Text

Annual Radiological Environ Operating Rept 1994
	ML20082Q780
Person / Time
Site:	Quad Cities
Issue date:	12/31/1994
From:	Pearce L; COMMONWEALTH EDISON CO.
To:	; NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM)
References
	LWP-95-044, LWP-95-44, NUDOCS 9505010089
	Download: ML20082Q780 (109)
	v • d • e

7 Commonwcalth Edison Company Quad Cities Generatmg $tation 22710 2With Avenue . North * + .

Cordova, II. 612 42-9'jo Tel,W His022ni LWP-95-044 1

April 24,1995 !

Document Control Desk l U. S. Nuclear Regulatory Commission l Mail Station PI-137 1 Washington, DC 20555 Enclosed is the 1994 Quad Cities Station Annual Radiological Environmental Operating Repon Docket Nun.bers 50-254 and 50-265. This report contains the results of the Radiological Environmental and Meteorological Monitoring Programs for the calendar year 1994. The Radioactive Effluents Reports were submitted under separate cover in February 1995 and Arpist 1994.

Two copies of the report are pmvided for your use. Two copies will be forwarded to the Region III and one copy to the Resident Inspector.

Sinceirly yours, C ] L Il.RJ.W. Pearce/ (LLce, Station Manager Quad Cities Station LWP/PM/kjv Enclosure 9505010089 941231 smomo44:95.twr f #MMM$f 1 1g -

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QUAD CITIES STATION ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 1994 I

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APRIL 1995 I

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I TABLE OF CONTENTS Eage INTRODUCTION.. . .. . . . . .

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SUMMARY

. . . . . . . . . 2 1.0 EFFLUENTS 1.1 Gaseous Effluents to the Atmosphere .

1.2 . . .

3 Liquids Released to Mississippi River .. . . . . . . . .

. . . . . . . 3 2.0 SOLID RADIOACTIVE WASTE.... . . ... ... . ... . . . . . . .

. . . . . 3 3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways . .. . . . ..

3.1.1 Noble Gases.. ... . . . . . . . . . . . . . . . . . . . . .

. . .. . 3 3.1.1.1 Gamma Dose Rates.. ..

.. 3 3.1.1.2 Beta Air and Skin Rates.. .

.. . .. 3 3.1.2 RadioactiveIodine... . . . . . . . . . . . .. . . ..

. 4 I 4 3.1.2.1 Iodine Concentrations in Air.. .. . ...

3.1.2.2 Dose to Infant's Thyroid. . . . .. .. ... . 4

. . . . .. 4 3.2 3.1.3 Concentrations of Particulates in Air.. .. ..

Liquid Effluent Pathways.. . .. ...

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3.3 Assessment of Dose to Member of Public... ... 5

. . . . . . . . . . . . . . . . 5 l

1 4.0 SITE METEOROLOGY.... .. .. ... ..

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............. .. 6 5.0 ENVIRONMENTAL MONITORING 5.1 Gamma Radiation... . . . . . . . . . . . . . . . . . . .

I 5.2 Airborne I-131 and Particulate Radioactivity.. . . . . .

5.3 Aquatic Radioactivity. . . . . ... . . . .. . ..

5.4 Milk .... . . . . . . .. . ... . ... . . . . . . .

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6 5.5 Sample Collections... . .. ..

. . . . . . . . . . 7 5.6 Listing of Missed Samples.. . .. . . . . . . .. .. 7 5.7 Program Modifications. .... . . . . .. . . . . . . . . . . . ...

. . . . . . . . .. . 7

. . . . . . . . . . . . . . . . .... 8 6.0 ANALYTICAL PROCEDURES.. . . . .. .. .

. . . . . . . . 8 7.0 MILCH ANIMALS AND NEAREST LIVESTOCK CENSUSES.. .. . . . 8 8.0 NEAREST RESIDENT CENSUS.. . . .

. . . . 8 9.0 INTERLABORATORY COMPARISON PROGRAM RESULTS.. . . 8 .. .

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TABLE OF COhTTENTS (continued) fage APPENDIX I - DATA TABLES AND FIGURES.. . .. . . . . . . . . . . . . . . . . . . . . . . . . 10 Station Releases Table 1.1-1 Gaseous Effluents Summation of all Releases...... . . . . . . 11 I Table 1.2-1 Table 2.0-1 Liquid Effluents Summation of all Releases..

Solid Radwaste Annual Report........ ..... . . . . . . . . . . . . . .

. . . . . . . 13 15 Figure 3.1 Figure 3.1-4 Isodose and Concentration Contours........ . .. . . . . . . . . 18 Table 3.1-1 Maximum Doses Resulting from Airborne Releases... .... 22 Table 3.2-1 Maximum Doses Resulting from Liquid Effluents.. . ... .. . . .. . . . . . . . . . . . . . . . . . . . 26 Table 3.3-1 10CFR20 Compliance Assessment.. . . . . . . . . . . . . . . . . . 28 Environmental Monitoring Figure 5.0-1 Inner Ring TLD Locations... . ..... .. . . . . . . . . . . . . 32 Figure 5.0-2 Fixed Air Sampling Sites and Outer Ring TLD Loca tions... .............. . . . . . . . . . . . . . . . . . . . 33 Figure 5.0-3 Milk, Fish, Water, and Sediment Sample Locations... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 34 Table 5.0-1 Radiological Environmental Monitoring Locations . . . . . . . . . 35 Table 5.0-2 Radiological Environmental Monitoring Program Sampling Locations, Sample Collection and Analyses... .. .. 36 Table 5.0 Table 5.0-6 I Table 5.1-1 Radiological Environmental Monitoring Program Quarterly Summary.. . . . . .... ... .

Gamma Radiation measured in mR by TLDs.. . . . ....

. 43 47 APPENDIX II - METEOROLOGICAL DATA............. ... . . . . . . . . . . . . . . . . . . 50 APPENDIX III - LISTING OF MISSED SAMPLES..... . . . . . 79 APPENDIX IV - MILCH ANIMALS, NEAREST LIVESTOCK, AND NEAREST RESIDENCES CENSUSES.. . .. . . . . . . . . . 81 APPENDIX V - INTERLABORATORY COMPARISON PROGRAM RESULTS.. . . 86 1

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I INTRODUCTION I Units 1 and 2 of the Quad Cities Station located near Cordova, Illinois next to the Mississippi River, are 2511 MWth boiling water reactors, similar in design to Dresden Units 2 and 3. The plant has been designed to keep releases to the environment at levels below those specified in the regulations.

Liquid effluents from Quad Cities are released to the Mississippi River in controlled batches after radioassay of each batch. Gaseous effluents are released to the atmosphere after delay to permit decay of short half-life gases. Releases to the atmosphere are calculated on the basis of analyses of grab samples of noble gases and continuously collected composite samples of iodine and particulate matter. The results of effluent analyses are summarized on a monthly basis and reported to the Nuclear Regulatory Commission as required per Technical Specifications.

Airborne concentrations of noble gases, I-131, and particulate radioactivity in offsite areas are calculated using isotopic composition of effluent and meteorological dw2.

Environmental monitoring is conducted by sampling at indicator and control (background) locations in the vicinity of the Quad Cities plant to measure changes in radiation or radioactivity levels that may be attributable to plant operations. If significant changes attributable to Quad Cities are measured, these changes are correlated with effluent releases.

External gamma radiation exposure from noble gases and I-131 in milk are the most critical pathways at this site; however, an environmental monitoring program is conducted which includes other pathways.

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SUMMARY

Gaseous and liquid effluents for the period contributed to only a small fraction of the Technical Specification limits. Calculations of environmental concentrations based on effluent, and meteorological data for the period indicate that consumption ty the public of radionuclides attributable to the plant are well below the regulatory limits. Radiation exposure from radionuclides released to the atmosphere represented the critical pathwa maximum individual dose estimated to be 4.61E-04 mrem for whenthea shielding year,y for the period wit and occupancy factor of 0.7 is assumed. The assessment of radiation doses are performed in accordance with the Offsite Dose Calculation Manual (ODCM). The results of analysis confirm that the station is operating in compliance with 10CFR50 Appendix 1,40CFR190, and 10CFR20.

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1.0 EFFLUENTS 1.1 Gaseous Effluents to the Atmosphere Measured concentrations and isotopic composition of noble gases, radioiodine, and particulate radioactivity released to the atmosphere during the year, are listed in Table 1.1-1. A total of 2.99E+01 curies of fission and activation gases was released with a maximum quarterly average release rate of 1.83 pCi/sec.

A total of 7.04E-04 curies of I-131 was released during the year, with a maximum quarterly average release rate of 2.97E-05 pCi/sec.

A total of 9.84E-03 curies of beta-gamma emitters was released as airborne particulate matter with a maximum quarterly average release rate of 5.72E-04 pCi/sec. A total of 1.08E-05 curies of alpha emitters was released during the year.

I A total of 2.84E+01 curies of tritium was released, with a maximum quarterly average release rate of 1.43 pCi/sec.

1.2 Liquids Released to the Mississippj A total of 1.49E+07 liters of radioactive liquid waste (prior to dilution) containing 6.00E-02 curies (excluding tritium, gases, and alpha) was discharged from the station.

I These wastes were released at a maximum quarterly average concentration of 1.76E-09 pCi/ml. No alpha radioactivity was detected in the liquid waste. A total of 4.72E+01 curies of tritium was released at a quarterly average concentration of 1.18E-06 pCi/ml. Quarterly release estimates and principal radionuclides in liquid effluents are given in Table 1.2-1.

2.0 SOLID RADIOACTIVE WASTE Solid radioactive wastes were shipped to Barnwell, South Carolina (CNSI); Oak Ridge, Tennessee (Quadrex, SEG), and Channahon, Illinois (CNSI). One mixed waste shipment was shipped to Kingston, Tennessee (Diversified Scientific Services, Inc.).

The record of waste shipments is summarized in Table 2.0-1.

3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways Table 3.1-1 summarizes the doses resulting from releases of airborne radioactivity via the different exposure pathways.

3.1.1 Noble Gases 3.1.1.1 Gamma Dose Rates Offsite gamma air and total body doses are shown in Table 3.1-1 and I were calculated based on measured release rates, isotopic composition of the noble gases, and average meteorological data for the period.

Isodose contours based on concurrent meteorological data for gamma dose are shown in Figure 3.1-1. Based on measured effluents and 3

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0l the maximum total dose to an individual would be 4.61E-04 mrem for the year, with an occupancy or shielding factor of 0.7 included and i based on measured effluents and concurrent meteorological data would E' be 1.55E-02 mrem. The maximum gamma air dose was 6.11E-04 mrad 5 and 1.08E-03 mrad based on concurrent meteorological data.

3.1.1.2 Beta Air and Skin Dose 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 l 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 clothing covering sensitive tissues. For purposes of this report the skin is taken to have a thickness of 7.0 mg/cm2 and an occupancy factor of 1.0 is used. The skin dose from beta and gamma radiation for the year was 5.09E-04 mrem.

The air concentrations of radioactive noble gases at the offsite receptor locations are given in Figure 3.1-2. The maximum offsite beta air dose for the year was 5.53E-05 mrad.

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3.1.2 Radioactive lodine The human thyroid exhibits a significant capacity to concentrate ingested or inhaled iodine. The radiciodine,1-131, r hased during routine operation of the plant, may be made available to a person resulting in a dose to the thyroid.

The principal pathway of interest for this radionuclide is ingestion of radiciodine in milk by an infant.

3.1.2.1 Iodine Concentrations in Air The calculated concentration contours for iodine in air are shown in Figure 3.1-3. These calculations include an iodine cloud depletion factor which accounts for the phenomenon of elemental iodine deposition on the ground. The maximum offsite concentration is estimated to be 3.62E-05 pCi/m3 for the year.

3.1.2.2 Dose to Infant's Thyroid The hypothetical thyroid dose to an infant living near the plant via ingesti.m. of milk was calculated. The radionuclide considered was I-131i M t : source of milk was taken to be the nearest dairy farm with the .43 pastured from May through October. The maximum infant's thyroid dose was 0.00 mrem during the year (Table 3.1-1).

3.1.3 Concentrations of Particulates in Air Concentration contours of radioactive airborne particulates are shown in Figure 3.1-4. The maximum offsite average level is estimated to be 5.33E-04 E pCi/m3 l 4

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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 shoreline. Not all of these pathways are significant or applicable at a given time or station 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 GI tracts, thyroid, bone, skin; specific parameters for use in the equations are given in the Commonwealth Edison Offsite Dose Calculation Manual. The maximum whole body dose for the year was 2.90E-04 mrem and no organ dose exceeded 4.01E-04 mrem (Table 3.2-1).

3.3 Assessment of Dose to Member of Public During the period January to December,1994, Quad Cites Station did not exceed the following limits as shown in Table 3.1-1 and Table 3.2-1 (based on yearly average meteorological data), as shown in Figure 3.1-1 (based on concurrent meteorological data), and as shown in Table 3.3-1:

The RETS limits on dose or dose commitment to an individual due to radioactive materials in liquid effluents from each reactor unit (3 mrem

, to the whole body or 10 mrem to any organ during any calendar quarter; 6 mrem to the whole body or 20 mrem to any organ during any calendar year).

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The RETS limits on air dose in noble gases released in gaseous effluents to a member of the public from each reactor unit (5 mrad for gamma radiation or 10 mrads for beta radiation during any alendar quarter; 10 mrads for gamma radiation or 20 mrad for beta r liation during any calendar year).

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).

The RETS 40CFR190 limits for total body dosr. or any organ (except thyroid) is less than 25 mrem annually for radioactive liquid and I gaseous effluents. The thyroid is limited to 75 mrem over 12 consecutive months.

The 10CFR20 limit on Total Effective Dose Equivalent to individual members of the public (100 mrem).

Nuclear Regulatory Commission, Regulatory Guide 1.109 (Rev.1).

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E LU 4.0 SITE METEOROLOGY A summary of the site meteorological measurements taken during each quarter of the year 3 is given in Appendix II. The data are presented as cumulative joint frequency 3 distributions of the wind direction for the 296' level and wind speed class by atmospheric stability class determined from the temperature difference between the 296' and 33' levels.

Average data recovery for all measurements on the tower was about 99.6%.

5.0 ENVIRONMENTAL MONITORING Table 5.0-1 provides an outline of the Radiological Environmental Monitoring Program (REMP) as required in current Technical Specifications. Table 5.0-2 identifies the sampling locations, sample collections and analyses for each location. This program went into effect in November 1977 and differs from previous programs in the number and types of analyses performed. Tables 5.0-3 to 5.0-6 summarize data for the year. Tabulated results of these analyses are not included in the annual report. All data tables are available for inspection at the Station or in Corporate Office.

5.1 Gamma Radiation External radiation dose from onsite sources and noble gases released to the atmosphere was measured using CaSO4:Tm thermoluminescent dosimeters (TLDs).

A comparison of the TLD results for control stations with onsite and offsite indicator stations is included in Table 5.1-1. The annual average external radiation dose was 14.5 mR at the indicator locations and 14.5 at the control locations. TLD re :ults are listed in Table 5.1-1 and locations are shown in Figures 5.0-1 and 5.0-2.

Quarteriy average of external radiation dose (including background) at sixteen air sampling locations averaged 14.lil.0 mR and was similar to levels measured in 1986 g (13.5 mR),1987 (14.1 mR),1988 (13.4 mR),1989 (14.5 mR),1990 (14.6 mR),1991 (15.8 mR),1992 (14.7 mR), and 1993 (14.1 mR). The differences are not statistically E significant.

5.2 Airborne I-131 and Particulate Radioactivity Locations of the air samplers are shown in Figure 5.0-2. Airborne I-131 remained g below the LLD of 0.10 pCi/m3 throughout the year. 3 Gross beta concentrations ranged from 0.010 to 0.056 pCi/m3 and averaged 0.022 3

pCi/m3 and was similar to overall average levels in 1985 (0.024 pCi/m ),1986 (0.025 pCi/m3, except for the period from May 17 through June 7 when it was influenced by the nuclear reactor accident at Chernobyl),1987 (0.023 pCi/m3),1988 (0.030 pCi/m3),

3 19S9 (0.028 pCi/m ),1990 (0.020 pCi/m3),1991 (0.022 pCi/m3),1992 (0.021 pCi/m3),

and 1993 (0.021 pCi/m3),

No radioactivity attributable to plant operation was detected in any sample.

5.3 Aquatic Radioactivity Water samples were collected daily and composited for analysis weekly from the ;

Station's Intake and Discharge Canal. These cooling water samples were analyzed 1

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weekly for gross beta concentrations. Annual mean gross beta concentration in the intake and discharge canal wat er samples averaged 3.9 and 5.5 pCi/L, respectively.

The results were similar to those obtained in 1986 (4.7 sud 5.1 pCi/L),1987 (3.5 and 3.5 pCi/L) ,1988 (3.6 and 3.4 pCUL),1989 (3.9 and 3.7 pCi/L),1990 '4.1 and 3.8 pCi/L),1991 (4.0 and 4.3 pCi/L),1992 (3.9 and 3.4 pCi/L), and 1993 (3.9 and 3.5 pCi/L).

Composite samples collected weekly from Discharge Canal during the month of May and June showed an increase in gross beta analysis results. A maximum gross beta I result of 29.4 pCi/L was seen from the May 5,1994, sample. The increase in gross beta analyses results was due to an increase in the activity of normal station releases.

Gamma isotopic analysis of the May 5 sample indicated primarily Co-60 (40.8 pCi/L),

which is below the 300 pCi/L reporting level, and other isotopes that correspond to the isotopic mixture of normal station releases.

Samples were collected weekly from the East Moline Water Works and Davenport Water Works. These samples were composited monthly for each location and analyzed for gamma emitters. All samples analyzed were below the limits of detection for the program indicating no measurable amount of radioactivity was found due to station operation.

Levels of gamma radioactivity in fish were measured and found in all cases to be below the lower limit of detection for the program. One upstream and one downstream sediment sample were analyzed by gamma spectrometry. All gamma-emitters were below the limits of detection indicating that no radioactivity was found due to station operation.

Water, sediment, and fish sample locations are shown in Figure 5.0-3.

5.4 Milk Milk samples were collected monthly from November through April and weekly from May through October and analyzed for I-131. Sampled locations were the Musal Dairy, located 6.0 miles west southwest of the Station, Bill Stanley Farm located 3.0 miles east northeast of the station, and Gerald Peterson Dairy located 5.0 miles east southeast of the station.

1-131 remued below the detection limits of 5.0 pCi/L during the non-grazing period (November through April) and 0.5 pCi/L during the grazing period (May through October).

Milk sample locations are shown in Figure 5.0-3.

5.5 SampleCollections All samples were collected as scheduled except those listed in the Listing of Missed Samples, Appendix III. Sample collection anomalies are also included in the Listing of Missed Samples.

5.6 Listing of Missed Samples 1

All samples were collected as scheduled except for those listed in Listing of Missed Samples, Appendix III.

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5.7 Program Modifications Various editorial changes were made to the ODCM Chapter 11. Table 11-1 was revised to document the addition of 4 TLD's added in third quarter of 1993, and to update the sector and direction of numerous locations. Figures 11-1,11-2, and 11-3 were revised to update TLD locations and dairy locations.

A more rigid definition for the quarter had been adopted for 1994. Each quarter is 13 weeks long. The week shall start on Monday .md end on Sunday, with week #1 (1994) beginning on the first Monday of January (1/3/94). Due to this new definition all samples collected prior to 1/3/94 were reported as 1993 samples, except for milk whose January monthly sample collections were performed on 12/31/93, and 1/2/94.

Q-31, Gerald Peterson Dairy Farm, went out of business on November 1,1994. As of December 31,1994, no replacement dairy has been found.

Q-19, East Moline Water Works, sample point was moved from the pumping station to the main filitration plant in the fourth quarter.

6.0 ANALYTICAL PROCEDURES Analytical procedures used for analyzing and reporting radioactivity in environmental samples have remained essentially unchanged. A summary of the procedures is given in Appendix VI of the 1993 Annual Radiological Environmental Operating Report.

7.0 MILCH ANIMALS AND NEAREST LIVESTOCK CENSUSES Censuses of milch animals and nearest livestock were conducted around the Station by G.

Kreuder. These surveys were conducted on August 31,1994.

Milch animal and nearest cattle results of each census are presented in Appendix IV.

8,0 NEAREST RESIDENT CENSUS A census of the nearest residences within a five (5) mile radius was conducted on August 31,1994 by G. Kreuder.

The nearest residence census results are presented in Appendix IV.

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

Commonwealth Edison's Thermoluminescent Dosimeter (TLD) Program is accredited by the National Voluntary Laboratory Accreditation Program (NVLAP) which requires 8

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j biennial review and evaluation. In addition to the biennial ANSI tested requirement, j Commonwealth Edison also tests to the ANSI standard during the non-NVLAP visitation

,3 year. Commonwealth Edison additionally has an internal irradiation program that tests 3 each of the six nuclear station TLD processors once per quarter. The results of all TLD performance tests are retained by Commonwealth Edison's Corporate Health Physics Support.

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APPENDIX I DATA TABLES AND FIGURES l

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TABLE 1.1-1 QCCP 100-16 UNIT 1(2)

REVISION O

_ ATTACHMENT A (Page 1 of 5) )

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EFFLUENT & WASTE DISPOSABLE SEMI-ANNUAL REPORT GASEOUS EFFLUENTS SUMMATION OF ALL RELEASES Period: January through June 1994 FIRST SECO @ Est. Total A. f!SSION & ACTIVAfl0M GASES UNIT GUARTER QUARTER Error 1

1. fotet Ratesse Cl 1.42E+01 5.33E00 12.4 I 2. Average reteese rate for the period

3. ' Percent of CDCM tielt Chieney &

Stock scl/see 2

1.83E00 5.65E 03 2.64E 04 6.f8E01 2.10E 03 1.00E 04 I

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1. Total lodine 131 Cl 2.31E-04 2.17E 04 40.0 l

2. Averese reteese rate for the period scl/see 2.97E 05 2.79E-05 C. PARTICULATES

1. Particutetes wfth half ilves >8 days Cl 4.45E-03 2.65E 03 39.1 l

2. Average reteese rate for the period scl/sec 5.72E 04 3.37E 04

3. Cross etM e radioectivity C1 2.61E-06 4.44E 06"

0. TRif ttet

1. Total Reteese' Cl 1.11E+01 8.03E00 6.2 l

2. Aversee reteese rate for the period sCf/see 1.43E00 1.02100 E. lodine 131 & II3,frf tfue & Portfeutete

1. Percent of (mot (lef t Chimney & Stack E 1.14E 02 9.61E 03

NOBLE CAS &McM/NOSLE GAS BETA DOSE LIMITS

" PROJECTED VALUE BASED 011 PREVIOUS SIX MONTMS AVAILABLE DATA I

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[3 TABLE 1.1-1 (Continued)

ATTACHMENT A (Page 1 of 5)

EFFLUENT & WASTE DISPOSABLE SEMI ANNUAL REPORT GASEOUS EFFLUEtrTS - SUMMATION OF ALL RELEASES Period: July through December 1994 THIRD FOURTH Est. Total A. PISSION & ACTIVATION GASES UNIT QUARTER QUARTER Error %

1. Total Release Ci 9.06E00 1.33E00 12.4

2. Average release rate for the period pCi/see 1.14E00 1.678 01

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Percent of ODCM limit Chimney & % 3.90E 03 5.53E-04 Stack 1.65E 04 2.41E 05 B. IODINE

1. Total Iodine 131 Ci 2.11E-04 4.54E 05 40.0 l

2. Average release rate for the period Ci/see 2.65E 05 5.718 06 C. PARTICULATES

1. Particulates with half-lives 30 days Ci 2.08E 03 6.62E 04 39.1 l

2. Average release rate for the period pCi/see 2.62E-04 8.33E-05

3. Gross alpha radioactivity Ci 1.SSE 06 2.22E-06**

D. TRITIUM I

1. Total Release Ci 7.05E00 2.18E00 6.2 l

2. Average release rate for the period pC1/sec 8.878 01 2.74E 01 E. Iodine 131 & 133, Tritium & Particulate

1. Percent of ODCM limit Chimney & Stack % 8.00E 03 2.97E 03

NOBLE GAS GAMHA/ NOBLE GAS BETA DOSE LIMITS

- PRCMECTED VALUE BASED ON PREVIOUS SIX MOtfrHS DATA 12 g

TABLE 1.2-1 QCCP 100 16 UNIT 1(2)

REVISION 0 ATTACHMENT A (Page 4 of 5)

EFFLUENT & WASTE DISPOSABLE SEMI-ANNUAL REPORT LIQUID NFFIDENTS - SUMMATION OF ALL RELEASES I A. FISSION & AC"TIVATION GASES UNIT FIRST QUARTER SECOND QUARTER Est. Total trror 4 ,

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Ci 2.06E-02 3.03E-02 I

1. Total Release (not including tritium, 5.6 1 gases & alpha) j pCi/mL 1.43E-09 l f 2. Average diluted concentration during 1.76E-09 batch discharges for the period ]

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3. Percent of applicable limit * % 9.79E-03 4.10E-03 l

4.23E-03 1.71E-03 f

I 4. Maximum diluted concentration during pCi/mL 6.43E-09 5.93E 09 batch discharges a B. TRITIUM l

I 1. Total Release

2. Average diluted concentration during batch discharges for the period Ci pCi/mL 1.70E+01 1.18E 06 1.70E+01 9.86E 01 4.0

3. Percent of applicable limit t 3.93E-02 3.293-02 C. DISSOLVED & ENTRAINED GASES

1. Total Release C1 1.62E-04 < LID $.6 l

2. Average diluted concentration during pCi/mL 1.13E 11 < LID batch discharges for the period

3. Percent of applicable limit t 5.65E 06 EA D. GROSS ALPHA AC*TIVITY

1. Total stelease Ci <LLD < LID 14.5

2. Average diluted concentration during pCi/mL <LLD < LID batch discharges for the period E. VOLUME OF WASTE RELEASED (prior to Liters 4.64E+06 5.175+06 En dilution)

F. VOLUME OF DIIFTION WATER USED Liters 1.44E+10 1.72E+10 I

DURING BATCH DISCHARGES

0. 'KrTAL VO10ME OF DILUTION Liters 2.61E+11 1.46E+11 WATER USED DURING PERIOD (quarter)

Whole Body / Organ (ODCM) 13 I

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QCCP 100-16 I UNIT 1(2) E1 REVISION 0 E1 ATTACHMENT A (Page 4 of 5)

EFFLUENT & WASTE DISPOSABLE SEMI-ANNUAL REPORT LIQUID EFFLUEtrrS - SUMMATION OF ALL RELEASES THIRD FOURTH Est. Total A. FISSION & ACTIVATION GASES UNIT QUARTER QUARTER Error %

1. Total Release (not including tritium, Ci 2.715-03 6.43E 03 5.6 gases & alpha)

2. Average diluted concentration during pCi/mL 1.20E 10 1.078 09 batch discharges for the period

3. Percent of applicable limita % 3.90E 03 1.59E 03 1.66E-03 6.70E-04

4. Maximum diluted concentration during pCi/mL 5.47E 09 3.11E 09 batch discharges 1

B. TRITIUM

1. Total Release Ci 1.02E+01 2.96E+00 4.0 l l

2. Average diluted concentration during pCi/mL 4.52E-07 4.93E 07 batch discharges for the period

3. Percent of applicable limit % 1.50E 02 1.64E-02 C. DISSOLVED & ENTRAINED GASES

1. Total Release Ci 5.93E-06 < LIA 5.6 l

2. Average diluted concentration during pCi/mL 2.628 13 cLim batch discharges for the period

3. Percent of app 1_icable limit t 1.315 07 N/A D. GROSS ALPHA ACTIVITY

1. Total Release Ci <LLD < LID 14.5 l

2. Average diluted concentration during pCi/mL <LLD cLID batch discharges for the period E. VOLUME OF WASTE RELEASED (prior to Liters 3.73E+06 1.40E+06 dilution) ,

F. VOLUME OF DILUTION WATER USED Liters 2.26E+10 6.00E+09 DURING BATCH DISCHARCES G. '!OTAL VOLUME OF DILUTION Liters 3.82E+11 3.10E+11 WATER USED DURING PERIOD (quarter)

Whole Body / Organ (ODCM) i l

I; 14 1

.l 1 l

TABLE 2.0-1 Solid RadWaste Annual Report JANUARY 1994 Shipping Date Carrier Site Volume (f t3) M1114mries 01/04/94 KINDRICK TRUCKING QUADREX 2080.0 0.02 I 01/10/94 CHEM-NUCLEAR (CNSI) 01/21/94 CHEM-NUCLEAR (CNSI) 01/28/94 HITTMAN BARNWELL BARNWELL SEG 205.8 205.8 1056.0 16560.0 15860.0 22.28 01/28/94 RAY TECH TRUCKING CHANNAHON 750.0 64.06 TOTALS: 5 4297.6 32506.36 FEBRUARY 1994 1

Shipping Date Carrier Site Volume (f t3) Millicuries 02/07/94 CHEM-NUCLEAR (CNSI) BARNWELL 120.3 259200.0 j 02/18/94 CHEM-NUCLEAR (CNSI) BARNWELL 120.3 298900.0 '

02/22/94 CHEM-NUCLEAR (CNSI) BARNWELL 120.3 263800.0 02/22/94 CHEM-NUCLEAR (CNSI) BARNWELL 105.0 554.0 02/23/94 HITTMAN SEG 1076.4 9.29 1 02/28/94 CHEM-NUCLEAR (CNSI) BARNWELL 120.3 26580.

TOTALS: 6 1662.6 849043.29 MARCH 1994 Shipping

Date Carrier Site Volume (f t3) Millicuries l 03/04/94 CHEM-NUCLEAR (CNSI) BARNWELL 120.3 68370.0 l 03/07/94 RAY TECH TRUCKING CHANNAHON 540.0 51.77 BARNWELL 170.8 I l 03/08/94 CHEM-NUCLEAR (CNSI) 68400.0 l

03/10/94 HIITMAN SEG 1066.0 16.98 03/15/94 CHEM-NUCLEAR (CNSI) BARNWELL 343.0 287.8 03/16/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 15370.0 03/16/94 HITTMAN SEG 1056.0 16.36 03/30/94 CHEM-HUCLEAR (CNSI) BARNWELL 180.1 3317.0 TOTALS: 8 3682.0 155829.91 15 I

- _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - _ - _ _ - _ _ _ _ _ _-__________-____A

E a

TABLE 2.0-1 (continued)

Solid RadWaste Annual Report APRIL 1994 Shipping j Date Carrier Site Volume ( 8 t ' ) Millicuries

._ _ _ _.. - - _--_. g 04/05/94 CHEM-NUCLEAR (CNSI) BARNWELL 180.1 911.5 g 04/06/94 RAY TECH TRUCKING CHANNAHON 690.0 182.3 04/15/94 CHEM-NUCLEAR (CNSI) BARNWELL 120.3 76860.0 04/15/94 HITIMAN SEG 1071.0 41.35 04/21/94 CHEM-NUCLEAR (CNSI) BARNWELL 83.4 1828.0 04/27/94 CHEM-NUCLEAR (CNSI) BARNWELL 83.4 22400.0 04/27/94 RAY TECH TRUCKING BARNWELL 105.0 607.7 04/29/94 CHEM-NUCLEAR (CNSI) BARNWELL 83.4 2183.0 TOTALS: 8 2416.6 105013.85 MAY 1994 Shipping Date Carrier Site Volume (f t3) Mill {mries 05/04/94 CHEM-NUCLEAR (CNSI) BARNWELL 105.0 586.5 05/06/94 RAY TECH TRUCKING CHANNAHON 690.0 161.9 05/09/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 28990.0 05/11/94 CHEM-FUCLEAR (CNSI) BARNWELL 105.0 339.1 05/16/94 CHEM-NUCLEAR (CNSI) BARNWELL 83.4 667.8 05/19/94 CHEM-NUCLEAR (CNSI) BARNWELL 83.4 326.4 05/19/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 30120.0 05/20/94 RAY TECH TRUCKING CHANNAHON 690.0 123.2 05/23/94 CHEM-NUCLEAR (CNSI) RARNWELL (NSSF) 105.0 1530.0 05/24/94 HITTMAN SEG 2080.0 2.29 05/25/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 27890.0 05/31/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 17550.0 TOTALS: 12 4765.0 108287.19 JUNE 1994 Shipping Date Carrier Site Volume (f t3) Mil 11 caries

===... - .

06/01/94 CHEM-NUCLEAR (CNSI) BARNWELL 105.0 934.4 06/02/94 RAY TECH TRUCKING BARNWELL 1056.0 85.33 06/07/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 8857.0 06/08/94 CHEM-NUCLEAR (CNSI) BARNWELL 105.0 1358.0 06/09/94 RAY TECH TRUCKING BARNWELL 1056.0 99.63 06/14/94 CHEM NUCLEAR (CNSI) CHANNAHON 682.5 161.7 06/15/94 CHEM-NUCLEAR (CNSI) BARNWELL (NSSF) 45.0 36.76 06/15/94 CHEM-NUCLEAR (CNSI) BARNWELL 60.0 55.65 j 06/16/94 CHEM-NUCLEAR (CNSI) BARNWELL 240.1 139.5 06/23/94 CHEM-NUCLEAR (CNSI) BARNWELL 205.8 30360.0 06/23/94 CHEM-NUCLEAR (CNSI) BARNWELL 105.0 338.0 06/27/94 RAY TECH TRUCKING BARNWELL 714.0 57.2 06/27/94 CHEM-NUCLEAR (CNSI) BARNWELL 170.8 39020.0 TOTALS: 13 4751.0 81503.17 16

=

I l TABLE 2.0-1 (continued)

Solid RadWaste Annual Report l 6/94 - 12/94 Mixed Waste Shipment I Shiping date Carrier Site Vol.(ft3) sci I 10-13-94 Kindrick Trucking Diversified Scientific Services, Inc.

352.5 .3164 I

I I

a

250

"' s k FIGURE 3.1-1 ,

Estimated Cumulative Gamma Dose (in mrom)

O from the Quad Cities Station for the period i ,

January-December 1994 3

REL gg .

lsooleth labels fE, Small figure - multiply by 10* /

Large figure multipty by 104 4 I 500 M"i o SCALE

^ ! I

/ witt s N ,o. , , -~17.*.* ' $.

p' ,

ss o

?

a :. <

IE' *-

I ~

o 1

c.

C L I N T O N

i

~

$ j. wifon

a Cienton g

/3 v s so ; 0* W'" ; Y 't 's 0) come 3[ N' us so M %N \

J 2.s uorris %

s comon'ere ,,'

e o oo., .. 4 ,,, ., ./ x,o al .

8' 1 0 0 I N . I L I N O I S ,f c < 250 c ar e g g ,,,

WH TESI lD E,-

"T '" h w s e,h

. ,,T. '

R O C K d, *

,g C O T ,

u ,u se...

y, ,

l -

, s f. .o P

y gyf 7

, s I ILL 92

.f I --

7

.x E N R p# ,

I

~

I SCALE

o. . . 9 e es t.o uitts O 9 @ #9 to t$ So s u I

18 I

E o

FIGURE 3.1-2 t.

Estimated Total Concentrations (in pCi/m3) of Noble Gases from the Quad Cities Station for the period January-December 1994 (gm a '

, 15 0 a

8

,v 130pleth Labels RELEASE P

J$

Small figure - multiply by 10-3 s .250 Large figure - multiply by 10,3 loo h j

=

SCALE

! I

/, unts

s. ; - * ' ! 8 g __

..... La*

,s , ;

.' $' I C L l N T O '*' '

+ i

+# , 25 = 's, ,' ,

, ulto >

'a

Chnf0A ,- h E Tlb;;,- U usid[* *, \' '#

~

W u,,,..a %

s com acu ..,

q ,

o*******'*** *,,, l 10 0

,, g

/

( #

1 O e W A .

' l L N O I S ,f so ; /- /w H IT 'EsI o e ., , , , ,,, p,.

. ~~ Y e,s S C 0 T T R O' s

~E"'

, , ......i. , *,/

7e .. _ ...o > .. f, gs g l

,4,

.. t- j- 1 - . -

f, ' y; __

~ SfaI**

ggg H E N R Y v:g [ *

%hn M*

Rata .

10 vss y

SCALE 9 , 9 e es ro unts a a .a is to es so . .

19 E

=

m-FIGURE 3.1-3

.. iso / . ;

I Estimated Total Concentrations (in pCi/m3) of lodine from the Quad Cities Station for the period January-December 1994

,3o ,

250 istoleth Labels ,

Small figure - multiply by 10' t /

Large figure . multiph by 10-' e, lQ , // e 150 SCALE

.., i".'.' 3.!: i, l ==

t i C L n - N $ i **:=

8 a et '.

+

+ h ci.ni.a -1

.__ v i no D '"

i' 'g af ja

,E "Y s co..~

f

,,,,,,.a *

.. .. iso .

~~

. I O e V A.

I, L L l N O I S c

ar ,, , I g WH IT SI D E -

l 30

'g =

4 .

p

, C O T R O C K N , Erie 28

usW8

""*menm_ w.ei E e'

-r,g f *

~. .;-

m. -

v

{

ky .

s sd f

.it ct ,

I.00 k .

~

SCALE

9. ...e e it ro ui..s O 5 9 'S to il 30 s u I

20

mi

~

FIGURE 3.1-4 .

. i , ,.

[ e l Estimated Total Concentrations (in pCVm3) 250 '

of Particulates from the Quad Cities Station / ,

for the period January-December 1994 i e ,on isooleth Labels Small figure - multiply by 10 8

/ n . *N3 bY j j Large figure - multiply by 10 -

50 .f j l <

e f SCALE I

^ ! I mitts

,/ , l l

w a ; .

f g

=u .l s

L 1 N T N *{* ,

is c) ', ~

4e '.x

5

'. Chaton

y U S 30 O' I J b j wy v s 50 w ~

f r '

7 uer, .a s c , ,

a nos.o ** . * .,

, ? -

f SITE I O W .

l L l N O I , j e = ,, , '4 jc evo ITESI D E -

g- -m}tW 2o ,H

, "v . $

a,

' d, C O _

R O C K l

., gA 3 *- -

m.,,.....

< gg g .

)f- .

. Me ten -

e' w .. / 4' W I. - ' f *'e H E N R Y

' {&M,em:

k. V . 4 l

t w

$CALE l

o. ,,,9 so is to uitrs O $ 80 #9 P0 19 30 s u 21

=

[ _ _ . _ _ . _ . . . _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ . _ __

TABLE 3.1-1 QUAD CITIES STATION UNIT ONE ACTUAL 1994 I MAXIMUM DOSES RESULTING FROM AIRBORNE RELEASES PERIOD OF RELEASE - 01/01/94 TO 12/31/94 INFANT RECEPTOR CALCULATED 03/08/95 IST 2ND 3RD 4TH TYPE QUARTER QUARTER QUARTER QUARTER ANNUAL JAN-MAR APR-JUN JUL-SEP OCT-DEC GAMMA AIR 1.86E-04 0.00E+00 5.52E-05 6.73E-06 2.48E-04 (MRAD) (NNE ) ( ) (NNE ) (NNE ) (NNE )

BETA AIR 1.70E-05 0.003+00 4.64E-06 5.64E-07 2.22E-05 (MRAD) (ESE ) ( ) (ESE ) (ESE ) (ESE )

TOT. BODY 1.40E-04 0.00E+00 4.17E-05 5.08E-06 1.87E-04 (MREM) (NNE ) ( ) (NNE ) (NNE ) (NNE )

SKIN 1.55E-04 0.00E+00 4.58E-05 5.57E-06 2.06E-04 (MREM) (NNE ) ( ) (NNE ) (NNE ) (NNE )

ORGAN 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 (MREM) ( ) ( ) ( ) ( ) ( )

THIS IS A REPORT FOR THE CALENDAR YEAR 1994 I COMPLIANCE STATUS - 10CFR 50 APP. I INFANT RECEP70R

% OF APP I. ------------

QTRLY IST QTR 2ND QTR 3RD QTR 4TH QTR YRLY t OF I GAMMA AIR (MRAD)

BETA AIR (MRAD)

OBJ 5.0 10.0 JAN-MAR 0.00 0.00 APR-JUN 0.00 0.00 JUL-SEP 0.00 0.00 OCT-DEC 0.00 0.00 OBJ 10.0 20.0 APP. I 0.00 0.00 TOT. BODY (MREM) 2.5 0.01 0.00 0.00 0.00 5.0 0.00 SKIN (MREM) 7.5 0.00 0.00 0.00 0.00 15.0 0.00 ORGAN (MREM) 7.5 0.00 0.00 0.00 0.00 15.0 0.00 I RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 ODCM SOFTWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 January 1995 I

.I

{I I

E TABLE 3.1-1 (continued)

QUAD CITIES STATION UNIT ONE ACTUAL 1994 MAXIMUM DOSES RESULTING FROM AIkBORim RELEASES g

PERIOD OF RELEASE - 01/01/94 TO 12/31/94 CALCULATED 03/08/95 g ADULT RECEPTOR IST 2ND 3RD 4TH TYPE QUARTER QUARTER QUARTER QUARTER JAN-MAR APR-JUN ANNUAL JUL-SEP OCT-DEC GAMMA AIR 1.86E-04 0.00E+00 (MRAD) 5.52E-05 6.73E-06 2.48E-04 =

(NNE ) ( ) (NNE )

BETA AIR 1.70E-05 (NNE ) (NNE )

0.00E+00 4.64E-06 5,64E-07 (MRAD) (ESE ) (

2.22E-05 TOT. BODY

) (ESE ) (ESE ) (ESE )

1.40E-04 0.00E+00 4.17E-05 5.08E-06 (MREM) (NNE ) ( ) (NNE i 1.87E-04 SKIN 1.55E-04 (NNE ) (NNE )

0.00E+00 4.58E-05 5.57E-06 (MREM) (NNE ) (

2.06E-04 ORGAN

) (NNE ) (NNE ) (NNE )

4.28E-04 2.05E-04 2.72E-04 1.11E-04 (MREM) (ESE ) (ESE ) 1.02E-03 (ESE ) (ESE ) (ESE )

GI_LLI GI_LLI GI_LLI GI_LLI THIS IS A REPORT FOR THE CALENDAR YEAR 1994 GI_LLI 5

COMPLIANCE STATUS - 10CFR St APP. I ADULT RECEPTOR I

r

! ------------ % OF APP I. ------------

QTRLY IST QTR 2ND QTR 3RD QTR OBJ JAN-MAR 4TH QTR YRLY % OF APR-JUN JUL-SEP OCT-DEC OBJ GAMMA AIR (MRAD) 5.0 0.00 0.00 APP. I BETA AIR (MRAD) 10.0 0.00 0.00 10.0 0.00 0.00 0.00 0.00 0.00 TOT. BODY (MREM) 2.5 0.01 0.00 20.0 0.00 SKIN (MREM) 7.5 0.00 0.00 0.00 5.0 0.00 0.00 0.00 0.00 15.0 0.00 ORGAN (MREM) 7.5 0.01 0.00 0.00 0.00 IS.O 0.01 l

E GI_LLI GI LLI GI..LLI GI_LLI GI LLI RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 i ODCM SOF7 WARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 January 1995 l

l I

I l

l I

2 I

i

c '

i

{.

E TABLE 3.1-1 (continued)

QUAD CITIES STATION UNIT WO

~

ACTUAL 1994 MAXIMUM DOSES RESULTING FROM AIRBORNE RELEASES PERIOD OF RELEASE - 01/01/94 TO 12/31/94 CALCULATED 03/08/95 INFANT RECEPTOR IST 2ND 3RD 4TH f TYPE QUARTER QUARTER QUARTER QUARTER L JAN-MAR APR-JUN JUL-SEP ANNUAL OCT-DEC GAMMA AIR 9.67E-05 1.05E-04 1.40E-04 2.09E-05 3.63E-04 (MRAD) (N ) (NNE )

BETA AIR (NNE ) (NNE ) (NNE )

9.42E-06 1.00E-05 1.19E-05 1.85E-06 (MRAD) (ESE ) 3.31E-05 (ESE ) (ESE ) (ESE ) (ESE )

TOT. BODY 7.30E-05 7.95E-05 1.06E-04 (MREM) 1.58E-05 2.74E-04 (N ) (NNE ) (NNE )

SKIN 8.12E-05 (NNE ) (NNE )

8.80E-05 1.16E-04 1.74E-05 3.03E-04 (MREM) (NNE ) (NNE )

ORGAN (NNE ) (NNE ) (NNE )

0.00E+00 0.00E+00 0.00E+00 0.00E+00 (MREM) ( )

0.00E+00

( ) ( ) ( ) ( )

THIS IS A REPORT FOR THE CALENDAR YEAR 1994 COMPLIANCE STATUS - 20CFR 50 APP. I INFANT RECEPTOR

% OF APP I. ------------

QTRLY IST QTR 2ND QTR 3RD QTR 4TH QTR OBJ JAN-MAR APR-JUN YRLY t OF JUL-SEP OCT-DEC OBJ APP. I GAMMA AIR (MRAD) 5.0 0.00 0.00 0.00 BETA AIR (MRAD) 10.0 0.00 10.0 0.00 0.00 0.00 0.00 0.00 20.0 0.00 TOT. BODY (MREM) 2.5 0.00 0.00 0.00 SKIN (MREM) 7.5 0.00 0.00 0.00 5.0 0.01 0.00 0.00 15.0 0.00 ORGAN (MREM) 7.5 0.00 0.00 0.00 0.00 15.0 0.00 RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 )

ODCM SOFWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 January 1995

[

1 24

me TABLE 3.1-1 (continued)

QUAD CITIES STATION UNIT TWO ACTUAL 1994 MAXIMUM DOSES RESULTING FROM AIRBORNE RELEASES PERIOD OF RELEASE - 01/01/94 TO 12/31/94 CALCULATED 03/08/95 ADULT RECEPTOR iST 2ND 3RD 4TH TYPE QUARTER QUARTER QUARTER QUARTER ANNUAL JAN-MAR APR-JUN JUL-SEP OCT-DEC GAMMA AIR 9.67E-05 1.05E-04 1.40E-04 2.09E-05 3.63E-04 (MRAD) (N ) (NNE ) (NNE ) (?RE ) (NIE )

BETA AIR 9.42E-06 1.00E-05 1.19E-05 1.85E-06 3.31E-05 (MRAD) (ESE ) (ESE ) (ESE ) (ESE ) (ESE )

TOT. BODY 7.30E-05 7.95E-05 1.06E-04 1.58E-l.3 2.74E-04 (MREM) (N ) (NNE ) (NNE ) (NNE ) (t#1E )

SKIN 8.12E-05 8.80E-05 1.16E-04 1.74E-05 3.03E-04 (MREM) (NNE ) (NIE ) (NNE ) (NNE ) (tRE )

ORGAN 4.27E-04 5.16E-04 3.28E-04 1.12E-04 1.38E-03 (MREM) (ESE ) (ESE ) (ESE ) (ESE ) (ESE )

GI_LLI GI_LLI GI_LLI GI_LLI GI_LLI l THIS IS A REPORT FOR THE CALENDAR YEAR 1994 m COMPLIANCE STATUS - 10CFR 50 APP. I ADULT RECEPTOR I

% OF APP I. ------------

QTRLY 1ST QTR 2ND QTR 3RD QTR 4TH QTR YRLY % OF OBJ JAN-MAR APR-JUN JUL-SEP OCT-DEC OBJ APP. I GAMMA AIR (MRAD) 5.0 0.00 0.00 0.00 0.00 10.0 0.00 BETA AIR (MRAD) 10.0 0.00 0.00 0.00 0.00 20.0 0.00 TOT. BODY (MREM) 2.5 0.00 0.00 0.00 0,00 5.0 0.01 SKIN (MREM) 7.5 0.00 0.00 0.00 0.00 15.0 0.00 ORGAN (MREM) 7.5 0.01 0.01 0.00 0.00 15.0 0.01 GI_LLI GI_LLI GI_LLI GI_LLI GI_LLI RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 ODCM SOF'IMARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 January 1995 l

E t

TABLE 3.2-1 QUAD CITIES STATION UNIT ONE' ACTUAL 1994 >

MAXIMUM DOSES (MREM) RESULTING FROM AQUATIC EFFLUENTS PERIOD OF RELEASE - 01/01/94 TO 12/31/94 CALCULATED 03/08/95 l

{' IST ADULT RECEPTOR 2ND 3RD 4TH DOSE TYPE QUARTER QUARTER QUARTER QUARTER ANNUAL Jl.N-MAR APR-JUN JUL-SEP OCT-DEC l TOTAL 4.08E-05 1.49E-05 3.68E-05 1.33E-05 1.06E-04 BODY

f. INTERNAL 5.82E-05 1.88E-05 5.26E-05 1.83E-05 1.48E-04 L ORGAN LIVER LIVER LIVER LIVER LIVER THIS IS A REPORT FOR THE CALENDAR YEAR 1994 COMPLIANCE STATUS - 10 CFR 50 APP. I

% OF APP I. ------------

QTRLY IST QTR 2ND QTR 3RD QTR 4TH QTR YRLY % OF OBJ JAN-MAR APR-JUN JUL-SEP OCT-DEC OBJ APP. I TOTAL BODY (MREM) 1.5 0.00 0.00 0.00 0.00 3.0 0.00 I

L CRIT. ORGAN (MREM) 5.0 0.00 0.00 0.00 0.00 10.0 0.00 LIVER LIVER LIVER LIVER LIVER RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 ODCM SOFWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 January 1995 E

E E

E 26 J

E O

TABLE 3.2-1 (continued)

QUAD CITIES STATION UNIT WO I

ACTUAL 1994 MAXIMUM DOSES (MREM) RESULTING FROM AQUATIC EFFLUENTS PERIOD OF RELEASE - 01/01/94 TO 12/31/94 CALCULATED 03/08/95 ADULT RECEPTOR IST 2ND 3RD 4TH "

DOSE TYPE QUARTER QUARTER QUARTER QUARTER ANNUAL JAN-MAR APR-JUN JUL-SEP OCT-DEC TOTAL 1.06E-04 67E-05 2.0CE-05 BODY 1.06E-05 1.84E-04

INTERNAL 1.52E-04 6.03E-05 2.62E-05 ORGAN 1.47E-05 2.53E-04 g LIVER W LIVER LIVER LIVER LIVER E THIS IS A REPORT FOR THE CALENDAR YEAR 1994 COMPLIANCE STATUS - 10 CFR 50 APP. I

% OF APP I. ------------

E QTRLY IST QTR 2ND QTR 3RD QTR 4TH QTR YRLY % OF OBJ JAN-MAR APR-JUN JUL-SEP OCT-DEC OBJ APP. I TOTAL BODY (MREM) 1.5 0.01 0.00 0.00 0.00 3.0 0.01 CRIT. ORGAN (MRDi) 5.0 0.00 0.00 0.00 0.00 10.0 0.00 LIVER LIVER LIVER LIVER LIVER RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 ODCM SOFWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 Janual'/ 1995 Ii i Il I

Il 27 l'

i I

l 1

TABLE 3.3-1 I QUAD CITIES STATION UNIT ONE 1

10 CFR 20 COMPLIANCE ASSESSMENT i PERIOD OF ASSESSMENT 01/01/94 TO 12/31/94 CALCULATED 03/08/95

1. 10 CFR 20.1301 (a) (1) Compliance.

Total Effective Dose Egivalent, mrem /yr 3.26E+00 10 CFR 20.1301 (a) (1) limit mrem /yr 100.0

% of limit 3.26 I

I RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JAtmARY 1994 ODCM SOFWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 January 1995 I

I I

28 I

E TABLE 3.31 (continued)

I QUAD CITIES STATION UNIT ONE I'

10 CFR 20 COMPLIANCE ASSESSMENT PERIOD OF ASSESSMENT 01/01/94 TO 12/31/94 CALCULATED 03/08/95

2. 10 CFR 20.1301 (d)/40 CFR 190 Compliance Dose Limit % of (mrem) (mrem) Limit Whole Body Plume 1.87E-04 (DDE) Skyshine 3.26E+00 Ground 0.00E+00 Total 3.26E+00 25.0 13.04 Organ Dose Thyroid 6.70E-04 75.0 (CDE) Gonads 7.11E-04 25.0 Breast 6.71E-04 25.0 Lung 6.70E-04 25.0 Marrow 6.81E-04 25.0 Bone 6.68E-04 25.0 Remainder 7.67E-04 25.0 CEOE 7.11E-04 l TEDE 3.26E+00 100.0 3.26 RESULTS BASED UPON: ODCM ANNEX PEVISION 1.0 JANUARY 1994 ODCM SOFTWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 Janu.ary 1995 29 I

=

LI l

l l

l TABLE 3.3-1 (continued)

QUAD CITIES STATION UNIT 'IMO I 10 CFR 20 COMPLIANCE ASSESSMENT PERIOD OF ASSESSMENT 01/01/94 TO 12/31/94 CALCULATED 03/08/95

1. 10 CFR 20.1301 (a) (1) Compliance Total Effective Dose Egivalent, mrem /yr 6.19E+00 10 CFR 20.1301 (a) (1) limit mrem /yr 100.0

% of limit 6.19 I

RESULTS BASED UPON: ODCH ANNEX REVISION 1.0 JANUARY 1994 ODCM SOF'IWARE VERSION 1.1 January 1993 ODCM DATABASE VERSION 1.1 January 1995 I

I

E

=

TABLE 3.3-1 (continued)

QUAD CITIES STATION UNIT TWO 10 CFR 20 COMPLIANCE ASSESSMENT PERIOD OF ASSESSMENT 01/01/94 TO 12/31/94 CALCULATED 03/08/95

2. 10 CFR 20.1301 (d)/40 CFR 190 Compliance Dose Limit % of (mrem) (mrem) Limit Whole Body Plume 2.74E-04 (DDE) Skyshine 6.19E+00 Ground 0.00E+00 Total 6.1SE+00 25.0 24.76 Organ Dose Thyroid 9.76E-04 75.0 (CDE) Gonads 9.94E-04 25.0 Breast 9.62E-04 25.0 Lung 9.63E-04 25.0 Marrow 9.73E-04 25.0 Bone 9.63E-04 25.0 Remainder 1.04E-03 25.0 CEDE 9.95E-;4 TEDE 6.19E+00 100.0 6.19 RESULTS BASED UPON: ODCM ANNEX REVISION 1.0 JANUARY 1994 ODCM SOFTWARE VERSION 1.1 January 1995 ODCM DATABASE VERSION 1.1 Janulry 1995 31

I FIGURE 5.0-1 Revision 1.0 I ,

January 1994

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l - no tmee QUAD CITIES STATION I INNER RING TLD LOCATIONS I

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~~FIGURE 5.0-2 Revision 1.o January 1994~~

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lilinois
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s -. 2054 sia-se ""
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' Moline ' % '
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5 Outer Aeg TLD Location i.n _ se
._ _ _s se ,o n w n.
se QUAD CITITES STATION FIXED AIR SAMLING SITES AND OUTER RING TLD LOCATIONS Q01 Onsite No.1 Q09 Ene QC2 Onsite No. 2 Q10 liillsdale ,
QO3 Onsite No. 3 Q11 Port Dyron Q04 Nitrin Q12 Bettendorf QOS Saddle Club Dairy Q13 Princeton Q-06 Fairbanks Q14 Utica Ridge Road Q07 Cimton Q15 DeWitt t
Q08 Sikkema Farrn Q16 Low Moor l
33 g'
-I i FIGURE 5.0-3 a.v2. ion :.o January 1994 l
i ir[s I sows 9M Co.ee Late US I # { as,se. sea [ppi u 64 Clinton ._
y,,, sowatw us e' " "
, Clinton can. " ' '
DeWit't
~~'"" ~ _i,- -~~
- . us m Nl - em 1
f , _ Morrison
{
~~aman ne~~
, , _ , , , , , a.g, J I I u r.
22,21 L ,
lilinois lows I " s18 e.
2a eggy 3, Whiteside ,
l' vs as gg,y a N !
owa es 4 ue a, i.e.am. em 7 a er #
""' "[
i hek Davenport 24
'*" ~ ~
Ws ILL 03 c Henry I
y
""* .,_ casse -
t sees 4 kI I N e as s
5 $4mpteng Station se I t.. * ? ? ? ""'"
1....f ? ? ? ? V '" l j
E QUAD CITIES STATION MILK, FISH, WATER, AND SEDIMENT I SAMPLE LOCATIONS f l
l Q18 Musal Dairy l 5 Q19 East Moline Water Works Q20 Davenport Water Works Q21 Intake Canal ,
Q 22 Discharge Canal )
l Q24 Pool #14 of Mississippi River )
Q26 Bdl Stanley Dairy Q27 Albany, Upstream on Mississippi River Q28 Cordova, Downstream on Mississippi River j QSP-29 MississippiRiver, Upstream QSP-30 MissLssippi River, Downstream Q31 Cerald Peterson Dairy 34 I l
, _ , . __ 4 .__.J_. _ .* e m -.4 _- u ---_.am-_.._ A .
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TABLE 5.0-1 I Quad Cities Station Radiological Environmental Monitoring - %
8 C
Locations y { j g j i 3 $ E 3 C E y ; g g y 0 0 =
x i d 5 "
k N is rf 5 3 <4 S
Q-01 Onsite No.1 0 0 . .
Q-02 Onsite No. 2 0 0 .
Q-03 Onsite No. 3 0 0 . .
Q-04 Nitrin 0 0 Q-05 Saddle Club Dairy Farm 0 0 Q-06 Fairbanks 0 0 Q-07 Clinton 0 0 Q-08 Sikkema Farm 0 0 Q-09 Erie 0 0 .
Q-1011illsdale 0 0 Q-11 Port Byron 0 0 Q-12 Bettendorf 0 0 Q-13 Princeton 0 0 Q-14 Utica Ridge Road 0 0 .
Q-15 DeWitt 0 0 Q-16 Low Moor 0 0 .
Q-18 Musal Dairy I
. O Q-19 East Moline Water Works 0 Q20 Davenport Water Works . 0 Q21 Intake Canal 0 . .
Q-22 Dixharge Canal 0 .
Q24 Pool #14 of Missippippi River I Q-26 Bill Stant Dairy Q27 Albany, Q-28 Cordova, tream on Mississippi River wnstream on Mississippi River 0
0 O
O QSP 29 Mississippi River, Upstream 0 I QSP-30 Mississippi River, Downstream Q-31 Gerald Peterson Dairya
. 0 .
0 I
CENSUS Dairy Residence Livestock a Gerald Peterson Dairy went out of business in November of 1994.
I
.I I
I 35 i
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f TABLE 5.0-2 QUAD CITIES STATION RADIOLOGICAL ENVIRON ~ MENTAL MONITORING PROGRAM, SAMPLING LOCATIONS L 1. AIR SAMPLERS Distance Direction Site Codea Location (miles) (OL
{
Q-01 Onsite No.1 0.5 7 p Q-02 Onsite No. 2 0.5 70 L Q-03 Onsite No. 3 0.6 177 Q-04 Nitrin 1.5 40 Q-05 Saddle Club Dairy Farm 1.8 175
{ Q-06 Q-07 (C)
Fairbanks Clinton 1.8 9.0 340 40 I
Q-08 (C) Sikkema Farm 7.0 70
~
Q-09 (C) Erie 13.0 110 Q-10 (C) Hillsdale 10.0 130 Q-11 (C) Port Byron 8.0 170 ,
Q-12 (C) Bettendorf 13.0 210 Q-13 Princeton 4.8 220 Q-14 (C) Utica Ridge Road 11.0 270 Q-15 (C) DeWitt 13.0 300 Q-16 Low Moor 6.0 330
{
m 2. ILRs L
~~a. Same as No. l.~~
I
b. Special TLD Samplers Distance Direction l Site Code (miles) (L Inner Ring Q-101-1,2 0.7 4 Q-102-1,2 1.7 21 I Q-103-1,2 Q-104-1 Q-104-2 1.2 1.1 1.0 58 60 77 l
Q-104-3 0.6 77 Q-105-1,2 0.8 91 Q-106-1 0.7 109 Q-106-2 0.7 118 Q-107-1 0.7 128 Q-107-2 0.7 137 Q-107-3 0.8 146 Q-108-1,2 0.9 155 a Control (background) locations are denoted by a "C" after site code. All other locations are indicators.
36
E as TABLE S.0-2 (continued)
QUAD CITIES STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM, SAMPLING LOCATIONS
~~2. ILD:i~~
~~b. SpecialTLD Samplers (continued)~~
Distance Direction Site Code (miles) (0)
Q-109-1,2 0.9 176 Q-111-1,2 2.6 230 Q-112-1,2 2.4 246 Q-113-1,2 2.5 264 Q-114-1,2 2.6 286 Q-115-1,2 2.3 310 Q-116-1,2 2.2 339 Outer Ring Q-201-1,2 4.0 356 Q-202-1,2 4.4 17 Q-203-1,2 5.5 34 g Q-204-1,2 Q-205-1,2,4 4.5 4.5 61 g 83 Q-206-1,2 4.8 113 Q-207-1,2,4 4.8 133 Q-208-1,2 4.4 158 Q-209-1,2,4 4.8 179 i
Q-210-1,2,4 4.4 210 Q-211-1,2 5.0 223 Q212-1,2 4.8 242 l Q-213-1,2 4.7 265 Q-214-1,2 4.8 310 Q-215-1,2 4.8 316 Q-216-1,2 4.5 333
~~3. MILK Distance Direction Site Codea Location Unde) ()~~
Q-18 Musal Dairy 6.0 240 Q-26 Bill Stanley Dairy 3.0 120 Q-31 Gerald Peterson Dairyb 5.0 105 a Control (background) locations are denoted by a "C" after site code. All other locations are indicators.
b Gerald Peterson Dairy went out of business on November 1,1994, and as of December 31,1994, no replacement dairy has been found.
37
TABLE S.0-2 (continued)
QUAD CITIES STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM, SAMPLING LOCATIONS
~~4. PUBLIC WATER SUPPLY Distance Direction Site Codea Location (miles) (0)~~
Q-19 East Moline Water Works 16.0 206 Q-20 Davenport Water Works 18.0 219
~~5. COOLING WATER Distance Direction Site Codea Location (miles) (0)~~
Q-21 (C) Intake Canal At Station )
Q-22 Discharge Canal At Station Distanceb Direction Site Codea Location (miles) (0)_._
l Q-24 Pool #14 of Mississippi River 0.5 330 l
QSP-29 (C) Mississippi River, Upstream 1.0 240 QSP-30 Mississippi River, Downstream 1.0 200
~~7. SHORELINE SEDIMFBIS Distance Direction Silgfedga Location (miles) (0)~~
Q-27 (C) Albany, Upstream on Mississippi 5.5 35 River Q-28 Cordova, Downstream on Mississippi 3.3 205 )
l River a Control (background) locations are denoted by a "C" after site code. All other locations arc indicators.
b Theses locations are approximations of the areas the fish are collected.
38
TABLE 5.0-2 (continued)
QUAD CITIES STATION l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM, SAMPLE COLLECTION AND ANALYSES 1
l Loca hon Collection Type of Frequency Sample Media Code a Site Frequency Analysis of Analysis Pearks
1. Aubome Onsite and Near Field Continuous Cross Beta Weekly On all samples.
Particulates operation Q41 Onsite No. I for one week Gamma isot. If gross beta in a sample exceeds SX the average concentration of the preceding QO2 Onsite No. 2 calendar quarter for the sample kxatmn.
Q43 Onsite No. 3 Gamma isot. Quarterly On Quarterly composite from each location.
QO4 Nitrin QOS Saddle Club Dairy Filter Weekly Farm Exchange Q46 Fairbanks Far Field Continuous Gross Beta Weekly See footnote *b."
operation w Q47 (C) Cimton for one week Gamma isot. See footnote "b"
Q48 (C) Sikkema Fann If gross beta in a sample exceeds 5X the Q09 (C) Ene Filter Weekly average concentration of the preceding Q 10 (C) Hdlsdale Exchange calendar quarter for the sample location.
, Q-11 (C) Port Byron l Q-12 (C) Bettendorf I
Q-13 Princeton Q-14 (C) Utica Ridge Road Q15 (C) DeWitt Q16 I,ow Moor I
l
2. AA- Same as 1. Continuous I-131 Bnwekly On all samples from onsite and near field; lodine operation for far field samples, see footnote "b."
for two weeks l 3. AirSampimg Same as 1. -
Test and Weekly On all samplers.
f Train Maintenance l
8 Control (background) kxatons are denoted by a "C"in this column. All other locations are indicators.
b Far-field samples are analyzed when near-field results are inconsistent with previous measurements and radioactivity is confirmed as having its orgin in airbome effluents released from the station or at the discretion of the Emergency Preparedness Director.
g .
g _
g -
m M EE
TABLE 5.0-2 (continued)
QUAD CITIES STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM, SAMPLE COLLECTION AND ANALYSES I> ration Collection Type of Frequency Sample Media Codea Site Frequency Analysis of Analysis Remarks ,
l TLD Two sets of TLD's at all air sampler
4. a. Same as 1. Quarterly Gamma Quarterly locatwns. All sets read Quarterly.
~~b. Q-101-1,2 Inner Ring Quarterly Gamma Quarterly All TLDs are read Quarterly.~~
102-1,2 103-12 104-1,2,3 105-1,2 1%1,2 107-1,2,3 108-1,2 109-1,2 111-1,2 112-1,2 113-1,2 8 114-1,2 115-12 116-1 2 Q-201-1,2 Outer Ring 202-1,2 203-1,2 2%1,2 205-1,2,4 2%1,2 207-1,2,4 208-1,2 209-1,2,4 210-1,2,4 211 1,2 212-1,2 213-1,2 214-12 215-1,2 216-1,2 a Control (background) locations are denoted by a "C"in this column. All other locations are indicators.
TABLE 5.0-2 (continued)
QUAD CITIES STAllON RADIOLOGICAL ENVIRONMESTTAL MONITORING PROGRAM, SAMPLE COLLECTION AND ANALYSES incation Collection Type of Frequency Sample Media Code a Site Frequency Analysis of Analysis Remarks
5. Milk Q18 Musal Dairy Weekly- I-131 Weekly- On all samples. LLD- 0.5 pCi/L while Q26 Billstanley Dairy May through May through on pasture Q31 Gerald Peterson Dairyb October October Monthly: I-131 Monthly: On allsamples. LLD 50pCi/Lwhile November November not on pasture through April through April i 6. Public Water Q19 East Moline Water Weekly Gamma Isot. Monthly On monthly composite from each l Works j location.
~~Q20 Davenport Water Works~~
~~7. Cooling Water Q21 (C) Intake Canal Weekly Gross Beta Weekly On all samples.~~
Q22 Dicharge Canal u 8. Fish Q24
- Pool #14 of Mississippi Semiannually Camma Isot. Saniannually On edibleportionsonly. Atleast River two speces.
QSP-29 (C) Mississippi River, Upstream QSP-30 Mississippi River, l Downstream
~~9. Shoreime 427 (C) Albany, Upstream on Annually Gamma Isot. Annually On allsamples.~~
~~Sediments Mississippi River Q28 Cordova, Dow nstream on Mississippi River~~
~~10. Land Use Census Milch Animals a. Site boundary to 2 miles -~~
~~a. Enumeration by Annually Dunng grazing season.~~
~~a door todooror equivalent counting technique.~~
~~b. 2 miles to 5 miles -~~
~~b. Enumeration by Annually Dunng grazing seasort using referenced information from county agncultural agents or other reliable sources.~~
a Control (background) locations are denoted by a "C"in this column. All other locations are indicators, b
Gerald Peterson Dairy went out of business on November 1,1994, and as of December 31,1994, no replacement dairy has been found.
g m e e m m m m m m EM
M M TABLE 5.0-2 (contmued)
QUAD CITIES STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM. SAMPLE COLLECTION AND ANALYSES Location Collection Type of Frequency Sample Media Code Site Frequency Analysis of Analyss Remarks
~~10. land Use Census (continued)~~
Milch Animals c. At dairies hsted in Item 5. -
c Inquire as to Annually During grazing season.
feeding practku:
~~1. Pastureonly.~~
~~2. Feed and chop only.~~
3. Pasture and feed:if both, ask farmer to estimate fraction of a food from pasture-N 25 %, 25-50 %, 50-75 %
or 75%.
Nearest In all16 sectors up to 5 miles Annually Residence Census l
l
E N
~
E TABLE 5.0-3 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY
~~SUMMARY~~
Name of Facility Ouad Cities Nuclear Power Station Docket No. 50-254.50-265 locationof Facility RockIsland Illinois Reportmg Period 1st Ouarter IW4 (County, State)
Sample Type and Indicator Incation with Highest Control Number of Type Number of locations Ouarterly Mean locations Non-routine (Unats) Analyses LLD Mean a Mean Mean a Resula Range location Range Range Air Particulates Gmss Beta 78 0.01 0.026 (78/78) Q.05, Saddle Club 0.027 (78/78) None 0 (pCi/m3) (0.011-0.054) Dairy Farm (0.015-0.053) 1.8 mi @ 175*
Gamma Spec. 6 0.01 <LLD -
None O Airborne Iodine I-131 36 0.10 <LLD - -
None 0 (pCi/m3)
A W Gamma Background Gamma Dose 100 3 13.5 (84/84) Q-211-1 16 6 (2/2) 13.9 (16/16) 0 (TLDs)(mR/Qtr.) (12.2-16.6) 5.0 mi @ 220* (11.4-15.7)
Milk I-131 12 5 <LLD - -
<LLD 0 (pCi/L)
Cooling Water Gmss Beta 26 5 3.5 (13/13) Q-21, Intake Canal 0 3.8 (13/13) 3.8 (13/13)
(pCi/L) (1.9-5.0) at Station (2.7-4.6)) (2.7-4.6)
Public Water Gamma Spec- 6 (pCi/L)
Cs-134 10 <LLD <LLD 0
Cs-137 10 <LLD <LLD 0
Other Gammas 20 <LLD <LLD 0
~~Mean and range based on detectable measurements only. Fractions indicated in parentheses.~~
~~TABLE 5.0-4 RADIOLOGICAL ENVIRONMENTAL MONTTORING PROGRAM QUARTERLY~~
~~SUMMARY~~
Name of Facility Ouad Cities Nuc1 car Power Statim Docket No. 50-254.50-265 location of Facility Rock Island. Ilhnen Reporting Pened 2nd Ouarter IW4 (County, State)
Sample Type and Indicator location with Highest Control Number of Type Number of locations Ouarterly Mean locations Non-routine (Units) Analyses LLD Mean 8 Mean Mean a Results Range location Range Range Air Particulates Gross Beta 78 0.01 0.017 (78/78) gog b,Onsite No.1, 0.017 (13/13) None 0 (pCi/m3) (0.010-0.024) 0.5 mi @ p (0.011-0.023)
Gamma Spec. 6 0.01 <LLD .
None O Airborne Iodine I-131 42 0.10 <LLD - -
None 0 3
(pCi/m )
Gamma Background Gamma Dose 100 3 14.5 (84/84) Q-211, 17.4 (2/2) 14.3 (16/16) 0
$ (TLDs)(mR/Qtr.) (12.4-17.5) 5 0 mi @ 220' (11.3-16.6)
Milk I-131 27 5.0/0.Sc <LLD - -
<LLD 0 (pCi/L)
Cooling Water Cross Beta 26 5 10.1(13/13) Q22, Dishcarge 10.1 (13/13) 4.3 (13/13) 1 (pCi/L) (3.6-29.4) Canal at Station (3.6-29.4) (3.2-5.9)
Public Water Gamma Spec. 6 (pCi/L)
Cs-134 10 <LLD - -
<LLD 0 Cs-137 10 <LLD - -
<LLD 0 Other Gammas 20 <LLD - -
<LLD 0 Fish Gamma Spec. 17 (pCi/g wet)
Cs-134 0.1 <LLD - -
None O Cs-137 0.1 <LLD - -
None 0 Other Gammas 0.2 <LLD - -
None 0
~~Mean and range based on detectable measurements only. Fractions indicated in parentheses.~~
b 3 Locations Q-01, QO2, Q-05 and Q46 had identical means of 0.017pCi/m . Only Q41 is detailed in this summary.
C November - April LLD=5.0 ; May - October LLD20 5.
g M M M E
m m M M M M TABLE 5.0-5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY
~~SUMMARY~~
Name of Facility Ouad citia Nuclear Power Station Docket No. % 254.50-265 Locationof Facility Rock kland Illinois Reporting Period 3rd Ouarter 1W1 (County, State)
Sample Type and Indicator location with Highest Control Number of Type Number of locations Ouarteriv Mean locations Non-routine (Units) Analyses LLD 8 Mean Mean Mean a Results Range Location Range Range Air Particulates Gross Deta 78 0.01 0.021 (78/78) Q-01, Onsite No.1, 0.022 (13/13) None 0 (pCi/m3) (0.013-0.039) 03 mi @ 7' (0.01M037)
Gamma Spec. 6 0.01 <LLD - -
None 0 AirborneIodine I-131 36 0.10 <LLD - -
None 0 (pCi/m3) b
Gamma Background Gamma Dose 100 3 15.0 (84/84) Q-211-1, 18.6 (2/2) 14.8 (16/16) 0 (TLDs) (mR/Qtr.) (13.1-18.6) 5.0 mi@ 223' (11.6-17.4)
Milk I-131 38 0.5 <LLD - -
<LLD 0 (pCi/L)
Coolmg Water Gross Deta 26 5 4 3 (13/13) Q-21, Intake Canal 4 3 (13/13) 4 3 (13/13) 0 (pCi/L) (3.4-4.9) at Station (3.4-5.4) (3.4-5.4)
Q-22, Discharge Canal 4 3 (13/13) at Station (3.4-4.9)
Public Water Gamma Spec. 6 (pCi/L)
Cs-134 10 <LLD - -
<LLD 0 Cs-137 10 <LLD - -
<LLD 0 Other Gammas 20 <LLD <LLD 0
~~Mean ind range based on detectable measurements only. Fractions indicated in parentheses.~~
~~TABLE 5.0-6 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY~~
~~SUMMARY~~
Name of Facility _ Quad Cities Nuclear Power Station Docket No. %254. 50-265 Location of Faality Rock hiand. Imnnis Reportmg Period 4th Ouarter 1W4 (County, State)
Sample Type and Indicator Location with Highest Control Number of Type Number of Ircations Ouarterly Mean Locations Non-routine (Umts) Analyses LLD Mean a Mean Mean a Results Range locat a Range Range Air Particulates Cross Beta 78 0.01 0.026 (78/78) qc4c, Nitrin 0.027(13/13) None 0 (pCi/m3) (0.016-0.0%) 13 mi @ 40* (0.018 4 052)
Gamma Spec. 6 0.01 <LLD - -
None O Airborne Iodine I-131 42 0.10 <LLD - -
None 0 (pCi/m3)
Gamma Background Gamma Dose 99 3 14.7 (83/83) Q214-2 20.1 (1/1) 15.1 (16/16) 0 (TLDs) (mR/Qtr.) (13.0-20.1) 4.8 mi@ 210* (12.3-17.1)
$ Muk I-131 17 5.0/0.5b <tLD - -
<LLD 0 (pCi/L)
Coolmg Water Gross Beta 25 5 4 3 (13/13) Q-22. Dische ge Canal 0 43 (13/13) 3.4 (13/13)
(pCi/L) (3.0-6.4) at Station (3.044) (2.4-5.0)
Pubhc Water Gamma Spec. 6 (pCi/L)
Cs-134 10 <LLD - -
<LLD 0 Cs-137 10 <LLD - -
<LLD 0 Other Gammas 20 <LLD - - <LLD 0 Fish Gamma Spec. 13 (pCi/g wet)
Cs-1M 0.1 <LLD - -
None O Cs-137 0.1 <LLD - -
None 0 Other Gammas 0.2 < LID - -
None o i
~~Mean and range based on detectable measurements only. Fractions indicated in parentheses.~~
b November- April LLD=5.0; May - Octotober LLD=03.
C 3 locations Q04, Q45, and Q-Oh had identical means of 0.027 pCi/m . Only Q-04 is detailed in this summary, g; e m m -
M M M EE
TABLE 5.1-1 Cosmormealth Edison Conapany Dates 3-MAR-95 Enytroneental Site Report for bad Citleg Pagel 1 Gamma Radiation Measured in mR by TLDs Site Miles Degrees Description Quarter 1 Quarter 2 Quarter 3 Quarter 4 1994 1994 1994 1994 Air Samotore (2 TLDs per location) 0-01 0.3 7 A 'R SAMPLE STATION - DNSITE 33.7 34.4 15.5 13.6 0-02 0.4 70 A 'R SAMPLE STAfl0N - ONSITE 33.9 13.3 14.2 14.2 0-03 0.6 177 A R SAMPLE STATION - ONSITE 13.0 13.1 13.7 13.7 Mean 1 S.D. 13.5 1 0.5 13.8 1 0.7 14.5 1 0.9 13.8 1 0.3 Annual Mean and S.D. 13.9 1 0.7 Air Samoters (2 TLSs per location) 0-04 1.5 40 AIR SAMPLE STATION - NITRIN 82.5 12.4 13.1 13.2 0-05 1.3 160 AIR SAMPLE STATION -- SA00LE CLU8 13.6 14.2 14.5 15.0 0-06 1.8 340 AIR SAMPLE STAT!DN - HrWSEN'S 14.3 15.2 15.7 15.8 Mean i S.D. 13.4 1 0.9 13.9 1 1.4 14.4 1 1.3 14.7 1 3.4 Annual Mean and S.D. 14.1 1 1.2 CONTROL LOCATIONS (2 TLDs per location) 0-07 9.0 40 AIR SAMPLE STATIN - CLINTON 13.0 13.5 13.4 14.1 0-08 7.0 70 A:.R SAMPLE STATION - SIKKEMA'S 14.3 14.8 15.3 15.3 0-09 13.0 110 Al R SAMPLE STATION - ERIE 18.9 13.8 14.4 14.7 0-10 10.0 130 A: R SAMPLE STAT:DN - HILLSOALE 14.7 14.7 15.4 16.2 I 0-11 0-12 0-13a 0-14 0-15 0-16' 8.0 13.0 4.8 11.0 13.0 6.0 170 210 220 270 300 330 A R SAMPLE STAT' ON - PORT BYRON A 'R SAMPLE STAT DN - BETTENDORF A R SAMPLE STAT, 0N - PRINCET0h AIR SArFLE STAT 'ON - SCOTT COLNTY AIR SAMPLE STAT' ON - DEWITT AIR SAMPLE STATION - LON MOOR 15.7 15.5 13.2 32.9 33.4 13.3 16.6 16.5 14.1 13.4 33.3 13.5
$7.4 16.8 14.7 13.7 13.8 13.6 17.1 16.9 14.6 14.0 12.3 14.3 Mean 1 W.D. 13.8 1 1.3 14.2 1 3.6 14.6 1 1.7 14.9 1 1.5 Annual Mean and S.D. 14.4 1 1.5 Inner Ring t100 Series)
I 101-1 101-2 102-1 102-2 0.7 0.7 1.7 1.7 21 El 4
4 RIVER ROAO PEAR E.O. LUECK MAILBOX RIVER ROAD NEAR H. NOLM M4!LDOX 222 AVE N. 12TH PQ.E 222 AVE N. 7TH POLE 12.8 12.8 14.3 13.0 13.1 13.4 15.4 13.6 13.6 15.0 16.3 13.8 14.2 14.3 15.9 14.3 1034 1.2 SS N. OF 206 AVE N. ON RT 84 11TH POLE 12.3 13.2 13.6 13.7
" Alt Sampler Indicator Locations Average of 103-1 and 103-2 1
l i
1 I
47
4 0
o TADLE 5.1-1 (continued)
I Dat e e Site 3-nAR-95 Environnent at Site Report for Quad Clties Page: 2 I
Miles De9rees Description Quarter 1 Quarter 2 Duarter 3 Quarter 4 1994 1994 1994 1994 104-1 1.1 60 N. OF 206 AVE N. ON RT S4 97H POLE 13.3 104-2 0.9 77 13.8 13.6 13.5 104-3 N. OF 206 AVE N. ON RT B4 2ND POLE 12.7 13.4 e 13.9 14.1 0.6 77 206 AVE N. 13.4 15.4 14.6 14.4 105 b 0.7 91 N. OF 192 AVE N. ON RT 84 18TH POLE 106-1 0.7 109 12.2 14.1 13.4 13.9 106-2 0.7 N. OF 192 AVE N. ON RT 84 ISTH POLE 13.0 13.3 13.5 14.1 189 N. OF 192 AVE N. ON RT S4 137H POLE 12.8 13.3 14.4 107-l 0.7 128 14.3 107-2 0.7 N. OF 192 AVE N. ON RT 84 10TH POLE 12.4 13.2 13.5 16.4 137 N. OF 192 AVE N. ON RT 84 7TH POLE 12.7 13.3 13.5 107-3 0.7 146 14.0 N. OF 192 AVE. N. ON RT. 84 4TH POLE 12.2 13.0 13.1 13.3
!88 4 09-1 8:3 til176 0.9 Eas ih ave. N. LEri Or NET T0wER.
7 POLES WEST CF MET TOWER ON 3 92 AVE N.
II:t 12.9 15:1 13.6
!!:1 14.0 18:8 l09-2 0.9 176 RIVER RD. 14.2 til-l 2.6 230 12.4 13.3 13.9 13.7 111-2 2.6 230 SOUTH ACROSS TRACKS TO IST POLE ON RIGHT 13.9 15.5 15.7 16.0 112-1 SOUTH .5 MILE ON LEFT ACROSS FROM BARN 12.9 14.1 14.0 14.4 2.4 246 SOUTH .4 MILE ON RIGHT NEAR WHITE HOUSE 12.9
!!2-2 2.4 246 .3.3 13.4 e 14.7 ACFOSS FROM HOUSE AND HOUSE TRAILER 13.1 ,4.8 15.6 14.3 113-1 2.5 264 FIRST ROAD SOUTH OF PRIDGE ON CORNER 113-2 2.5 264 12.5 : 3.1 13.9 14.2 SOUTH ON RT 67 .7 MILE LEFT OF BRIDGE 12.6 13.2 13.3 13.7 114-1 2.6 286 SOUTH ON RT 67 .4 MILE ON LEFT 12.2 114-2 2.4 286 13.0 13.6 13.6 135-8 .2 MILES S. OF FOLLETTS ON RT 67 RISHT 14.2 14.7 15.1 16.0 4 2.3 310 BACK CORNER OF FOLLETTS PARK ON LEFT 12.6 12.9 115-2 2.3 310 14.0 13.8 e 116-1 RIGHT PAST SHAFFTON QUARRY 2ND POLE Od R 14.1 15.2 16.3 16.1 2.2 339 RIGHT ON RT 67 .5 MILE ON RIGHT 13.5 116-2 2.2 339 CONTINUE ON RT 67 .5 MILE 14.2 15.5 14.7 D. PETERS FRM 14.4 14.5 15.3 15.2 M*8a t S.D. 13.0 1 0.6 13.8 1 0.8 14.2 1 0.9 14.5 1 0.9 Annual Mean and S.D.
13.9 11.0 Ikler Ring (200 Series!
201-1 4.0 356 NEAR R. PRUETT FARM 15.9 201-2 4.0 356 15.7 15.9 15.5 ""
DN POLE ACROSS FROM ROBERT NISSEN FARM 14.6 15.5 e 85.3 15.3 202-1 4.4 17 HAZEL LAKE ROAD W AR HAZEL LAKE SIGN 12.9 202-2 9.4 17 17TH AVE. & 97H ST. COMANCHE, IOWA 19.0 13.3 13.9 203-1 le.9 13.1 13.3 13.9 5.5 34 IITH AVE E IST ST. COMANCHE. !DinA 13.5 14.4 14.3 l
203-2 5.5 34 MEREDOSIA & BUNKER HILL RD. 15.5 16.3 14.9 !
204-1 4.5 63 17.4 16.5 204-2 NEREDOSI A .8 MILE S. OF BUNKER HILL RD. 15.0 16.6 16.9 17.1 i
4.5 61 ACROSS FROM F. NICKES' RESIDENCE 16.2 a 205-1 4.5 83 THOME ROAD 17.1 16.3 16.8 205-2 4.5 83 14.3 15.7 16.3 15.3 l 20*,-4 CORNER OF GAULRAPP h RJLLER RD. 13.7 e 13.9 14.3 14.3 4.5 83 14.8 15.5 206-1 4.8 16.6 16.1 113 MEREDOSIA RD. NEAR RON RUSS FARM 13.0 13.9 14.7 14.6 i
206-2 4.8 113 STROPES RD. 13.2 l 207-1 4.3 133 D. PETREN FARM 14.5 14.2 14.2 207-2 4.3 133 13.4 15.5 16.0 16.6 1
207-4 CORNER 150 AVE. N. 6 256 ST. N. 12.9 14.0 14.6 15.0 l 4.8 179 12.8 14.3 1 208-1 4.4 158 250 ST. N. I COUNTY S RD. I 14.8 14.6 l 208-2 4.4 158 13.6 14.7 16.4 15.4 209-1 .6 MI . S. OF 203-1 CN RIGHT FARM DRIVE. 14.4 16.0 16.3 16.5 4.3 179 l .3 MI . ON 228 ST. N. NEAR T. DAVIS FARM 13.2 14.9 209-2 4.8 179 15.7 15.1 SHANROCK INN AREA 13.4 14.3 14.3 209-4 4.a 179 14.2 13.9 14.6 15 5 15.2
..... o m 0,., ._ ,,,.,
I!
I' I
48 5
l TABLE 5.1-1 (continued)
Dates 3-MAR-95 Environmental Site Report for Quad Cities Pages 3 Site Mlles Degress Descrtotton Quarter 1 Quarter 2 Quarter 3 Querter 4 1994 1994 1994 1994 210-1 4.4 210 PRINCETON CITY Pt.RK ON POLE NEAR WTR TWR 13.5 14.3 15.3 16.6 210-2 4.4 210 EST OF STANDARD STATION .7 MILE ON LEFT 15.8 17.3 87.7 17.2 210-4 4.4 210 14.6 15.0 15.8 15.7 211c 5.0 223 EST .4 MILE ON LEFT AT ROY HOLST FtWI 16.6 17.4 18.6 18.3 212-1 4.3 242 ACROSS FROM A-FRAME HOUSE 14.3 16.4 17.3 16.6 212-2 4.0 242 F-33 2 MILES ON RIGHT CCHNER 13.2 13.7 15.1 14.6 213-l 4.7 265 N ON GRAVEL ROAD .5 MILE TO H. KUNDE 12.2 13.9 14.4 14.9 213-2 4.7 265 NORTH .7 MILE ON LEFT BEFOM HAZEL LA6N 12.0 12.9 13.6 13.7 214-1 4.8 310 WEST ON Z-36 .5 MILE CN RIGHT CORNER 15.2 16.0 e 17.3 16.9 214-2 4.8 310 SOUTH .9 MILES ON RIGHT NEAR WHITE HOUSE 14.3 16.2 17.1 20.1 215-t 4.8 316 WEST 1.4 MILES ON LEFT CORNER 14.5 16.1 16.5 17.0 215-2 4.8 316 2ND GRAVEL ROAD AFTER TURNING ON TO 2-36 15.8 17.5 17.4 17.7 I 216-1 216-2 4.5 4.5 Mean i S.D.
333 Annual Mean and S.D.
LYLE BOYSEN FARM 333 ACROSS FROM DON NISSEN FARM 14.5 15.1 14.1 1 1.2 15.6 16.4 15.2 1 1.3 16.1 16.7 15.8 1 1.3 16.0 17.4 15.0 1 1.4 15.2 1 1.5 SPECIAL INTEPEST LOCAT'ONS (1 TLD per locations l 0301-1 0.0 0 PUBLIC OBSERVATION TOWER 29.1 34.3 35.7 16.5 1 0302-1 0.0 0 V SITORS r*NTER 21.9 32.8 32.3 22.6
! 0302-2 0.0 0 F RE TRA't: 40 TOWER 12.6 13.9 14.2 13.2 0302-3 0.0 0 S"MULATL JILDING 17.1 20.1 20.4 14.5 0303-1 0.0 0 TRAINING BUILDING 14.0 e 15.8 17.1 12.3 G305-1 0.0 0 WAREHOUSES ON UPPER ACCESS ROAD 17.0 14.5 15.1 14.0 0305-2 0.0 0 WAMHOUSES ON UFPER ACCESS ROAD 22.6 21.2 23.1 20.1 G305-3 0.0 0 WAREHOUSES ON UPPER ACCESS ROAD 19.5 15.6 18.3 13.5 Mean g S.D.
l I Annual Mean and S.D.
SPECIAL INTEREST LOCATIONS (1 TL.D per locations 19.2 1 5.3 21.0 g 8.2 22.1 1 8.1 15.8 1 3.7 19.5 1 6.7 l
307-8 0.3 140 RESTRICTED AREA FENCE-NORTN OF DAW BLDG - - -
29.3 307-2 0.3 140 RESTRICTED AREA FENCE- EAST OF DAW BLDG - - -
145.4 307-3 0.3 145 RESTRICTED AREA FENCE-SOUTH OF DAW E4.DG - - -
329.4 i 307-4 0.3 145 RESTRICTTD AREA FENCE- WEST OF DAW BLGD - - -
88.0 307-5 0.3 142 RESTRICTED AREA FENCE- S.E. OF DAW BLD8 - - -
225.0 1
310-1 0.3 180 RESTRICTED AREA FENCE- WEST OF DAW BLOG - - =
12.7 Mean + S.D. 148.3 goes. I l
Annual Mean and S.D. 148.3 gasse j I COMMENTS *a" Indicates lost desteeter. A portion of the Dose was estimated.
'O' Indicates edited dostseter. The ortgtnal Dose was replaced with an estimated value.
C Average of 211-1 and 211-2 i
l 1
1
! l 1
h l
I 49 l
~~. -_..a _. --. . . . ...~~
A . . . . . ,
i 1
I l
i g
i l
s l
i 1
4 4
4 i i 1 I
i
~~APPENDIX II METEOROLOGICAL DATA I~~
I I
50 :
1 i
l I QUAD CITZES NUCLEAR POWER STATION PERIOD OF RECORO: JANUARY-MARCH 1994 l STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 296-33 FT) _
, WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND N O 1 0 0 0 0 1 NNE O O O O O O O j NE O O O O O O O ENE O O 1 0 0 0 1 E O O O O O O O l
-1 ESE O O O O O O O 1; i SE O O O O O O O 1
SSE O O O 3 0 0 3 S O O O O O O O SSW O O 2 0 0 0 2 l
SW 0 0 3 3 0 0 6 WSW 0 0 0 1 0 0 1 W O O O O O O O WNW 0 0 0 4 0 0 4 NW 0 0 0 1 2 2 5 NNW 0 0 1 0 0 0 1 lI VARIABLE O O O O O O O TOTAL 0 1 7 12 2 2 24 ours 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 51
E
=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JANUARY-MARCH 1994 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 296-33 FT) g WINDS MEASURED AT 296 FEET g WIND SPEED (in mph)
WIND DIRECTION O 9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O O O O O O O NNE O O O O O O O NE O 1 1 0 0 0 2 ENE O O 2 0 0 0 2 E O O O O O O O ESE O O O O O O O SE O O O O 3 0 3 SSE O O 1 1 0 0 2 S O O 1 0 0 0 1 SSW 0 0 0 0 0 0 0 SW 0 0 3 1 0 0 4 WSW 0 0 5 3 0 0 8 W 0 0 4 3 2 0 9 WNW 0 1 2 2 8 1 14 NW 0 2 5 5 6 3 21 NNW 0 7 6 1 0 0 14 VARIABLE O O O O O O O TOTAL 0 11 30 16 19 4 80 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missin9 stability measurements in all stability classes: 3 I
52 I
=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JANUARY-MARCH 1994 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET u WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL
{ _________ _____ _ _ _ . - _ _____ _____ _____ _____ _____
N O 1 6 1 0 0 8 NNE O 1 4 1 0 0 6 NE O 2 3 2 0 0 7 ENE O O 2 0 0 0 2
{ E O O 3 0 0 0 3 ESE O O 2 0 1 0 3 SE O 1 2 2 1 4 10 SSE O 1 6 2 1 0 10 S O O 2 0 0 0 2
{ SSW 0 0 0 1 0 0 1 SW 0 1 5 3 0 0 9 WSW 0 5 5 6 1 0 17 W 0 1 9 16 12 1 39 WNW 0 0 8 7 7 2 24 j
{ NW 1 3 8 3 1 1 17 NNW 0 3 8 4 0 0 15
[ VARIABLE O O O O O O O
{ TOTAL 1 19 73 48 24 8 173 Houro of calm in this stability class: 0
[-Hoursofmissingwindmeasurementsinthisstabilityclass: 0 Hours of missing stability measurements in all stability classes: 3
[ 53 i
j 1
E, a i QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JANUARY-MARCH 1994 STABILITY CLASS - NEUTRAL (DIFF TEMP 296-33 FT) g WINDS MEASURED AT 296 FEET 3 WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N 2 4 19 15 0 0 40 NNE 1 10 12 19 0 0 42 NE 2 2 7 27 8 2 48 ENE O 9 20 28 12 16 85 E O 4 18 18 12 9 61 ESE 1 5 17 12 7 0 42 SE O 4 25 19 8 2 58 SSE O 1 19 10 5 0 35 S O 3 1 3 1 0 8 SSW 1 2 6 8 2 0 19 SW 1 6 15 7 1 0 30 WSW 1 10 17 19 3 0 50 W O 13 18 52 17 11 111 WNW O 7 55 80 65 16 223 NW O 9 39 54 20 1 123 NNW 3 12 26 26 3 0 70 VARIABLE O O O O O O O TOTAL 12 101 314 397 164 57 1045 I
Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 3 54
l QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JANUARY-MARCH 1994 l
STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET l
l WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 2 11 12 0 0 25 l
10 NNE 2 3 1 0 0 16 1 NE 1 3 7 3 0 0 14 l
ENE 1 2 12 7 0 0 22 l E O 7 8 10 0 0 25 ESE 1 7 6 12 16 0 ^2 l SE O 3 5 14 2 1 25 SSE 1 5 3 11 4 1 25 S O 3 5 12 10 12 42 SSW 0 4 8 13 22 5 52 SW 0 4 26 7 1 0 38 WSW 0 2 8 31 5 1 47 W 0 4 20 19 10 2 55 WNW 0 5 27 27 20 0 79 NW 1 2 25 18 1 0 47 NNW O 2 11 19 0 0 32 VARIABLE O O O O O O O I TOTAL 7 58 192 216 91 22 586 I Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 3 I
55
I El us i 1
QUAD CITIES NUCLEAR POWER STATION I PERIOD OF RECORD: JANUARY-MARCH 1994 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph) E WIND E DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL

~~----- ----- ----- ----- ----- ----- ----- )~~

N 1 0 1 0 0 0 2 ;
NNE 2 2 1 0 0 0 5 i
NE 1 0 2 0 0 0 3 ENE O 1 3 0 0 0 4 E 1 1 5 0 0 0 7 ESE O 7 1 1 0 0 9 SE 1 3 9 10 1 0 24 SSE 1 1 0 7 1 2 12 S 1 1 4 9 4 1 20 SSW O 3 5 19 12 0 39 SW 0 2 6 0 0 0 8 WSW 0 0 3 5 0 0 8 W 0 0 4 7 0 0 11 WNW 0 0 3 0 0 0 3 NW 0 2 4 7 0 0 13 ,
NNW 3 1 O O O O 4 VARIABLE O O O O O O O TOTAL 11 24 51 65 18 3 172 -
Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability cless: 0 Houre of missing stability measurements in all stability classes: 3 56 l=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JANUARY-MARCH 1994 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
I WIND DIRECTION O.9-3 4-7 8-12 13-18 19-24
> 24 TOTAL N O 1 0 0 0 0 1 NNE O O 2 0 0 0 2 NE O 1 0 0 0 0 1 ENE O 1 0 0 0 0 1 E O 6 1 0 0 0 7 ESE O 3 3 1 0 0 7 SE 2 3 5 2 0 0 12 SSE O O 3 5 0 0 8 S O O O 3 0 0 3 SSW 1 0 1 6 4 0 12 SW 0 1 4 0 0 0 5 WSW 1 0 3 0 0 0 4 W 0 1 5 3 0 0 9 WNW 0 0 1 0 0 0 1 NW 0 0 0 0 0 0 0 NNW 1 0 0 0 0 0 1 VARIABLE O O O O O O O TOTAL 5 17 28 20 4 0 74 hours8.564815e-4 days <br />0.0206 hours <br />1.223545e-4 weeks <br />2.8157e-5 months <br /> of calm in this stability class: 0 Houro of missing wind measurements in this stability class: 0 3
fours of missing stability measurements in all stability classes:
57
E QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 296-33 FT) a WINDS MEASURED AT 296 FEET g WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 1 4 7 1 0 13 NNE O 3 6 2 ? O 13 NE O 1 3 5 1 0 10 ENE O O 4 0 0 0 4 E O O 1 0 0 0 1 ESE O O O O O O O SE O O 1 3 1 0 5 SF 0 0 3 2 4 0 9
- 0 0 0 3 4 2 9 SSW O O 6 19 4 0 29 SW 0 0 3 1 0 0 4 WSW 0 0 2 2 0 0 4 W 0 0 5 0 0 0 5 WNW 0 2 9 12 3 0 26 I NW 0 0 6 11 0 0 17 I'
NNW 0 1 4 1 0 0 6 VARIABLE O O O O O O O TOTAL 0 8 57 68 20 2 155 Hours of calm in this stability class: 0 ;
Hours of missing wind measurements in this stability class: 0 i Hours of missing stability measurements in all stability classes: 1 58
l l QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL l -----
I N O O 4 5 0 0 9 .
I NNE O 6 0 6 2 0 14 NE O 3 2 3 0 0 8
)
ENE O 1 3 0 1 0 5 l E O 1 2 2 0 0 5
}
ESE O 1 3 1 0 0 5 l
l SE O 4 3 5 0 0 12 i SSE O 1 2 2 0 0 5 S O 2 1 3 5 0 11 1 l
1 SSW 0 3 8 8 4 1 24 l SW O 3 4 4 0 0 11 WSW 0 1 4 2 1 0 3 W 0 2 6 0 2 0 10 WNW 0 1 10 6 7 2 26 NW 0 1 5 1 1 1 9 NNW 0 3 5 2 0 0 10 VARIABLE O O O O O O O TOTAL 0 33 62 50 23 4 172 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 stabilit y classes: 1 IHours of missing stability measurements in all I
59 I
E QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 -
STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET
[
m WIND SPEED (in mph)
WIND ,
DIRECTION G.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL I N O 1 4 6 0 0 11 NNE O 5 0 1 2 0 8 NE O 5 2 1 0 0 8 ENE 1 6 1 1 3 0 12 E O 1 2 4 0 1 8 ESE O 2 6 1 0 0 9 SE O 5 4 1 0 0 10 SSE O 2 4 2 0 0 8 S 0 6 1 1 3 0 11 SSW 0 3 4 5 6 3 21 SW 1 5 1 3 1 0 11 WSW 0 6 2 4 2 0 14 W 1 7 4 7 2 0 21 WNW 0 5 2 5 3 1 16 NW O 5 2 1 3 1 12 NNW 0 4 5 2 1 0 12 VARIABLE O O O t' O O O TOTAL 3 68 44 #5 26 6 192 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 1 I
60
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 l STABILITY CLASS - NEUTRAL (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION O.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 4 13 13 7 0 37 NNE 1 3 5 22 12 2 45 i
NE O 4 6 7 2 1 20 ENE 1 6 17 15 22 3 64 E 2 7 9 7 19 10 54 ESE 2 1 10 9 0 0 22 SE O 4 13 7 2 0 26 SSE 2 10 7 6 2 2 29 l S O 4 2 5 5 3 19 SSW 1 24 13 16 18 6 78 SW 0 29 9 15 1 4 58 WSW O 10 14 8 9 10 51 j W 1 10 9 10 22 14 66 i 2A WNW 2 3 10 11 9 6 41 l g.
( NW 4 4 9 13 11 5 46 NNW 1 5 12 13 1 0 32 VARIABLE O O O O O O O I TOTAL 17 128 158 177 142 66 688 I Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 1 61 I
l l
_ _ _ _ ________ _ . _ _ _ _ _ _ __ ______ -_ _ _____ ---------------u
E QUAD CfTIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 ,
STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 2 5 6 1 0 14 NNE 1 2 6 6 2 0 17 NE 1 1 12 13 0 0 27 ENE O 3 17 9 5 0 34 E 2 4 25 11 3 0 45 ESE O 2 3 17 4 0 26 SE 1 0 5 11 4 0 21 SSE 1 3 5 11 4 0 24 S 0 7 6 19 4 4 40 SSW 2 7 11 43 32 0 95 SW 1 6 12 23 6 3 51 WSW 2 5 6 21 2 1 37 W 0 6 10 19 10 9 54 WNW O 2 13 12 8 0 35 ,
NW 1 5 9 11 3 0 29 NNW 0 1 6 11 5 0 23 VARIABLE O O O O O O O TOTAL 12 56 151 243 93 17 572 I ,
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: 1 62 I
I OUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N 2 4 2 5 0 0 13 NNE 1 2 2 3 0 0 8 NE 3 3 4 1 0 0 11 ENE 2 6 3 0 I 0 12 1
E 2 7 10 1 0 0 20 ESE 3 1 4 7 1 0 16 SE 2 3 12 9 0 0 26 SSE 3 3 10 7 2 0 25 S 2 3 9 20 1 0 35 SSW 1 5 14 15 2 0 37 SW 2 3 5 10 0 0 20 WSW O O 12 4 0 0 16 W 0 2 10 5 0 0 17 WNW O 2 6 7 1 0 16 NW 0 1 7 6. 0 0 14 NNW 1 1 0 6 1 0 9 VARIABLE O O O O O O O TOTAL 24 41 113 199 8 0 295 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: 1 63
E
=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: APRIL-JUNE 1994 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N 2 1 1 0 0 0 4 NNE 1 0 1 0 0 0 2 NE O 3 3 0 0 0 6 ENE 1 3 1 0 0 0 5 E 1 5 0 1 0 0 7 ESE O 1 1 1 0 0 3 SE O 2 1 4 1 0 8 SSE O 1 5 4 1 0 11 S O O 5 5 0 0 10 SSW 1 1 9 9 0 0 20 SW 0 1 4 2 0 0 7 WSW 0 1 0 1 0 0 2 W 0 0 0 1 0 0 1 WNW 0 0 5 0 0 0 5 NW 1 1 4 6 0 0 12 NNW 0 1 1 1 0 0 3 VARIABLE O O O O O O O TOTAL 7 21 41 35 2 0 106 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: 1 I
64 E
=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JULY-SEPTEMBER 1994 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
I WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24
> 24 TOTAL N O O 5 0 0 0 5 NNE O O 2 1 0 0 3 NE O O 3 0 0 0 3 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 1 0 0 0 1 SSE O O 10 0 0 0 10 S 0 0 2 3 0 0 5 SSW 0 3 6 14 1 0 24
~
SW 0 1 1 0 0 0 2 i WSW 0 1 1 0 0 0 2 W 0 0 2 1 0 0 3 WNW 0 0 3 4 0 0 7
.- NW O O 6 2 0 0 8 l
~
NNW 0 0 7 2 0 0 9
~
VARIABLE O O O O O O O
~
TOTAL 0 5 49 27 1 0 82 h
t Hours of calm in this stability class: 0
[Hoursofmissingwindmeasurementsinthisstabilityclass: 0 Hours of missing stability measurements in all stability classes: 1 W
F - - - - - -- - - - -
C Cl QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JULY-SEPTEMBER 1994 I,
l STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND E DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL l) j j
N O 1 1 0 0 0 2 NNE O O O O O O O NE O 1 0 0 0 0 1 ENE O 2 0 1 0 0 3 E O 3 0 1 0 0 4 ESE O O O O O O O SE O O 3 0 0 0 3 SSE O 1 3 1 0 0 5 S 1 1 6 8 0 0 16 SSW 0 6 6 8 1 0 21 SW 0 1 12 4 1 0 18 WSW 0 4 1 1 0 0 6 W 0 3 7 7 0 0 17 I WNW 0 4 6 1 0 0 11 NW 0 4 9 6 1 0 20 NNW 1 1 7 5 0 0 14 VARIABLE O O O O O O O TOTAL 2 32 61 43 3 0 141 I
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: 1 66 E
=
I QUAD CIT!ES NUCLEAR POWER STATION PERIOD OF RECORD: JULY-SEPTEMBER 1994 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 1 3 0 0 0 4 NNE O O 1 0 0 0 1 NE O O O O O O O ENE O 1 0 1 0 0 2 E O 4 5 2 0 0 11 ESE O O O O O O O SE O O 5 0 0 0 5 SSE O O 3 0 0 0 3 S 0 3 8 8 1 0 20 SSW 0 6 13 6 3 0 28 SW O 6 7 5 0 0 18 WSW 0 6 3 3 0 0 12 W 1 5 6 8 1 0 21 WNW 0 4 5 5 0 0 14 NW 0 4 6 5 0 0 15 NNW 1 1 7 3 0 0 12 VARIABLE O O O O O O O TOTAL 2 41 72 46 5 0 166 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing st abilit y measurement s in all stability classes: 1 67 M
E o
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JULY-SEPTEMBER 1994 STABILITY CLASS - NEUTRAL (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph) g, WIND DIRECTION O.9-3 4-7 8-12 E
13-18 19-24 > 24 TOTAL N O 10 16 7 3 0 36 NNE 2 6 7 1 1 0 17 NE 1 5 3 1 1 0 11 ENE 3 10 7 2 0 0 22 E O 20 24 5 0 0 49 ESE 1 8 9 10 3 0 31 SE 3 11 12 11 7 0 44 SSE 2 24 23 13 1 0 63 S 3 8 16 11 4 0 42 SSW 2 11 14 19 9 1 56 SW 4 13 19 22 6 0 64 WSW 5 17 8 16 0 0 46 '
W 0 22 12 11 7 0 52 WNW 3 15 26 25 0 0 69 '
NW 2 12 31 11 2 0 58 NNW 3 8 18 12 0 0 41 VARIABLE O O O O O O O TOTAL 34 200 245 177 44 1 701 Hours of calm in this stability class: 0 I
Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 y
68 l
I
u
_ QUAD CITIES NUCLEAR POWER STATION
_ PERIOD OF RECORD: JULY-SEPTEMBER 1994
-~
STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET
- WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N 1 6 12 4 0 0 23 NNE 1 7 6 5 1 0 20 NE O 1 5 9 2 0 17 ENE 1 0 9 8 0 0 18 E 2 6 15 3 0 0 26 l
~
ESE 1 3 16 18 3 0 41 1
SE 1 3 13 16 2 0 35
- SSE O 2 21 13 1 0 37 S O 6 19 22 4 0 51
{ SSW 2 4 22 55 13 0 96 SW 0 3 19 37 3 0 62 WSW 3 6 18 11 3 0 41 W 0 5 10 14 3 0 32
~
WNW 1 0 12 27 3 0 43 NW 1 1 17 16 0 0 35 NNW 0 5 22 16 0 0 43 VARIABLE O O O O O O O
{ TOTAL 14 58 236 274 38 0 620 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: 1 69 ,
1
E QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: JULY-SEPTEMBER 1994 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N 1 2 13 8 0 0 24 NNE 1 5 8 1 0 0 15 NE 2 4 3 3 0 0 12 ENE 1 1 1 2 0 0 5 E 3 0 0 1 0 0 4 ESE 1 0 2 4 2 0 9 SE O 3 9 23 1 0 36 SSE O 1 23 23 1 0 48 S O 4 11 26 0 0 41 SSW 1 5 10 33 0 0 49 SW O 3 11 10 4 0 28 WSW 1 4 6 3 0 15 I
1 W 0 4 3 1 0 0 8 WNW 0 1 5 10 0 0 16 NW 0 1 8 15 0 0 24 NNW 0 0 3 5 0 0 8 VARIABLE O O O O O O O TOTAL 11 38 116 168 8 1 342 i
l Hours of calm in this stability class: 0 l Hours of missing wind measurements in this stability class: 0
[ Hours of missing stability measurements in all stability classes: 1 l
I 70
E QUAD CITIES NUCLEAR POWER STATION
{.-
PERIOD OF RECORD: JULY-SEPTEMBER 1994 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 296-33 FT) i WINDS MEASURED AT 296 FEET j i
WIND SPEED (in mph) l WIND {
DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL !

----- - --- ----- ----- ----- ----- ----- 1 N O 4 5 0 0 0 9 h~ NNE O 3 4 0 0 0 7 NE O 1 1 0 0 0 2 {

ENE O 3 1 0 0 0 4 E O 1 0 0 0 0 1 I
ESE 1 3 0 0 0 0 4
[ SE O O 1 7 0 0 8 SSE 1 4 8 11 0 0 24 S 2 4 11 9 0 0 26 SSW 1 6 8 10 0 0 25 SW 0 3 8 7 0 0 18
{ WSW 1 4 4 0 0 0 9 W O 2 3 0 0 0 5 WNW 0 2 0 0 0 0 2 NW 0 0 0 0 0 0 0
[
NNW 0 1 7 3 0 0 11 VARIABLE
{ O O O O O O O TOTAL 6 41 61 47 0 0 155 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: 1
( 71
E e
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph) g WIND DIRECTION 0.9-3 4-7 g
8-12 13-18 19-24 > 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 a i SE O O O O O O O SSE O O O 1 0 0 1 S 0 0 0 0 1 0 1 SSW 0 0 4 4 0 0 8 SW O O O O O O O WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 3 0 1 0 4 NW 0 0 0 1 0 0 1 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 7 6 2 0 15 Hours of calm in this stability class: 0 I i Hours of missing wind measurements in this stability class: 0 Hours of missin9 stability measuremerts in all stability classes: )
6 72 I.
OUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 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 3 0 1 0 4 SE O O 1 0 0 0 1 SSE O O 1 3 5 0 9 S O O O 4 0 0 4 SSW 0 0 3 3 0 0 6 t SW 0 0 0 0 0 0 0 WSW 0 0 1 0 0 0 1 W 0 0 1 2 5 0 8 WNW 1 0 2 2 2 0 7 NW 0 0 1 2 2 0 5 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O I TOTAL 1 0 13 16 15 0 45 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: 6 73 I
E
=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 296-33 FT) g WINDS MEASURED AT 296 FEET 3 WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 1 0 0 0 0 1 NNE O 3 1 0 0 0 4 NE O 3 1 0 0 0 4 '
ENE O 2 0 0 0 0 2 E O 1 4 4 1 0 10 ESE O 1 7 1 3 0 12 SE O O 2 0 0 0 2 SSE O O 4 3 3 0 10 S O O 3 3 0 0 6 SSW O O 3 1 0 0 4 SW 0 0 1 0 0 0 1 ,,
WSW 0 1 0 0 2 0 3 W 0 1 3 6 8 1 19 l
WNW O 1 2 6 2 0 11 NW 0 0 1 1 1 0 3 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 14 32 25 20 1 92 I
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: 6 l
l
=,
l
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - NEUTRAL (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL !
N O 10 22 9 1 0 42 NNE 2 8 10 6 6 1 33 NE 1 4 21 15 8 0 49 ENE 2 3 11 18 7 0 41 '
E 1 7 26 24 7 2 67 ESE 5 8 15 25 8 8 69 SE 3 13 12 13 1 0 42 SSE 1 9 9 11 10 4 44 S 2 6 11 15 19 7 60 SSW 5 6 20 19 16 7 73 SW 1 2 13 16 8 3 43 WSW 1 7 9 12 1 19 49 W 0 14 16 42 18 13 103 WNW 3 16 27 46 I NW 2 19 38 46 27 7
8 0
127 112 NNW 6 10 15 12 2 0 45 VARIABLE O O O O O O O I TOTAL 35 142 275 329 146 72 999 IHours of calm in this stability class: 0 Hours of missin9 wind measurements in this stability class: 47 HourO of missing stability measurements in all stability classes: 6 75 I
E
=
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 296-33 FT)
WINDS MEASURED AT 296 FEET WIND SPEED (in mph)
WIND l E
DIRECTION 0.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 3 4 0 0 0 7 NNE 1 4 2 6 0 0 13 NE 1 9 16 3 1 0 30 ENE 1 1 10 21 0 0 33 E O 2 22 15 1 0 40 ESE O 2 22 41 4 0 69 SE O 3 18 20 7 0 48 SSE O 3 8 33 4 6 54 S 1 0 7 25 22 4 59 SSW 0 2 6 44 39 9 100 SW 1 1 2 6 13 4 27 WSW 0 1 7 7 3 0 18 W 1 4 8 31 9 0 53 WNW 2 4 10 14 5 0 35 NW 0 3 5 17 3 0 28 NNW 0 0 6 10 1 0 17 i
! VARIABLE O O O O O O O TOTAL 8 42 153 293 112 23 631 Hours of calm in this stability class: 0 I
Hours of missin9 wind measurements in this stability class: 6 Hours of missing stability measurements in all stability classes: 6 76 l
l.
i l
QUAD CITIES NUCLEAR POWER STATION !
PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 296-33 FT)
!I WINDS MEASURED AT 296 FEET ,
WIND SPEED (in mph)
WIND DIRECTION O.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N O 2 2 4 0 0 8 NNE 1 1 3 3 0 0 8 NE O 2 5 10 0 0 17 ENE O 2 5 2 0 0 9 E 4 14 10 4 0 0 32 ESE O 1 9 14 4 0 28 SE O O 8 21 3 0 32 SSE O 2 8 20 2 0 32 S 1 0 5 15 1 0 22 SSW 1 2 6 23 0 0 32 SW 0 2 1 2 1 0 6 WSW 0 0 2 0 0 0 2 W 0 2 0 3 0 0 5 WNW 0 1 2 1 1 0 5 NW 0 1 3 5 0 0 9 NNW 1 0 3 5 0 0 9 VARIABLE O O O O O O O TOTAL 8 32 72 132 12 0 256 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 6 77
E e
QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD: OCTOBER-DECEMBER 1994 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 296-33 FT) E WINDS MEASURED AT 296 FEET E WIND SPEED (in mph)
WIND DIRECTION O.9-3 4-7 8-12 13-18 19-24 > 24 TOTAL N 2 0 1 0 0 0 3 NNE O 1 2 0 0 0 3 NE O 4 5 2 0 0 11 ENE O 3 3 0 0 0 6 E 1 0 1 1 0 0 3 ESE O O 1 10 0 0 11 SE O 3 4 4 2 0 13 SSE O O 4 1 0 0 5 S 0 0 2 13 0 0 15 SSW 0 1 5 8 0 0 14 SW O 2 6 0 0 0 8 WSW 0 2 2 0 0 0 4 W 0 1 1 0 0 0 2 WNW O O 1 0 0 0 1
{
NW 0 1 1 0 0 0 2 NNW 0 1 7 1 0 0 9 VARIABLE O O O O O O O TOTAL 3 19 46 40 2 0 110 I
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: 6 I'
78
L-E c
L b
E F
L APPENDIX III LISTING OF MISSED SAMPLES r
L
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[
[ 4
[ ,
[
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[
79 u...m.... . .
QUAD CITIES LISTING OF MISSED SAMPLES E Expected iE Collection Sample Type Location Date Reason TLD Q-303-1 03-05-94 Missing from location.
I AP Q-07 03-19-94 Missing from location.
l AP Q-07 08-19-94 Filter missing due to broken retaining ring spring.
TLD Q-112-1 09-03-94 Missing from location.
MILK Q-31 11-05-94 Gerald Peterson Dairy went out of business on 11-01-94.
I Sampling variances 1 Public Water Q-19 10-07-94 Compositor not operating due to facility maintenance; grab sample obtained.
I 1
Public Water Q-19 10-15-94 Compositor not operating due to facility maintenance; grab sample obtained.
i l
I
' 1 Sampling Variances are samples which have not been missed but indicate unusual sample ,
resu ts or factors which contribute to sample anomalies. '
t AP = Air Particulate (Filter) l 80
W 4 - -- . - m . ,_ --
o-m -- -e. - =- - -
4 i
e l
J l
l
! 1 i
APPENDIX IV l
l MILCH ANIMALS, NEAREST LIVESTOCK, AND )
l NEAREST RESIDENCES CENSUSES l i
i iI I
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i l
1 I
1 i
, I 81
I QUAD CITIES MILCH ANIMALS CENSUS,1994 A. There are five dairy farms within a 6.5 mile radius of Quad Cities Station.
B. Samoline Locations Q-18 Musal Dairy Farm 6.0 miles @ 240 Nurnber of cows - 90 I Diet consists of: 40% aasture 60% 2ay, silage, and supplement Q-26 Bill Stanley Dairy 3.5 miles @ 120 Number of cows - 24 Diet consists of: hay, grain, and supplement Q-31 Gerald Peterson Dairy Farm 5.0 miles @ 100 Number of cows - 24 Diet consists of: 35% pasture 50% corn and hay 15% protein supplement Julie DePauwa 6.3 miles @ 158' Number of cows - 100 Diet consists of: 10% pasture 90% choped and feed a Non-participating l
82
==
QUAD CITIES MILCH ANIMALS CENSUS,1994 I
I B. Sampling Locations (continued)
Carl Ottea 6.0 miles @ 100 Number of cows -No Data Available Diet consists of: No Data Available a Non-participating I ,.
j Census conducted by G. Kreuder on August 31,1994.
l I
I I
83
QUAD CITIES NEAREST LIVESTOCK CENSUS,1994 Nearest livestock of the Quad Cities Station within a 6.5 mile radius.
Sector Direction Distance A N None B NNE None
~
C NE None i D ENE 3.0 miles 1 E E 3.0 miles
~E F ESE 3.2 miles
,E G SE None H SSE 4.0 miles J S 1.5 miles K SSW None i
L SW 3.5 miles q
M WSW 3.5 miles 1 N W 4.5 miles 1
P WNW 3.5 miles Q NW 4.5 miles R NNW 2.3 miles Census conducted by G. Kreuder on August 31,1994.
84
E
=
QUAD CITIES NEAREST RESIDENCE CENSUS,1994 I
Nearest resident of the Quad Cities Station within a 6.5 mile radius.
Sector Direction Distance A N I
0.5 miles B NNE 0.8 miles C NE 1.3 miles D ENE 1.3 miles E E 2.3 miles F ESE 3.0 miles G SE 2.5 miles H SSE 1.0 miles J S 0.8 miles K SSW 3.0 miles L SW 3.0 miles '
M WSW 2.0 miles N W 2.3 miles ;
P WNW 2.3 miles Q NW 2.3 miles R NNW l.8 miles Census conducted by G. Kreuder on August 31,1994.
s 80 as
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E ,
I APPENDIX V l
l INTERLABORATORY COMPARISON PROGRAM RESULTS 5
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3 I
1 i i
i '
1 4
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I t
4 1
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, 86 i
~,-
Appendix A Interlaboratory Comparison Program Results Teledyne Brown Engineering Environmental Services, Midwest Laboratory (formerly Teledyne isotopes I and Hazelton Environmental Services) has participated in interlaboratory comparison (crosscheck) programs since the formulation of it's quality control program in December 1971. These programs are operated by agencies which supply environmental type samples (e.g., milk or water) containing concentrations of radionuclides know to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent check on the laboratory's analytical procedures and to alert it to any possible problems.
Participant laboratories measure the concentration 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 I controllimits indicate a need to check the instruments or procedures used.
I The results in Table A-1 were obtained through participation in the environmental sample crosscheck program for milk, water, air filters, and food samples during the current year. This program is conducted by the U.S. Environmental Protection Agency Intercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Laboratory, Las Vegas, Nevada.
Table A-2 lists results of the analyses on in-house " spiked" samples.
Table A-3 lists results of the in-house " blank" samples.
Table A-4 lists results of the in-house " duplicate" program.
Out-of-limit results are explained directly below the result.
I I
87
Tcble A 1. U.S. Environmental Protection Agency's crosscheck program, comparison of EPA and Teledyne Brown Engineering Environmental Services, Midwest Laboratory results for various sample media'.
Concentration in pCi/L6 Lab Sample Date EPA Result' Control TBEESML Results Code Type Collected Analysis 1s,N=1 Limits i 2 Sigma d STW-702 WATER Jan,1994 Sr-89 25.015.0 16.3 - 33.7 20.0 i 1.7;2.6 STW-702 WATER Jan,1994 Sr-90 15.015.0 6.3 - 23.7 14.0 1.0 ; 1.7 STW-703 WATER Jan,1994 Gr. Alpha 15.0 5.0 6.3 - 23.7 20.3 i 0.6;2.5 STW-703 WATER Jan,1994 Gr. Beta 62.0110.0 44.7 - 79.3 55.3 i 3.2;9.1 STW 704 WATER Feb,1994 I-131 119.0 i 12.0 98.2 - 139.8 110.0 i 2.7;11.3 STW-705 WATER Feb,1994 Ra-226 19.913.0 14.7 - 25.1 19.411.5;2.5 STW 705 WATER Feb,1994 Ra-228 14.7f 3.7 8.3 - 21.1 15.010.8;1.7 STW-705 WATER Feb,1994 Uranium 10.113.0 4.9- 15.3 9.710.4;1.0 STW-706 WATER Mar,1994 H-3 4936.0 494.0 4078.9 - 5793.1 4843.3 i 231.2;698.1 STW-707 WATER Mar,1994 Pu-239 27.612.8 22.7 - 32.5 28.210.9;3.0 STW-708 WATER Apr,1994 Gr. Alpha 86.0122.0 47.8 - 124.2 73.3 i 2.9; 9.4 STW-708 WATER Apr,1994 Ra-226 20.013.0 14.8 - 25.2 16.911.2;2.1 STW-708 WATER Apr,1994 Ra-228 20.115.0 11.4 - 28.8 19.7 i 0.7;2.1 STW-708 WATER Apr,1994 Uranium 25.013.0 19.8 - 30.2 25.1 i 0.1;2.5 STW-709 WATER Apr,1994 Co-60 20.015.0 11.3 - 28.7 20.3 i 0.6;3.0 STW-709 WATER Apr,1994 Cs-134 34.015.0 25.3 - 42.7 32.310.6;4.7 STW 709 WATER Apr,1994 Cs-137 29.015.0 20.3 - 37.7 31.3 i 0.6;4.5 STW-709 WATER Apr,1994 Gr. Beta 117.0 18.0 85.8 - 148.2 101.0 i 10.5;18.8 STW-709 WATER Apr,1994 Sr-89 20.0 i 5.0 11.3 - 28.7 15.0 i 1.7;2.3 STW-709 WATER Apr,1994 Sr-90 14.015.0 5.3 - 22.7 14.3 i 0.6;1.6 STW-710 WATER Jun,1994 Ba-133 98.0 i 10.0 80.7 - 115.3 87.310.6;12.6 STW-710 WATER Jun,1994 Co-60 50.015.0 41.3 - 58.7 48.7 i 3.2;7.7 STW-710 WATER Jun,1994 Cs-134 40.015.0 31.3 - 48.7 35.0 i 2.7;5.7 STW-710 WATER Jun,1994 Cs-137 49.015.0 40.3- 57.7 51.3 i 0.6; 7.4 88
E um Table A 1. U.S. Environmental Protection Agency's crosscheck program, comparison of EPA and Teledyne Brown Engineering Environmental Services, Midwest Laboratory results for various sample media *.
Concentration in pCi/L" Lab Sample Date Ccde Type Collected Analysis EPA Result' 1s, N=1 Control TBEESML Results g Limits i 2 Sigma d _ E STW-710 WATER Jun,1994 Ru-106 252.0 25.0 208.6 - 295.4 184.7 i 6.7;27.4 A Letter from the EPA was received with the report. It states,"The Radiation Quality Assurance Program has been experiencing problems with the Ruthenium-1% currently used in the Performance Evaluation (PE) Studies and in the Standards Distribution Program. If these problems can be satisfactorily resolved, this analyte will once again be placed into this PE Study. If the problems cannot be resolved, the Ruthenium-106 E 3
will be replaced. Formal written notice will be given to all participants in the Gamma in Water PE Study before the Ruthenium-106 is reintroduced or replaced. At that time, new calibration standards will be available to all participants in the Gamma in Water PE Study." Teledyne will continue to monitor this situation, but at this time, plans to take no additional action.
STW-710 WATER Jun,1994 Zn-65 134.0 1 13.0 111.4 - 156.6 135.3 1 2.3;19.6 STW-711 WATER Jun,1994 Ra-226 15.012.3 11.0 - 19.0 15.010.4;1.6 STW-711 WATER Jun,1994 Ra-228 15.4 i 3.9 8.6 - 22.2 14.8 i 0.3;1.5 STW-711 WATER Jun,1994 Uranium 52.6 i 5.3 43.4 - 61.8 45.7i 0.2;4.6 STW-712 WATER Jul,1994 Sr-89 30.0 i 5.0 21.3 - 38.7 26.011.7;3.1 STW-712 WATER Jul,1994 Sr-90 20.0 i 5.0 11.3 - 28.7 18.7 i 0.6;2.0 STW-713 WATER Jul,1994 Gr. Alpha 32.018.0 18.1 - 45.9 19.3 i l.2 ; 2.6 STW-713 WATER Jul,1994 Gr. Beta 10.015.0 1.3- 18.7 12.7 i 1.5;2.5 STW-714 WATER Aug,1994 H-3 9951.0 i 995.0 8224.7 - 11677.3 10186.7 i 66.6;1387.0 STAF-715 AIR FILTER Aug,1994 Cs-137 15.015.0 6.3 - 23.7 14.010.0;1.4 STAF 715 AIR FILTER Aug,1994 Gr. Alpha 35.0 i 9.0 19.4 - 50.6 29.311.2;3.2 STAF-715 AIR F1LTER Aug,1994 Gr. Beta 56.0110.0 38.7 - 73.3 56.010.0;5.6 STAF-715 AIR FILTER Aug,1994 Sr-90 20.015.0 11.3 - 28.7 18.0 i 1.0;2.1 STW-716 WATER Sep,1994 Ra-226 10.011.5 7.4 - 12.6 10.1 i 0.3;1.1 STW-716 WATER Sep,1994 Ra-228 10.212.6 'i 6 - 14.7 9.8 i 0.1 ; 1.0 STW-716 WATER Sep,1994 Uranium 35.0 i 3.0 29.8 - 40.2 31.9 i 1.8;3.7 STW-718 WATER Oct,1994 1-131 79.0 i 8.0 65.1 - 92.9 81.3 i 3.1; 8.7 89 l1
=
Table A-1. U.S. Environmental Protection Agency's crosscheck program, comparison of EPA and Teledyne Brown Engineering Environmental Services, Midwest Laboratory results for various sample media'.
Concentration in pCi/L' Lab Sample Date EPA Result' Control TBEESML Results Code Type Collected Analysis 1s, N=1 Limits i 2 Sigma d
Results obtained by Teledyne Brown Engineering Environmental Services Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Intercomparison and Calibration Section, Quality Assu;ance Branch, Environmental Monitoring and Support Laboratory, U.S. Environmental Protection Agency (EPA), Las Vegas, Neveda.
I
~~All results are in pCi/L, except for elemental potassium (K) data in milk, which are in mg/L; air filter samples, which are in pCi/ Filter; and food products, which are in mg/Kg.~~
~~USEPA results are presented as the known values and expected laboratory precision (1s,1 determination) and control limits as defined by the EPA.~~
d Unless otherwise indicated, the TBEESML results are given as the mean i 2 standard deviations for three determinations. The numbers after the semi-colon are the Total Propagated Uncertainty of the result.
I 90 !
l l
I
I Tr.ble A-2. In-house " spike" samples.
I Concentration in pCi/L' L-b Sample Date Accepted Known TBEESML Results Code Type Collected Analysis Rejected Activity Control Limits
2s, n=1' SPW-4821 WATER Jan,1994 Cc-144 A 2692.5 2158.2- 3226.8 2593.1 1 54.9;265.1 SPW-4822 WATER Jan,1994 Ce-144 A 1749.8 1397.7- 2101.9 1705.1 1 48.1;177.2 SPW-4823 WATER Jan,1994 Ce-144 A 49.0 25.7- 72.3 55.4 1 17.5;18.4 SPW-4825 WATER Jan,1994 Gr. Alpha A 41.7 33.7- 49.7 34.411.6;3.8 SPW-4825 WATER Jan,1994 Gr. Beta A 30.2 23.6- 36.8 33.6 1.2;3.6 SPW-4826 WATER Jan,1994 Gr. Alpha R 83.4 68.1- 98.7 66.812.1;7.0 A review of the raw data for the Alpha analysis revealed no errors in calculations or transcribing of data. The technician was observed performing this analysis; no discrepancies where noted. The technician's performance in the future will be monitored. It should be noted that TBEESML's results are within the EPA specified controllimits. No further action is planned.
SPW-4826 WATER Jan,1994 Gr. Beta A 60.4 47.8- 73.0 63.8 i l.5 ; 6.6 SPMI-4848 MILK Jan,1994 Cs-134 A 31.7 22.2- 41.2 27.215.7;6.3 SPMI-4848 MILK Jan,1994 Cs-137 A 34.8 22.4- 47.2 34.618.2;8.9 SPMI-4848 MILK Jan,1994 Sr-89 A 35.0 26.8- 43.2 28.2 i 3.8;4.7 SPMI-4848 MILK Jan,1994 Sr-90 A 40.7 32.3- 49.1 41.211.2;4,3 SPMI-4849 MILK Jan,1994 Sr-89 A 11.9 8.8- 15.0 9.511.6;1.9 SPMI-4849 MILK Jan,1994 Sr-90 A 20.1 16.0 - 24.2 19.4 i 0.8;2.1 SPMI-4862 MILK Jan,1994 Cs-134 A 338 0 267.5- 408.5 328.3 1 16.3;36.7 SPMI-4862 MILK Jan,1994 Cs-137 A 1114.4 899.4- 1329.4 1019.6 1 18.3;103.6 SPAP-4953 AIR FILTER Jan,1994 Gr. Beta A 4.2 3.3 - 5.1 4.8 i 0.1 ; 0.5 SPAP-4954 AIR FILTER Jan,1994 Cs-137 A 1.3 1.0- 1.6 1.4 0.1 ; 0.2 SPW-4955 WATER Jan,1994 H-3 A 17163.0 13700.3- 20625.7 17080.0 i 364.0;1746.4 SPW-4956 WATER Jan,1994 Co-60 A 1545.0 1232.2- 1857.8 1514.0 i 46.2;158.3 SPW-4956 WATER Jan,1994 Cs-134 A 479.0 380.8- 577.2 433.71 25.5;50.3 WATER Jan,1994 Cs-137 A 732.0 571.5- 892.5 742.7 i 45.9;87.3 I SPW-4956 SPCH-492 ClIARCOAL Feb,1994 I-131(g) A 1452.8 1148.6- 1757.0 1449.9 1 65.1;158.9 CANISTER SPW-4934 WATER Feb,1994 I-131 A 90.8 74.0- 107.6 76.4 i 1.4; 7.8 SPW-4934 WATER Feb,1994 I-131(g) A 90.8 69.9- 111.7 90.217.6;11.8 SPMI-4935 MILK Feb,1994 I-131 A 43.6 35.1- 52.1 40.411.0;4.2 SPMI-4935 MILK Feb,1994 I-131(g) A 43.6 31.3- 55.9 41.816.7;7.9 j
SPBS-5102 SEDIMENT Mar,1994 H-3 A 105.4 85.1- 125.7 97.211.0;9.8 SPW-5146 WATER Mar,1994 St-89 A 26.4 19.1- 33.7 25.513.9;4.7 SPW-5146 WATER Mar,1994 Sr-90 A 18.8 15.0- 22.6 16.2 i 1.1;2.0 SPW-646 WATER Apr,1994 H-3 A 9855.0 7841.5- 11168.5 9847.8 1 294.9;1028.0 ,
SPW-648 WATER Apr,1994 Co-60 A 22.6 13.4 - 31.8 21.616.6;6.9 1
91 1
J
E.
Table A 2. In-house " spike" samples.
Concentration in pCi/L' Lab Sample Date Accepted Known TBEESML Results Code Type Collected Analysis Rejected Activity Control Limits 6 2s, n=1' SPW-648 WATER Apr,1994 Cs-134 A 33.6 21.1- 46.1 33.3 i 8.5;9.1 SPW-648 WATER Apr,1994 Cs-137 A 36.3 22.2- 50.4 37.6 i 9.8;10.5 SPMI-650 MILK Apr,1994 Cs-134 A 50.6 38.1- 63.1 52.015.3;7.4 SPMI-650 MILK Apr,1994 Cs-137 A 54.5 38.7- 70.3 61.6 8.3;10.3 SPW-652 WATER Apr,1994 Gr. Alpha A 41.6 32.8- 50.4 44.811.2;4.6 SPW-652 WATER Apr,1994 Gr. Beta A 25.4 20.3- 30.5 24.111.0;2.6 SPAP-654 AIR FILTER Apr,1994 Cs-137 A 1.3 1.0 - 1.6 1.310.1;0.2 SPW-974 WATER May,1994 Fe-55 A 58.5 39.4- 77.6 56.7 i l2.0;13.3 SPF-1023 FISH May,1994 Cs-137 A 6.8 5.4 - 8.2 6.910.1;0.7 OELLO)
SPBS-1024 SEDIMENT May,1994 Cs-137 A 6.0 4.8 - 7.2 6.210.1;0.6 SPW-1850 WATER Jun,1994 1-131 A 51.8 42.0- 61.6 46.0 0.7 ; 4.7 SPW-1350 WATER Jun,1994 1-131(g) A 51.8 36.9- 66.7 50.918.3;9.7 SPMs-1851 MILK Jun,1994 I-131 A 51.8 41.4- 62.2 51.710.6;5.2 SPMI-1851 MILK Jun.1994 1-131(g) A 51.8 34.7 - 68.9 51.3 1 10.8;12.0 SPVE-1854 VEGETATIO Jun, '.?94 1-131(g) A 1.0 0.8 - 1.2 0.9 i 0.1 ; 0.1 N
(SAWDUST)
SPCil-185 CHARCOAL Jun,1994 1-131(g) A 1.8 1.4 - 2.2 1.910.1;0.2 CANISTER SPW-3278 WATER Jun,1994 Gr. Alpha A 23.4 18.7- 28.1 20.811.1;2.4 SPW-3278 WATER Jun 19M Gr. Beta A 31.8 25.5- 38.1 29.5 i 1.1;3.1 SPW-3276 WATER Jul,1994 11-3 A 25019.0 20030.6- 30007.4 24504.6 1 421.7;2486.5 SPMI-3282 MILK Jul,1994 Sr-89 A 22.5 15.2- 29.8 16.4 4.8 ; 5.1 SPMl-3282 MILK Jul,1994 St-90 A 25.4 20.0- 30.8 25.3 i 1.4;2.9 SPW-3284 WATER Jul,1994 Cs-137 A 221.5 168.5- 274.5 240.8 1 19.3;30.9 SPAP-3^,88 AIR FILTER Jul,1994 Gr. Beta A 8.3 6.7- 9.9 7.910.1;0.8 SPAP-3390 AIR FILTER Jul,1994 Cs-137 A 1.3 1.0- 1.6 1.310.1;0.2 SPF-3603 FIS11 Jul,1994 Cs-137 A 8.5 6.1- 10.9 8.311.3;1.5 UELLO)
SPW-5549 WATER Oct,1994 1-131 A 79.9 64.1 - 95.7 77.4 i 0.9; 7.8 SPW-5549 WATER Oct,1994 I-131(g) A 79.9 59.1- 100.7 85.5 i 9.5;12.8 SPMI-5550 MILK Oct,1994 Cs-134 A 36.4 25.8- 47.0 35.016.0;6.9 SPMI-5550 MILK Oct,1994 Cs-137 A 44.1 29.2- 59.0 46.119.4;10.5 SPMI-5550 M1LK Oct,1994 I.131 A 63.9 50.9- 76.9 65.2 i 0.9;6.6 SPMI-5550 M1LK Oct,1994 I-131(g) A 63.9 44.5- 83.3 68.4 i 11.1;13.0 SPW-5594 WATER Oct,1994 I-131 A 95.8 76.9- 114.7 92.5 i 1.0;9.3 92
=
Tcble A-2. In-house " spike" samples.
Concentration in pCi/L' Lab Sample Date Accepted Known TBEESML Results Code Type Collected Analysis Rejected Activity Control Limits
2s, n= 1' SPW-5594 WATER Oct,1994 I-131(g) A 95.8 72.1 - 119.5 98.2 10.1;14.1 Oct,1994 I-131(g) A 1.6 1.2 - 2.0 1.7 0.1 ; 0.2 I SPVE-6067 VEGETATIO N (SAWDUST)
SPS-5946 SEDIMENT Oct,1994 Cs-134 A 0.3 -23.9- 24.6 0.3 24.2;24.2 (BOTTOM)
SPF-6208 FISH Oct,1994 Cs-137 A 12.1 9.7- 14.4 11.610.1;1.2 (JELLO)
SPW-6955 WATER Nov,1994 Ni-63 A 1931.0 1549.6- 2312.4 1851.6 1 34.3;188.3 SPW-6994 WATER Nov,1994 Tc-99 A 66.0 49.3- 82.6 63.2 7.8;10.0 SPW-7440 WATER Nov,1991 H-3 A 24260.0 19387.1- 29132.9 24099.2 1 423.9;2446.9 l
SPAP-7507 AIR FILTER Nov,1994 Cs-137 A 1.9 1.5 - 2.3 2.2 0.0 ; 0.2
~~All results are in pCi/L, except for elemental potassium (K) data in milk, which are in mg/L.; air filter samples, which are in pCi/ Filter; and food products, which are in mg/Kg.~~
~~6 Control limits are based on the known value i 10%+TPU (Where all parametric uncertainties, other than counting statistics, are less than 5%).~~
~~All samples are the results of single determinations. The result is reported in the following format:~~
Activity i Counting Error ; Total Propagated Uncertainty.
I l
1 93
Table A-3. In-house " blank" samples.
Concentration pCi/L'.
Teledyne Results Acceptance Lab Sample Sample (4.66 Sigma) Criteria Code Type Date Analysis LLD Activity" (4.66 Sigma)
SPW-4820 WATER Jan 1994 Cs-134 < 1.9 -1.76 i 7.24;7.24 < 10.0 SPW-4820 WATER Jan 1994 Cs-137 <4.4 -0.31 i 2.67;2.67 < 10.0 SPW-4824 WATER Jan 1994 Gr. Alpha <0.3 0.00 i o.20;0.20 < 1.0 SPW-4824 WATER Jan 1994 Gr. Beta <0.9 0.40 1 0.59;0.59 <3.2 SPW-4827 WATER Jan 1994 Co-60 < 1.8 1.10 1 1.04;1.05 < 10.0 SPW-4827 WATER Jan 1994 Cs-134 < 1.9 0.51 i 6.76;6.76 < 10.0 SPW-4827 WATER Jan 1994 Cs-137 <2.0 0.43 i 0.84; 0.84 < 10.0 SPW-4827 WATER Jan 1994 Gr. Alpha < 0. 4 0.12 1 0.25;0.25 < 1.0 SPW-4827 WATER Jan 1994 Gr. Beta <0.8 0.21 1 0.55;0.55 < 3.2 SPW-4827 WATER Jan 1994 H-3 <192.0 133.90 1 101.00;102.63 < 200.0 SPW-4827 WATER Jan 1994 I-131 <0.3 -0.12 0.14;0.14 <0.5 SPMI-4846 Mill: Jan 1994 Co-60 <3.6 0.62 1 2.67;2.67 < 10.0 SPMI-4846 MILK Jan 1994 Cs-134 <5.4 0.52 i 3.83;3.83 < 10.0 SPMI-4846 MILK Jan 1994 Cs-137 <3.4 -0.74 i 2.93:2.93 < 10.0 SPMI-4846 MILK Jan 1994 I-131 <0.5 0.27 i 0.34;0.34 <0.5 SPMI-4846 MILK Jan 1994 Sr-89 <0.5 -0.54 1 0.79;0.79 < 5.0 SPMI-4846 MILK Jan 1994 St-90 N/A 1.93 1 0.44;0.48 < 1.0 Low level of Sr-90 concentration in milk (1-5 pCi/L) is not unusual.
SPAP-4950 AIR FILTER Jan 1994 Co-60 <2.2 -2.6) i 2.19;2.21 < 10.0 j SPAP-4950 AIR FILTER Jan 1994 Cs-134 < 3.1 -0.31 i 3.65;3.65 < 10.0 '
SPAP-4950 AIR FILTER Jan 1994 Cs-137 <2.9 2.78 i 23.94;23.94 < 10.0 SPAP-4952 AIR FILTER Jan 1994 Gr. Beta <0.9 0.00 1 0.58;0.58 <3.2 SPCli-4951 CliARCOAL Feb l994 I-131(g) <7.0 0.64 1 4.80;4.80 <9.6 CANISTER SPW-5054 WATER Mar 1994 Ra-226 < 0.1 0.01 i 0.03;0.03 < 1.0 SPW-5054 WATER Mar 1994 Ra-228 < 1.0 0.54 i 0.67;0.67 < 1.0 SPBS-5101 SEDIMENT Mar 1994 Co-60 <5.9 -0.19 1 1.63;1.63 < 10.0 SPBS-5101 SEDIMENT Mar 1994 Cs-134 < 6. 2 -31.20 1 13.10;13.47 < 10.0 SPBS-5101 SEDIMENT Mar 1994 Cs-137 <4.4 -0.261 2.75;2.75 < 10.0 SPW-647 WATER Apr 1994 Co-60 <5.8 0.56 i 0.53;0.54 < 10.0 I SPW-647 SPW-647 WATER WATER Apr 1994 Cs-134 Apr 1994 Cs-137
< 3. 4
< 5.1 0.86 1 0.72;0.73 2.65 i 2.75;2.78
< 10.0
< 10.0 SPW-647 WA'I ER Apr 1994 H-3 <191.5 148.40 1 100.90;102.90 < 200.0
{ SPW-647 WATER Apr1994 I-131 <0.5 -0.34 1 0.22:0.22 <0.5 SPMI-649 MILK Apr1994 Co-60 < 6.5 0.55 1 1.39;1.39 < 10.0 94
E
=
Table A-3. In house " blank"iamples.
Concentration pCi/L*.
Teledyne Results Acceptance Lab Sample Sample (4.66 Sigma) Criteria Code Type Date Analysis LLD Activity" (4.66 Sigma)
SPMI-649 MILK Apr 1994 Cs-134 <3.4 -3.45 i 5.60;5.62 < 10.0 SPMI-649 MILK Apr 1994 Cs-137 <4.6 0.59 1 3.98;3.98 < 10.0 SPMI-649 MILK Apr 1994 I-131 <0.5 -0.11 1 0.19;0.19 <0.5 SPW-651 WATER Apr 1994 Gr. Alpha <0.4 0.14 1 0.25;0.25 < 1.0 SPW-651 WATER Apr 1994 Gr. Beta <0.8 0.12 i 0.54;0.54 < 3.2 SPAP-653 AIR FILTER Apr 1994 Cs-134 <2.1 -0.12 f 0.18 ; 0.18 < 10.0 l
SPAP-653 AIR FILTER Apr 1994 Cs-137 <3.4 1.05 1 1.55;1.55 < 10.0 SPCH-654 CHARCOAL Apr 1994 1-131(g) < 6.1 0.96 1 3.84;3.84 < 9.6 L CANISTER SPAP-4956 AIR FILTER Apr 1994 Gr. Beta < 1.0 0.32 i 0.96;0.96 < 3.2 SPW-974 WATER May 1994 Fe-55 <0.8 0.10 1 0.47;0.47 < 1000.0 SPF-1022 FISH (JELLO) May 1994 Cs-134 <9.2 12.70 1 31.70;31.73 < 10.0 SPF-1022 FISH (JELLO) May 1994 Cs-137 < 10.0 27.30 1 58.30;58.36 < 10.0 SPW-1075 WATER May 1994 Ra-226 < 0.1 0.01 i 0.04;0.04 < 1.0 SPBS-3254 SEDIMENT May 1994 Co-60 <5.8 5.93 i 8.06;8.08 < 10.0 SPBS-3254 SEDIMENT May 1994 Cs-134 <2.0 5.67 1 6.69;6.71 < 10.0 SPBS-3254 SEDIMENT May 1994 Cs-137 <5.0 -2.11 i 4.69;4.69 < 10.0 SPVE-1852 VEGETATION Jun1994 Cs-134 <5.4 -1.47 i 2.14;2.15 < 10.0 (SAWDUST)
SPVE-1852 VEGETATION Jun1994 Cs-137 < 6. 6 2.12 1 3.44;3.45 < 10.0 (SAWDUST) ,
SPVE-1852 VEGETATION Jun1994 I-131(g) <5.6 -0.73 1 1.08;1.08 < 20.0 (SAWDUST) f SPW-3277 WATER Jun 1991 Gr. Alpha <0.3 0.10 i 0.22;0.22 < 1.0 l SPW-3277 WATER Jun1994 Gr. Beta <0.8 0.14 i 0.54;0.54 < 3.2 SPW-3275 WATER Jul 1994 H-3 <154.9 22.81 i 77.81;77.87 < 200.0 SPMI-3281 MILK Jul1994 Co-60 <3.6 0.87 1 2.22;2.22 < 10.0 SPMI-3281 MILK Jul1994 Cs-134 <2.3 -0.451 2.61;2.61 < 10.0 SPMI-3281 MILK Jul1994 Cs-137 <4.2 0.07 1 2.28;2.28 < 10.0 SPMI-3281 MILK Jul1994 I-131 <0.2 0.10 1 0.16;0.16 < 0.5 SPMI-3281 MILK Jul1994 St-89 <0.9 -0.54 t l.32 ; 1.32 <5.0 SPMI-3281 MILK Jul 1994 Sr-90 N/A 2.29 i 0.56;0.61 < 1.0 Low level of Sr-90 concentration in milk (1-5 pCi/L)is not unusual.
SPW-3283 WATER Jul1994 Co-60 <2.2 -3.09 i 3.52;3.55 < 10.0 SPW-3283 WATER Jul1994 Cs-134 <5.4 0.79 i 3.13;3.13 < 10.0 95 g
=
l Table A-3. In-house " blank" samples.
Concentration pCi/L'.
Teledyne Results Acceptance Lab Sample Sample (4.66 Sigma) Criteria Code Type Date Analysis LLD Activity" (4.66 Sigma)
SPW-3283 WATER Jul1994 Cs-137 <5.0 -0.10 1 3.05;3.05 < 10.0 SPW-3283 WATER Jul1994 I-131 <0.4 0.14 1 0.22:0.22 < 0.5 SPAP-3389 AIR FILTER Jul1994 Gr. Beta <0.2 0.16 i 0.26;0.26 <3.2 ,
SPAP-3391 AIR FILTER Jul1994 Co-60 < 1.7 -0.74 i 1.44;1.44 < 10.0 I SPAP-3391 AIR FILTER Jul 1994 Cs-134 <2.3 0.95 1 4.86;4.86 < 10.0
( SPAP-3391 AIR FILTER Jul1994 Cs-137 < 4.1 -3.03 1 3.15;3.16 < 10.0 l SPF-3602 FISH (JELLO) Jul 1994 Co-60 <3.6 -4.451 4.27;4.29 < 10.0 SPF-3602 FISH (JELLO) Jul1994 Cs-134 < 4.1 -3.91 5.63;5.64 < 10.0 l
! SPF-3602 FISH (JELLO) Jul1994 Cs-137 <4.7 -5.171 5.80;5.82 < 10.0 SPMI-5551 MILK Oct 1994 Cs-134 <4.3 0.90 1 3.34;3.34 < 10.0 SPMI-5551 MILK Oct 1994 Cs-137 <4.1 -0.551 3.43;3.43 < 10.0 SPMI-5551 MILK Oct 1994 I-131 <0.2 -0.03 1 0.16;0.16 <0.5 SPSO-5947 SOIL Oct 1994 Cs-134 <2.3 -4.84 i 4.84;4.86 < 10.0 SPSO-5947 SOIL Oct 1994 Cs-137 <6.4 -0.50 1 4.71;4.71 < 10.0 SPW-6995 WATER Nov l994 Tc-99 <4.2 1.24 1 2.19;2.19 < 10.0 SPW-7441 WATER Nov l994 H-3 <169.0 -74.64 i 80.48;81.12 < 200.0 SPW-7442 WATER Nov 1994 H-3 <169.0 -37.02 1 82.14;82.29 < 200.0 SPW-7451 WATER Nov 1994 Gr. Alpha <0.3 0.11 1 0.19;0.19 < 1.0 l-l SPW-7451 WATER Nov 1994 Gr. Beta <0.8 0.10 1 0.52;0.52 < 3.2 I SPAP-7506 SPAP-7506 AIR FILTER Nov 1994 Co-60 AIR FILTER Nov 1994 Cs-134
< 2.1
< 1. 6
<3.0 0.17 t 1.63 ; 1.63
-1.08 1 1.70;1.70
-0.55 i 1.65;1.65
< 10.0
< 10.0
< 10.0 SPAP-7506 AIR FILTER Nov 1994 Cs-137
~~Liquid sample results are reported in pCi. Liter, air filter sample results are in pCi/ filter, charcoal sample results are in pCi/ charcoal, and solid sample results are in pCi/ kilogram.~~
~~The activity reported is the net activity result.~~
!I I
1 96 !
lI i
I Table A-4. In-house " duplicate" prograrn.
Concentration in pCi/L' Date Lab Accepted' First Second Collected Analysis Codes
Rejected Result Result Jm,1994 Gr. Beta WATER-4607, 4608 A 1.410.7;0.7 1.410.7;0.7 J*n,1994 Co-60 M1LK-166,167 A 1.4 3.7 ; 3.7 -1.1 i 4.3 ; 4.3 I Jan,1994 Cs-137 Jan,1994 I-131(G)
MILK-166,167 MILK-166,167 J'n,1994 Gr. Beta WATER-4711,4712 A
A A
-0.313.4;3.4
-0.110.2;0.2 1.7i 0.6 ; 0.7
-0.7 f 2.6 ; 2.6 0.210.2;0.2 1.8 i 0.6 ; 0.7 J n,1994 Co-60 MILK-187,188 A 0.1 i 2.9 ; 2.9 -1.413.4;3.4 l Jan,1994 Cs-137 MILK-187,188 A 0.2 i 1.9 ; 1.9 1.912.6;2.6 Jan,1994 I-131 MILK-187,188 A 0.210.2;0.2 0.1 i 0.2 ; 0.2 l
Jan,1994 Gr. Beta WATER-4664,4665 A 8.811.8;2.3 4.4 1.4 ; 1.6 )
J;n,1994 H-3 WATER-4664, 4665 A 93.0 i 95.9;96.7 37.2 1 93.6;93.8 l
g Jr.n,1994 Gr. Alpha WATER-4687,4688 A 1.611.5;1.5 0.0 i l .2 ; 1.2
{
3 Jan,1994 Gr. Beta WATER-4687,4688 A 3.210.8;1.0 2.510.8;0.9 )
Jm,1994 H-3 WATER-4687,4688 A 171.8 i 99.0;101.7 183.4 1 99.4;102.5 Jan,1994 H-3 WATER-4741, 4742 A 105.0 1 101.0;102.0 127.0 i 102.0;103.5
'I Jr.n,1994 K-40 MILK-208, 209 A 1,396.0 i 148.0;240.7 1,586.0 1 162.0;269.8 Jan,1994 Sr-90 MILK-208, 209 A 3.010.6;0.6 3.610.7;0.8 J:.n,1994 H-3 WATER-4830,4831 A 73.8 i 89.4;89.9 79.3 i 89.6;90.2 Jan,1994 Gr. Beta WATER-4865,4866 A 1.9 i 0.2 ; 0.4 1.9 i 0.2 ; 0.3 Jan,1994 Gr. Beta WATER-5052, 5053 A 2.210.6;0.6 2.610.6;0.7 Jin,1994 H-3 WATER-4890,4891 A 421.9 i 109.0;123.2 454.8 1 106.6;123.2 Jan,1994 Gr. Beta WATER-4919, 4920 A 2.8 i 0.8 ; 0.9 3.4 i 0.8 ; 1.0 l
Feb,1994 Gr. Beta WATER-4952, 4953 A 2.710.6;0.7 2.110.5;0.6 l Feb,1994 H-3 WATER-5010,5011 A 142.0 1 99.0;100.9 119.0 i 98.0;99.3 Feb,1994 K-40 MILK-250, 251 A 1,087.0 1 77.0;166.7 1,036.0 1 98.0;171.6 j Feb,1994 Sr-90 MILK-250, 251 A 3.710.6;0.7 4.110.6;0.7
" Feb,1994 MILK-271,272 K-40 A 1,510.0 i 90.0;224.2 1,520.0 1 110.0;234.2 Feb,1994 H-3 WATER-4978, 4979 A 83.8 i 97.0;97.6 69.8 i 96.4;96.9 Feb,1994 Co-60 MILK-229, 230 A -1.5 i 4.2 ; 4.2 -1.615.5;5.5 Feb,1994 Cs-137 M1LK-229, 230 A -0.7 i 3.1 ; 3.1 -2.0 i 3.7; 3.7 Feb,1994 1-131 MILK-229, 230 A 0.2i 0.2 ; 0.2 0.1 i 0.2 ; 0.2 Feb,1994 H-3 WATER-5081,5082 A 28.0 1 95.0;95.1 72.0 i 96.0;96.5 Feb,1994 H-3 WATER-5124,5125 A 465.8 i 113.7;130.1 358.0 i 109.8;120.1 I Feb,1994 Gr. Beta WATER-5212, 5213 F;b,1994 Co-60 WATER-5183,5184 Feb,1994 Cs-137 WATER-5183, 5184 A
A A
2.9 i 0.7 ; 0.8 1.511.6;1.7 0.311.6;1.6 2.210.6;0.7
-0.712.0;2.0 0.4 i 2.1 ; 2.1 Feb,1994 Gr. Beta WATER-5183, 5184 A 4.9 i 1.1 ; 1.3 4.5 i 1.1 ; 1.3 97
E a
l Table A-4. In-house " duplicate" program.
Concentration in pCi/11 Date Lab Accepted' First Second Collected Analysis Codes 6 Rejected Result Result Mar,1994 K-40 MILK-292, 293 A 1,377.0 i 85.0;205.7 1,364.0 100.0;210.7 Mar,1994 Sr-90 MILK-292, 293 A 1.210.4;0.4 1.5 i 0.4 ; 0.4 Mar,1994 Gr. Beta MILK-5246,5247 A 6.510.8:1.1 6.410.9;1.1 Mar,1994 Gr. Beta WATER-5270, 5271 A 3.311.0;1.1 2.811.0;1.1 Mar,1994 H-3 WATER-5293, 5294 A 620.2 1 118.7;145.6 582.3 1 117.5;141.7 Mar,1994 I-131(G) MILK-313, 314 A 1.3147.7;47.7 -0.310.8;0.8 Mar,1994 K-40 MILK-334, 335 A 1,392.0 i 95.0;211.8 1,437.0 1 115.0;226.8 Mar,1994 H-3 WATER-5400, 5401 A 77.7 1 97.2;97.8 66.8 1 96.5;97.0 Mar,1994 H-3 WATER-5485, 5486 A 336.0 1 107.0;116.3 272.0 1 105.0;111.3 Mar,1994 Co-60 WATER-5446,5447 A 1.814.4;4.4 0.110.5;0.5 Mar,1994 Cs-137 WATER-5446,5447 A 0.711.6;1.6 1.0 1.9 ; 1.9 Mar,1994 Gr. Beta WATER-5446, 5447 A 3.8 i 1.3 ; 1.4 3.7i 1.3 ; 1.4 Mar,1994 H-3 WATER-5510,5511 A 396.0 i 89.0;104.0 458.5 i 113.1;129.2 Mar,1994 Gr. Beta WATER-5538, 5539 A 2.6 i 0.6 ; 0.7 2.010.6;0.7 Mar,1994 H-3 WATER-5593,5594 A 139.9 i 101.1;102.9 169.4 i 101.8;104.3 Mar,1994 Co-60 WATER-5614, 5615 A 0.4 i 1.0 ; 1.0 0.2 i 2.2 ; 2.2 Mar,1994 Cs-137 WATER-5614,5615 A 0.9 i 3.8 ; 3.8 -0.412.6;2.6 Mar,1994 Gr. Beta WATER-5566,5567 A 2.8 i 0.5 ; 0.7 2.2 i 0.5 ; 0.6 Mar,1994 Gr. Beta WATER-72, 73 A 1.6 i 0.5 ; 0.6 1.5 i 0.5 ; 0.5 Apr,1994 Gr. Beta WATER-49, 50 A 3.410.9;1.1 3.410.9;1.1 Apr,1994 Gr. Beta WATER-102,103 A 2.010.5;0.6 2.110.5;0.6 Apr,1994 H-3 WATER-102,103 A 165.0 i 102.0;104.4 79.0 1 98.0;98.6 Apr,1994 Gr. Beta WATER-187,188 A 3.410.7;0.8 3.210.6;0.8 Apr,1994 Co-60 MILK-246, 247 A 1.8 t l.6 ; 1.6 1.8 1.6 ; 1.6 Apr,1994 Cs-137 MILK-246,247 A 0.1 i 1.9 ; 1.9 g
0.111.9;1.9 3 Apr,1994 I-131 MILK-246, 247 A 0.110.2;0.2 0.210.3;0.3 Apr,1994 Gr. Beta WATER-257, 258 A 3.310.7;0.9 Apr,1994 Cs-137 WATER-267, 268 3.310.8;0.9 g A 0.212.7;2.7 1.2 2.2 ; 2.2 E Apr,1994 Gr. Beta WATER-281, 282 R 15.7 i 2.0;3.2 30.412.6;5.4 A review of the raw data revealed no errors or discrepancies. Both samples were recounted. The results of the recounts were in agreement with the initial results. The sample was reanalyzed. The result of the reanalysis was 30.712.1 pCi/L N3 further action is planned.
Apr,1994 H-3 WATER-281, 282 A 381,181.0 1 1,740.0;51,869.8 378,406.0 1 1,733.0;51,492.4 Apr,1994 Gr. Beta WATER-454, 455 A 3.3 i 2.1 ; 2.2 3.7 i 2.2 ; 2.3 Apr,1994 H-3 WATER-405, 406 A 65.9 1 98.2;98.6 62.0 i 98.1;98.4 Apr,1994 K-40 MILK-464, 465 A 1,630.0 1 130.0;257.0 1,589.0 i 162.0;270.1 Apr,1994 H-3 WATER-516, 517 A 37.6 i 95.0;95.1 69.3 i 95.8;96.2 I
98 e
i
l Table A-4. In house " duplicate" program.
Concentration in pCi/L' Date Lab Accepted' First Second Collected Analysis Codes
Rejected Result Result Apr,1994 Cs-137 WATER-267, 268 A 0.212.7;2.7 1.212.2;2.2 l Apr,1994 Gr. Beta WATER-616, 617 A 2.510.5;0.6 3.010.6;0.7 Apr,1994 H-3 WATER-616, 617 A 193.0 1 102.0;105.3 203.0 i 103.0;106.6 Apr,1994 Co-60 WATER-739, 740 A 0.8 i 11.4;11.4 0.310.4;0.4 l
E Apr,1994 Cs-137 WATER-739, 740 A -0.3 i 3.6 ; 3.6 0.8 i 3.2 ; 3.2 Apr,1994 Cs-137 WATER-739, 740 A -0.313.6;3.6 0.8 3.2;3.2
]
E Apr,1994 Co-60 WATER-697, 698 A 3.4 i 4.4 ; 4.4 2.1 i 2.8 ; 2.8 Apr,1994 Gr. Beta WATER-697, 698 A 2.911.0;1.1 3.110.8;0.9 M:y,1994 Gr. Beta WATER-1003,1004 A 2.810.3;0.5 2.610.3;0.5 Mty,1994 Gr. Beta WATER-796, 797 A 1.7 i 0.5 ; 0.5 2.1 i 0.5 ; 0.6 Mzy,1994 H-3 WATER-931, 932 A 531.3 i 109.7;131.4 554.5 i 110.6;133.8 Miy,1994 Co-60 WATER-893, 894 A -1.5 i 4.1 ; 4.1 1.313.2;3.2 L May,1994 Cs-137 WATER-893, 894 A 0.912.3;2.3 1.5 i 3.1 ; 3.1 May,1994 Gr. Beta WATER-893, 894 A 1.311.9;1.9 -0.2 i l .8 ; 1.8
~
Mxy,1994 H-3 WATER-893, 894 A 159.0 i 95.6;98.0 118.3 i 94.0;95.4 Miy,1994 Co-60 MILK-900, 901 A -2.813.0;3.0 -1.7i 6.1 ; 6.1 M y,1994 Cs-137 MILK-900,901 A -0.1 i 1.3 ; 1.3 0.5 i 1.7; 1.7 I Miy,1994 I-131 MILK-900, 901 A 0.110.2;0.2 0.110.2;0.2 Mty,1994 K-40 MILK-1001,1002 A 1,250.0 1 180.0;247.6 1,370.0 1 140.0;233.1 Miy,1994 Gr. Beta WATER-1171,1172 A 9.7 i 2.0 ; 2.5 7.512.2;2.5 L Mr-y,1994 H-3 WATER-1171,1172 A 950.0 i 108.0;168.4 1,012.0 1 109.0;175.6 M:y,1994 Co-60 MILK-1214,1215 A 0.712.4;2.4 0.210.6;0.6 7 Mty,1994 Cs-137 MILK-1214,1215 A -0.4 1.5 ; 1.5 ? .4 i 1.8 ; 1.8 l
Mty,1994 I-131 MILK-1214,1215 A 0.1 i 0.2 ; 0.2 0.1 i 0.2 ; 0.2 M:y,1994 Gr. Beta WATER-1565, lh A 2.610.9;1.0 2.610.9;1.0 Miy,1994 Gr. Beta WATER-1399,1400 A 6.010.7;1.1 5.5 i 0.7 ; 1.1 Mry,1994 I-131(G) MILK-1301,1302 A -0.110.2;0.2 0.010.2;0.2 Miy,1994 Gr. Beta SEDIM EN15-1550, A 2.1 i 0.1 ; 0.2 2.210.1;0.2
{ Miy,1994 Gr. Beta WATER-1545,1546 M:y,1994 Co-60 W ATER-1670,1671 A
A 6.6 i 0.6 ; 1.2
-0.310.6;0.6 5.410.6;1.0 1.412.4;2.4 Msy,1994 Cs-137 WATER-1670,1671 A 1.713.0;3.0 -1.7i 2.6 ; 2.7 M:y,1994 1-131(G) MILK-1510,1511 A 0.110.1;0.1 -0.1 i 0.1 ; 0.1 M:y,1994 H3 WATER-1520,1521 A 48.4 i 97.3;97.5 79.9 i 98.5;99.1 Jun,1994 I-131 MILK-1744,1745 R 0.9 i 0.2 ; 0.2 0.110.2;0.2 Jun,1994 Gr. Deta WATER-1786,1787 A 31.4 i 3.1; 5.8 31.413.0;5.7 Jun,1994 H-3 WATER-1786,1787 A 236,078.0 1 1,364.0;32,135.6 235,776.0 i 1,363.0; 32,094.5 E -
99
___m __ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - . _ - . _ _ _ - - _ _-___ _ _ _
E Table A-4. In-house " duplicate" program.
Concentration in pCi/L' Date Lab Accepted' First Second Collected Analysis Codes
Rejected Result Result Jun,1994 Co-60 WATER-1843,1844 A 1.311.0;1.0 0.512.2;2.2 l Jun,1994 Cs-137 WATER-1843,1844 A 0.011.1;1.1 1.011.8;1.8 Jun,1994 H-3 WATER-1843,1844 A 138.7 79.6;81.8 69.6 i 76.7;77.3 Jun,1994 Co-60 MILK-1818,1819 A -1.3 i 3.1 ; 3.1 0.2 i 4.5 ; 4.5 Jun,1994 Cs-137 MILK-1818,1819 A 0.312.3;2.3 1.9 i 3.5 ; 3.5 Jun,1994 I-131(G) MILK-1818,1819 A -0.2 i 0.2 ; 0.2 0.0 i 0.1 ; 0.1 Jun,1994 Gr. Beta WATER-1882,1883 A 5.010.7;1.1 5.6 i 0.8 ; 1.2 Jun,1994 H-3 WATER-1882,1883 A -32.6 i 76.9; 77.0 -55.8 i 76.9;77.3 i Jun,1994 Be-7 GRASS-1900,1901 A 0.5 i 0.1 ; 0.1 0.510.1;0.1 Jun,1994 K-40 GRASS-1900,1901 A 4.310.2;0.5 4.310.2;0.5 ,
Jun,1994 I-131 MILK-1982,1983 A 0.010.2;0.2 0.1 i 0.1 ; 0.1 i Jun,1994 K-40 MILK-1982,1983 A 1,562.0 1 98.0;233.9 1,553.0 i 116.0;241.0 Jun,1994 Cr. Beta WATER-1972,1973 A 25.7 i 2.4;4.6 23.712.3;4.3 Jun,1994 K-40 MILK-2092, 2093 A 1,430.0 170.0;258.3 1,430.0 1 140.0;239.6 Jun,1994 C-14 WATER-2116, 2117 A -28.0 49.0;49.1 -9.0 i 52.0;52.0 Jun,1994 Gr. Alpha WATER-2116,2117 A 0.610.5;0.5 1.l i 0.6 ; 0.6 Jun,1994 Gr. Beta WATER-2116,2117 A 8.410.8;1.5 7.2i o.7; 1.3 Jun,1994 H-3 WATER-2116,2117 A 2,544.0 1 152.0;377.9 2,522.0 i 152.0;375.2 Jun,1994 U-233/4 WATER-2116,2117 A 1.510.2;0.3 1.5 i 0.2 ; 0.2 Jun,1994 U-235 WATER-2116,2117 A 0.0 i 0.1 ; 0.1 0.0 i 0.1 ; 0.1 Jun,1994 U-238 WATER-2116, 2117 A 0.910.2;0.2 1.110.2;0.2 Jun,1994 Gr. Beta WATER-2198, 2199 A 5.3 0.9 ; 1.2 5.2 i 0.8; 1.2 Jun,1994 Co-60 MILK-2156,2157 A -0.5 i 3.1 ; 3.1 1.5 i 4.0 ; 4.0 Jun,1994 Cs-137 MILK-2156,2157 A 1.313.6;3.6 1.215.9;5.9 Jun,1994 I-131(G) MILK-2156,2157 A -0.1 i 0.2 ; 0.2 g
0.0 i 0.2 ; 0.2 E
Jun,1994 I-131 MILK-2194, 2195 A 0.210.3;0.3 0.1 1 0.2; 0.2 Jun,1994 Gr. Deta WATER-2238, 2239 A 1.5 i 0.6 ; 0.7 1.710.6;0.7 g Jun,1994 Gr. Beta WATER-2363, 2364 A 69.5 1 84.0; 84.7 5.9 i 81.3;81.3 E Jun,1994 Gr. Beta WATER-2336, 2337 A 6.2 t l.3 ; 1.6 6.411.3;1.6 Jun,1994 H-3 WATER-2336, 2337 A 23.6 i 80.1;80.1 -20.9 i 78.2;78.3 Jun,1994 Be-7 SLIME-2480,2481 A 0.4 i 0.2 ; 0.2 0.410.2;0.2 Jun,.1994 Cs-137 SLIME-2480,2481 A 0.0 i 0.0; 0.0 0.0 i 0.0 ; 0.0 Jun,1994 K-40 SLIME-2480,2481 A 1.310.2;0.2 1.310.2;0.2 Jun,1994 1-131 MILK-2334,2335 A 0.110.2;0.2 0.010.2;0.2 Jun,1994 Gr. Beta WATER-2733,2734 A 2.010.5;0.5 1.6 0.4 ; 0.5 Jun,1994 Sr-89 WATER-3056,3057 A -0.6 i 1.1 ; 1.1 -0.110.8;0.8 100
=
p Table A-4. In-house " duplicate" program.
{
Concentration in pCi/L' Date Lab
( Collrcted Analysis Codes
~~Accepted' Rejected First Result Second Result Jun,1994 St-90 WATER-3056, 3057 A 0.510.4;0.4 0.310.3;0.3~~
( Jun,1994 K-40 MILK-2405,24% A 1,730.0 1 190.0;302.4 1,710.0 i l20.0;261.7 Jun,1994 H3 WATER-2432, 2433 A 26.9 i 81.9;82.0 123.2 i 85.9;87.5 Jun,1994 H-3 WATER-3000,3001 A 213.6 i 86.2;91.0 192.4 i 85.3;89.2 Jun,1994 Gr. Alpha WATER-2459,2460 A 0.110.2;0.2 0.0i0.2;0.2 Jun,1994 Gr. Beta WATER-2459, 2460 A 2.3 i 0.2 ; 0.4 2.010.2;0.4 Jun,1994 H-3 WATER-2712,2713 A 260.0 i 90.0;96.7 170.0 i 80.0;83.3
{ Jun,1994 H-3 WATER-2501,2502 A 70.0 1 80.0;80.6 137.0 1 80.0;82.1 Jun,1994 Gr. Beta WATER-2662, 2663 A 5.010.9;1.2 5.5 i 0.9 ; 1.2 Jun,1994 Gr. Beta WATER-2691,2692 A 2.410.5;0.6
( WATER-2691,2692 2.110.5:0.6 Jun,1994 H-3 A 192.6 i 87.0;90.9 108.3 i 83.6;84.8 Jul,1994 Co-60 MILK 2522,2523 A 5.7i 4.5 ; 4.5 -3.215.3;5.3 h Jul,1994 Cs-137 MILK-2522,2523 A 0.213.3;3.3 2.0i 3.3 ; 3.3 Jul,1994 I-131(G) MILK-2522,2523 A 0.110.2;0.2 0.1 i 0.2 ; 0.2 Jul,1994 Gr. Beta WATER-2543,2544 A 1.110.3;0.4 1.1 i 0.4 ; 0.5
[ Jul,1994 K-40 WATER-2543,2544 A 1.2i 0.1; 0.2 1.2i 0.1 ; 0.2 Jul,1994 Gr. Alpha WATER-2631,2632 A 0.310.9;0.9 0.8 t l.0; 1.0 Jul,1994 Gr. Beta WATER-2631, 2632 A 8.111.0;1.6 7.1 i 1.0; 1.5
{ MILK-2863,2864 Jul,1994 I-131 A 0.110.2;0.2 0.010.2;0.2 Jul,1994 K-40 MILK-2863,2864 A 1,360.0 130.0;226.1 1,450.0 100.0;221.1
( Jul,1994 Be-7 GRASS-2754,2755 A 2.210.2;0.3 2.210.1;0.2 Jul,1994 K-40 GRASS-2754, 2755 A 7.3 i 0.4 ; 0.8 6.9 i 0.2 ; 0.7 Jul,1994 Co-60 WATER 2775,2776 A -0.5 i 3.1 ; 3.1 0.3 i 3.3 ; 3.3 Jul,1994 Cs-134 WATER 2775,2776 A -0.8 i 3.4 ; 3.4 -1.013.2;3.2 !
Jul,1994 Cs-137 WATER-2775,2776 A 1.913.0;3.0 0.7i 2.9; 2.9 Jul,1994 Gr. Beta WATER-2775,2776 A 3.0i 0.5 ; 0.7 2.9i 0.5 ; 0.7 l Jul,1994 I-231 WATER-2775,2776 A 0.0 i 0.2 ; 0.2 0.l i 0.2 ; 0.2 !
Jul,1994 I131 MILK 2889,2890 A 0.110.2;0.2 0.210.2;0.2 l Jul,1994 Gr. Beta WATER-2842,2843 A 4.0 i 1.1 ; 1.3 5.211.2;1.4
{ Jul,1994 H-3 WATER-2842,2843
{
A 65.8 i 83.7; 84.1 32.3 1 82.2;82.3 ;
Jul,1994 Gr. Beta WATER-2910,2911 A 1.610.4;0.5 1.510.5;0.5
( Jul,1994 H-3 WATER-2910, 2911 A 74.9 i 82.6;83.2 146.8 i 85.6;87.9 I jul,1994 Gr. Beta WATER-2930,2931 A 1.70.6;0.6 2.2 i 0.6 ; 0.7 i p Jul,1994 1-131 MILK-2958,2959 A -0.110.2;0.2 -0.110.2;0.2 l Jul,1994 K-40 MILK-2958,2959 A 1,445.0 1 122.0;231.3 1,445.0 1 134.0;237.9 l Jul,1994 Sr-89 MILK-3010,3011 A -0.511.0;1.0 -0.4 i 0.7 ; 0.7 1
101 m_-________ _ -. -- -. ---- -- --- -
N_
Table A-4. In-house " duplicate" program.
Concentration in pCi/L' Date Lab Accepted' First Second Collected Analysis Codes 6 Rejected Result Result Jul,1994 Sr-90 MILK-3010,3011 A 1.6 i 0.6 ; 0.6 1.310.4;0.4 Jul,1994 1-131 WATER-3031, 3032 A 0.2 i 0.2 ; 0.2 0.2 i 0.3 ; 0.3 Jul,1994 I-131 MILK-3083,3084 A 0.210.2;0.2 0.110.2;0.2 Jul,1994 K-40 MILK-3083,3084 A 1,420.0 1 170.0;257.3 1,380.0 i l50.0;240.3 Jul,1994 H-3 WATER-3106,3107 A 79.1 1 80.4;81.1 98.4 i 81.3;82.4 Jul,1994 Gr. Beta WATER-3154, 3155 A 1.710.8;0.8 2.210.8;0.9 Jul,1994 C-14 URINE-3748, 3749 A 76.0 i 83.0;83.3 74.0 i 96.0;96.3 -
Jul,1994 Gr. Alpha URINE-3748,3749 A 0.3 i 2.3 ; 2.3 2.1 i 2.5 ; 2.5 Jul,1994 Gr. Beta URINE-3748, 3749 A 3.912.5;2.5 3.3 i 2.7 ; 2.7 Jul,1994 H-3 URINE-3748, 3749 A 175.0 1 583.0;583.3 198.0 i S84.0;584.3 Jul,1994 H-3 WATER-3209,3210 A -25.3 i 82.3;82.4 0.9 i 83.4;83.4 Jul,1994 H-3 WATER-3234, 3235 A 7.7 i 82.8;82.8 -38.3 1 80.8;81.0 Jul,1994 Gr. Beta WATER-3261, 3262 A 4.410.8;1.1 4.8 f 0.9 ; 1.1 Jul,1994 Gr. Beta WATER-3310,3311 A 2.611.3;1.4 1.4 i 1.2 ; 1.2 Jul,1994 K-40 VEGETATION-340 A 3.4i0.4;0.5 3.510.4;0.6 Jul,1994 H-3 WATER-3469,3470 A 563.1 1 99.6;125.6 510.6 i 97.7;119.9 g Jul,1994 Co-60 WATER-3811,3812 A 5.614.2;4.3 0.l i 2.3 ; 2.3 3 Jul,1994 Cs-137 WATER-3811,3812 A 2.914.0;4.0 -0.4 i 2.3 ; 2.3 Jul,1994 H-3 WATER-3358,3359 A 180.0 i 100.0;103.0 200.0 i 100.0;103.6 Aug,1994 Gr. Beta WATER-3559,3560 A 2.110.8;0.8 1.4 i 0.7 ; 0.8 Aug,1994 Be-7 GRASS-3586, 3587 A 3.510.5;0.6 3.710.5;0.6 Aug,1994 Gr. Beta GRASS-3586, 3587 A 7.4 i 0.3 ; 0.8 7.1 0.2 ; 0.7 Aug,1994 K-40 GRASS-3586, 3587 A 7.4 i 0.8 ; 1.1 7.1 i 0.8 ; 1.1 Aug,1994 Sr-89 GRASS-3586, 3587 A, 0.010.0;0.0 0.0 i 0.0 ; 0.0 Aug,1994 Sr-90 GRASS-3586, 3587 A 0.010.0;0.0 0.010.0;0.0 Aug,1994 Gr. Beta WATER-3611,3612 A 1.9 i 0.6 ; 0.6 2.0 i 0.5 ; 0.6 Aug,1994 I-131 MILK-3942,3943 A -0.110.2;0.2 0.210.3;0.3 Aug,1994 K-40 MILK-3942,3943 A 1,544.0 i 128.0;245.9 1,416.0 i 191.0;271.2 Aug,1994 H-3 WATER-3638, 3639 A 147.4 i 86.3;88.6 38.6 i 81.7;81.9 Aug,1994 H-3 WATER-3683, 3684 A 7.1 i 81.0;81.0 38.9 1 82.3;82.5 Aug,1994 Gr. Beta WATER-3727, 3728 A 4.510.8;1.0 4.8 i 0.8 ; 1.1 Aug,1994 K-40 MILK-3S42,3843 A 1,419.0 i 120.0;227.3 1,411.0 i 142.0;238.7 j Aug,1994 Gr. Beta WATER-3869, 3870 A 4.2 i 0.7; 0.9 3.2 i 0.6 ; 0.8 Aug,1994 H-3 WATER-3869, 3870 A 43.8 i 81.8;82.1 33.3 i 81.4;81.5 Aug,1994 Gr. Deta VEGETAT10N-389 A 2.5 i 0.1 ; 0.3 2.510.1;0.3 Aug,1994 K-40 VEGETATION-389 A 1.910.3;0.3 2.3 i 0.3 ; 0.4 102 g
1 l Table A-4. In-house " duplicate" prograrn.
I Concentration in pCi/L' l Date Lab Accepted' First Second l
I Collected Analysis Aug,1994 Gr. Beta WATER 3964,3965 Aug,1994 Gr. Deta WATER-3913,3914 Codes
~~Rejected A~~
A Result 3.9 i 0.7 ; 0.9 4.3 i 0.8 ; 1.1 Result 4.910.8;1.1 3.8 i 0.7; 0.9 Aug,1994 Tc-99 WATER-3991, 3992 A 84.9 i 9.3; 12.6 96.4 i 9.9;13.8 Aug,1994 Co-60 MILK-4016, 4017 A 1.013.6;3.6 -0.910.4;0.4 l
! Aug,1994 Cs-137 MILK-4016,4017 A -0.3 i 2.7 ; 2.7 2.3 3.9 ; 3.9 Aug,1994 I-131 MILK-4016,4017 A 0.2 i 0.2 ; 0.2 0.010.2;0.2 Aug,1994 Sr-89 MILK-4040,4N1 A 0.911.1;1.1 -0.110.8;0.8 j --
l Aug,1994 Sr-90 MILK-4040,4041 A 0.9 i 0.5 ; 0.5 1.1 i 0.4 ; 0.4 j Aug,1994 K-40 MILK-4459,4460 A 1,528.0 1 170.0;268.5 1,481.0 1 151.0;251.7 l l Aug,1994 Gr. Beta WATER-4061,4062 A 4.610.8;1.1 4.6 i 0.8 ; 1.1 l Aug,1994 Gr. Beta WATER-4113,4114 A 1.6 i 0.6 ; 0.7 1.810.6;0.7 Aug,1994 K-40 MILK-4168,4169 A 1,300.0 i 140.0;225.5 1,390.0 i 140.0;235.2 l Aug,1994 Gr. Beta WATER-4284, 4285 A 5.410.9;1.2 5.210.9;1.2 Aug,1994 H-3 WATER-4504, 4505 A 378.0 99.0;111.6 428.0 i 100.0;115.7 i Aug,1994 Gr. Beta WATER-4259,4260 A 2.9 i 0.5 ; 0.7 2.510.5;0.6 I
Aug,1994 Gr. Beta WATER-4308,4309 A 2.110.5;0.6 2.110.5;0.6 Aug,1994 H3 WATER-4308,430) A 172.7i 89.0;92.0 148.1 1 88.0;90.2 Aug,1994 Gr. Beta WATER-4333,4334 A 5.112.1;2.3 4.1 i 2.0 ; 2.1 l
l I Aug,1994 Aug,1994 Aug,1994 H-3 K-40 K-40 WATER-4333,4334 VEGETATION-440 MILK 4459,4460 A
A A
161.31 87.4;90.1 2.710.1;0.3 1,528.0 1 170.0;268.5 98.0 i 84.9;85 9 3.011.0;1.0 1,481.0 i 151.0;251.7 Aug,1994 Gr. Deta WATER-4475, 4476 A 2.8 i 0.3 ; 0.5 2.9 i 0.3 ; 0.5 Aug,1994 H-3 WATER-4475,4476 A 51.1 1 80.3;80.6 56.3 i 80.5;80.9 l
Sep,1994 Co-60 MILK-4423,4424 A -1.015.0;5.0 -0.9 i 4.1 ; 4.1 Sep,1994 Cs-137 MILK-4423,4424 A 0.714.1;4.1 -0.6 i 2.8 ; 2.8 Sep,1994 I-131 MILK-4423, 4424 A 0.210.2;0.2 0.210.2;0.2 Sep,1994 H-3 WATER-4446, 4447 A 186.2 i 89.0;92.5 223.4 i 90.4;95.4 Sep,1994 Co-60 MILK-4525,4526 A 2.813.5;3.5 1.212.9;2.9 Sep,1994 Cs-137 MILK-4525,4526 A 0.413.2;3.2 1.3 i 2.4 ; 2.4 Sep,1994 I-131 MILK-4525,4526 A 0.210.3;0.3 -0.110.3;0.3 Sep,1994 Gr. Beta WATER-4571,4572 A 0.li0.2;0.2 0.110.2;0.2 S2p,1994 K-40 WATER-4571, 4572 A 7.211.0;1.2 7.2 1.0 ; 1.2 Sep,1994 H-3 WATER-3636,3637 A 445.2 1 99.0;116.1 529.7 i 102.0;124.9 b S2p,1994 I-131 MILK-4550,4551 A 0.010.2;0.2 0.310.3;0.3 L Sep,1994 K-40 MILK-4550,4551 A 1,410.9 i 109.0;220.7 1,398.1 1 155.0;245.3 Sep,1994 Ra-226 SLUDGE-4613, A 1.410.0;0.1 1.4i0.1;0.1 E
103
um Table A-4. In house " duplicate" program.
Concentration in pCi/L' Date Lab Accepted' First Second Collected Analysis Codes' Rejected Result Result Sep,1994 H-3 WATER-4810,4811 A 36,966.3 1 557.2;5,058.2 37,783.0 i 563.1;5,169.2 Sep,1994 H-3 WATER-4688,4689 A 62.8 i 82.1;82.6 -9.4 i 79.0; 79.0 sep,1994 I-131 MILK-4886, 4887 A 0.010.3;0.3 -0.1 i 0.2 ; 0.2 Sep,1994 K-40 MILK-4886,4887 A 1,397.9 1 152.0;243.4 1,319.0 1 171.0;247.8 Sep,1994 Gr. Alpha WATER-4744,4745 A 7.112.5;2.5 7.612.2;2.4 Sep,1994 Gr. Beta WATER-4744, 4745 A 16.4 i 1.7;3.0 g
16.011.7;3.0 3 Sep,1994 K-40 SEDIMENTS-6570, A 7.8 0.6 ; 1.0 7.710.6;0.9 Sep,1994 K-40 MILK-4934,4935 A 1,519.5 i l70.0;267.6 1,421.3 190.0;271.0 Sep,1994 Gr. Beta SEDIMENT-5000, A 8.612.0;2.2 8.6 i 2.0 ; 2.2 Sep,1994 I-131 MILK-5022,5023 A 0.210.2;0.2 0.310.3;0.3 Sep,1994 Sr-89 VEGETAT10N-525 A 0.010.0;0.0 0.0 i 0.0 ; 0.0 Sep,1994 Sr-90 VEGETATION-525 A 0.010.0;0.0 0.0 i o.0; 0.0 Sep,1994 Co-60 WATER-5952, 5953 A 1.7 2.5 ; 2.5 1.2 i 2.4 ; 2.4 Sep,1994 Cs-137 WATER-5952,5953 A 1.8 i 2.4 ; 2.4 0.3 i 2.2 ; 2.2 Sep,1994 Sr-89 AIR F1LTER-5348, A 420.1 i 11.4;43.5 439.4 i 22.0;49.1 Sep,1994 Sr-89 FILTER-5348,5349 A 420.1 i 11.4;43.5 439.4 1 22.0;49.1 Sep,1994 Sr-90 AIR FILTER-5348, A 5.6 i 1.2 ; 1.3 7.112.0;2.1 Sep,1994 Gr. Alpha FILTER-5728,5729 A -0.812.6;2.6 1.912.6;2.6 Sep,1994 Gr. Alpha FILTER-5728,5729 A -0.8 i 2.6 ; 2.6 1.9 i 2.6 ; 2.6 Sep,1994 Sr-89 FILTER-5728,5729 A 2.016.3;6.3 -3.0 i 3.6 ; 3.6 Sep,1994 Sr-90 FILTER-5728,5729 A 0.9 1.9 ; 1.9 1.7i1.3;13 Sep,1994 i{-3 WATER-5373, 5374 A 565.0 i 96.0; 123.0 561.0 1 96.0;122.6 Oct,1994 I-131 MILK-5274,5275 A 0.2 0.2 ; 0.2 0.210.3;0.3 Oct,1994 Be-7 SOIL-5394, 5395 A 0.7 i 0.4 ; 0.4 0.9 i 0.5 ; 0.5 Oct,1994 Cs-137 SOIL-5394, 5395 A 0.2 i 0.1 ; 0.1 0.2 i 0.1 ; 0.1 Oct,1994 Cs-137 SOIL-5394, 5395 A 0.210.1;0.1 0.2 i 0.1 ; 0.1 Oct,1994 Gr. Alpha SOIL-5394,5395 A 8.9 i 2.5 ; 2.7 9.7 i 2.7 ; 2.9 Oct,1994 Gr. Beta SO!L-5394, 5395 A 27.212.4;3.6 27.8 i 2.2;3.6 E
m Oct,1994 K-40 SOIL-5394, 5395 A 22.9 i 1.2; 2.6 22.4 1.4 ; 2.6 Oct,1994 Sr-89 SOIL-5394, 5395 A 0.010.0;0.0 0.0 i 0.0 ; 0.0 Oct,1994 Sr-90 SOIL-5394, 5395 A 0.1 0.0 ; 0.0 0.11.0.0;0.0 Oct,1994 Gr. Beta WATER-5421,5422 A 2.610.5;0.7 3.5 i 0.5 ; 0.7 Oct,1994 K-40 WATER-5421,5422 A 0.910.1;0.1 1.0 i 0.1 ; 0.1 Oct,1994 Co-60 MILK-5527,5528 A 1,113.3;3.3 0.9 i 3.9 ; 3.9 Oct,1994 Cs-137 MILK-5527,5528 A 3.212.4;2.5 -0.513.5;3.5 Oct,1994 I-131 MILK-5527, 5528 A 0.010.2;0.2 0.0 0.2 ; 0.2
Table A-4. In-house " duplicate" program.
Concentration in pCi/L' Date Leb Accepted' First Second Collected Analysis Codes
Rejected Result Result Oct,1994 K-40 VEGETATION-557 A 3.010.3;0.4 2.8 i 0.4 ; 0.5 Oct,1994 Co-60 MILK-5552,5553 A 2.0 i 3.3 ; 3.3 1.314.1;4.1 Oct,1994 Cs-134 MILK-5552,5553 A -0.8 i 2.8 ; 2.8 0.213.0;3.0 Oct,1994 Cs-137 MILK-5552,5553 A 1.012.6;2.6 -0.5 i 3.6 ; 3.6 Oct,1994 I-131 MILK-5552,5553 A 0.1 i 0.2 ; 0.2 -0.110.2;0.2 Oct,1994 I-131 MILK-5552,5553 A 0.1 i 0.2 ; 0.2 -0.1 i 0.2 ; 0.2 Oct,1994 K-40 MILK-5552,5553 A 1,468.1 1 122.0;234.0 1,322.0 1 146.0;231.6 Oct,1904 St-89 MILK-5552,5553 A 0.7 i l .1 ; 1.1 -0.110.9;0.9 Oct,1994 Sr-90 MILK-5552,5553 A 1.7i 0.4 ; 0.5 1.4 i 0.4 ; 0.4 Oct,1994 I-131 WATER-5595,5596 A 0.1 i 0.2 ; 0.2 0.110.3;0.3 Oct,1994 Co-60 FISH-5637, 5638 A -0.1 i 1.3 ; 1.3 -0.8 i 1.9 ; 1.9 Oct,1994 Cs-137 FISH-5637, 5638 A 0.3 i 1.3 ; 1.3 2.0 i 1.7 ; 1.7 Oct,1994 Cs-137 SEDIMENT-5850, A 0.210.0;0.0 0.2 i 0.0 ; 0.1 Oct,1994 K-40 SEDIMENT-5850, A 13.5 i 0.9;1.6 12.2 i 0.9;1.5 Oct,1994 Gr. Beta WATER-5658,5659 A 7.4 1.1 ; 1.6 8.0 i l.0 ; 1.6 -
Oct,1994 Co-60 WATER-5682,5683 A 0.2 i 3.4 ; 3.4 2.0i 3.5 ; 3.6 Oct,1994 Cs-137 WATER-5682,5683 A 0.2 i 3.1 ; 3.1 0.713.7;3.7 Oct,1994 H-3 WATER-5682,5683 A 78.6 i 76.4; 77.2 -41.8 i 71.1;71.4 '
I Oct,1994 Oct,1994 H-3 Co-60 WATER-5707,5708 SEDIMENTS-5829, Oct,1994 Cs-137 SEDIMENTS-5829, A
A A
12,727.1 i 1,756.4;2,465.9 0.4 i 1.5 ; 1.5 0.2 i 0.0 ; 0.0 12,799.1 1 1,766.1;2,479.8
-0.6 i 1.7 ; 1.7 0.2 i 0.0 ; 0.1 Oct,1994 Be-7 GRASS-5879,5880 A 2.4 i 0.1 ; 0.3 2.410.1;0.3 Oct,1994 K-40 GRASS-5879,5880 A 6.5 i 0.2 ; 0.7 6.6 0.2 ; 0.7 Oct,1994 K-40 VEGETATION-590 A 3.4 i 0.4 ; 0.5 3.1 i 0.3 ; 0.4 Oct,1994 Sr-89 VEGETATION-590 A 0.0 i 0.0 ; 0.0 0.010.0;0.0 Oct,1994 Sr-90 VEGETATION-590 A 0.0 i 0.0 ; 0.0 0.010.0;0.0 Oct,1994 H-3 WATER-5928,5929 A 402.9 1 94.7;109.4 446.3 1 96.2;113.8 Oct.1994 Gr. Beta WATER-6018,6019 A 2.4 i 0.7 ; 0.8 1.6 i 0.4 ; 0.5 Oct,1994 Co-60 SEDIMENTS-6301, A 1.1 i 0.1 ; 0.1 1.1 i 0.1 ; 0.1 Oct,1994 Cs-137 SEDIMEN'IS-6301, A 1.6 i 0.1 ; 0.2 1.6 i 0.1 ; 0.2 Oct,1994 Gr. Beta SEDIMENTS-6301, A 11.8 i l.7; 2.1 8.311.8;2.0 Oct,1994 Mn-54 SEDIMENTS-6301, A 0.71 0.1;0.1 0.8 i 0.1; 0.1 Oct,1994 J-131 WATER-6070,6071 A 0.110.2;0.2 -0.210.2;0.2 Oct,1994 H-3 WATER-6116,6117 A -7.5 i 76.8;76.9 -21.5 i 76.2; 76.3 Oct,1994 Gr. Beta SEDIMENT-6256, A 5.5 i 1.7 ; 1.8 7.4 i 1.4 ; 1.6 Oct,1994 K-40 SEDIMENT-6256, A 9.310.3;1.0 9.3 i 0.3 ; 1.0 1
105
E o
. Table A-4. in-house " duplicate" program.
Concentration in pCi/L' Date Lab Accepted
~~First Second Collected Analysis Codes~~
Rejected Result Result Oct,1994 Ra-226 SEDIMENT-6256, A 0.1 i 0.0 ; 0.0 0.110.0;0.0 Oct,1994 Ra-228 SEDIMENT-6256, A 0.110.0;0.0 0.0 0.0 ; 0.0 Oct,1994 1-131 MILK-6091,6092 A 0.210.2;0.2 0.010.2;0.2 Oct,1994 H-3 WATER-6139, 6140 A 23,478.0 1 782.0;3,287.4 23,509.0 1 782.0;3,291.5 Oct,1994 Co-60 FISH-6162, 6163 A 0.0 i 0.0 ; 0.0 0.010.0;0.0 Oct,1994 Co-60 FISH-6162, 6163 A 0.1 i 0.0 ; 0.0 g
0.110.0;0.0 g Oct,1994 Co-60 WATER-6635, 6636 A 1.8 i 2.4 ; 2.4 -0.211.7;1.7 Oct,1994 Cs-137 WATER-6635, 6636 A 1.113.4;3.4 0.712.3;2.3 Oct,1994 Ue-7 GRASS-6235, 6236 A 1.910.1;0.2 1.910.1;0.2 Oct,1994 K-40 GRASS-6235, 6236 A 7.0 i 0.3 ; 0.8 6.8 i 0.2 ; 0.7 Oct,1994 Gr. Beta WATER-6277, 6278 A 2.4 i 0.6 ; 0.7 2.410.6;0.7 Oct,1994 H-3 WATER-6277, 6278 A -4.1179.6;79.6 66.3 1 89.9;90.3 Oct,1994 Gr. Deta WATER-6489, 6490 A 2.0 i 0.5 ; 0.6 2.0 i 0.5 ; 0.6 Oct,1994 H-3 WATER 4489,6490 A 742.2 i 106.5;146.7 763.2 1 107.2;149.2 Oct,1994 H-3 WATER-6214, 6215 A 4,466.0 i 189.0;636.1 4,595.0 1 191.0;653.5 Oct,1994 H-3 WATER-6327, 6328 A 131.6 i 82.8, '4.7 147.3 i 83.5;85.9 Oct,1994 AC-228 SOIL 4447, 6448 A 0.7i 0.1 ; 0.1 0.710.0;0.1 Oct,1994 BI 212 SOIL-6447, 6448 A 0.7 i 0.2 ; 0.2 0.710.1;0.1 Oct,1994 BI-214 SOIL-6447, 6448 A 0.5 i 0.0 ; 0.1 0.510.0;0.1 Oct,1994 Gr. Alpha SOIL-6447, 6448 A 6.5 i 2.7 ; 2.7 6.6 i 2.5 ; 2.6 Oct,1994 Gr. Beta SOIL-6447, 6448 A 21.5 i 2.4; 3.2 20.6 i 2.4;3.2 Oct,1994 K-40 SOIL-6447, 6448 A 18. l i 0.4 ; 1.8 18.710.3;1.9 j Oct,1994 PB-212 SOIL 4447, 6448 A 0.710.0;0.1 0.710.0;0.1 '
Oct,1994 PB-214 SO!L-6447, 6448 A 0.6 i 0.0 ; 0.1 0.6 i 0.0 ; 0.1 Oct,1994 RA-226 SOIL-6447, 6448 A 1.2 i 0.2 ; 0.2 1.010.2;0.2 Oct,1994 TL-208 SOIL-6447, 6448 A 0.2 i 0.0 ; 0.0 0.210.0;0.0 Oct,1994 Co-60 FISH-6372, 6373 A 0.010.0;0.0 0.010.0;0.0 Oct,1994 Cs-137 FISH-6372, 6373 A g
0.010.0;0.0 0.010.0;0.0 g Oct,1994 Gr. Beta WATER-6468, 6469 A 1.8 i 0.5 ; 0.5 1.810.5;0.6 Oct,1994 H-3 WATER 4468, 6469 A 137.6 i 84.6;86.6 90.4 i 82.6;83.5 ,
Nov,1994 Gr. Beta WATER-6401, 6402 A 1.810.5;0.5 1.7 i 0.6 ; 0.7 Nov,1994 Gr. Beta SEDIMENTS 4422, A 6. l i 0.6 ; 0.9 6.410.6;0.9 Nov,1994 K-40 SEDIMENU-6422, A 8.2 i 0.5 ; 1.0 7.2 i 0.6 ; 0.9 I Nov,1994 Sr-89 SEDIMENE-6422, A 0.0 i 0.0 ; 0.0 0.0 i 0.0 ; 0.0 Nov,1994 Sr-90 SEDIMENE4422, A 0.010.0;0.0 0.010.0;0.0 Nov,1994 H-3 WATER-6534, 6535 A 67.9 i 82.6;83.1 36.3 1 81.2;81.4 106 au
! Table A-4. In-house " duplicate" program.
Concentration in pCi/L' D:te Lv Accepted' First Second I
Cell:cted Analysis Coded Nov,1994 Gr. Beta WATER-6614, 6615 Rejected A
Result 5.012.0;2.1 Result 3.9 1.8 ; 1.9 L Nov,1994 H-3 WATER-6614, 6615 A 30.7 i 81.5; 81.6 -4.1180.0;80.0 Nov,1994 H-3 WATER-6746, 6747 A 2,734.0 1 176.0;411.4 2,851.0 i 178.0;426.6 E Nov,1994 H3 WATER-6767, 6768 A 107.0 1 83.0;84.3 95.0 i 82.0;83.0 Nov,1994 Co-60 WATER-6788, 6789 A -1.9 i 2.2 ; 2.2 -0.213.2;3.2 Nov,1994 Cs-137 WATER-6788,6789 A 1.613.7;3.7 1.8 i 3.0 ; 3.1 Nov,1994 Gr. Beta WATER-6788, 6789 A 5.211.3;1.5 3.0i0.9;1.0 '
l Nov,1994 Gr. Beta WATER-6985, 6986 A 2.0io.5;0.6 2.010.5;0.6 Nov,1994 Gr. Beta WATER-7059, 7060 A 8.6 f l.3 ; 1.9 7.711.7;2.1 )
L Nov,1994 H3 WATER-7059, 7060 A 0.01100.1;100.1 0.0 1 100.1;100.1 Nov,1994 Co-60 WATER-7615, 7616 A 1.312.7;2.7 1.413.1;3.1 m Nov,1994 Cs-137 WATER-7615, 7616 A -1.613.8;3.8 1.113.0;3.0 L Nov,1994 I-131 MILK-7144,7145 A 0.2 i 0.3 ; 0.3 0.310.3;0.3 Nov,1994 K-40 MILK-7144, 7145 A 1,226.8 i 161.0;231.9 1,298.2 1 152.0;233.0 Nov,1994 Sr-89 MILK-7144,7145 A 0.510.7;0.7 -0.5 i 0.8 ; 0.8
{ Nov,1994 Sr-90 MILK-7144, 7145 A 0.8 i 0.4 ; 0.4 1.110.5;0.5 Nov,1994 Cs-137 SOIL-7193, 7194 A 0.110.0;0.0 0.110.0;0.0 Nov,1994Cr. Alpha SOIL-7193, 7194 A 11.714.0;4.2 8.213.4;3.5
[
Nov,1994 Gr. Beta SOIL-7193, 7194 A 22.012.8;3.6 18.012.6;3.2 l Nov,1994 K-40 SOIL-7193, 7194 A 15.910.8;1.8 17.110.8;1.9 l Nov,1994 Co-60 WATER-7594, 7595 A 2.413.0;3.0 -2.7 i 3.2 ; 3.2 l Nov,1994 Cs-137 WATER-7594, 7595 A 1.5 i 2.6 ; 2.6 1.6 i 2.9 ; 2.9 l
Nov,1994 Be-7 GRASS-7246, 7247 A 5.310.2;0.6 5.310.2;0.6 l Nov,1994 K-40 GRASS-7246, 7247 A 5.810.3;0.6 6.0 i 0.4 ; 0.7 l Nov,1994 Gr. Beta WATER-7367, 7368 A 6.0 i 0.6 ; 1.1 4.9 0.5 ; 0.9 Nov,1994 H-3 WATER-7367, 7368 A -67.8 i 80.9;81.5 -98.7 i 79.5;80.7 i i
Dec,1994 Gr. Beta WATER-7288, 7289 A 2.2 i 0.7 ; 0.8 2.610.7;0.8 l Dec,1994 Co-60 WATER-7330,7331 A -0.312.8;2.8 -1.012.7:2.7 Dec,1994 Cs-137 WATER-7330, 7331 A 1.4 i 2.8 ; 2.8 1.212.4;2.4 Dec,1994 Gr. Deta WATER-7330, 73.11 A 2.510.8;0.8 2.410.8;0.9 l Dec,1994 I-131(G) MILK-7391, 7392 A 1.612.8;2.8 -3.014.6;4.6 l Dec,1994 H-3 W TER-7536,7537 A 142.3 1 83.5;85.7 61.0 1 79.8;80.3 Dec,1994 Gr. Deta WATER-7639, 7640 A 5.510.8;1.2 4.810.8;1.1 Dec,1994 H-3 WATER-7639, 7640 A 60.9 1 82.6;83.1 23.6 i 81.0;81.0 Dec,1994 H-3 WATER-7691, 7692 A 117.1 1 84.5;86.0 89.9 i 83.3; 84.2 Dec,1994 Co-60 WATER-7838, 7839 A 3.8 i 2.8 ; 2.9 -0.3 i 2.2 ; 2.2 107
E
=
Table A-4. In-house " duplicate" program.
Concentration in pCi/L' Date Lab Accepted' First Second Collected Analysis Codes6 Rejected Result Result Dec,1994 Cs-137 WATER-7838,7839 A 1.2 2.9 ; 2.9 -0.2 i 2.7 ; 2.7 l Dec,1994 Gr. Beta WATER-7838,7839 A 2.710.8;0.9 3.911.0;1.1 I Dec,1994 Gr. Beta WATER-7940, 7941 A 2.010.4;0.5 2.410.5;0.6 Dec,1994 H-3 WATER-7940,7941 A 212.5 1 85.8;90.5 208.8 i 87.6;92.1 Dec,1994 K-40 MILK-7889,7890 A 1,468.I t 191.0 ; 276.3 1,373.2 1 160.0;245.9 Dec,1994 Gr. Beta WATER-7961,7962 A 2.011.1;1.1 2.6 i 1.1 ; 1.1 Dec,1994 H-3 WATER-7961,7962 A 49.8 82.7;83.0 -10.0 1 80.0;80.0 Dec,1994 Gr. Alpha WATER-8107,8108 A 0.310.8;0.8 0.610.8;0.8 Dec,1994 Gr. Beta WATER-8107,8108 A 1.210.7;0.7 1.510.7;0.7 Dec,1994 Gr. Beta WATER-8086,8087 A 3.310.6;0.8 2.510.6;0.7 Dec,1994 H-3 WATER-8009,8010 A 71.4 82.3;82.9 11.8 i 79.6;79.6
~~All concentrations are reported in pCi/L, except solid samples, which are reported in pCi/g wet. Results are reported as Activity Counting Error; Total Propagated Uncertainty (TPU).~~
~~6 Lab codes are comprised of the sample media and the sample numbers. Client codes have been eliminated to protect client anonymity.~~
Acceptance is bad an the difference of the two results divided by the pooled standard deviation being less than two, where, the pooled standard deviation is the square root of the sum of the squares of the TPU's.
I I
1 1
1 I
108 g
=
s

ML20082Q780

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