22.1 2.6 22.628.0 8.7 Cs-137 29.421.5 27.5 8.0 8.7 QC-W-55 Water Oct 1989 l-131 33.3 1.3 35.3210.0 10.4 l

114 l

Table A-3. In-house spiked samples (continued)

Concer.tration (pC1/L)

Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-W-56 Water Oct 1989 Co-60 15.210.9 17.425.0 8.7 Cs-134 22.124.4 18.918.0 8.7 Cs-137 27.221.2 22.928.0 8.7 QC-W-57 Water Oct 1989 H-3 3334122 33792500 724 QC-W-58 Water Nov 1989 Sr-89 10.9 1.4d 11.121.0d 8.7 Sr-90 10.4tl.0d 10.331.od 5.2 QC-W-59 Water Nov 1989 Sr-89 101.016.0d 104.1210,5d 17.5 Sr-90 98.023.0d 95.0110.0d 17,o QC-W-60 Water Dec 1989 Gr. alpha 10.811.1 10,624.0 8.7 Gr. beta 11.620.5 11.424.0 8.7 QC-MI-26 Mil k dan 1990 Cs-134 19.321.0 20.818.0 8.7 Cs-137 25.211.2 22.818.0 8.7 QC-MI-27 Mil k Feb 1990 Sr-90 18.0 1.6 18.815.0 5.2 QC-MI-28 Mil k Mar 1990 1-131 63.822.2 62.6 6.0 6.3 QC-MI-61 Water Apr 1990 Sr-89 17.9 5.5 23 lt8.7 8.7 Sr-90 19.422.5 23.525.2 5.2 QC-MI-29 Mil k Apr 1990 1-131 90.719.2 82.5 8.5 10.4 Cs-134 18.3il.0 19.715.0 8.7 Cs-137 20.311.0 18.225.0 8.7 QC-W-62 Water Apr 1990 Co-60 8.7 0.4 9.415.0 8.7 Cs-134 20.0 0.2 19.725.0 8.7 Cs-137 28.721.4 22.7 5.0 8.7 QC-W-63 Water Apr 1990 1-131 63.5 8.0 66.0 6.7 6.6 QC-W-64 Water Apr 1990 H-3 19411130 1826.01350.0 724 QC-W-65 Water Jun 1990 Ra-226 6.4 0.2 6.9 1.0 1.0 QC-W-66 -Water Jun 1990 V 6.220.2 6.0 6.0 6.0 115

k .

r 1 Ta'ble A-3.. In-house spiked samples (continued) 1 Concentration (pCi/L)

Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Acti vity 1s, n=3a-QC-MI-30 Mil k Jul 1990 Sr 12.810.4: 18.4110.0 8.7 Sr-90 18.221.4 18.7t6.0 5.2 i Cs-134 46.021.3 49.0t5.0 8.7 C s-137 27.621.3 25.315.0 8.7 r QC-W-68 Water Jun 1990 Gr. alpha 9.8t0.3 10.6t6.0 8.7 Gr. beta 11.4 0.6 11.3t7.0- 8.7 QC-MI Mil k Aug 1990- 'I-131 .68.821.6 61.4 t12.3 -10.4 QC-W-69 ' Water Sep,1990 Sr-89 17.721.6 19.2-110.0 8.7 Sr-90 13.911.6 17.4t10.0 5.2 _

QC-MI-32 ' Mil'k Oct'1990 .I-131 . 34.8 0.2 32.426.5 8.7 Cs-134 - 25.821.2' 27.3210.0 8.7 25.322.0 Cs-137 22.4 t10.0 8.7 QC-W-70 Water' .0ct'1990 H-3 2355259 2276t455 605 QC-W-71 Water. Oct 1990 1-131 55.9 0.9 51.8110.4 10.4

QC-W Water- Oct 1990 Co-60 18.3 2.7 16.8 5.0- 8.7.

Cs-134 28'3 2.3

. 27.0t5.0 - 8.7<

Cs-137 22.7 1.3 22.4t5.0 ;8.7 QC-W-74. - Water Dec 1990. Gr. alpha. 21.411.0- 26.116.5 11.3

.Gr. beta 25.921.0. 22.3 5.6 9.7

~

'ai n =. 3 unless noted ' otherwi se. -

' b _n = '2 "unless _noted otherwise.

c:n =.1 unless .not'e d otherwise, d-Concentration inipC1/ml.

1 I

116

Table A-4 In-house " blank" samples.

Concentration (pCi/L)

Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66 o) (4.66 o)

BL-1 0.1, Water Nov 1985 Gross alpha <0.1 <1 Gross beta <0.4 <4 BL-2 D.I . Water Nov 1985 Cs-137 (gamma) <1.9 <10 BL-3 0.1. Water Nov 1985 Sr-89 <0.5 <5 Sr-90 <0.6 <1 BL-5 0.1. Water Nov 1985 Ra-226 <0.4 <1 Ra-228 <0.4 <1 SPW-2265 0.1. Water Apr 1985 Gross alpha <0.6 :1 Gross beta <2.2 <4 Sr-89 <0.2 <5 Sr-90 <0.4 <1 1-131 <0.2 <1 Cs-137 (9amma) <7.4 <10 BL-6 D. I . Water Apr 1986 Gross alpha <0.4 <1 BL-7 0.1. Water Apr 1986 Gross alpha <0.4 <1 BL-8 D.I. Water Jun 1986 Gross alpha <0.4 <1 BL-9 0.1 Water Jun 1986 Gross alpha <0.3 <1 SPW-3185 D.I. Water Jan 1987 Ra-226 <0.1 <1 Ra-228 <0.9 <1 SPS-3292 Mil k Jan 1987 I-131 < 0 . '. <1 Cs-134 <6.2 <10 Cs-137 <6.4 <10 SPW-3554 0.I. Water Feb 1987 H-3 <180 <300 Gross beta <2.6 <4 SPS-3555 Mil k Feb 1987 Sr-89 <0.6 <5 Sr-90 1.9 0.4a <1 SPS-3731 Mil k Mar 1987 Cs-134 <2.? <10 Cs-137 <2.5 <10 117

Table A-4 In-house " blank" samples (continued)

Concentration (pCi/L)

Acceptance 1.ab Sample Date Results Criteria Code Type Collected Analysis (4.66 c) (4.66o)

SPS-3732 D.I. Water Mar 1987 Sr-89 <0.9 <5 Sr-90 <0.8 <1 1-131 <0.3 <1 Co-60 <2.3 <10 Cs-134 <2.2 <10 Cs-137 <2.4 <10 Ra-226 <0.1 <1 Ra-228 <1.0 <1 Np-237 <0.04 <1 Th-230 <0.05 <0.1 Th-232 <0.02 <0.1 V-234 <0.05 <0.1 U-235 <0.03 <0.1 U-238 <0.03 <0.1 SPS-4023 Mil k May 1987 1-131 <0.1 <1 SPS-4203 D.I. Water May 1987 Gross alpha <0.7 <1 Gross beta <1.7 <4 l SPS-4204 Mil k May 1987 Sr-89 <0,5 <5 e

Sr-90 2.4 0.6a <1 SPS-4390 Mil k Jun 1987 Cs-134 <4.7 <10 Cs-137 <5.2 <10 SPS-4391 D.I. Water Jun 1987 Sr-89 <0.4 <5 Sr-90 <0.4 <1 1-121 <0.1 <1 Co-60 <3.8 <10 Cs-137 <5.7 <10 Ra-226 <0 .1 <1 Ra-228 <0.9 <1 SPW-4627 D.I. Water Aug 1987 Gross alpha <0.6 <1 Gross beta <1.4 <4 Tritium <150 <300 SPS-4628 Mil k Au9 1987 Sr-89 <0.6 <5 Sr-90 2.4:0.6a <1

)

i 118

o Tabi'e A-4. - In-house " blank" samples - (continued)

Concentration (pCi/L)

Acceptance ilab - Sample . Date Results- Criteria

Code Type Collected Analysis '(4.66 o) (4.66o)
SPS-4847 L Mil k Sep 1987 Cs-134 <4.4 <10 Cs-137 <5.3 <10 D.I. Water SPS-4848l Sep 1987 I-131 <0.2 <1

-SPW-4849-D.I.~ Water Sep 1987 Co-60 <4.1 <10 Cs-134 <4.8 <10 Cs-137 <4.0 <10 Sr-89 <0.7 <5 1 Sr-90 <0.7 <1  !

?SPW-4850 D.I. Water Sept 1987 Th-228 <0.04 <1 l Th-232 <0 . 8 <1 U-234- <0.03 <1 U-235 <0.03 <1 U-238 <0.02 <1

' /a-241 <0.06 <1 Cm-242- <0.04 <1 L

Ra-226 -<0.1 <1 Ra-228 <1.0 <2 o

SPW-4859: D.I. Water Oct 1987 Fe-55 .<0.5: <1 7 SPS-5348J JMilk 'Dec.1987 (Cs-134 <2 . 3 <10 $

Cs-137 <2 . 5 .<10 SPW-53841 D.I. Water Dec 1987 C o-60 . <2.8 <10 1 Cs-134 <2.6 .<10 I' Cs-137 <2.8 <10 131- <0.2 <1 Re-226: <0.1- <1 Ra-228 < 1 '. 2 <2 ,

Sr <0;5- <1 Sr-90 <0.4: <1

~SPW-5385 . D.I. Water Nov-1987 Gross alpha <0.4- <1 Gross beta <2.2 <4 o Fe-55 <0.3 -<1 l SPS-5386 Milk Jan 1988 I-131 <0.1 <1 5

<SPW-5448 " Dead" Water Jan-1988 H-3 (177 <300 s

119

- -- - A. - - - - - - - - - -- - - - - , , , .- +, e --er ,-,mn

~

. .. i

Table A-4 In-house " blank" samples (continued)-

. I .

' Concentration (pCi/L)

Acceptance

, Llab- ~ Sample Date Results Criteria

Code
Type- -Collected Analysi s (4.6L J) (4.66_o)

SPS-5615' Mil k - Mar 1988 Cs-134 <2.4 <10 Cs-137 <2.5 <10 .

1-131 <0.3 <1 Sr-89 <0.4 <5 Sr-90 2.420.Sa <1 <

SPS-5650 D.!'. Water Mar 1988 Th-228. - <0. 3. .<1 i Th-230 <0.04 <1-Th-232 <0.05 <1 U-234~ <0.03 <1-U-235 <0.03 <1 U-238 <0.03 <1 Am-241 <0.06 <1 Cm-242 .<0.01 <1 Pu-238- <0.08 <1

'Pu-240 <0.02 <1 3

SPS-60' 9.0 - Hil k Jul-1988 Sr-89 -<0.5 <1 S r-90 1.810.5 <1 1-131 <0.4- '1<

Cs-137 ~<0.4'- <10

~

SPW-6209; :WaterT Jul-1988 Fe ' <0.8 < 1 -:

SPW-6292

. Wat e r-- .Sep 1988- Sr-89 <0.7 -<1 Sr-90 <0.7. <1-J SPS-6477 Mil k ' :Oct 1988 11-131 <0 . 2 <1 Cs-134 < 6.1- < 10 .

Cs-137 <5.9 : <10

'SPW-6478 .- Wat er =0ct-1988 'l-131 <0.2 '1< '

SPW-6479' - Water Oct;1988- -Co-50 ' <5.7 <10 Cs-134 <3.7' <10 Cs-137 <4.3' <10L

p. SPW-6480' Water Oct 1988 H-3 <170 <300 J SPW-6625 Water ~Dec 1988 Gross alpha <0.7 <1

--Gross beta- <1.9 <4 i

120 i.

Table A-4 In-house " blank" samples (continued)

Concentration (pCi/L)

Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66 c) (4.66 o)

SPS-6723 Mil k Jan 1989 Sr-89 <0.6 <5 Sr-90 1.920.Sa <1 1-131 <0.2 <1 Cs-134 <4.3 <10 C s-137 <4.4 <10 SPW-6877 Water Mar 1989 Sr-89 <0.4 <5 Sr-90 <0.6 <1 SPS-6963 Milk Apr 1989 l-131 <0.3 <1 Cs-134 <5.9 <10 Cs-137 <6.2 <10 SPW-7561 Water Apr 1989 H-3 (150 <300 SPW-7207 Water Jun 1989 Ra-226 <0.2 <1 Ra-228 <0.6 <1 SPS-7208 Mil k Jun 1989 Sr-89 <0.6 <5 Sr-90 2.1 0.5a <1 i 1-131 <0.3 <1 Cs-134 <6.4 <10 C s-137 <7.2 <10 SPW-7558 Water Jun 1989 Gross alpha < u . <. <1 Gross beta <1.0 <4 SPS-7322 Mil k Aug 1989 Sr-89 <1.4 <5 Sr-90 4.821.03 <1 1-131 <0.2 <1 Cs-134 <6.9 <10 Cs-137 <8.2 <10 SPW-7559 Water Sep 1989 S r-89 <2.0 <5 Sr-90 <0.7 <1 SPW-7560 Water Oct 1989 l-131 <0.1 <1 SPW-7562 Wat er Oct 1989 H-3 <140 <300 I

121

. - , . - . - - - . .- n. ~ . . - . - - _ . . - - ~ - ~ _ . -.__.

' Table-A-4 In-house " blank" samples (continued)

Concentration (pC1/L)

Acceptance Lab Sample Date Resul t 5 - Criteria y Code  : Type Collected Analysis (4.66c) (4.66 o)

SPS-7605 Mil k Nov 1989 l-131 <0.2 <1 Cs-134 <8.6 <10 Cs-137' <10 <10-jsPW-7971 Water

-Dec 1989 Gross alpha <0.4 '1<

Gross beta <0.8 <4 SPW-8039- Water Jan 1990 Ra-226 <0.2 <1 SPS-8040' Mil k Jan 1990 =Sr-89 <0.8 <5- 4 Sr-90 <1.0 <1 SPS-8208- Mil k- Jan 1990 Sr-89 <0.8 <5  :

Sr-90 1.620.5a <1 ..

Cs-134 <3.6- <10 Cs-137 <4 . 7 <10

'SPS-8312. Mil k Feb 1990 Sr-89 <0.3 <5 Sr-90 1.210.3a <1 l

'SPW-8312A; ' Water Feb 1990- -Sr-89 <0.6 <5 Sr-90 <0.7~ <1 LSPS-8314 - Mil k Mar 1990 1-131 . <0.3 .<1  !

iSPS'-85IO Mil k .May 1990 l'-131- <0.2' <1 Cs-134: <4.6. . <10 Cs-137 <4.8- - <10

>SPW-8511A> Water May 1990 LH-3 <200- <300

'SPS-8600L Mil k- Jul : 1990 Sr-89 <0.8 <5- d Sr-90 .1 ' 710. 6 a - <

.1-131: <0.3 <1

-Cs-134 -

<5.0- <10

.Cs-137 <7.0 <10~

SPM-8877 - Mil k Aug 1990- I-131 <0.2: <1  !

l :SPW-8925 Water Aug 1990- H-3 <200 <300 122 i

-Table A-4 In-house " blank" samples (continued)

Concentration (pCi/L)

Acceptance Lab Sample Date Resul ts Criteria Code Type Collected Analysi s (4.66c) (4.66 c)

SPW-8926 Water Aug 1990 Gross alpha <0.3 <1 Gross beta <0.7 <4 SPW-8927 Water Aug 1990 U-234 <0.01 <1 U-235 <0.02 <1 U-238 <0.01 <1 SPW-8928 Water Aug 1990 Mn-54 <4.0 <5 Co-58 <4.1 <5 Co-60 <2.4 <5 Cs-134 <3.3 <5 Cs-137 <3.7 <5 SPW-8929 Water Aug 1990 Sr-89 <1.4 <5 Sr-89 <0.6 <1 SPW-69 Water Sep 1990 Sr-89 <1.8 <5 Sr-90 <0.8 <1 SPW-106 Water Oct 1990 H-3 <180 <300 SPM-107- Mil k Oct 1990 1-131 <0.4 <1 Cs-134 <3.3 <5 Cs-137 <4.3 <5 SPW-370 Water Oct 1990 Mn-54 <1.7 <5 Co-58 <2.6 <5 00-60 <1.6 <5 Cs-134 <1.7 <5 Cs-137 <1.8 .<5 SPW-372 Water Dec 1990 Gross alpha <0.3 <1 Gross beta <0.8 <4 a low level of Sr-90 concentration in milk (1 - 5 pCi/L) is not unusual .

l 123

iIML-BLIND-01 Revision 0, 12-29-86. ,

j _ ATTACHMENT B ACCEPTANCE CRITERI A FOR "$P!KED" SAttPLES LABORATORY PRECISION: ONE STANDARD DEVIATION VALUES FOR VARIOUS NIALYSESa One Standard Deviation Analysis Level for Single Determination Gama Emitters 5 to 100 pCi/ liter or kg 5 pct / liter

>100 pCi/ liter or kg 5% of known value Stronti um-89b 5 to 50 pCi/ liter or kg 5 pC1/ liter

>50 pCi/ liter or kg 10% of known value Strontium-90b 2 to 30 pCi/ liter or kg 3.0 pCi/ liter

>30 pC1/ liter of kg 10% of known value Potassium >0.1 g/ liter or kg 5% of known value Gross Alpha <20 pCi/ liter 5 pC1/ liter

>20 pCi/ liter 25% of known value Gross Beta <100 pCi/ liter 5 pCi/ liter

>100 pCi/ liter 5% of known value Tritium <4,000 pCi/ liter is = (pC1/ liter) =

169.85 x (known).0933

>4,000 pCi/ liter 10% of known value Radium-226, <0.1 pCi/ liter 15% of known value Radium-228 Plutonium 0.1 pCi/ liter, gram, 10% of known value or sampie lodine-131, b <55 pC1/ liter 6 pCi/ liter lodine-129 >55 pC1/ liter 10% of known value Uranium-238 <35 pCi/ liter 6 pCi/ liter Nickel-63b , >35 pCi/ liter 15% of known value Technetium-99b Iron-55b 50 to 100 pCi/ liter 10 pCi/ liter

>100 pCi/ liter 10% of known value

" From EPA publication, " Environmental Radioactivity Laboratory Intercompari-b son Studies Program, Fiscal Year 1981-1982, EPA-600/4-81-004.

TIML limit.

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ADDENDUM TO APPENDIX V The following is an explanation of the reasons why certain samples were outside the control limit specified by the Environmental Protection Agency for the Interlaboratory Comparison Program starting January 1987.

EPA TIML Control Result Limit Lab Code Analysis (pCi/L)a (pCi/L)o Expl anation STM-504 S r-89 57.014.3 60-3-77.7 Milk had high f at content which Sr-90 32.0 1.0 32.4-37.6 made analyses dif ficult. Ad-dition of errors to TIML result would put values within EPA control limits. EPA also had the same problem in analyzing its own sample.

STW-511 Ra-228 8.111.4 .6-8.0 TIML results are usually within EPA control limits. Analysis of the next sample was within EPA control limits. No further action is planned.

STW-516 Cr-51 80.3217.5 61.3-78.7 Results in the past have been wi thin EPA control limits and TIML will monitor the situation in the future.

STF-524 K 1010.71158.5b 1123.5-1336.5b Error in transference of data.

Correct data was 1105133 mg/kg.

Results in the past have been within the limits and TIML will monitor the situation in the future.

STW-532 I-131 9.0 2.0 6.2-8.8 Sample recounted t.f ter 12 days.

The average result was 8.821.7 pCi/L (within EPA control limits). The sampl e was recounted in order to check the decay. Results in the past have been within the limits and TIML will continue to monitor the situation in the future, a Reported in pCi/L unless otherwise noted.

b Concentrations are reported in mg/kg.

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ADDENDUM TO APPENDIX A (continued) l EPA TIML Control Result limit Lab Code Analysis (pCi/L)a (pCi/L)a Explanation STW-534 Co-60 63.321.3 41.3-58.7 High level of Co-60 was due to contamination of beaker. Beaker was discarded upon discovery of I contamination and sample was recounted. Recount results 53.213.6 and 50.922.4 pCi/L.

STM-554 Sr-90 51.022.0 54.8-65.2 The cause of low result was due to very high fat content in the mil k, it should be noted that 63% of all participants failed this test. Also, the average for all participants was 54.0 pCi/L before the Grubb and 55.8 pCi/L af ter the Grubb.

STW-560 Pu-239 5.8 1.1 3.5-4.9 The cause of high results is not known it is suspected that the standard was not properly calibrated by supplier and is under investigation. New Pu-236 standard was obtained and will be used for the next test.

STW-568 Ra-228 2.611.0 2.7 -4 .5 The cause of low results is not known. Next EPA crosscheck results were within the control limits. No further action is planned.

STM-570 Sr-89 26.0210.0 30.3-47.7 The cause of low results was Sr-90 45.724.2 49.8-60.2 falsely high recovery due to suspected incomplete calcium removal. Since EPA sample was used up, internal spike was prepared and analyzed. The results were within control limits (See table A-3, sample QC-MI-24). No further action is planned, a Reported in pCi/L unless otherwise noted.

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_ADDEl40VH TO APPEtiDlX A (continued) l EPA TIML Control Result Limit Lab Code Analysis (pCi/L)a (pC1/L )a Explanation STW-589 Sr-90 17.3il.2 17.4-22.6 Sample was reanalyzed in tri-plicate; results of reanalyses 18.8.t l . 5 pC i /L . No further action is planned.

STM-599 K 1300.0 69.2c 1414.7-1685.3c Sample was reanalyzed in trip-11cate. Results of reanalyses, 1421.7195.3 mg/L. The cause of low results is unknown.

STW-601 Gross 11.012.0 11.6-32.4 Sample was reanalyzed in trip-Alpha licate. Results of reanalyses, 13.4 1.0 pCi/L.

a Reported in pCi/L unless otherwise noted, c Concentrations are reported in mg/L.

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