ML20042E851
| ML20042E851 | |
| Person / Time | |
|---|---|
| Site: | Byron  |
| Issue date: | 12/31/1989 |
| From: | Pleniewicz R COMMONWEALTH EDISON CO. |
| To: | Bradley Davis NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III) |
| References | |
| BYRON-90-0368, BYRON-90-368, NUDOCS 9005030233 | |
| Download: ML20042E851 (63) | |
Text
{{#Wiki_filter:-- . . . . g' ~> . , . t Byron Nucirer Statitn , 4450 North German Church Road 6' Cimm:nwrith Edison
' Byron. lilinois 61010 i
April.10, 1990 g , I LTR: BYRON 90-0368
- TILE s - 2.12.1718 Mr. Bert Davis .j
. Administrator -'
Nuclear Regulatory Commission Region III : 799' Roosevelt' Road :l Glen.Ellyn, IL 60137 ;
Dear Mr. Davis:
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Enclosed is Part 3 of the.1989 Byron Station Operating Report. Docket Huir.bers STN 50-454.. and STN 50-455. This report contains ., the-results of the Radiological Environmental and Meteorological ~ ')' Monitoring Programs.. Part 1. Facility Operating Experience was submitted under' separate cover in February, and Part 2, Radioactive , Effluents in February and August. Two copies of the report are provided for your use. Two copies will be' forwarded to the Document Control Desk and one copy to the Resident Inspector. Sincerely yours, l YR. Pleniewicz ,/
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Station Manager / Byron Nuclear Power Station RP/vb Enclosure .i s
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BYRON STATION , V ANNUAL ENVIRONMENTAL RADIOLOGICAL OPERATING REPORT p.
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1989 I 1
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. MAR CH 1990
7,f a < m t J*; TABLE 10F CONTENTS
- c. 1 C Page I NTR OD UCTI ON . . . . . . . . . . . . . . . . . . . . . . . . . . . l' SU MM AR Y . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 -
y 1.0 ' EFFLUENTS '[ 3 4 1.1 Gaseous . . . . . . . . . . . . . . . . . . . . . . . . . ...
.1. 2 Liquid . . . . . . . . . . . .. . . . . . . . . . . . . . . . ,3 2.0 SOLID R ADI0 ACTIVE WASTE . . . . . . . . . . . . . . . . . . . . . . 3 U
-3;0 -DOSE-T0 MAN 5
3.1 Gaseous Effluent Pathways . . . . . . . . . . . . . . .. . . 3 1 3.2 Liquid Ef fluent Pathways . . . . . . . . . . . . . . . . . . . 5 3.3 Direct Radiation . . . . . . . . . . . . . . . . . . . . . .
'5 4.0 SITE METEOROLOGY. . . . . . . . . .-. . . . . . . . . . . . .. . . 6 5.0 ENVIRONMENTAL MONITORING . . . . . . . .-. . . . . . . . . .. . . 6 5.1 Gamma Radiation . . . . . . . . . . . . . . . . . . . .. . . 6 5.2 ' Airborne I-131 and Particulate Radioactivity ........ 6 i 5.3 Terrestrial Radioactivity.
H ................. 7 L 5.4 Aquatic Radioactivity ............... .- . . . 7 5.5 Milk . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 5.6 S ampl e Col l ecti ons . . . . . . . . . . . . . . . . . . . . . 8. q; 5. 7. Program Modifications ............... . . . . 8
-6.0. ANALYTICAL PROCEDURES . . . . . . . . . . . . . . . . . . . .. . . 8 ,
i 7.0 MILCH ANIMAL CENSUS . . . . . . . . . . . . . . . . . . . . .. . . 8 8.0 NEAREST RESIDENCES CENSUS. . . . . . . . . . . . . . . . . . . . . 8'
.i y 9.0 INTERLABORATORY COMPARISON PROGRAM RESULTS . . . . . . . . . . . . . 8 7
10.0 ADDENDA ............................. 8 l s
~ APPENDIX I - DATA TABLES AND FIGURES . . . . . . . . . . . . . . . . . . 9 l
Station Releases Table 1.1-1 Gaseous Effluents ................. 10 Table 1.2-1 Liquid Effl uents . . . . . . . . . . . . . . . . . . 18 1 l iii s
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TABLE OF CONTENTS (continued) Page APPENDIX ! - DATA TABLES AND FIGURES Station Releases (continued) Table 2.0-1 Solid Waste Shipments ................ 22 Figure 3.1 Figure 3.1-4 Isodose and Concentration Contours . . . . . . . . . . 34 Table 3.1-1 Maximum Doses Resulting from Airborne Releases . . . . 38 Table 3.2-1 Maximum Doses Resulting from Liquid Discharges . . . . 42 Environmental Monitoring Figure 5.0 Figure 5.0-4 Locations of Radiological Environmental Stations . . . . 44 Table 5.0-1 Radiological Environmental Monitoring Sampl i ng Si t es . . . . . . . . . . . . . . . . . . . 48 Table 5.0-2 Radiological Environmental Monitoring Program .... 49 Table 5.0 Table 5.0-6 Environmental Summary Tables ...... 55 APPENDIX II - METEOROLOGICAL DATA . . ................. 62 APPENDIX III - INTERLABORATORY COMPARISON PROGRAM RESULTS. . . . . . . . 91 APPENDIX IV - REVISION TO THE ODCM RADIOLOGICAL ENVIRONMENTAL MONITORING PROGR AM SI NCE 1986 . . . . . . . . . . . . . . . . . . . . 124 APPENDIX V - ADDENDA ......................... 128 APPENDIX VI - 1989 REMP SAMPLE RESULTS . . . . . . . . . . . . . . . . 13 4 iv _ = _ _ _ _ _ - _ _ _ - - . - _ _ __ _s
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'NTRODUCTION Byron Station, a two-unit PWR plant, is located about two miles east of the Rock River and approximately three miles southwest of Byron in Ogle County, north central Illinois. Each reactor is designed to have a capacity of. ,
1120 MW net. Unit No I loaded fuel in November-1984 and went on line February 2, 1985. Unit . No. 2 went on line January 9,1987. The plant has been designed to keep releases to the environment at levels below those specified in the regulations. Liquid effluents from Byron Station are released into the Rock River in controlled batches af ter radioassay of each batch. Gaseous effluents are released to the atmosphere and are calculated on the basis of analyses of daily 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. Airborne concentrations of noble gases, I-131 and particulate radioactivity in off-site areas are calculated using effluent and meteorological data on isotopic composition of effluents. Environmental monitoring is conducted by sampling at indicator and reference (background) locations in the vicinity of the Byron Station to measure changes in radiation or radioactivity levels that may be attributable to plant opera-tions. If significant changes attributable to Byron Station 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 of less importance. l-1 l l l 4 1
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SUMMARY
Gaseous and liquid effluents for the period remained at a fraction of the Technical Specification limits. Calculations of environmental concentrations 1 based on effluent, Rock River flow, and meteorclogical data for the period indicate that consumption by the public of radionuclides attributable to the plant are well below the regulatory limits. Radiation exposure from radio-nuclides released to the atmosphere represented the critical pathway for the period with a maximum individual dose estimated to be 6.60E-04 mrem for the year, when a shielding and occupancy factor of 0.7 is assumed. The assessment of radiation doses is performed in accordance with the Offsite Dose Calcu-lation Manual (ODCM). The results of analysis confirm that the station is operating in compliance with 10CFR50 and 40CFR190. An assessment of radiation doses from liquid and gaseous effluents to members of the public' due to their activities inside the site boundary during the re-porting -period is not included because it is not applicable to Byron Station. No additional operational controls were implemented in 1989. No measurements exceeded reporting levels but not result of plant - effluents. , The results of the current radiological environmental monitoring program approx-imate those found during the preoperational studies conducted at Byron Station. !~
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4 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 atmos-phere during the year, are listed in Table 1.1-1.- A total of 8.14E+02 curies of fission and activation ' gases was released with a maximum release rate of 3.74E+03 uCi/sec. A total of 2.21E-03 curies of I-131 and I-133 was released during the year. A total of 3.40E-05 curies of beta-gamma emitters and an undetect-able amount of alpha emitters were released as airborne particulate matter. A total of 1.84E+02 curies of tritium was released. 1.2 Liquids Released to the Rock River A total of 3.17E+07 liters of radioactive liquid waste (prior to dilution) containing 0.65 curies (excluding tritium, gases, and alpha) were discharged af ter dilution with a total . of- 3.58E+10 i liters of- water. These wastes were released at a monthly average w' concentration of 1.82E-08 uCi/ml, discharged on an unidentified nuclide basis. An undetectable amount of alpha radioactivity and
-1.29E+03 curies of tritium were released. Monthly 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 Nuclear Center, South Carolina and Richland, Washington. The record of waste shipments is summarized in Table 2.0-1. 3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways Gamma Dose Rates Gamma air and whole body dose rates off-site were calculated based on measured release rates, isotopic composition of the noble gases, and average meterological data for the period (Table 3.1-1). Isodose contours of whole body dose are shown in Figure 3.1-1 for the year. 3
i Based on measured effluents and meteorological data, the maximum dose to an individual would be 6.60E-04 ' mrem for the year, with an
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occupancy or shielding factor of 0.7 included.- The maximum gamma air dose was 2.58E-03 mrad. t Beta Air and Skin Rates The range of beta particles in air. is relat vely small (on the order of a few meters or less): consequently, plumes of. gaseous effluents may be considered " infinite" for purpose of calculating' the dose from beta radiation incident on the skin. Mcwever, 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 mg/cm2 and an occupancy factor of 1.0 is used. The skin dose from beta and gamma radiation for the year was 5.34E-03 mrem. The air concentrations of radioactive noble gases at the off-site receptor locations are given in Figure 3.1-2. The maximum off-site , beta air dose for the year was 1.06E-02 mrad. R'adioactive Iodine The human -thyroid concentrates ingested or inhaled iodine, and the radiot odine, 1-131. Minimal levels released. during routine oper-ation of the plant, may be made available to man thus resulting in a dose to the thyroid. The pathway of interest for this : radio-nuclide is ingestion of radioiodine in milk by an infant. Calcul-ations are performed annually but the levels released from the station in previous years indicate that contributions to doses from J inhalation of I-131 and I-133, and I-131 in milk, are negligible. l l Iodine-131 Concentrations in Air The calculated concentration contours for I-131 in air are shown in Figure 3.1-3. Included in these calculations is an iodine cloud depletion factor which accounts for the phenomenon of elemental ! The maximum off-site concentration iodine deposition is estimated on the ground.3 to be 4.30E-04 pCi/m for the year. 1 1 Dose to Infant's Thyroid l The hypothetical thyroid dose to an infant living near the plant via ingestion of milk was calculated. The radionuclide considered was I-131 and the source of milk was taken to be the nearest dairy farm with the cows pastured from May to October. The maximum infant's thyroid dose was 6.07E-02 mrem during the year (Table 3.1-1). 4
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Concentrations of Particulates in Air Concentration contours of radioactive airborne particulates are shown in. Figure 3.1-4. The maximum off-site level is estimated to be.4.43E-06 pC1/m3 Summary of Doses Table 3.1-1 summarizes the doses resulting from releases of airborne radioactivity via the different exposure pathways. 3.2 Liquid Effluent Pathways The three principal pathways through the aquatic environment for pctential doses to man from liquid waste are ingestion of potable water, eating aquatic foods, and exposure while walking on the j shoreline. Not all of these pathways are applicable at a given .I time or station but a reasonable approximation of the dose can be .l made by adjusting the dose formula for season of the year or type ! and degree of use of the aquatic environment. ' NRC* developed I equations were used to calculate the doses to the whole body, lower GI tract, thyroid, bone and skin; specific parameters for use in the c' equations are given in the' Commonwealth Edison Off-site Dose Calcu- 4 lation Manual . The maximum whole body dose for the. year was .i' 4.76E-02 mrem and no organ dose exceeded 8.88E-02 mrem. 3.3 Direct Radiation - c in section 3/4.11 of the Byron Technical Specifications, 40CFR190 calculations of total dose due to the Uranium fuel Cycle are required only when calculated doses from liquid or gaseous releases of radio . activity exceed certain levels. These levels are twice the following - limits:
- The RETS limits on dose or dose commitment to a Member of <
the Public due to radioactive materials in liquid effluents from - each reactor unit (1.5 mrem to the whole body and 5' s mrem to any organ during any calendar quarter; 3.0 mrem to the whole body and 10 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 reat-L tor unit (5 mrad for gamma radiation or 10 mrad for beta.
radiation during any calendar quarter; 10 mrad for gamma radiation or 20 mrad for beta radiation during any calendar year). ,a The RETS limits on dose to a Member of the Public due to iodine-131, iodine-133, tritium, and radionuclides in part-K iculate form with half-lives greater than 8 days in gaseous effluents released from each reactor unit (7.5 mrem to any , organ during any calendar quarter; 15 mrem to any organ I during any calendar year)., i -
- Nuclear Regulatory Commission, Regulatory Guide 1.109 (Rev.1).
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p, y L During the period January to December,1989, Byron Stations did not i exceed these criteria. L 4.0 SITE ME,TEOROLOGY ; A summary of the site meteorological measurements taken during each quarter of the year is given in Appendix II. The data are' presented as cumulative joint frequency distributions of 250' level wind direction and wind speed class by atmospheric stability class determined from the temperature diff-erence between the 250' and 30' levels. Date recovery for these measure-- ments was about 99.6%. 5.0 ENVIRONMENTAL MONITORING Tables 5.0-1 and 5.0-2 provide an outline of the radiological environmental I monitoring program as required in the Technical Specifications. Sampling . locations are shown in Figures 5.0-1 through 5.0-4. Concentrations of radioactivity in' various media are sumarized in Tables 5.0-3 through 5.0-6. Tables listing all data are presented in Appendix VI. Specific findings for various environmental media are discussed below. 5.1 Gamma Radiation External radiation dose from on-site sources and noble gases released to the atmosphere was measured at nine indicator and three reference (background) locations using CaSO 4 :Dy thermoluminescent dosimeters l (TLD). Additional TLDs, a total- of 64, were installed on September 28, l 1981, such that each sector was covered at both five miles and the . l site boundary. Quarterly external radiation dose at twelve air samp.. " , ling locations averaged (14.6 4.6) mR and was similar to that measured H in 1985 (14.4 mR), 1986 (14.9 mR), 1987 (15.3 mR), and 1988 (15.2 mR). The differences are not statistically significant. 5.2 Airborne I-131 and Particulate Radioactivity 1 Airborne I-131 concentration remained below the LLD of 0.07 pC1/m3 throughout the year in all samples. ! Gross beta concentrations ranged from 0.005 to 0.066 pCi/m3, and averaged 0.0g6 pC1/m3, similar to _the average concentrations in 1985 (0.026 pC1/m ),1986 (0.026 pCi/mo , except for the period from- May l 12 through June 9 when it was influenced by the reactor accident at-L Chernobyl), 1987 (0.027 pC1/m3), and 1988 (0.031 pC1/m3). All' gamma-emitting isotopes activities were below their respective LLD levels. No radioactivity attributable to plant operation was detected in any of the samples. l 1 1 1 l 6
4 i 5.3 Terrestrial Radioactivity Vegetables were collected in August and October and. analyzed for gamma-emitting isotopes. In addition, green leafy vegetables were analyzed for iodine-131. All isotopes were below the limits of de- . tection indicating that there was no measurable amount of radioactiv- ' ity attributable to the station releases. Identical results were obtained during the period 1985 through 1988. > Well water was collected quarterly from two off-site wells and ana-lyzed for gross beta, tritium, and gamma-emitting isotopes._ Gross 4 beta concentration was below LLD of 2.6 pC1/1 in all samples and was-similar to that measured in 1988 (2.0 pC1/1) and lower than in 1985 (7.3 pC1/1), 1986 (7.5 pt:1/1), and 1987 (7.5 pC1/1). Tritium was detected (232 pCi/1,in ene samp(le 1986 <200(236 pCi/1) and pCi/1),1987 waspC1/1) (<200 similar and to that = in 1985 in 1988 (260 pCi/1)). All other results were below the lower limits of de-tection. The results were similar to those obtained in 1988. r 5.4 Aquatic Radioactivity Surface water samples were collected weekly from three locations. Weekly samples were composited monthly and- analyzed for gamma-emitters. Quarterly composites were analyzed for tritium. Cesium- i 134 and 137 concentrations were below the LLD level of 10 pC1/1. Tritium concentration was below the LLD of 200 pCi/1 in all samples collected from Woodland Creek (BY-09) and Upstream (BY-13). These levels were similar to those obtained in-1985 through 1988. Downstream from discharge, tritium averaged-.847 - pCi/1, ranging from 532 to 1470 pC1/l. Cs-134 and Cs-137 levels were below the LLD level of 10 pC1/1. All other gamma-emitters were below their respective LLDs. Elevated levels of tritium at discharge pipe are attributable to the station operation. These- levels were similar to those ob-tained in 1985 through 1988. Sediment samples were collected two times, from one control and one indicator location, and analyzed for gamma-emitters. All concentra-tions were below the lower limit of detection. Level s of gamma radioactivity in fish were measured and found in all cases to be below the lower limits of detection for the program. The resulis were identical to those obtained in 1985 through _1988. 5.5 Milk s Milk samples were collected monthly from November through April and bi-weekly from May througs ]ctober and analyzed for iodine-131 and m gamma-emitting isotopes. Ivdine-131 level was below the LLD level of 0.5 pC1/1 in all samples. 7 4
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V ,< Cs-134 and- Cs-137 were below the LLO level of 5 pC1/1. All other . .! gama-emitting isotopes, except naturally-occurring K-40, were below their respective .LLDs. There was no indication of the effect on the environment due to station operation. The results for I-131, Cs-134
- and Cs-137 were identical to those -obtained during the period 1985 through ' 1988, except during several. months following accident at Chernobyl, which occured on April 26, 1986. During those = months I-131 ranged from 0.9 to 58.6 pC1/1, Cs-134 ranged from' 5.8 to 10.7 pC1/1 ' and Cs-137 ranged from 5.3- to 17.8 pC1/l .
5.6 Sample Collections All samples were collected as scheduled except those listed in
-Listing of Missed Samples, Appendix VI.
5.7 Program Modifications In April of 1988, milk farm at location BY-16, -K. Druien, 3.3 mi' 134' was changed- to BY-25, B. Leupkes, 3.7 mi- 190'. In February of 1989, milk farm at location BY-20 was changed from Ed Seabold, 2.5 mi' @ 41* to K. Reeverts, 2.1 mi 9 37*. For additional changes in the program see Appendix IV. 6.0 ANALYTICAL PROCEDURES Procedures used during the period covered by this report remained essent-1 ally unchanged. A sumary of the precedures used for analyzing radio-activity in environmental samples is given in Appendix V of the report for the period January-December 1988.
/.0 MILCH ANIMAL CENSUS A census of milch animals was conducted within five miles of the Station.
The survey was conducted by " door to-door" canvas and by information from Illinois Agricultural Agents. The census was conducted by L. Coleman on August 21, 1989. 8.0 NEAREST RESIDENCES CENSUS The census of nearest residences within a.five (5) mile radius, was conducted by L. Coleman on August 21, 1989. Results of milch animals and nearest residence census are presented in Appendix VI. I 9.0 INTERLABORATORY COMPARISON PROGRAM RESULTS Interlaboratory Comparison Program Results are presented in Appendix III. 10.0 ADDENDA l-
- l. Addenda for January - December,1989, effluent and waste disposal semi-annual reports are presented in Appendix V.
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e ! TABLE 1.2-1 (continued) > l-
- l. SV90It sesCLEAR Penna STAlless L Eff ttfEset Ase ten 51E DI5peSat SEsegammanna sEpeef fee January - June,1989 l-184U89 EffttIEsets
.15alerEs afstatri I emitti NY IFEBReallRY I feutCH I Ist --- rral april i IWLV I JUIE I 2 tid ---a
- 8. Iequid Effluents Sr-at ti - - - I - - -
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<a na Sa/ta-148 5_55E-5 1.68E-5 2_eGE-5 B_55E-5 1_24E-E 1_7M -5 1_17E-E e_2sE-i Ma-133 2_77E-1 4_ BM-2 4.7E-2 1_7 N- 1 t _1X 2 7_7ar- 2 t _ %X 1 2_ ant-1 r $ me-n35 2.inE-a 2 ass-a a mr-5 a 7er a <a a a 6.84E-5 5.00E-5 1.26E-4
. Others (Specifyl Cr-51 1.72E-2 9.30E-3 8.10E-3 3.46E-2 1.0K-2 8.5AE-3 2.41E- 3 2.1H-2 ! h 54 4.18E-3 2.50E-3 3.6M-3 1.03E-2 1.26E-3 6.02E-3 2.95E- 3 1.02E-2 Fe-59 1. 39E-2 5.44E-3 6.90E-3 1.37E-2 2.40E-3 3. 26E-3 1.69E-3 7.3M-3 Co-57 5.41E-5 9.76E-5 5.00E-5 f.12E-4 9.04E-6 1.7N-4 4. Set-5 2.26E-4 iib-95 B.70E-3 3.42E-3 4.84E-3 1.70E-2 1.21E-3 4.2eE-3 2. lW-3 7.64E-3 Zr-95 4.84E-3 1.84E-3 2.72E-3 p.40E-3 6.02E-4 2.4M-3 I.12E-3 4.17E-3 Sb-122 (LLO <tLD <tLB rLLD <LLD (LLS <tLB (LLD Sb-124 3.51E-4 3.35E-5 4.30E-4 p.20E-4 2.30E-5 1.29E-5 <tLS 3.59E-5
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v ., s 3 .- TABLE 1.2-1 (continued) sween uuttEma rewa starseu EfttuEar ass unsti etspo5mL w m - mErsat renJ"IF'8'C- II8I LIguse Eartums 4 t== rs ass anut I naasts I JULY g AUG g Mf'T I - ::ma OCT g IIDW g OEC 3 O. Ligold Efflesets ; i s,-me En --- --- - --- <LLS --- --- --- . s,-en --- --- ---
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to matta-tea (LLB 3.87E-5 3.81-6 4.25E-5 3.03E-6 9.79E-4 p.31E-5 1.0FE 3 i
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m -In 2.14E-1 5. 7M-2 2.57E-3 2.74E-1 5.79E-4 8.7W-2 3.87E-1 4.75E-1 m.-13s inw-5 <a a <a a a 3.eu-5 <na 2.6 K-5 6.2tE-5 0.8M-5 ethers (Specify) Cr-51 1.16E-4 2.30E-4 <tLS 3.46E-4 <tLS 1.2tE-3 2.2W-4 s.44m-1 Mn-54 1.0M-3 9.09E-4 1.80E-3 2.9K -3 3.82E-4 1.32E-3 9. 3M-4 2.64E-3 Fe-59 1.59E-4 8.13E-5 <LLS 2.40E-4 (RS 2.67E-3 1.92E-4 2.77E-3 nin-95 5.60E-4 4.40E-4 t.72E-4 1.20E-3 4.11E-5 6.6tE-4 3. 3K-4 I.04E-3 Zr-95 2.23E-4 1.57E-4 1.20E-4 5.00E-4 1.7M-5 1.7eE-4 2.2eE-4 4.14n-4
- Ee-131m 1.33E-3 2.7 M -4 (LLS 1.61E-3 (LLB 7.53E-4 3.aM-3 4.5aE-3 Xe-133m 6.57E-4 5.61E-5 <tLB 7.1X-4 <n s a 5.12E-4 2.97E-3 3_4aE-3 Mo-99 7.00E-5 (LLB (RB 7.0AE-5 <t i a 1.eaE-5 <aaa 1.maE-1
_Ln-65 <tLB 1.70E-5 <e n n 1_7M-5 <a n a 3 mar-1 <a n a 3_ au -5 Sn-ll3 <LLD 1.16E-5 1.51E-5 2.67E-5 <t a a <a a n $ _ eM-5 5_au-5 Co-57 <LLS (LLB 1.6AE-5 1.6AE-5 <a a a 1.1 M-5 1.17E-5 2.2EE-1 Sb-125 <tLD <tLB 3 2X-5 3.2X-5 2.4E-4 <a a a s. sat-5 3.1af-4 Br-82 (LLD (LLB <tLB <tia 5. 7 X-6 <a a a 1.5g-4 1.Eu-4 Ar-41 <us <a a a <t a n <t a n (1 a a 2.MK-5 3.46E-6 2_ EM-5 , 84-133 <LLD (LLB <LLB (LLS <LLB <i t a 4.011-5 4.aM-1 . i Fe-55 --- --- --- < tis --- --- --- i l
- Analysis completed by offsite vendor. Reselts are not available at this time.
i l- - _ _ _ _ _ _ _ _ _ _ m _ , _ _ , - _ . . _ . __+____-___m_.____-______-________________________________.__________._m .
l TABl.E 2.0-1 I Sve ut le ttEAR N eE t SWAf90s EfftWest Ae3 MhSIE M1relAt SEsetassment AEMe.1 l SALES AA300AfffwE tenSIE l seases JAs. MAe 1989 i I etsposetten of easteelet 3 l maar am.au smata._ r w a _sa _ ha amaa-a== - -
- ^ as t= - -
' - ' -am. - - - - am, = = saa a t=naan mar -- -
' Dewatered Resta. Class A. LSA. Liner in Cask, none Enclusive use Barnwell. SC 177.3 1.46 l-3 l
Exclusive Use Barnwell. SC 135.8 330 . 1-9 Dewatered Resta. Class C. LSA. HIC in Cask. none . Enclusive Use Barnwell. SC 135.8 53.7
- l-11 Dewatered Resta. Class C. LSA. HIC in Cask none Dewatered Resin. Class A. LSA. HIC in Cask, none Enclusive Use Saramell. SC 178.9 9.69 1-20
~
1-26 DAW. Class A. LSA, drums, none Emelusive Use vendor fen- 300.6 0.39 N m Lanpection (final burial volune) i Dewatered Resin. Class A. LSA. HIC in Cask, none Exclusive Use Barnuell. SC 178.9 24.1 1-30 l i sesseety sotats: 6 line 419 1
- '- <+- - ~ * , ._. , __ , _ _ _, _ _ _ _ ,,_, _ __ _
h
TABLE 2.0-1 (continued) sogen auttEAa fe we svarsen EfftWest ABS emSWE MSfolat MMauggght MfMT satse anseenCrew innset sesseet fra MAa teme es iae .f si.e.,eei I ~ I j aart sa.ar,tmana.. r e -- _sm _ satadas '
-- at ?_- - 1 -"--a - * - mer ~ ' asa n t rama mar -- -
2-1 Dewatered Resin Class A. LSA. Liner in Cash, none Esclustee 'dse Bernme11.5C 177.3 0.1T Dewatered Resin. Class A. LSA. Liner in Cask, none Enclusive Use Barnwell.5C 177.3 2.33 l 2-10 2-15 Dewstered Nesta. Class A. LSA. Liner in Cask, none Esclusive Use Bernmell.5C 177.3 4.46 2-24 DAW. Class A. LSA, drums, none Enclusive Use To vendor 307.1 0.21 1- for (ffeel burieI volume) Compaction av G3 I I L F i l I L i i
"' MI' 4 3 39 F.51
-. - . . . . . - _ .. . , - - . ~ _- __ ___ _____ ___ . . _ _ _ _
ar l { TABLE 2.0-1 (continued) evuem auttEma femte starsam L Ettamm as tenSM stSpelat sisulassaunt effett ! 10Lle emettatitW tetSM , eenne IWRCN Man 1999 _ l l l es ins .e m .rs.i j _s _ satamaa a-- - -
-- er sc -
- - -am. - - -- mar - - art ,a c ,tma ame -> --
_t&IL Immurlottam_ tamaa 3-8 Dewatered Resin. Class A. LSA. Liner in cask. none Enclusive Use Bernme11. SC 171.3 1.07 l 3-13 Dewatered Resin. Class A. LSA. Liner in cask none Enclusive Use Baromell SC 177.3 0.M 3-17 Dewatered Restn. Class A. LSA. Liner in cash. none Enclusive Use Bernwell. SC 177.3 1.81 l' 3-22 Dewatered Restn. Class A. LSA. Liner in cask. none Enclusive Use Barnwell. SC, 177.3 0.76 l 3-29 Dewatered Resin. Class A. LSA. Liner in task, none Exclusive Use Barnwell SC 171.3 e.78 l i L I
. . 4 1
! , = vats: 5 m7 5... 1
/
, , , .. .-. .- ~ . _ . . . , . .. . . . . , . - _ , _ - _ ~
TABLE 2.0-1 (continued) sonen easttEmo powe statsen -
- EfftWEsst ABS 1ARSTE DESFWlat SEtelasBAbbt SEFORT Sette massentitwE tenStt passges APRIL was 1989 es., as .f sene.rs.1 marr an..,,amasan riman _s _ sal ads f = - -- - - - amm 3
-- af 31-- -
-=-w== att a t- Ama h -- -
4-10 DAU. Class A. LSA. Seavan, none Exclusive Use To Vendor for *I280 0.33
)
Compection 4-17 DAW Class A. LSA. Seaven. none Exclusive Use To vendor for *1280 0.I1 Compaction 4-19 Dewetered Resin. Class A. LSA. Liner in cask. none Exclusive Use Barnwell. SC 171.3 2.20 U i i i t b I l "I **EII 3 2740 2.48
- Volume sent to venitor. This is not final bwetal v.lems.
TABLE 2.0-1 (continued) f suces aattfan peute $satsen EfftEset age unSft M9pmat SEselaannata SEpWV i-SALES GASIGACTtwE tens M sempes tutV VEAR 1999 , sespee as .e sentereet , 3 MIf h errlattam_ tt-- _ gama . Salidt f-!- " - -
- ^ ^ ^ af L -
"--- -Ram --h"" aft a t rtas far "" ^
5-5 Dewatered Resin. Class A. LSA. Liner la Cask. none Exclusive Use Barnuell. SC 177.3 1.65 4 5-11 Spent Filters. Class A, HIC in cask aone Enclusive Use' Barnwell. SC 73.4 3.92 5-16 Dewatered Restn. Class A. LSA. Liner in cask none Exclusive Use Barnmell. SC 177.3 0.68 5-26 Dewatered Resin. Class C. LSA. HIC in cask, none Exclusive Use Barnwell. SC 73.4 269 ; BGBWeety vesatS
- 4 gg v5 t
A, a
.- . at,a .4,.r __ .--m--..+ * --4 m __. _a c A. ._he--- ..a__
- i
=
t , j e 2 l 4- ! t 1 i J , 6 t d . j d d 2
~
i l . 1 I dd t 18 5 11 a a
~
a s'II a 3 R l- ". 8 .. ' *- ,
. 3 l=lgl s I:E I g Is i ; ;
. 2
" I '
W W E w w w i a e I-l .
! ?! l ,
ii 3 i.
, 1 2 3 M M g a x 5
I I.b 3
< J J l . .
,G G E d 3 L% %
2 2 1 i',3 t e 3 t Jj 3 S I 3 . 27
- v-+ + 4 -ye 5-e- +-# .2 , -t ,_,-- - - - ' - ' ' ' * ' '
TABLE 2.0-1 (Continued) eVWWI tesCLEAR pedER ST4f fes Efftweet AIS ten 5TE M$felat SiteIAssesnt effMT sette emetenCitw innsit smette Julv vtaa 1989 Dispeeltlen of festerial 3 aan famarrlattaa. O man _ Imme . Solidifmina "
^
"" ' af Irm--t a a = - - sm. mn- par " * ^ ift h turima mar ""
^
e 7-5 Dewatered Resin. Class A. L5A. HIC in Cask. leone Exclusive Use Barnwell 177.3 14.6 7-7 Dewatered Resto. Class A. LSA. Liner in Cash, leone Exclusive Use Barnwell 177.3 4.72 1-13 DAW. Class A. L54. Seaven, lione En iusive Use Vendor for 297.0 0.29 Compaction (Final 8erial Volume) 1-19 Dewatered Resin. Class A. LSA. Liner in Cask, leone Exclusive Use Barnwell 177.3 2.16 souvesty votats: ' 4* 829 21.s
. .-- . _ _m_ .-- _._.__m_- _ _ _ _ _ _ - - -
. I
.. a r 2 a
g 2 6 5
, s .
2 9 i p S 0 $ _ g c 3 . g ) g e . m u
- l o -
V 3 3 l a a - n 1 0 i 1 3 r 1 3 u B w p l a n i _ i f ( m t , n a . r o e r g l l oi f t t e c s a a w n r o p a 2
) t r d m .
n m. a n o d M a B eC e Sa s m v u n I T s E9 89
~ A lat o s 1 i T s n t :
t S E u ' s n S - e e t o R E t v E R - s s a c W ai AE - U U v ( O5 r - e o P oC V e s P n r v v 1 T i i y . R S e s s 0
- A I s E Ds at f a l u l u n i
L c m C t ms u c o 2 - x x , U f N5 not ev ' E E n . E - L Nt e t A B 0 e . A aest vf i t . T oA w - o T - N s E - I t e i m n f a i o f t l E - , f i k d s a a l C a n S i r
. e s n c i
. L t.
e e . e n s m- A 5 o L N
- e. 1 . . .
. A s
. m i s u t s r a D
- s. l
.a pm C .
A
.a . 5 s i n L eC i s .
e A s R a s l d s t r, e a r l i r e C _ t a . n
- u. w e
W A i D D 1 4 E 1 2 T - a 8 n 8 L
TABLE 2.0-1 (continued) , ovaBu saattEma mwa svarian EFftWEtet AAS tanSTE el5Fe5AL SEsegammaana aEP3al seLie omvenCstw innsit 8SIITH 5epteseer YEma 1989 stapestaten of sentertal 8 3 marr samarriattaa_ [Eman Imma - Solidifmiam ^-- " " ' af tr------a m..alamataa ** - par m- ' afa n [matma far w ^ 9-15 Dewatered Resin Class A. L5A. Liner in Cask, none Exclusive Use Barnwell. SC 177.3 4.41 9-22 Dewatered Resin. Class A. L5A. Liner in Cask, leone Exclugive Use Barnwell. SC 117.3 1.06 I l 1 h i ! 1
#GlefteLY lefAL5: 2* 355 5.41
, , , . w < a w , , - --
TABLE 2.0-1 (continued) SVSON GAKLEAR FOIES $3418410 EffLIElst AIS Mh5ft DISFD$At SEsel- AEFSBf
$4 Lie aADIGACIEW unSTE ISIstM ac'
- r MAe test plapesillen of testerial hima par "" -
aan a n.u s t a l c a... v.ma _ Smindif.ima "-- ' - ' af In------t h at u taa " - Far m' - sia n Emclusive Use Barnwell. SC 171.3 0,.205 10 4 Dewatered Resin. Class A. LSA. Liner in Cask. Isone Exclusive Use Barnwell. SC 117.3 1.36 10-16 Dewatered Resin Class A. LSA. Liner in Cask. Ilone Enclusive Use Barnwell. SC 139.1 1.14 I 10-16 Dewatered Resin. Class A. L$A. Liner in Cask. Isone i W i Eactustve Use vender for 314.7 0.91 l 10-30 DAW Class A. LSA. Drums. Isone Compactton (Final Surial Volume) l i ; i i I I: 8818tt0LY 19f AL5
- 4 M 3.67
] TABLE 2.0-1 (continued) - Sve0N IRICLEas p0MER STATitN EffttfENT Ase tenSTE Bl5MSAL SeeeImammana aErget SOLIS BASIGACitwE ten $tt pguin Isovember yEAg 1989 I Dispeettien of Meterial I
. fuen _1alldifmina "
^ ^ ^ af Ir - ---t Besa n _a g , an _ p., un - ggg g g,, g , p , m a - - - -
a&If theuriattaa_ Cham 11-1 Dewatered Resin. Class A. LSA. Liner in Cask. Fene Enclusive Use 8ernwell. SC 177.3 0.094 DAW (Fuel Racks). Class A. LSA. Steel Bon, leone Exclusive Use Richland. W 78.0 5.53E-5 11-2 Exclusive Use Rie/41and. W 190.0 7.94E-5 11-2 DAW (Fuel Racks). Class A. L5A. Steel Box. Isone 11-6 Dewatered Resin. Class C. L5A. HIC in Cask. feone Exclusive Use 8arnwell. SC 73.4 271 U Exclusive Use Barnwell. SC 135.8 75.4 11-20 Dewatered Resin. Class B. L5A. HIC in Cash, leone 11-20 VAfl. Class A. LSA. Drums. Isone Exclusive Use Richland. W 630 0.86 1 11-27 Dewatered Resin. Class A. LSA. Liner in Cask, leone Exclusive Use Barnwell. SC 135.8 9.01
~*
s septesLY I6 tat $ 7 1420 3%
-. . + . - ,, , . , - - , ...,.~.-,e. - ,n.. , , - . - . , , . . ,
= .
F TABLE 2.0-1 (continued) evegu muCLEAR PWEe Stafleu EFFLUEast Ass tetSTE MSPOSAL SEsclamassas atreet SOLIS AASIGACIIVE tahSTE 1989 i gange, December ygag Stepeeltlen of testerial 3 ^
. Imma
" af Ir - - t *--*^- ^ tam ' * - Par h^ ^ fit n fmrama mar "'"
a&If famarriattam_ C1m== Salldifulas ^- Exclusive Use Vendor for 320.2 8.28 12-4 DAW. Class A. LSA. Drums. None Compaction Exclusive Use Richland. W 197 5.36E-6 12-5 DAW (Fuel Racks). Class A. LSA. Steel 80s. Ilone e Exclusive Use Barnwell. SC 178.9 3.1 12-5 Dewatered Resta. Class A. L5A. HIC in Cask. None Exclusive Use Richland. W 17.5 7 16E-6 12-12 DAW (Fuel Rocks). Class A. LSA. Steel Bon. None
~
12-13 Dewatered Resin. Class A. L5A. Liner in Cask, leone Exclusive Use Barnwell. SC 12-18 DAW, Class A. L5A. Drums. None Emclusive Use Richland. W 630 8E-4 12-19 DAW. Class A. L5A, Seavan. None Enciestve Use Vendor for *928 0.08 Compaction , 12-20 Dewatered Resin. Class A. LSA. Hl0 fr. Cask, leone Exclusive Use 8arnwell. 50 177.3 1.11 12-26 Dewatered Resin. Class A. L5A, HIC in Cask. None Exclusive use Barnwell. SC 177.3 0.703 l P l l ausstselv totAts: 9* 2800 34.8
- Volume sent te vendor. This is not fenal (nertal veieme.
_ _ _ _ _ . _ _ . __ _ . . _ . _ . _ _ . _ _ _ _ ~ ______ _ . . . _ . . _ _ _ . . _ _ _ . 1 l FIGURE 3.1-1 ,
, Estimated Cumulative Gamma Dose (in mrem)
R 10 0 ' 1 l from the Byron Station for the period ' January-December 1989 3 ... Isopleth Labels r yt ~0 p.f 25 g I Small figure - multiply by 10 5 5 Large figure - multiply by 10- ( l ;. 100 m F j loo" , s% 4
/ !
\_
o , e .. I RoCKFoRO ,
,, yf - - - - -
( 6 1 10
-:o
'*' /
( r.,,..... mg 10 0 3 l Inn l ,
.. .- 1 . " " ' ' ;/
i i
. I 1
- o,.... N - e.
l
- p. i 20 l
[ =
), .. ..ii. i j oisee ' ' *j'*
l \ 2 l 34 ) l o. s s. to. is. to mi
, , - . . _ . _ .1
- l. .
. FIGURE 3.12 Estimated Total Concentrations (in pC1/m3) of Noble Gases from the Byron Station for / 500 the period January-December 1989 r 250 7
Isopleth labels N .... a Small figure - multiply by 10'I 00 Large figure - multiply by 10*1 k ! ' 250 . l
\ /
. N_ 3
- o e p
- p.ut..ie. ,oc ,,
.?N f ,_
t 3,,........ .,, , m a m ,, _. ioo 1 r l e,,
- y .. ',"*" lI l 15 25 gl g..
. ,...- .n.
s o.. Y...... MD I d
I I FIGURE 3.1-3 e-Estimated Total Concentrations (in pC1/m3) ; of lodine from the Byron Station for the . 10 period January-December 1989 a f 1 ... i Isopleth labels 30 p,l l Small figure - multiply by 10-6 Large figure - multiply by 10-6
" 250
\ l ,
, / l 3i 0 e t o.
J ' l ROCKFotD, 80 ;id l (h I
/I 25 to I 1
H........ . ,
\
, .. T
= So
\ l "L . , , ,,..
l, f..... 2.5
- 10 G "
h ,/ n. Disea * * *j "
/
^
4 o 5 lo* is* 2,o mi 36 m.
l1 FIGURE 3.1-4 Estimated Total Concentrations (in pCi/m3) [ of Particulate Matter from the Byron Station for the period January-December 1989 r 250 50 , Isopleth Labels
- Small figure - multiply by 10-8 Large fi9ure - multiply by 10-8 T
( %\ ( So ,! . g t
. ~ ;
100
. A _
0 e t
- N 88*i RoCKFoRo,,
/ i o g
j _--- 2 0 -
- ...- i
\,r.,,.see. ,
100 te s (i ,, e, u.,,se 4 I g3 u . o,....
*e.i. M
...n.
5 o.3-x 7 - o 5 'O @ 8,0 '"' 37
o 4 TABLE 3.1 1 8YRON UNIT ONE 1989 ANNUAL REPORT RAE!nUR 00888 RSSULTING FRon AIR 90RNE ESLEAst8 PERIOD OF R$ LEA 88
- 01/01/09 TO 12/31/09 CALCULAfs0 01/16/90 INFANT RSCEPTOR 1ST 2ND 3RD 47s TYPt 00ARTSR QUARTER QUARTER QUARTER ANNUAL JAN-RAR APR-JUN JUL-88f OCT-DSC GAnnA AIR l.275-05 9.378-05 5.875-04 3.275-04 1.068-03 (nRAD) (88 ) (88 ) (88 ) (85 ) (88 )
teTA AIR 2.315 04 3.978-04 2.438-03 1.338-03 4.308-03 (nRAD) (st 1 (st ) (sa 1 (ss ) (se ) TOT. BODY 1.348-0$ 2.308-15 1.505-04 8.393-05 2.718-04 (naan) (85 ) (St I (88 ) (SR I (St ) SRIN 1.10B-04 2.018-04 1.228-03 6.755-04 2.218-03 (ARBK) (58 ) (88 ) ISB ) (SB ) (88 ) ORGAN 2.935-02 5.018-05 6.328-04 1.208-03 3.118-02 6 (nBan) (Ws ) (Ws ) , (Ns ) (Ws ) (Ns ) Tavhoto TRYRotD TarR0!D TRYRO10 TaYR010 7 7518 !$ A REPORT POR TSB CAL 8NDAR YEAR 1999 ConPL!ANCE STATUS - 10 CPR 50 APP. ! INFANT RSCEPTOR
------------ % OF AFP !. ------------
QTRLY 18T 075 2ND OTA 3RD OTR 47s OTA YRLY % or OsJ JAN-MAR APR=JUN JUL-SEP OCT-NOV OBJ APP.! GAnnA AIR (neAD) 5.0 0.00 0.00 0.01 0.01 10.0 0.01 asTA AIR (nRAD) 10.0 0.00 0.00 0.02 0.01 20.0 0.02 TOT. D00Y (MSRA) 2.5 0.00 0.00 0.01 0.00 5.0 0.01 BRIN (nSan) 7.5 0.00 0.00 0.02 0.01 15.0 0.01 ORGAN (MRan) 1.5 0.39 0.00 0.01 0.02 15.0 0.21 TRYSCID TRYS0!D TNYR010 TRYROID TNYRO!D RBSULTS RASED UPON ODCm REVISION 11 UPDATE CS204 FESRUARY 1986 l l 38 g -
-e,-
m nm-- e w ,,we- n
i
.- 1 I
s I J J i
)
i TABLE 3.1-1 (continued)
> aYRON UN:? CNs 19e9 ANNUAL RsPORT :
RARINUM 00888 RBOULTING PROR A!RSCRNE RELEASES ! PsRIOD OF RELSA88 - 01/01/09 TO 12/31/09 CALCULATSD 01/16/90 ADULT RSCRPTOR 1 18T 2ND 3RD 475 TYPE QUARTBR QUARTsR OuARTet QUARTea ANNUAL Jam-AAA APR-JUN JUL-SSF OCT-DSC
- GAMAA AIR $.27B-05 9.378-05 S.878-04 3.27s-04 1.048-03 (nRAD)
BETA Att (SR ) (se ) (88 ) (as ) (St ) 2.318-04 3.975-04 2.438-03 1.33s-03 4.30s-03 (RRAD) (88 ) (se ) (se ) (se ) (ss ) 707. BODY 1.345-0$ 2.345 4 l 1.508-04 0.393-05 2.718-04 (MREN) (SR ) (88 ) (58 ) (88 )- (88 ) Satu 1.188-04 2.018-04 1.228-03 4.758-04 2.215-03 (nBam) (85 ) (38 ) (se ) (sa ) (Ss )
- ORGAN 1.908-02 7.585-05 3.758-04 6.145-04 2.078-02 I
(RREN) ( NS ) (BSE I (RSS ) (BSE ) (NE ) L , TRYROID 787R010 75YR0!D TRYROID TWYRotD i- TSIS IS A REPORT POR 785 CALENDAR YEAR 1909 > l i ConPL!ANCE STATUS . 10 CPR 50 APP. I i ADULT RBCEPTOR
~
L
............ g of AFP 3, ............
OTALY 1ST QTR 2ND QTR 3RD QTR 4Tu 078 YRLY % CP 04J JAN-AAR APR-JUN JUL-Stt CCT-NOV OBJ APP.! GAnnA AIR (nRAD) S.0 0.00 0.00' O.01 0.01 10.0 0.01 BatA AIR (RRAD) 10.0 0.00 0.00 0.02 0.01 20.0 0.02 TOT. 90DY (NREM) 2.5 0.00 0.00 0.01 0.00 5.0 0.01 SRIN (MatR) 7.5 0.00 0.00 0.02 0.01 15.0 0.01 ORGAN (MRaa) 7.5 0.26 0.00 0.01 0.01 15.0 0.14 TsYRotD TRYRotD TRYROID TRYR010 TNYRotD BR$ULTS RASED UPON ODCM REVISION 11 UPDATE CS204 PBSRUARY 1986 39
i l l R TABLE 3.1 1 (continued) a 1 i 1 SYa0N UNIT TWO 1949 ANNUAL asp 0af RARINUn DOSS 3 eBSULTING FRon Alst0 mms astsA8ss Psa!0D 0F ast8ASE - 01/01/09 TO 12/31/09 CALCULAfso 01/14/90 INFANT asCsPTOR 1ST 2ND 3a0 475 TYPs 00 Antes 00Aatta QUAafsa 00Aafsa AwwUAL JAN-ras APa-JUN JUL-8sP OCT Dsc GAAAA Att 1.738-04 5.25s-05 4.845-04 0.095-04 1.525 03 i (ntAO) (St ) (8s I (88 ) (Se ) (88 ) I DsTA Ala 7.245 04 2.30s-04 2.005-03 3.235-03 6.193-03 (naADI (St ) (8s I (St ) (88 ) (8s ) TOT. 800Y 4.205-05 1.368 46 1.25s-04 2.00s.04 3.898-04 l (nass) (8s ) (St ) (8s I (8s ) (8s ) 1 SEIN 3.57s-04 1.195-04 1.015-03 1.648-03 3.135-03 (Masal (St ) (8s ) (8s ) (8s ) (8B ) i CaGAN 2.935-02 5.07s-05 2.115-04 4.758-06 2.965-02 " (naan) (Ns ) (Ns ) (Ns ) (Ns I (Ns ) TuYm0!n TaymotD TuYROID TRYm0!D TNYactD TWIS IS A asPost F0s Tas CALsNDAa YsAR 1989 ConPLIANCs STATUS . 10 Crt 50 Art. t ' l INFANT asCsPTOs
............ g or app 1. ............
OtaLY IST 07a 2No OTa 3RD 07a 4Ts 073 YaLY 4 0F OSJ JAN AAR APR-JUN JUL-8st OCT-NOV OnJ APP.! GAnnA Att (naAD) 5.0 0.00 0.00 0.01 0.02 10.0 0.02 asTA Att (naAD) 10.0 0.01 0.00 0.02 0.03 20.0 0.03 ( TOT. DoDY (Masa) 2.5 0.00 0.00 0.00 0.01 5.0 0.01 ' ! SEIN (naan) 7.5 0.00 0.00 0.01 0.02 15.0 0.02 DeGAN (naan) 7.5 0.39 0.00 0.00 0.00 15.0 0.20 T3Ym0!D TRYROID TNYa0!D TRYa0!D TNYa0!D RESULTS aASED UPON ODCF asVISION 11 UPDAfs C8204 FttmUARY 1946 40 2_ __ .__
_ _ _ .. ~ ._ t
)
I i TABLE 3.1 1 (continued)
'i SYRON UNIT 140 1949 ANNUAL REPORT ;
RAIlhUR DOSES RESULTING FRON A!nt0RNE RSLEAsts PERIOD OF RSLEA38 - 01/01/09 TO 12/31/R9 CALCULATBD 01/18/90 . ADULT RfCEPTOR 1ST 2ND 3RD 4Tu TYPE QUAATER OUARTBR (IUARTER 00ARTen AmWUAL JAN-RAR APR JUN ML-Str CCT-DBC CAnaA AIR 1.738 04 5.258-05 4.848-04 0.095-04 1.528 33 (MRAD) (se I (St ) (St ) (88 ) (St ) SETA AIR 7.245*04- 2.305-04 1 005-03 3.238 03 6.195-03 (MRAD) (se I (se ) (:Is ) (85 ) (38 ) TOT. 00DY 4.20s-05 1. 36 B45 1.258-04 2.088-04 3.898-04 (MRAM) (St - ) (85 ) (SE I (SR ) (85 ) i SRIN 3.575-04 1.195-04 1.018-03 1.648-03 3.135 03 i (NRBR) (SB ) (SR I (SR ) (88 ) (88 ) ORGAN 1.988-02 7.50s-05 1.778-04 5.498-05 2.018-02 ! (MREN) (NB ) (ESS ) (ESS ) (St ) (N8 ) { TNYRCID TRYR0!D TRYSCID TRYB010 TNYPotD T518 IS A REPORT POR TNR dLENDAR YEAR 1999 l, COMPLIANCE STATUS . 10 Crt 50 APP. 1 ADULT RECIFTOR
............ g or App I, ............
OTRLY IST OTR 2ND QTR 3RD OTR 4Ta OTR YRLY g or OsJ JAN-MAR APR-JUN JUL-SEP OCT NOV ORJ APP.! GAAAA AIR (MRAD) 5.0 0.00 0.00 0.01 0.02 10.0 0.02 ttTA AIR (RRAD) 10.0 0.01 0.00 0.02 0.03 20.0 0.03 TOT. 30DY (MRSM) 2.5 0.00 0.00 0.00 0.01 5.0 0.01 SRIN (Matn) 1.5 0.00 0.00 0.01 0.02 15.0 0.02 ORGAN (MRER) 7.5 0.26 0.00 0.00 0.00 15.0 0.13 ,
, TsYROID 78YROID TRYR0!D TRYROID TRYRotD RESULTS SASED UPON ODCR REVISION 11 UPDATB C3204 FEBRUARY 1986 l
41
l
.- I 3 !
i 1 l i . 1 i i 1 i
.j
.i TABLE 3.2 1 .
I I SYRON UN!T ONE t ADULT RECEPTOR 1989 ANNUAL REPORT RARINUn 008B8 ( ARSM) 888ULTING FROM LIQUID BFFLUENTS l PER100 0F RELEAsk . 01/01/89 TO 12/31/89 CALcVLAft0 01/16/90
- 187 2ND 3RD 4TE D088 TYPS QUARTET OUARTet OUARTat 00ARTSR ANNUAL JAN.AAR APR.JUN JUL. SSP OCT.DSC TOTAL 1.458 02 5.498 03 1.208 03 S.495 04 2.388 02 <
DOOY I INTsRNAL 2.748 02 1.275 02 2.358 03 2.015 03 4.445 02 ORGAN GI.LLt GI.LLI GI.LLI GI.LLI GI.LLI ; TWIS!$AREEDRTFORTESCALENDERYRAR1999 1
' 1) l 1
COMPLIANCE STATUS . 10 CFR 50 APP. I l
............ g Or App 3. ............ !
QTRLY 187 QTR 2ND QTR 3RD QTR 4Ts QTR YRLY g 0F 1 OBJ JAN.AAR APR.JUN JUL.887 OCT.NOV OSJ APP.! I TOTAL RODY (Mass) 1.5 1.10 0.37 0.00 0.04 3.0 0.79 CRIT. ORGAW(Masn) $.0 0.55 0.25 0.05 0.04 10.0 0.44 l 1 GI.LLI GI.LLI Ot.LLI GI.LLI GI.LLI I at3ULTS RA$tD UPON ODCM REVISION 11 { UPDATE CS204 i FEBRUARY 1986 1 l 42 1
i e i 1 i 4
. 1
)
1 i ?
.e 1
4 TABLE 3.2-1 (continued) , BYRON UNIT 1980 ACULT RSCEPTOR 1999 ANNUAL REPORT AAXINUM D0888 ( AREN) 888ULTING PROM LIQUID EPPLUSNTS PERIOD OF RELSASE a 01/01/89 TO 12/31/09 CALCULATED 01/16/90 e 1st 2ND 3RD 47s i Does TYPS QUARTSR QUARTER QUARTSR QUARTER ANNUAL - JAN-MAS APR-JUN JUL-SSP OCT-DSC TOTAL 1.65s-02 S.498-03 1.20s-03 5.49s-04 2.388-02 toDY INTERNAL 2.748-C2 1.275-02 2.355-03 2.015-03 4.445-02 ORGAN GI-LLI GI-LLI , GI-LLI GI-LLI GI-LLt TE!S IS A REPORT POR TSB CALENDAR YEAR 1989 6 ConPLIANCE STATUS - 10 CPR SO APP. !
............ g 0F APP g. ............
OTRLY 1ST QTR 2ND OTR 3RD OTR 4Ts QTR YRLY % OP - ! OSJ JAN*RAR APRaJUN JUL-5EP OCT-MOV OSJ APP.! TOTAL BODY (nSan) 1.5 1.10 0.27 0.00 0.04 3.0 0.79 : CRIT. ORGANIMREMI 5.0 0.55 0.25 0.05 0.04 10.0 0.44 GI LLI O!-LLI 01-LLI 01-LLI GI-LLI RESULTS BASED UPON ODCA REVISION 11 UPDATE C3204 PEDRUARY 1986 t. 43
i e
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BYRON ST ATION ' e wee..a et ; i. . i int,ta a!NG ANO QUTER R!NG TLQ LOCA7:0*4 4 47 l
f 1 1 a TABLE 5.0-1 ; i L
~
, Byron Station , , g Radiological Environmental Monitoring ; J t 3 . ,
a
- Locations . j k -. J- ;
-- f e e . . .a-
- 2
.t - f + . o. 4 M .c ..a .- c -- .
- .c .x - ..a. % 8 LO O- M - .0 .D 'O L , 0
.ee -J 0 .M .a.t-d 3 . . 3 L 1 4 >= U 6 w E L G: M M > CD BY-01 Byron OO.................,.....
' BY.02 5tillman Valley 00.....,,..........,.....
BY-03 Nearsite East OO....................... BY 04 Paynes Point 00.............,,........ BY 05 Nearsite South 00....................... BY-06 Oregon - 00....................... BY 07 Mt. Morris OO................, ..... BY 08 Leaf River 00 ...................... BY 09 Woodland Creek ..........-.......O....... BY 12 Oregon Pool of Rock River .....O.........O.O.......
- BY.13 Rock River. Upstream .....O.........O.O.......
. BY 14 0frsite Well Water ................,.....O.
. BY 15 J. A. Reeverts Pine Hill Dairy .........O........... ,,,
BY 17 Whitten Holstein Dairy .........O... .......... BY 18 McCoy Farmstand Well ...............,,......O. BY 191966 E Weld Bark Rd ................. ,O...., , BY 19 2 6993 N River Rd ..........t. ......,O..... L BY 20 Kenneth Reeverts Farm .........O........ ,, ... BY.21 Near Site N 00 ............,,........ BY.22 Near Site ESE 00..............,,....... BY 23 Near Site S 00 ...................... BY.24 Near site SW 00..................... . BY 25 Bit! Leupkes Farm ~00....................... ,
.........O...............
CENSUS . Driry Residence l l t l l l 48 , 1. 1
r-- r.- TABLE 5.0-2 BYRON STATION ENVIRONMENTAL RADIOLOGI AL MONITORING PROGRAM, SAFPLING LOCATIONS ,
- 1. AIR SAMPLERS Distance Direction Site Codea- Location (miles) *(*)
BY-01 Byron 3.5 25 BY-02'(C) Stillman Valley 6.2 56 BY-03 Nearsite - East 3.8 85 BY-04 Paynes Point 4.5_ 140
.BY-05 Nearsite - South 3.6 180 BY Oregon' 4.6 213-BY-07(C) Mt. Morris 7.8 240 BY-08 (C) Leaf River 7.0 315 BY-21' Nearsite North 0.3 9 BY-22 Nearsite East-Southeast 0.3 101 BY-23 Nearsite South 0.6 182 BY-24 Nearsite Southwest 0.6 229
- 2. TLDs
- a. Same as Wo. 1
- b. Special TLD Samplers Distance Direction Site Code (miles) (')
Inner Ring BY-101-1,2 1.2 13 _ BY-102-1,2 1.0 25 BY-103-1,2 1.7 51 BY-104-1,2 1.4 64 BY-105-1,2 1.3 84 BY-106-1,2 1.4 108 BY-107-1,2 1.4 141 BY-108-1,2 0.6 158 BY-109-1,2 0.6 183 BY-110-1,2 0.6 201 BY-111-1,2 0.9 235 BY-112-1,2 0.8 247 a Control (reference) locations are denoted by a "C" after site code. All other locations are indicators. 49
. 1 TABLE 5.0-2 (continued)
BYRON STATION ENVIRONMENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS t
- 2. -TLDs
- b. Special TLD- Samplers (continued) s Distance 01'rection '
Site Code (miles) L(') BY-113-1,2 0.7 270 BY-114-1,2 0.8 298 BY-115-1,2 1.0 314 BY-116-1,2 1.4 -329 e Outer Ring BY-201-l',2 4.8 360 BY-202-1,2 4.5 13 BY-203-1,2 5.1 42 BY-204-1,2 4.2 66 BY-205-1,2 3.9 89 BY-206-1,2 4.2 112 BY-207-1,2 4.2 140 BY-208-1,2 4.1 159 BY-209-1,2 3.8 189 , BY-210-1,2 3.6 218 BY-211-1,2 5.2 238 BY-212-1,2 4.9 257
.BY-213-1,2 5.0 280 BY-214-1,2 4.8 298 BY-215-1,2 5.2 322 BY-216-1,2 4.8 -337
- 3. . MILK-Distance Direction Site Codea Location (miles) '(*) ,
i BY-15 Warren Danakas Dairy 3.3 110 BY-17 (C) Whitten Holstein Dairy 9.0 270 BY-20 Kenneth Reeverts Farm 2.1 37 BY-25 Bill Leupkes Farm 3.7 190 a Control (reference) locations are denoted by a "C" after site code.. All other locations are indicators. 50
. , _, , .r ; > ; ,
TABLE 5.0-2 (continued) BYRON STATION ENVIRONMENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS
- 4. VEGETABLES Distance Direction Site Code Location (miles) _,
(*) BY-19-1 966 East Weld Park Road 5.1- 200 BY-19-2 6993 North River Road 5.1- 200
- 5. GR0VND/WELL WATER Distance Direction Site Code location (miles) (*)
By-14 CECO Off-site Well 0.3 101 BY-18 McCoy Farmstead 1.0 235 (Ceco-owned well)
- 6. SURFACE WATER Distance Direction Site Code Location (miles) (*)
BY-09 Woodland Creek 2.1 320
-BY-12 Oregon Pool of Rock River 4.5 213 BY-13 Rock River Upstream 2.6 302
- 7. FISH Distance Direction Site Code Location (miles) ()
BY-12 Oregon Pool of Rock River 4.5 213 BY-13 Rock River Upstream 2.6 302
.8. SHORELINE SEDIMENTS 4 Distance Di rection Site Code Location (miles) (*)
BY-12 Oregon Pool of Rock River 4.5 213-BY-13 Rock River Upstream 2.6 302 51
Table $.0-2 (continued) BVRON STATION ENVIRONMENTAL RAD 10tOGICAL MONITORING PROGRAM. $AMPtE COLLECT 104 AND ANALYSE $ tocation Collection Type of Frequency Sample Media Codes $lte Frequency ' Analysts of Analysts Renark s
- l. Airborne SY-1 Syron Continuous Gross beta Iseetly On all samples.
Particv?ates BY-2 (C) $ttliman Valley operetton Gamma Isot Guarterly On quarterly composttes from each location. BT-3 Nearsite East for a week Cannia Isot Weekly If gross bets activity in air particulate 87-4 'Paynes Point samples >10 times the yearly mean of df-5 Nearsite South control samples. 8Y-6 Oregon Filter Weekly 8Y-7 (C) Mt. Morris Exchange 8Y-8 (C) teaf River 87-21 Near $tte North BY-22 Mear $tte East-Southeast BY-23 Near $tte South BY-24 Meer $tte Southwest u, .__ . ............ .-- _._.. ........ ro
- 2. Atrborne same as 1. Continuous I-131 - Weekly On all samples.
Iodine operation for a tseek
. _ . _ ~ . - . - _
- 3. Air Samp1tng $ame as 1. .- Test and Weekly On all samples.
Train Maintenance
- 4. TLD Same as 1. Quarterly Gamma Quarterly Two sets at all AP locations. One set read quarterly. Second set read of BY-101-1.2 Inner Ring required by Commonwalth Edison. At other 102-1.2 locations, all sets read quarterny.
603-1,2 104-1,2 Minimum of two TLDs per set. 105-1,2 106-1,2 107-1,2 108-1,2 109-1,2 110-1,2 111-1.2 112-1.2 113-1.2 114-1,2 115-1,2 116-1.2 a Control (re crence) locations are denoted by a "C" in this column. All other locations are indicators. e %,. . - f * , , . , v- w 4eF-
;n ~
, v- .,
9- . 1 TABLE 5.0-2 (continued) BYROM STAT 10M - ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM, SAMPLE COLLECTION AND ANALY$ES Location Collection Type of Frequency. Sample Media Codea $1te Frequency ' Analysts of Analysis Remarks
- 4. TLD's BY-201-1,2 Outer Ring (continued) 202-1,2 203-1,2 204-1,2
~
205-1,2 206-1,2 201-1,2 208-1,2 - 209-1,2 210-1,2 211-1,2 212-1,2 213-1,2 214-1,2 215-1,2 x 216-1,2
~
(n 5. " Milt BY-15 W. Danakas Salmonthly 1-131 Semimonthly On all samples. May-October Games Isot. May-October 87-17 (C) Whitten Holstein Dairy Monthly BY-20 K. Reeverts Monthly November-April ,
- toevenber-April BY-25 Stil Leuptes Farm Monthly
- 6. Vegetables 8Y-19-1 Annually at Gamma Isot Annually - Four varieties from each location as BY-19-2 harvest available at harvest. (Gasuna isotopic on edible portion only.)-
- 7. Ground /Well BY-14 CEto Off-site Well Seminoethly Gross beta Monthly On monthly composite for each location.
Water Office Gammia Isot Monthly On monthly composite for each loca*.lon. 87+18 McCoy Farmstead Tritium Quarterly On quarterly composite for each location. 1-131 Senteenthly On sentmenthly composite when dose calcu-lated for water consumption is greater-than one pres per year.
~
- - . - ~ ~ - . - - - - - - - . - _
- 8. Surface hter 8Y-09 Woodland Creek Weekly . .Trttfum, Quarterly On quarterly composite frcus each locatica.
81-12 Oregon Pool of h Isot - Monthly On monthly composite from each location. Rock River ' 87-13 (C) - Rock River, opstream 8 Control (references) locations are denoted by a *C* fn this column. All other locations are indicators.
.i<str,. M' g wii p. 9*- <=,ycr --ig e 94 g- -
1u- e y- y.:- g
E TABLE 5.0-2 (continued) BYRON STATION E WIRONMENTAL RADIOLOGICAL MONITORING PROGRAM. SAMPLE COLLECTION Afe ANALYSES
~~
tocation Collection Type of Frequency Sample Media Codea 5tte Frequency Analysis of Analysis ~ Remark s
- 9. fish BY-12 Oregon Pool of 'Three times Gamuna Isot Three times Fren Oregon pool of Rock River, on adtble Rock River a year, a yeir. portions only. At least two species.
8Y.13 Rock River, upstream Spring. Susumer, and Fall
- 10. Shoreline BY-12 Oregon Pool of Sealannual Canna Isot Sant annual on all samples Sediments Rock River BY-13 t)pstream of Oregon Dam
' - ~ ~ --~ ----
- 11. Dairy Census a. Site boundary to 2 miles -
- a. Enumeration Annually During grazing season.
by a door-to-door or equiva-lent counting technique. -$ b. 2 miles to 5 miles -. b. Enumeration Annually During grazing season. by using referenced information from county agricultural
-agents or other reliable sources.
- c. At dairies listed in item 5. -- c. Inquire as Annually During grazing season.
to feeding practices:
- 1. Pasture only.
- 2. Feed and chop only.
- 3. Pasture and feed; if both, ask farmer to estimate fraction of food from pasture: c255, 25-501, 50-751, or >751.
- 12. Nearest in all 16 sectors up to 5 attes- Annually - During growing season.
Residence Census 8 Control (reference)-lor:4 tons are denoted by a *C* in this column. All other locations are indicators. As . \- _ af *
/~- a pr - .,y- -<y.%- f g ga'.-c- +, .v. _m_. _ _ - *_._s__a _ _ e-M
^
.-~ . .+- --
. 3
-TABLE 5.0 ENVIRONMENTAL R ADIOLOGICAL M0nlTORING PROGR AM QU4tTERLY SUFMARY Name of Facility Byron Nuclear Power Station Docket No. 50-454. 50-455 l
Location of Factitty Ogle. 1111ncis Reportleg Perlod 1st Ouarter 1989 (County, 5 tate) Indicator Location with Highest Control Quarterly Mean Locations mus4>er of Sample Type and Locations Non-routine Meana Mean- Meana Type Number of Range Results Analyses LLD Range Location Range' (Units) By-24. Near-site 5.W. 0.035 (13/13) 0.031 (38/39) 0 Air Particulates Gross Beta 156 0.01 0.032 (117/117) (pCf/m )3 (0.012-0.066) 0.65 at 229* (0.023-0.066) (0.015-0.056)
<tLD
<tt p 0 Gamma Spec- 12' O.01
- <tto . O' Airborne lodine 1-131 156 0.07 <t LD -
(pct /m3) Sy-22, Onstte 15.3 (1/1) 11.5 (3/3) 0 Game Background Gamma Dose 12 3.0 12.3 (9/9) (9.6-15.3) 0.3 el 101* - (10.9-12.0) (TLDs) (se/Qtr.)
<ttD <tt D 0 Milk 1 131 11 0.5 - -
(pCl/1) Gaar-a Spec. 11
<t t0 0 Cs-134 5.0 <tLD - -
o m 5.0 <tLD - - <t t 0 (n Cs-137 - <tt0 0 . Other Gammas 10.0 <tLD - Surface Water Gassna spec. 6 10 <ttD - - <t t 0 0 (pC1/1) Cs-134 <t t D 0 Cs-137 10 <ttD - -
<tLD - - <t to O Other Gammas 15 o Tritten 3 200 596 (1/2) By-12, counstream of 5% (1/2) <tto fatate 4.5 ml 213*
1.8 <tLD - - tione 0 Well Water Gross Beta 5 (pct /1) Garma Spec. 5 10 <tLD - - none O Cs-134 - *ione 0 Cs-137 10 <tLD - 15 <tLD - - Mone 0 Other Gammes - None 0 TrItfum 2 200 <tLD - a Mean and range based on detectetle measurements only. Fraction Indicated in parenthesis.
. ~~ -.-_ . _ -.
TABLE 5.0-4' ENVIR0fe9 ENTAL RADIOLOGICAL MONITORING PROGRAM QUmtTERLY SUNtARY Name of Facility _ Byron Nuclear Power Station Docket No. __50-454. 50-455 _. _ tocation of Facility Ogle. Illinois Reporting Period 2nd Quarter 1989 (County. State) Indicator Location with Highest Control Sample Type and locations Quarterly Mean Locations mer of Type Mamber of Meana Mean Meana Non-routine (Units) Analyses LLD Range location Range Range Results Gross Beta 156 0.01 0.021 (116/117) By-06 0.024 (13/13) 0.020 (39/39) 0 AirPartgculates (pCl/m ) (0.005-0.042) 4.6mlh213Orep (0.015-0.042) .(0.010-0.035) Gansna Spec. 12 0.01 <ttD - - <ttD 0 Airborne lodine 1-131 156 0.07 <ttD - - - <t tD 0 (pCl/m3) Gaeuna Background Gama Dose 12 3.0 16.0 (9/9) By-05. Near site Soute 19.0 (1/I) 14.6 (3/3) 0 (TLDs) (eft /Qtr.) (11.0-19.0) 3.6 al 9 180* - (13.3-15.8) Hilk 1-131 20 0.5b <ttD - - <ttD 0 m Gama Spec. 20 cn (pCl/1) 0 Cs-134 5.0 <ttD - -
<ttD Cs-137 5.0 <ttD - - <tt D 0 Other Games 10.0 <ttD - - <tt0 0 Surface Water Gama Spec. 9 (ptl/1) Cs-134 to <tto - - <tto O C5-131 10 <tt0 - - <ttD 0 Other Ganunas 15 <ttD - - <tI D 0 Tritium 3 200 .790 (1/2) Sy-12. Downstream of 790 (1/2) <tto 0 Intake 4.5 mit 213*
Well Water Gross Beta 6 2.4 <tto - - None 0 (pCl/1) Gauuna Spec. 6 Cs-134 10 <tLD - - None O Cs-137 10 <tt0 . Mone 0 Other Gammas 15 <ttD - - Mone 0 Tritium 2 200 <ttD - - Mone 0 j .
- /
. , .- c . _ _ .
.+w
. .- .- -a TABLE 5.0-4.(continued)
(Nylp0 MENTAL R)0f0 LOGICAL MONITORING PROGRAM QUARTERLY SUP99RY Mame of Factitty Byron haclear Power Station Docket No. 50-454. 50-455 - Location of Facility Ogle. Illinois Reporttag Period 2nd Quarter 1989 (County. 5 tate) Indicator location with Highest Control Semple Type and locations Quarterly Mean tocations huut>er of Type humber of 'Meena Rean Meena non-rootine (Units) Analyses LLO Range location Range , aange Results F1sh Gasune Spec. 4 (pC1/g wet) Cs-134 0.1 <LLO - -
<tLD 0 Cs-137 0.1 <tLO - -
<t to 0
$ Other Gasunas 0.13 <LLO - -
<t t 0 0 Bottom Sediments Gamma Spec. 2 (PC1/g dry) Cs-134 0.1 <tLO - -
<t t 0 0 Cs-137 0.1 <tLO - -
<tto 0 Other c-s 0.2 <LL C, - -
cme.ae p wy 79, ,m-~ , .,_-a--s.,_. (-g y
TABLE S.0-5 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGt AM QUARTERLY
SUMMARY
Byron Nuclear Power Station Docket No. 50-454, 50-455 Mame of Facility tocation of Facility Ogle, Illinois Reporting Period 3rd Quarter 1989 (County, State) Indicator location with Highest Cont rol Quarterly Mean tocations Number of Sample Type and locations Non-routine Meana Mean Neana Type Number of R ange Results Range tocation Range (Units) Analyses LLO Sy-21 Nearsite North 0.025 (13/I3) 0.021 (39/391 0 Atr Particulates Gross Beta 156 0.01 0.022 (111/117) (pCf/m3) (0.006-0.041) 0.7 al 9* (0.018-0.038) (0.007-0.034) 0.01 < tic - - <tio O Gama Socc. 12
<it 0 0 Afrborne lodine 1-131 156 0.07C <tto - -
s (pCf/m3) By-22, Onstte ESE 18.0 (1/l) 14.0 (3/2) 0 Gama Background ' Gamma Dose 12 3.0 15.1 (9/9) (11.4-18.0) 0.3 mi 10l* - (13.3-14.4) (Ttos) (#W/Otr.) 0.5 <tt0 - - <tto O
$ Milk 1-131 24 (pCl/1) Gamma Spec. 24 Cs-134 5.0 <tt0 - - <tto o Cs-137 5.0 <tto - - <tto 0
<tto - <tt o 0 Other Camas 10.0 -
Surface Water Gamma Spec. 9
- - <tto O (pCf/1) Cs-134 10 <tto
- - <tto 0 Cs-137 10 <tto
<tto - - <tt p 0 Other Games 15 . 0 Tritfum 3 200 532 (1/2) By-12. Downstream of 532 (1/I) <tt 0 Oregon Dam, 4.6 mi 213*
a Pean and range based en detectable measurements only. Fractions indicated in parentheses. G
- V
TABLE 5 0-5 (continued) ENVIROIMENTAL RADIOLOGICAL MONITORING PROGRAM QUARTERLY StM4ARY Name of Fac111ty __ Byron Nuclear Pouer Station Docket No. _ ___ 50-454. 50-455 Location of Factitty Ogle. Illinois Reporting Period 3rd Overter 1969 _ (County. State) = . Indicator Location with Highest Contral Sample Type and Locations Quarterly Mean Locations thaber of Type hamber of Meana Mean ' -~ Meana . non. routine (Units) Analyses LLD Range LocatIce aange Range.- Results bell Water Gross Beta 6 2.6 <tLD - - mene 0 (PCf/11 c= == Spec. 6 Cs-134 10 <tLD - - None 0 O -137 10 <tLD - - None 0 Other Gemas 15 <tLD - - none 0 Trittum 2 ?00 236 (1/?) BY-14. Offstte hell 236 (1/1) None 0 .; 0.3 at 9 101* ;
$ Ftsh (pC t / *: wet)
Gamma Spec. 4 . Cs-134 0.10 <LLD - - <tLD 0 Cs-137 0.10 <tLD - - <tLD - 0 Other Gammas 0.13 <tLD - - <tLD 0 Vegetables r.= == Spec. 7 (pct /g wet) Cs-134 0.1 <tLD - - hone O Cs-137 0.1 <tLD - - none 0 0.2 Other Gammes (LLD - - hone 0 1-131 0.06 <tLO - -
- 0 a Mean and range based on detectable seasurements only. Fractlens indicated in parentheses.
_ ._ , ,.- _. . . _ . _ , , . _ . ~ ,.. , , , . _ , . . ,. .-.
TABLE 5.0-6 ENVIR0099fNTAL RADIOLOGICAL MoulTORlWG PE0 GRAM OUARTERLY SimMARY Name of Factitty Byron Nuclear Power Station Docket No. 50-454, 50-455 Location of Facility Ogle,1111act s Reporting Period 4th Quarter 198 (County, State) Indicator Location with Highest Control Sample . Type and Locations Quarterly Mean Type Number of Locatloss. Number of Meana. Mean oleone (Units) Analyses Non-routf ne ~' LLO Range Location Range Range Resul ts Air Part culates Gross Beta 156 'O.01 0.029 (116/117) BY-24 Nearsite South- 0.032 (13/13) 0.029 (39/39) :0 Iptt/ ) (0.007-0.051) . west 0.65 mi 9 229' (0.020-0.051) .'(0.014-0.045) Gamma Spec. 12 0.01 4LD - - 4LD '0 Airborne lodine - I-131 156 0.07 4LD (pct /m3) 4t0 0 cn Gamme Background 3.0 C Gasura Dose 12 15.5 (9/9) By-22, Onstte, 0.3 18.5 (1/1) . 14.6 (3/3) 0 (TLDs) (mR/Qtr.) 111.5-18.5) et 9 10l* - (14.0-15.61 Milk I-131 16 0.5 4LD (pct /11 4LB 0 Gamma Spec. 16 s ts-134 5.0 <tLD - - 4LO O Cs-137 5.0 <tLO - -' <t L O O Other Gammes 10.0 4LD - 4t0 0 Surface Water Gamma Spec. 9 (pCf/1) . Cs-134 ' 10 4LD - - 4t0 0 Cs-137 10 ALD ' 4LO O Other Gasmas 15 4LO - - 4LO O Tritium 3 200 1470 (1/2) BT-12. Downstream 1470 (1/1) <tto 0
, of &ge De 4.6 el 9 213*
a 6'*h 6 -P'N
, i a a + - . . - . m - . ~ , .
- _ - -
% ,.m.i ,c. - . .
TABLE 5.0-6(continued) ENVIRONMENTAL RADIOLOGICAL I40NITORING PROGtAM tresaft!"._? y3= tai =ff Name of Factitty Byron Nuclear Power Station Docket No. 50-454, 50-455 Location of Facility Ogle, Illtects Reporting Period , ' 4th Quarter 1989 (County 5tatel Indicator Location with Highest Control Sample Type and Locations. Quarter 1 3 ' 14een locations thumber of Type leumber of Meena sq,ait feeana Non-routtne (Units) Analyses LLD Range Location Range Range Results Well water Gross Beta 2 2.6 <tLD - - None 0 (pct /11 Gamuna Spec. 2 Cs-134 10 <tLD - - None O Cs-137 10 <tLD - - None 0 Other Gasunas 15 <tLO - - None 0 Trittum 2 200 <tLD - - None 3
, Fish Gamma Spec. 4 ~ (pCf/g wet)
Cs-134 0.10 4LD - -
<t t D 0 Cs-137 0.10 4LD - -
4LD 0 Other Gamuuas 0.13 4LD - - <tt 0 0 Botton Sediments Gamusa Spec. 2 (pct /g dryl , Cs-134 0.1 <LLD - -
<Lt D 0 Cs-137 0.1 <tLD - -
<tt 0 0 other Gammes 0.2 <tLD - -
<tte O Vegetables I-131 2 0.06 (LLD - -
None 0 a 14ean and range based on detectable measurements only. Fractions indicated in parentheses. e
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-f APPENDIX II 4 t
1 1
- METEOROLOGICAL DATA >
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3 BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1989' STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) l DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT .24 TOTAL \: N O O O O O O O NNE O O O O O O O NE O O O O O O 0 1 . ENE O O O O O O O { E O O O O O O O ESE O O O O O O O SE O O 0 0 0 0 0 II SSE O O O O O O O S 0 0 0 =0 0 0 0 SSW 0 0 0 0 0 0 O ! SW 0 0 0 0. 0 0 0 WSW 0 0 0 0 0 0 -O , l W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 C NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 j VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 Hours of calm in this stability classa 0 Hours of missing wind measurements in t.his stability class: 0 Hours of missing stability measurements in all stability classes: 77 63
.m (4,.
1 - 3 '1
', .' s . .; ,
g BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1989 STABILITY. CLASS MODERATELY UNSTABLE (DIFF TEMP 250-30 FT) WINDS MEASUllED AT 250 FEET-1 < L WIND WIND SPEED (IN MPH) i DIRECTION- .8-3 4- 7 i8-12 13-18 19-24 GT 24 TOTAL: , 8
. I N O O O O O O O 1 O NNE O O O O O O O
- 1 NE O O O O O O 'O ENE O O 0- 0 0 0 0 E O O O O O O O ESE O 0- 0 0 0 0 0 >
SE O O O O O O O SSE O O O O O O O S O O O O O O O= SSW 0 0 0 0 0 0 0 SW 0~ 0 0 0 0 0 0 .< WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 1 0 1 ; NW O O O O O 0 O NNW- 0 0 0 0 0 0 0 VARIABLE O O O O O O O i i TOTAL 0 0 0 0 1 0 1 1' Hours of calm in this stability class: 0 - Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classess' 77 64
p 4 . BYRON NUCLEAR. POWER STATION PERIOD OF. RECORD : JANUARY-MARCH 1989 i? STABILITY CLASS - SLIGHTLY UNSTABLE' (DIFF TEMP 250-30 FT)
- 7 WINDS MEASURED AT 250 FEET i
I WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL i N O O O O- 0 0 0 ! NNE O O O O O O , O NE O O O O .0 0 0 ENE O O O O -0 0 0
.E O O O O O O 0- 4 ESE O O O O O O O !
SE O O O O O O O ! SSE O O O O O O O S O O O O O O O SSW. O. O O O 1 0 1 . SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0
-j W 0 0 0 0 1 1- 2 -j WNW 0 0 1 0 0 0 1 1 4
NW 0 0 3 0 0 0 3 NNW 0 0 0 0 0 0 0 ! VARIABLE O O O O O O O TOTAL 0 0 4 0 2 1 7 , Hours of calm in this stability class: 0 t Hours of missing wind measurements.in this stability class: 0 Hours of-missing stability measurements in all stability classes: 77 i l l 65
e BYRON NUCLEAR POWER STATION
' PERIOD OF RECORD - JANUARY-MARCH 1989 STABILITY CLASS - NEUTRAL (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) i DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL
-N O 4 27 42 20 8 101 4
22 7 69 NNE O 2 21 17
'NE O 9 20 16 25 11 81 ENE ,
1 3 9 32 16 0 61 j l E O 1 15 29 5 2 52 ESE O 1 0 7 1 0 9-
'SE O 2 6 13 9 8 38 SSE 1 5 24 32 14 3 79 S 2 5 20 31 29 9 96 SSW 0 5 7 10 28 15 65 kW. 1 4 14 18 17 3 5'i WSW 0 4 18 42 21 3 88 W 2 6 13 44 17 19 101 WNW 2 6 17 29 19 10 83 NW 1 3 19 28 13 8 72 NNW 3 6 22 50 14 1 96 VARIABLE O O O O O O O ,
TOTAL 13 66 252 445 265 107 1148 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: 77 24 66 }? -a
7 -- << l b .. l BYRON NUCLEAR POWER' STATION- . PERIOD OF RECORD -JANUARY-MARCH 1989 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET '- WIND WIND SPEED'(IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL . L N 1 1 8 14 5 2 31 i NNE 1 4 2 .10 12 0 29 i NE 1 3 5 5 1 1 16 ENE 3 4 3 4 3- 0 -17 I E O 4 7 16 15 2 44 ESE- -0 0 5 8 4 3 20 SE 1 3 5 9 5 0 23 SSE 1 2 7 20 21 3 54 S O 2 7 27 27 17 80 SSW 0 5 10 22 43 26 106 -; SW- 0 4 9 12 13 12 50 , WSW 1 3 6 25 19 0 54 W 1 4 10 32 18 11 76 , WNW 0 4 8 32 24 5 73 NW- 1 7 11 41 12 1 73 ' NNW 0 4 12 21- 3 3 43 VARIABLE O O O O O O O TOTAL 11 54 115 298 225 86 789 Hours of calm 11n this stability class: 0 Hours of missing wind measurements in this stability class: 0 , Hours of missing stability measurements in all stability classes: 77 67
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BYRON' NUCLEAR. POWER STATION PERIOD OF RECORD JANUARY-MARCH 1989-Lir STABILITY CLASS - MODERATELYLSTABLE (DIFF' TEMP 250-30 FT)' WINDS MEASURED AT 250 FEET WIND' WIND SPEED (IN MPH) .,
. DIRECTION ;8-3 4- 7 8-12 13-18 19-24 ,GT 24 TOTAL 4
N. 0 0 0 2 5 0 7 NNE O O O O O O O NE O 1 0 2 0 0- 3 ENE 0' 3. S' O O O 8 E O O 1 0 0 0 1 ESE O O 3 1 2 0 6 SE. 0 0 1 4 4 4 ~13 i SSE O 1 0 6 7 3 17 i S O 2 1 3 5 2 13 j SSW 0 0 2- 3 3 0 8 j SW 0. 0 6' 1 0 0 7 j WSW 0 0 2 4 0 0 6 -s W 0 0 0 2 0 0 2 ;l
.1 WNW 0 0 1 5 0 0 6 NW 0 0 0 10 0 0 10 !
NNW 0 0 1 3 3 0 .7 VARIABLE O O O O 0 0 0 ) TOTAL 0 7 23 46 29 9 114 l
-i L -Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class:
Hours of missing stability measurements in all stability classes: 0 77 l l i l
;/>
o - 68
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BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1989 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O 3 0 0 0 3 ENE O 2 2 0 0 0 4 E O O O O O O O l ESE O O O O O O O SE O O 1 0 0 0 1 SSE O O O 1 0 0 1 S O O O 3 2 0 5 SSW 0 0 2 3 1 0 6 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 1 0 1 0 0 2 NW O O 1 1 0 0 2 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 3 9 9 3 0 24 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: 77 69
. 'a-.
4 BYRON NUCLEAR POWER STATION PERIOD OF RECORD -' APRIL-JUNE l'989 STABILITY CLASS - EXTREMELY UNSTABLE' (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET
- i
. WIND WIND-. SPEED (IN MPH)
DIRECTION .8-3 4- 7 8 ~ 13-18 19-24 'GT-24 TOTAL N O O 0 2 0 0 2 NNE 0. 0 0 0 2 0 2 NE O O O O O O O i ENE O O O O O O 0. E- 0 0 0 0 0 0 0 ESE O O O O O O O SE O O O 1 0 0 1 3 SSE O O O O O 1 1 S 0 0 0 0 0 0 O SSW' O O O 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 'O O O O O O C W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0- 0 0 NNW. 0 0 0 0 0 0 0-VARIABLE O O O O O O O H TOTAL 0 0 0 3' 2 1 6 i I Hours of calm in this stability class: 0 ;
-Hours of missing wind measurements in this stability class: 0 L Hours of missing stability measurements in all stability classes: 11 I. 70 9
l i BYRON NUCLEAR POWER STATION
-PERIOD OF RECORD - APRIL-JUNE 1989
-STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT,250 FEET - i WIND WIND SPEED (IN MPH) DIRECTION- .8-3 4 '7 8-12 13-18 19-24 GT 24 TOTAL N O' O 1 3 0 0 4 i NNE. 0 0 0 4 7 -0 11.
'NE- 0 0 0 0 0 0 0- l ENE O O O 1 0 0 1 E O O' O O O O O ESE O O O O 1 4 5 SE O O O O O O O SSE O O O 3 0 1 4 S _0 0 01 0 2 0 2 _;
i SSW 0 0 0 0 0 0 0 , SW 0 0 0 1 0 0 1 ; WSW 0- 0 1 0 0 0 1 , W 0 0 0 0 0 0 0. WNW O O O O O O O NW- 0 0 0 1 0 0 1 NNW 0 0 0 1 0 0 1 VARIABLE O O O O O O O' r TOTAL 0 0 2 14 10 5 31 Hours of calm in this stability class: 0
; Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 11 71
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l : .g ; BYRON NUCLEAR POWER STATION-PERIOD OF RECORD - APRIL-JUNE 1989
. . STABILITY CLASS --SLIGHTLY UNSTABLE (DIFF-TEMP-250-30 FT)
WINDS MEASURED AT 250 FEET WIND : WIND SPEED'(IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 '19-24 GT 24 TOTAL i N 0- 1 0 3 0 0 4 -; NNE O 1' 1 .1- 4 0- 7 NE O 1 0 2 0 0 3 ENE O O 1 4 1 0- 5 E O O 2 0 l' O 3 i ESE O O 1 1 2 1 5 SE O O O O 1 0 1 SSE O O O 1 0 0 l' S 0 'O O O 1 0 1 l SSW 0 0 1 0 0 1 2 i SW 0 0 0 0 0, O O WSW 0 0 0 2 0 0 2 a. W 0 2- 1 0 0 0 3 WNW 0 0 3 2 0 0 5 i
-NW. 0 0 5 6 0 0 11 NNW 0 1 2 2 0 0 5 l'
VARIABLE O O O O O O 0-TOTAL 0 6 17 24 10 2 59 a 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: 11 1
i 72
. 1 l
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1989 STABILITY CLASS - NEUTRAL (DIFF TEMP 250-30 FT) ; WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 2 14 23 29 7 0 75 NNE 1 12 19 4 7 1 44 NE 1 8 6 8 2 2 27 ENE O 4 11 18 10 0 43 E O 7 14 26 10 0 57 ESE O 2 20 11 9 1 43 SE 2 5 11 17 11 4 50 SSE 1 11 20 19 19 6 76 S 1 7 22 20 18 10 78 SSW 3 7 17 12 13 7 59 SW 1 1 14 31 15 1 63 6 ' WSW 0 13 22 24 4 4 67 i W 3 13 26 14 12 14 82 WitW 1 17 22 41 22 12 115 i NW 1 15 45 47 13 9 130 NNW 2 17 30 19 4 0 72 VARIABLE O O O O O O O TOTAL 19 153 322 340 176 71 108: , Hours'of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 11 73
2 0 0 BYRON NUCLEAR POWER STATION < PERIOD OF RECORD - APRIL-JUNE 1989 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 3 5 7 2 0 17 NNE 1 2 3 12 7 1 26 NE 1 5 2 13 5 0 26 ENE O 3 3 11 15 1 33 E 1 2 4 16 20 2 45 ESE 1 1 1 11 16 1 31 SE O 3 2 23 8 9 45 SSE 1 1 11 6 13 6 38 S 0 3 7 17 24 6 57 SSW 0 2 22 18 16 2 60 SW 0 5 14 36 9 0 44 WSW 0 4 14 14 2 0 34 W 0 5 15 13 0 0 33 i WNW 0 9 20 19 3 0 51 NW 1 7 16 25 0 0 49 NNW 3 6 12 13 0 0 34 VARIABLE O O O O O O O TOTAL 9 61 151 234 140 28 623 Hours of calm in this otability class: 0 Hours of missing wind measurements in this stability class: 1 H urs of missing stability measurements in all stability classes: 11 l l 74
r (- BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1989 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRdCTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 4 3 4 0 0 11 NNE O O 4 7 2 0 13 NE 1 1 3 1 0 0 6 ENE O 2 0 0 0 0 2 E O O 2 7 10 2 21 ESE , 2 1 2 4 12 1 22 SE O 1 2 5 9 0 17 , l SSE
- O 3 1 6 11 2 23 S 0 4 4 11 12 0 31 ;
SSW 0 2 7 28 5 0 42 SW 0 1 6 15 1 0 23 9 WSW 3 0 7 6 0 0 16 W 0 2 6 9 0 0 17 WNW 0 1 9 6 0 0 16 NW 0 2 8 13 0 0 23 NNW 0 3 7 2 0 0 12 VARIABLE O O O O O O O TOTAL 6 27 71 124 62 5 295 Heurs of calm in this stability classt 0 Hours of missing wind measurements in this stability class: 0 Hours of uissing stability measurements in all stability classes: 11 o
~
75
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, BYRON NUCLEAR POWER STATION !
f F PERIOD OF RECORD - APRIL-JUNE '1989' STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT) !
~ WINDS MEASURED AT 250 FEET- ;
i
. WIND . WIND SPEED (IN MPH) !
. DIRECTION' .8-3 '4- 7 8-12 13-18 19-24 GT 24 TOTAL l I
. t g, N O O 6 4 0 0- 10 l NNE 0. 0 1 2 0- 0 3 I i .!
L NE O O 1 0 0- 0 1 1 ENE .0 2 0 0 0 0 2 , E O O O O 1 0 1 ; (- i ESE O O O O O O O ; SE 1 0 1 3 8 0 13 i SSE O O O 1 0 0' 1 , S O 1 1 0 1 0 3 :
?
SSW 0 0 ? 4 2 0 8 s SW 0 0 1 6 0 0 7 [ WSW 0 0 2 3 0 0 5-L W 0 0 2 0 0 0 2 WNW 0 2 5' 2. 0 0 9 ; lDi 0 0 3 0 0 0 3 [ to NNW 0 1 7 1 0 0 9 VARIABLE O O O O O O O q TOTAL 1 6 32 26 12 0 77 i, Hours of calm 1n this stability class 0 ; Hours of missing wind measurements in this stability class 0 ; Hours of missing stability measurements in all stability classes: 11 ( L 76
y 1
- s BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1989 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O 3 0 0 3 NE O O O O O O O ENE O O O O O O O E O O 2 0 0 0 2 ESE O O O O O O O SE O O 1 0 0 0 1 SSE O O O O O O 3 S 0 0 4 4 0 0 8 SSW 0 0 2 0 0 0 2 t SW 0 0 0 3 0 0 3 WSW 0 0 0 5 0 0 $ W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 1 0 4 1 0 6 VARIABLE O O O O O O O TOTAL 0 1 12 19 1 0 33 ; 1 Hours of calm in this stability class 0 Hcurs of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 9 V 77 ,
I-
-n G- 5 f
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1989 l STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 250-30 FT) : WINDS MEASURED AT 2$0 FEET i WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL t ......... ..... ..... ..... ..... ..... ..... ..... N O 1 5 1 0 0 7 NNE O 1 0 4 0 0 5 i NE O 0 0 1 1 0 2 ENE O O 1 0 0 0 1 E O O 2 0 0 0 2 l-ESE O O O O O O O , SE O O 2 0 0 0 2 SSE o 0 0 0 0 0 0 S 0 0 5 0 0 0 5 SSW 0 0 4 1 0 0 5 [ SW 0 0 0 2 0 0 2 WSW 0 0 0 4 0 0 4 W 0 0 0 1 0 0 1 L WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 l NNW 0 0 1 1 0 0 2 VARIABLE O O O O O O O TOTAL 0 2 20 15 1 0 38 Hsurs 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: 9 78
BYRON NUCLEAR POWER STATIOh PERIOD OF RECORD - JULY-SEPTEMBER 1989 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 0 0 1 0 0 1 NNE O O 7 1 0 0 8 NE O O O 2 0 0 2 ENE O O O 1 0 0 1 E O 3 5 1 0 0 9 ESE O O 1 2 0 0 3 SE O O 2 0 0 0 2 SSE O O 2 2 0 0 4 S O O 2 2 0 0 4 SSW 0 2 3 0 0 0 5 SW 0 3 0 0 1 0 4 WSW 0 0 0 4 0 0 4 W 0 1 0 2 0 0 3 WNW 0 1 0 0 0 0 1 NW 0 2 0 0 0 0 2 NNW 0 1 0 0 0 0 1 VARIABLE O O O O O O O TOTAL 0 13 22 18 1 0 54 H urs 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 classest 9 79
t o BYRON NUCLEAR POWER STATION i PERIOD OF RECORD - JULY-SEPTEMBER 1989 s STABILITY CLASS - NEUTRAL (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL rt N 1 12 19 30 0 1 63 NNE- 1 8 25 16 10 2 62 NE O 13 20 17 2 0 52 ENE O 10 17 9 1 0 37 E O 11 17 6 2 0 36 ESE 2 11 8 8 0 0 29 SE 1 11 10 6 0 0 28-SSE 2 14 20 25 3 0 64 S 2 13 25 21 2 0 63 SSW 1 18 22 14 5 1 61 SW 0 17 22 22 1 0 62 WSW 4 13 14 10 5 0 46 W 2 21 20 16 3 0 62 WNW 0 7 7 5 0 0 19 NW 0 . 8 16 5 0 0 29 NNW 2 16 13 11 2 0 44 VARIABLE O O O O O O O f 203 275 221 36 757 TOTAL 18 4 Hcurs of calm in this stability class: O d Mours of missing wind measurements in this stability class: 0 H;urs of missing stability measurements in all stability classes: 9 00 a
r h p BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1989 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT)
'JINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 5 10 14 7 3 40 NNE O 5 11 24 18 2 60 . NE O 9 11 22 4 0 46 ENE O 8 11 13 8 0 40 E O 6 14 13 9 0 42 ESE 1 5 9 8 4 0 27 SE O 5 8 15 7 0 35 SSE 2 10 11 24 7 0 54 S 1 4 16 22 10 1 54 SSW 0 8 17 24 6 1 56 SW 2 6 16 13 9 0 46 WSW 1 5 19 20 2 0 47 W 1 9 9 2 0 1 22 WNW l' 2 3 5 0 0 11 NW 3 4 5 7 2 1 22 NNW 1 3 15 13 7 2 41 VARIABLE O O O O O O O TOTAL 14 94 185 239 100 11 643 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: 9 t 81
1 F I
- i; BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1989 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 2 2 8 2 0 14 NNE 2 5 3 5 0 0 15 NE O 3 6 5 0 0 14 ENE O 1 1 2 1 0 5 E O 1 7 11 7 0 26 ESE O 2 3 15 7 0 27 SE 1 2 18 24 9 0 54 SSE O 2 18 20 10 1 51 S 0 5 10 10 16 0 41 SSW 1 0 8 23 9 0 41 SW 1 4 15 14 2 0 36 WSW 1 2 14 4 0 0 21 W 0 1 5 4 0 0 10 WNW 2 1 4 4 1 0 12 NW 0 4 7 16 1 0 28 NNW 1 4 3 11 0 0 19 VARIABLE O O O O O O O TOTAL 9 39 124 176 65 1 414 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 . l Hours of missing stability measurements in all stability classes: 9
)
I i 82
BYRON NUCLEAR POWER STATION 1 PERIOD OF RECORD - JULY-SEPTEMBER 1989 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 2 0 4 0 1 0 7 NNE 1 2 3 3 1 0 10 NE o 4 5 1 0 0 10 ENE 3 2 4 0 0 0 9 E *O 3 3 8 3 0 17 ESE O 2 2 9 3 0 16 = SE 2 2 10 14 2 0 30 SSE O 4 6 17 16 1 44 S 1 1 11 17 18 1 49
~
p SSW 1 2 5 12 1 0 21 i SW 3 1 5 8 0 0_ 17 r WSW 1 2 4 2 0 0 9 W 2 2 2 1 0 0 7 WNW 0 1 3 5 0 0 9 NW 0 0 0 1 0 0 1 NNW 1 0 0 3 0 0 4. =F VARIABLE O O O O O O O
. TOTAL 17 28 67 101 45 2 260 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: 9 E
83 t
i-p i'. BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1989 STABILITY CLASS . EXTREHELY UNSTABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19 24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O 1 0 0 1 SE O O O O O O O , SSE O O O O O O O S 0 0 0 1 C 0 1 SSW 0 0 0 0 0 0 0 g\ SW 0 0 0 0 0 0 0 WSW 0 0 0 0 1 0 1 W 0 0 0 0 0 0 0 WNW 0 0 1 2 0 0 3 NW 0 0 1 0 0 0 1 NNW 0 0 2 0 0 0 2 VARIABLE O O O O O O O TOTAL 0 0 4 4 1 0 9
- Hours of calm in this stability class: 0 l Hsurs of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 i
I L , i 84 j
E . ,.
< I I i L
s] i BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1989 ! STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND. WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 3 0 0 0 3 i NNE O O O O 1 2 3 NE O O O O O O O ENE O O O O O O O i E O O O 2 0 0 2 ESE O O O 1 0 0 1 SE O O O O O O O SSE O O 2 1 0 0 3 S 0 0 0 0 0 0 0 SSW 0 0 0 1 0 O 1 - SW 0 0' O O O O O WSW 0 0 0 4 0 0 4 W 0 0 1 1 1 0 3 WNW 0 0 0 3 1 0 4 NW 0 0 1 3 1 0 5 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 7 16 4 2 29 Heurs 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 85
r_ o BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1989 STABILITY CLASS ~ SLIGHTLY UNSTABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 2 0 0 0 2 NNE O O O O , 1 0 1 NE O O O O O O O ENE O O 1 0 0 0 1 E O O 0- 0 0 0 0 ESE O O O O O O O SE O O O O O O O SSE O O 1 7 1 0 9 S 0 0 2 2 0 1 5 SSW 0 1 0 2 3 1 7 SW 0 0 2 1 3 0 6 WSW 0 0 2 5 0 0 7 W 0 3 1 2 0 0 6 WNW 0 1 2 2 1 0 6 NW 0 0 5 3 3 0 11 NNW 0 1 4 1 1 0 7 VARIABLE O O O O O O O TOTAL 0 6 22 25 13 2 68 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 H9urs of missing stability measurements in all stabil$ty classes: 1 1 86
- _ _j
s BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1989 STABILITY CLASS - NEUTRAL (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET, WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 11 12 38 37 8 106 ; NNE 1 8 17 6 27 5 64 ; NE o 2 8 5 0 2 17 ENE O 8 10 24 0 0 42 E o 5 4 0 0 0 9 ESE O 2 1 0 2 0 5 SE 1 0 8 11 0 1 21 SSE O 4 9 16 9 5 43 S 1 7 24 38 24 12 106 SSW 0 13 29 32 35 5 114 SW 2 6 32 35 7 4 86 WSW 1 8 16 33 7 0 65 V 4 9 19 30 21 2 85 WNW 0 13 32 TJ 19 14 128 NW 0 7 32 49 47 16 151 NNW 0 8 9 26 42 ,3 88 VARIABLE O O O C 0 0 0 TOTAL 10 111 262 393 277 77 1130 Hours of calm in this stability class: 0 H;urs of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 87
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1989 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) 7 DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 2 3 15 5 0 25 NNE O 3 6 5 1 0 15 NE O O 6 2 1 0 9 ENE O O O 3 0 0 3 E 1 3 1 0 1 0 6 ESE o 0 2 0 3 6 11 SE O 3 3 3 2 2 13 SSE 1 0 6 11 13 5 36 S 0 0 14 23 31 20 88 SSW 0 1 5 14 16 18 54 SW 1 2 8 12 14 6, 43 WSW 0 4 7 20 7 0 38 W 0 2 14 48 16 0 80 WNW 0 3 22 46 6 0 77 NW 0 6 22 68 11 0 109 NNW 0 2 9 36 12 1 60 VARIABLE O O O O O O O TOTAL 3 33 128 306 139 58 667 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 88
BYRON NUCLEAR POWER STATION ! . PERIOD OF RECORD - OCTOBER-DECEMBER 1989 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 250-30 FT) .~. WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 2 3 2 0 0 7 NNE O 1 0 0 0 0 1 NE 1 0 0 0 0 0 1 ENE O 1 0 0 0 0 1 E 2 1 1 0 0 0 4 1
;, ESE O 1 0 1 1 1 4 SE O O 1 2 5 1 9 SSE o 0 3 3 9 0 15 S 0 0 4 11 64 7 8 6 --
SSW 0 2 4 8 8 0 22 SW 0 0 4 2 1 0 7 6 i WSW 0 2 6 3 1 0 12 l W 0 0 1 6 1 0 8 WNW 0 2 2 8 0 0 12 i NW 1 1 2 9 0 0 13 NNW O O 3 11 0 0 14 VARIABLE O O O O. 0 0 0 j TOTAL 4 13 34 66 90 9 216 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
! 89
p , t e i c r BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1989 - STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT) WINDS MEASURED AT 250 FEET c WIND WIND SPEED (IN MPH) l DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL , N 0 1 1 0 0 0 2 NNE O 1 0 0 0 0 1 NE O O O O O O O ENE O 1 0 0 0 0 1 E O O O O O O O ESE O O O 1 0 0 1 SE . 0 1 0 0 1 0 2 SSE O O O 1 5 3 9 ! S 1 1 3 5 19 1 30 , SSW 0 1 2 9 5 0 17 , SW 0 0 2 5 2 0 .9 WSW 0 0 2 0 0 0 2 W 0 0 0 0 0 0 0 WNW 0 0 1 0 0 0 1 ; NW 0 1 1 5 0 0 7 NNW 0 0 1 5 0 0 6 VARIABLE O O O O O O O TOTAL 1 7 13 31 32 4 08 Hours of calm in this stability class 0 Hours of missing wind measurements in this stability cicss 0 Hours of missing stability measurements in all stability classes: 1 90 _
g Y
'e g.
r i I - I t APPENDIX III : INTERLABORATORY COMPARISON PROGRAM RESULTS J b b 91
Interlaboratory Comparison Program Results Teledyne Isotopes Midwest Laboratory (formerly Hazleton Environmental Sciences) has participated in interlaboratory comparison (crosscheck ) programs since the formulation of its quality control program in December 1971. These programs are operated by agencies which supply environmental-type samples (e.g., milk or water) containing concentrations of radionuclides known 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 analytica? procedures and to alert it to > any possible problems. Participant laboratories measure the concentrations of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used. The results in Table A-1 were obtained through participation in the environmental sample crosscheck program for milk, water, air filters, and food samples during the period January 1986 through November,1989. This program has been conducted by the U.S. Environmental Protection Agency Intercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Labora- " tory, Las Vegas, Nevada. The results in Table A-2 were obtained for thermeluminescent dosimeters (TLD's) during the period 1976, 1977, 1979, 1980, 1984, and 1985-1986 through partici-pation in the Second, Third, Fourth, Fifth, Seventh, and Eighth International Intercomparison of Environmental Dosimeters under the sponsorships listed in Table A 2. Also Teledyne testing results are listed. Table A-3 lists results of the analyses on in-house spiked samples. Table A-4 lists results of the analyses on in-house " blank" samples. Attachment B lists acceptance criteria for " spiked" samples. Addendum to Appendix A provides explanation for out of limit results. i l 92
I Table A-1. U.S. Environmental Protection Agency's crosscheck program, com- ) parison of EPA and Teledyne [sotopes Midwest Laboratory results 1 for milk, water, air filters, and food samples, 1986 through 1989.4 i Concentration in pCi/l b j Lab Sample Date TIML Result EPA Resultd l Code Type Collected Analysis 12sc Is, N=1 Control Limits l STF-447 Food Jan 1986 Sr-89 24.312.5 25.025.0 16.3-33.7 l Sr-90 17.320.6 10.011.5 7.4-12.6 1-131 22.712.3 20.010.6 9.6-30.4 i Cs-137 16.320.6 15.025.0 6.3-23.7 K 927146 9502144 701-1199 i STW-448 Water Feb 1986 Cr-51 45.0t3.6 38.015.0 29.3-46.7 Co-60 19.711.5 18.025.0 9.3-26.7 Zn-65 44.013.5 40.015.0 31 .3-4 8.7 Ru-106 <9.0 0.0i5.0 0.0-8.7 Cs-134 28.322.3 30.015.0 21.3-38.7 Cs-137 23.720.6 22.015.0 13.3-30.7 STW-449 Water Feb 1986 H-3 5176248 52272525 4317<6137 STW-450 Water Feb 1986 0 total 8.010.0 9.026.0 0.0-19.4 STM-451 Milk Feb 1986 I-131 7.020.0 9.026.0 0.0-19.4 STW-452 Water Mar 1986 Ra-226 3.820.1 4.110.6 3.0-5.2 Ra-228 11.010.5 12.421.8 9.2-15.5 STW-453 Water Mar 1986 Gr. alpha 6.710.6 15.015.0 6.3-23.7 Gr. beta 7.320.6 8.015.0 0.0-16.7 STW-454 Water Apr 1986 I-131 7.020.0 9.016.0 0.0-19.4 STW-455 Water Apr 1986 456 (Blind) Sample A Gr. alpha 15.021.0 17.025.0 8.3-25.7 Ra-226 3.120.1 2.920.4 2.1-3.7 Ra-228 1.520.2 2.020.3 1.5-2.5 , Uranium 4.720.6 5.026.0 0.0-15.4 l L Sample B Gr. beta 28.711.2 35.025.0 26.3-43.7 l Sr-89 5.7t0.6 7.025.0 0.0-15.7 l Sr-90 7.020.0 7.021.5 4.4-9.6 Co-60 10.721.5 10.015.0 1.3-18.7 Cs-134 4.021.7 5.025.0 0.0-13.7 Cs-137 5.320.6 5.025.0 0.0-13.7 s 93 g
l o Table A-1. (continued) Concentration in DCi/lb " Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis 120c 15, N=1 Control Limits i STAF-457 Air April 1986 Gr. alpha 13.710.6 15.015.0 6.3-23.7 Filter Gr. beta 46.3i0.6 47.0t5.0 38.3-55.7 Sr-90 14.7t0.6 18.011.5 15.4-20.6 Cs-137 10.7t0.6 10.025.0 1.3-18.7 STU-458 Urine April 1986 Tritium 4313170 4423t189 4096-4750 STW-459 Water May 1986 Sr-89 4.310.6 5.Di5.0 0.0-13.7
. Sr-90 5.010.0 5.0tl.5 2.4-7.6 STW-460 Water May 1986 Gr. alpha 5.310.6 8.015.0 0.0-16.7 ,
Gr. beta 11.3tl.2 15. 0t5. 0 6.3-23.7 STW-461 Water June 1986 Cr-51 <9.0 0.0t5.0 0.0-8.7 Co-60 66.0tl.0 66.015.0 57.3-74.7 . 2n-65 87.3tl.5 86.0t5.0 77.3-94.7 Ru-106 39.7t2.5 50.015.0 41.3-58.7 i Cs-134 49.312.5- 49.0t5.0 40.3-57.7 Cs-137 10.311.5 10.015.0 1.3-18.7 STW-462 Water June 1986 Tritium 3427i25 3125t361 2499-3751 STM-464 Milk June 1986 Sr-89 <1.0 0.015.0 0.0-8.7 Sr-90 15.310.6 16.0tl.5 13.4-18.6 I-131 48.312.3 41.Di6.0 30.6-51.4 Cs-137 43.711.5 31.015.0 22.3-39.7 K 1567t114 1600180 1461-1739 STW-465 Water July 1986 Gr. alpha 4.7t0.6 6.0f5.0 0.0 14.7 Gr. beta 18.711.2 18.015.0 9.3-26.7 STW-467 Water August 1986 I-131 30.310.6 45.016.0 34.4-55.4 STW-468 Water August 1986 Pu-239 11.310.6 10.111.0 8.3-11.9 STW-469 Water August 1986 Uranium 4.0t0.0 4.0t6.0 0.0-14.4 STAF-470 Air Sept 1986 Gr. alpha 19.3tl.5 22.015.0 13.3-30,7 471 Filter Gr. beta 64.0i2.6 66.0t5.0 57.3-74.7 472 Sr-90 22.011.0 22.015.0 19.4-24.6 ' Cs-137 25.711.5 22.015.0 13.3-30.7 STW-473 Water Sept 1986 Ra-226 6.010.1 6.lt0.9 4.5-7.7 Ra-228 8.711.1 9.111.4 6.7-11.5 94
Table A-1. (continued). Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis 120C 15, N=1 Control Limits STW-474 Water Sept 1986 Gr. alpha 16.313.2 15. 0t5.0 6.3-23.7 Gr. beta 9.0t1.0 8.015.0 0.0-16.7 STW-475 Water Oct 1986 Cr-51 63.315.5 59. 0t5.0 50.3-67.7 Co-60 31.0t2.0 31.0t5.0 22.3-39.7 Zn-65 87.315.9 85.0t5.0 76.3-93.7 Ru-106 74.7t7.4 74.0t5.0 65.3-82.7 Cs-134 25.7t0.6 28.0t5.0 19.3-36.7 Cs-137 46.311.5 44.0t5.0 35.3-52.7 STW-476 Water Oct 1986 H-3 5918160 5973tS97 4938-7008 SPW-477 Water Oct 1986 478 (Blind) P Sample A Gr. alpha 34.0t6.0 40.0*5.0 31.3-48.7 Ra-226 5.8t0.2 6.0f0.9 4.4-7.6 Ra-228 2. 7tl . 0 5.0t0.8 3.7-6.3 Uranium 11.0t0.0 10.016.0 0.0-20.4 Sample B Gr. beta 38.7tl.2 51.0*5.0 42.3-59.7 Sr-89 5.010.0 10.0t5.0 1.3-18.7 Sr-90 3.0t0.0 4.0tl.5 1.4-6.6 Co-60 24.711.2 24.0t5.0 15.3-32.7 Cs-134 11.0t2.0 12.0*5.0 3.3-20.7 Cs-137 9.3tl.2 8.0 5.0 0.0-16.7 STM-479 Milk Nov 1986 Sr-89 7.711.2 9.015.0 0.3-17.7 Sr-90 1.0t0.0 0.0tl.5 0.0-2.6 I-131 52.3t3.1 49.016.0 38.6-59.4 Cs-137 45.7t3.1 39.015.0 30.3-47.7 K 14891104 1565t78 1430-1700 STU-480 Urine Nov 1986 H-3 5540t26 5257t912 4345-6169 STW-481 Water Nov 1986 Gr. alpha 12.0 4.0 20.015.0 11.3-28.7 Gr. beta 20.013.5 20.015.0 11.3-28.7 STW-482 Water Dec 1986 Ra-226 6.7t0.2 6.811.0 5.0-8.6 Ra-228 5.220.2 11.1tl.7 8.2-14.0 STW-483 Water Jan 1987 Sr-89 19.7t5.0 25.015.0 16.3-33.7 Sr-90 21.0t2.0 25.011.5 22.4-27.6 l 95 l
i i .. Table A-1. (continued).
- Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis 120C 15, N=1 Control Limits STW-484 Water Jan 1987 Pu-239 17.0t2.3 16.711.7 13.8-19.6 STF-486 Food Jan 1987 Sr-90 36.0t4.0 49.0*10.0 31.7-66.3 I-131 78.0t3.4 78.028.0 64.1-91. 9 Cs-137 89.723.0 84.015.0 75.3-92.7 K 942tS6 980149 895-1065 STF-487 Food Jan 1987 SR-90 2.0t0.0 ---
(Blank) I-131 '
<3 ---
Cs-137 <2 --- K 993t102 --- STW-488 Water Feb 1987 Co-60 49.0i0.0 50.0t5.0 41.3-58.7 Zn-65 96.0t7.2 91.015.0 82.3-99.7 Ru-106 92.0120.2 100.0t5.0 91.3-108.7 Cs-134 53.0f3.4 59.0t5.0 50.3-67.7 Cs-137 89.314.6 87.0t5.0 78.3-95.7 STW-489 Water Feb 1987 H-3 4130t140 42091420 3479-4939 STW-490 Water Feb 1987 Uraniurr 8.3tl.2 8.0f6.0 0.0-18.4 STM-491 Milk Feb 19.87 I-131 10.0t0.0 9.010.9 7.4-10.6 STW-492 Water Mar 1987 Gr. alpha 3.711.2 3.015.0 0.0-11.7 Gr. beta 11.3tl.2 13.015.0 4.3-21.7 STW-493 Water Mar 1987 Ra-226 7.0t0.1 7.311.1 5.4-9.2 Ra-228 7.122.3 7.5tl.1 5.5-9.5 STW-494 Water Apr 1987 I-131 8.0t0.0 7.0t0.7 5.8-8.2 STAF-495 Air Apr 1987 Gr. alpha 15.0t0.0 14.0t5.0 5.3-22.7 Filter Gr. beta 41.0t2.0 43.0t5.0 34.3-51.7 Sr-90 16.3tl.2 17.011.5 14.4-19.6 Cs-137 7.010.0 8.0*5.0 0.0-16.7 STW-496 Water Apr 1987 497 (Blind) { Sample A Gr. alpha 30. 7tl . 2 30.0t8.0 16.1-43.9 i Ra-226 3.910.2 3.910.6 2.9-4.9 Ra-228 4.9t0.9 4.010.6 3.0-5.0 Uranium 5.0f0.0 5.016.0 0.0-15.4 96
l . L , Table A-1. (continued) Concentration in pCi/lb
~
Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis t2ac 15, N=1 Control Limits STW-496 Water Apr 1987 497 (Blind) Sample 8 Gr. Beta '69.319.4 66.015.0 57.3-74.7 Sr-89 16.3t3.0 19.0t5.0 10.3-27.7 Sr-90 10.0t0.0 10.0tl.5 7.4-12.6 Co-60 8.3t3.0 8.0t5.0 0.0-16.7 Cs-134 19.012.0 20.015.0 11.3-28.7 Cs-137 14.7tl.2 15.0t5.0 6.3-23.7 Apr 1987 STU-498 Urine H-3 6017t494 5620t795 4647-6593. 1 STW-499 Water May 1987 Sr-89 38.0t6.0 41.0t5.0 32.3-49.7 Sr-90 21.0t2.0 20.0tl.5 17.4-22.6 STW-500 Water May 1987 Gr. alpha 9.0t3.4 11.015.0 2.3-19.7 Gr. beta 10.3tl.2 7.0t5.0 0.0-15.7 STW-501 Water June 1987 Cr-51 40.018.0 41.015.0 32.3-49.7 Co-60 60.3t3.0 64.0t5.0 55.3-72.7 Zn-65 11.315.0 10.0*5.0 1.3-18.7 Ru-106 78.3t6.4 75.0t5.0 66.3-83.7 Cs-134 36.713.0 40.0t5.0 31.3-48.7 Cs-137 80.314.2 80.0i5.0 71.3-88.7 STW-502 Water June 1987 H-3 2906t86 2895t357 2277-3513 STW-503 Water June 1987 Ra-226 6.910.1 7.311.1 5.4-9.2 Ra-228 13.311.0 15.212.3 11.2-19.2 STM-504 Milk June 1987 Sr-89 57.0td.3 69.0t5.0 60.3-77.7 l Sr-90 32.0tl.0 35.0il.5 32.4-37.6 I-131 64.0t2.0 59.016.0 48.6-69.4 Cs-137 77.7t0.6 74.0t5.0 65.3-82.7 K 1383t17 1525t76 1393-1657 STW-505 Water July 1987 Gr. alpha 2.3t0.7 5.015.0 0.0 13.7 , Gr. beta 4.011.0 5.015.0 0.0-13.7 STF-506 Food July 1987 1-131 82.7t4.6 80.0t8.0 66.1-93.9 Cs-137 53.713.0 50.015.0 41.3-58.7 K 1548tS7 1680184 1534-1826 STW-507 Water Aug 1987 I-131 45.714.2 48.0i6.0 37.6-58.4 STW-508 Water Aug 1987 Pu-239 5.8t0.2 5.320.5 4.4-6,2 97
q T able A-1. (continued) Concentration in pC1/lb L ab S ample Date TIML Result EPA Result 0 C ode Type Collected Analysis 12cc Is, N=1 Control Limits s STW-509 Water Aug 1987 Uranium 13.320.3 13.026.0 2.6-23.4 STAF-510 Air Aug 1987 G r. alpha 9.720.4 10.025.0 1.3-18.7 Filter Gr. beta 28.320.6 30 .0 25.0 21.3-38.7 S r-90 10.020 .9 10.021.5 7.4-12.6 C s-137 10.011.0 10 .025.0 1.3-18.7 i STW-511 Water Sept 1987 R a-226 9.920.1 9.721.5 - 7.2-12.2 R a-228 8.121.4 6 .3 21 .0 4.6-8.0 STW-512 Water Sept 1987 G r. alpha 2.020.6 4 .0 25 .0 0.0-12.7 G r. beta 11.321.3 12 .0 25 .0 3.3-20.7 STW-513 Water Oct 1987 H-3 44732100 44922449 3714-5270 STW-514 Water Oct 1987 (81ind) Sample A Gr. alpha 29.322.6 28.017.0 15.9-40.1 R a-226 4 .9 20 .1 4 .8 20 .7 3.6-6.1 R a-228 4.211.0 3.620.5 2.7-4.5 Uranium 3 .0 20 .1 3 .0 26 .0 0.0-13.4 Sample B S r-89 14.3 1.3 16 .025 .0 7.3-24.7 S r-90 9.720.4 10.0 2d .5 7.4-12.6 C o-60 16.723 .0 16.025.0 7.3-24.7 C s-134 16.712.3 16 .0 25 .0 7.3-24.7 C s-137 24 .3 23 .3 24 .025 .0 15.3-32.7 STW-516 Water Oct 1987 C r-51 80.3117.5 70.0 25.0 61.3-78.7 C o-60 16.022 3 15.025.0 6.3-23.7 Z n-65 46 .3 25 .6 46.025 .0 37.3-54.7 R u-106 57.3215.4 61 .0 25 .0 52.3-69.7 C s-134 23.722.5 25 .0 25.0 16.3-33.7 C s-137 51.723.2 51.025.0 42.3-59.7 STU-517 Urine Nov 1987 H-3 72672100 74321743 6145-8719 STW-518 Water Nov 1987 G r. alpha 3 .0 22 .0 '7.025.0 0.0-15.7 Gr. beta 15.722.3 19 .0 25.0 10.3-27.7 STW-519 Water Dec 1987 1-131 26.0 23 .0 26.0 6.0 15.6-36.4 , 98 ,
L. Table A-1. (continued) Concentration in pCi/lb Lab Sample Date , TIML Result EPA Resultd Code Type Collected Analysi s 12aC 1s, W=1 Control Limits STW-520 Water Dec 1987 Ra-226 5.120.8 4.820.7 3.6-6.0 Ra-228 3.4t0.1 5.320.8 3.9-6.7 STW-521 Water Jan 1988 Sr-89 27.325.0 30.025.0 21.3-38.7 Sr-90 15.321.2 15.021.5 12.4-17.6 STW-523 Water Jan 1988 Gr. alpha 2.311.2 4.015.0 0.0-12.7 Gr. beta 7.7tl.2 8.015.0 0.0-16.7 STF-524 Faed Jan 1988 Sr-89 44.024.0 46.015.0 37.3-54.7 Sr-90 53.022.0 55.022.8 50.2-59.8 ) 1-131 102.324.2 102.0t10.2 84.3-119.7 Cs-137 95.7t6.4 91.015.0 82.3-99.7 K 1011t158 1230162 1124-1336 STW-525 Water Feb 1988 Co-60 69.312.3 69.015.0 60.3-77.7 Zn-65 99.013.4 94.0t9.4 77.7-110.3 Ru-106 92.7214.4 105.0210.5 86.8-123.2 Cs-134 61.718.0 64.015.0 55.3-72.7 Cs-137 99.723.0 94.015.0 85.3-102.7 STW-526 Water Feb 1988 H-3 34531103 33271362 2700-3954 STW-527 Water Feb 1988 Uranium 3.020.0 3.016.0 0.0-13.4 ST -52 Water Mr 98 Ra 226 0.6 7. t . 5. -9 6 Ra-228 nae 7.721.2 5.7-9.7 STW-530 Water Mar 1988 Gr. alpha 4.311.2 6.025.0 0.0-14.7 Gr. beta 13.3tl.3 13.015.0 4.3-21.7 STAF-531 Ai r Mar 1988 Gr. alph'a 21.022.0 20.015.0 11.3-28.7 Filter Gr. beta 48.020.0 50.025.0 41.3-58.7 I Sr-90 16.7tl.2 17.011.5 14.4-19.6 Cs-137 18.721.3 16.025.0 7.3-24.7 STW-532 Water Apr 1988 I-131 9.0t2.0 7.520.8 6.2-8.8 n i 99
r , Table A-1. .(continued) Concentration in pCi/1b Lab Sampie 0 ate TIML P.esult EPA Resultd Code Type. Collected Analysis 12b C 1s, N=1 Control Limits STW-533 Water Apr 1988 534 (Blind) Sample A Gr. alpha NDf 46.0111.0 27.0-65.0 Ra-226 2 6.421.0 4.7-8.1 Ra-228 G 5.620.8 4.2-7.0 Uranium 6.Jt0.0 6.026.0 0.0-16.4 Sample 8 Gr. beta 2 57.025.0 40.3-65.7 Sr-89 3.321.2 5.015.0 0.0-13.7 Sr-90 5.321.2 5.0tl.5 2.4-7.6 Co-60 63.3tl.3 50.025.0 41.3-58.7 Cs-134 7.721.2 7.0t$,0 0.0-15.7 Cs-137 8.3tl.2 7.015.0 0.0-15.7 STU-535 Urine Apr 1988 H-3 6483t155 62022620 5128-7276 STW-536 Water Apr 1988 Sr-89 14.711.3 20.025.0 11.3-28.7 , Sr-90 20.012.0 20.0tl.5 17.4-22.6 i STW-538 Water June 1988 Cr-51 331.7113.0 302.0130.0 250.0-354.0 Co-60 16.0t2.0 15.0t5.0 6.3-23.7 Zn-65 107.7211.4 101.0210.0 83.7-118.3 Ru-106 191.3211.0 195.0120.0 160.4-229.6 Cs-134 18.314.6 20.025.0 11.3-28.7 Cs-137 26.3tl.2 25.015.0 16.3-33.7 STW-539 Water June 1988 H-3 5586192 55652557 4600-6530 STM-541 Milk June 1988 Sr-89 33.7211.4 40.025.0 31.3-48.7 ' Sr-90 55.3t5.8 60.013.0 54.8-65.2 I-131 103.7t3.1 94.029.0 78.4-109.6 52.723.1 51.025.0 42.3-59.7 Cs-137 K 1587t23 1600280 1461-1739 STW-542 Water July 1988 Gr. alpha 8.714.2 15.015.0 6.3-23.7 Gr. beta 5.321.2 4.015.0 0.0-12.7 STF-543 Food July 1988 Sr-89 ND 33.025.0 24.3-41.7 Sr-90 ND 34.022.0 30.5-37.5 I-131 115.015.3 107.0211.0 88.0-126.0 4 Cs-137 52.7t6.4 49.015.0 40.3-57.7 ! K 1190166 1240162 1133-1347 ! i 100
, . . . .. . , - . . r. . .- l
E ., Table A-1. (continued) Concentration in pCi/lb Lab Sample Date TIML Result _ EPA Resul td Code- Type Coll ected Analysis 12cC 1s, N=1 Contrcl Limits STW-544 Water Aug 1988 1-131 80.020.0 76.028.0 62.1-89.9 STW-545 Water Aug 1988 Pu-239 11.020.2 10.221.0 8.5-11.9~ STW-546 Water Aug 1988 Uranium 6.020.0 6.026.0 0.0-16.4 STAF-547 Air Aug 1988 Gr. alpha 8.020.0 8.015.0 0.0-16.7 Filter Gr. beta 26.311.2 29.025.0 20.3-37.7 Sr-90 8.022.0 8.0tl.5 5.4-10.6 Cs-137 13.0t2.0 12.025.0 3.3-20.7 STW-548 Water Sep 1988 Ra-226 9.320.5 8.422.6 6.2-10.6 Ra-228 5.820.4 5.421.6 4.0-6.8 STW-549 Water Sep 1988 Gr. alpha 7.022.0 8.0t5.0 0.0-16.7 Gr. beta 11.3tl .2 10.025.0 1,3-18.7 STW-550 Water Oct 1988 Cr-51 252.0t14.0 251.0225.0 207.7-294.3 Co-60 26.022.0 25.015.0 16.3-33.7 Zn-65 158.3210.2 151.0115.0 125.0-177.0 Ru-106 153.029.2 152.0t15.0 126.0-178.0 Cs-134 28.725.0 25.025.0 16.3-33.7 Cs-137 16.3tl.2 15.025.0 6.3-23.7 STW-551 Water Oct 1988 H-3 2333t127 2316t350 1710-2927 STW-552 Water Oct 1988 553 (Blind) Sample A Gr. alpha 38.328.0 41.0210.0 23.7-58.3 Ra-226 4.St0,5 5.020.8 3.6,6.4 Ra-228 4.420.6 5.220.8 3.6-6.4 Uranium 4.7tl.2 5.026.0 0.0-15.4 Sample B Gr. beta 51.323.0 54.015.0 45.3-62.7- , Sr-89 3.7tl.2 11.025.0 2.3-19.7 l Sr-90 10.7t1.2 10.021.5 7.4-12.6 Cs-134 15.322.3 15.025.0 6.3-23.7 Cs-137 16.7tl.2 15.025.0 6.3-23.7 l i 1' l l 101 l
K Tabl e
- A-1.- (continued)-
Concentration in pCi/lb Lab Sample Date TIML Result _ EPA Re sul td= Code Type Collected Analysi s 2 2t7C 15, N =1- Control Limits STM-554 Milk Oct 1988 Sr-89 40.317.0 40.025.0 31.3-48.7 Sr-90 51.0t2.0 60.013.0 54 .8 -6 5.2 _ l-131 94.0t 3. 4 91.029.0 75.4-106.6 i Cs-137 45.014.0- 50.015.0 41.3-58.7' K 1500145 1600280 1461-1739 STU-555 Urine Nov 1988 H-3 3030t209 3025t359 2403-3647 STW-556 Water Nov 1988 Gr. alpha' 9.013.5 9.015.0 0.3-17.7 l Gr. beta 9.721.2 9.015.0 0.3-17.7 j STW-557 Water Dec 1988 1-131 108.723.0 115.0t12.0 94.2-135.8 -l l STW-559 Water Jan 1989 Sr-89 40.028.7 40.025.0 31.3-48.7 ;
, Sr-90 24.323.1 25.0tl.5 22.4-27.6 l STW-560 ' Water Jan 1989 Pu-239 5.821.1 4.220.4 3.5-4.9 j STW-561 Water Jan 1989 Gr. alpha 7.3tl.2 8.0t5.0 0.0-16.7 !
Gr. beta- 5.3t1.2 4.025.0 0.0-12.7 STW-562 Water Feb 1989 Cr-51 245t46 235 24 193.4-276.6 Co-60 10.012.0 10.0t5.0 1.3-@.7' 1 Zn-65 170t10 159t16 139.2-186.7 Ru-106 181t7.6 178118 146.8-209.2 Cs-134 9.723.0 10.015.0 1,3-18.7 l Cs-137 11.721.2 10.015.0 1.3-18.7 - r lI . l~ l L 1 l l l l
, 1 l
l l 102 l
vs V
-Table A-1. (continued)
Concentration in pCf/l b
- Lab Sample -Date c TIML Result EPA Resultd Code Type Collected Analysis 12cC 1s, N=1 Control Limits STW-563- Water Feb 1989 I-131 109.0 4.0 106.0211.0 86.9-125'1.
-l STW-564 Water Feb 1989 H-3 2820 20 27542356 2137-3371 'l i
STW-565 Water Mar 1989 Ra-226 4.2 0.3 4.910.7 3.7-6.1 K Ra-228 1.921.0 1.7 0.3 1,2-2.2' STW-566 Water Mar 1989 U 5.0 0.0 5.026.0 0.0-15.4 STW-567 AirFilter Mar 1989 Gr._ alpha 21.711.2 21.015.0 12.3-29.7 4 Gr. beta 68.324.2 62.025.0 53.3-70.7 Sr-90 20.0 2.0 20.011.5 17.4-22.6 Cs-137 21.321.2 20.0 5.0 11.3-28.7 9 STW-568 Water Apr 1989 569 (811nd)
. Sample A Gr. alpha 22.722.3 29.0t7.0 16.9-41.2 - ,
Ra-226 3.610.6 3.5 0.5 2.6-4.4 't Ra-228 2.621.0 3.610.5 2.7-4.5 U 3.020.0 3.0t6.0 0.0-13.4-Sample B Gr. beta 52.326.1 57.0t5.Q 43.3-65.7 ' Sr-89 S.125.4 8.015.0 0.0-16.7 Sr-90 7.0 0.0 8.0 1.5 5.4-10.6 1 Cs-134 21.0 5.2 20.025.0 11.3-28.7 ! l Cs-137 23.0 2.0 20.025.0 11.3-28.7 L STM-570' Milk Apr 1989 Sr-89 26.0210.0 39.025.0 30.3-47.7 I Sr-90 45.7 4.2 55.0 3.0 49.8-60.2 Cs-137 54.0 6.9 50.0t5.0 41.3-58.7 K-40 15212208 1600280 1461-1739 L I L I 1 L 103 l r
i Table A-1. ( continued) Concentration in pCi/lb Lab Sample Date TIML Result _ EPA Resultd
. Code Type Collected Analysis 2 2aC 15, N=1 Control Limits 9
STW-571 Water May 1989 Sr-89 40.7 6.025.0 0.0-14.7 Sr-90 5.021.0 6.021.5 3.4-8.6 STW-572 Water May 1989 Gr. alpha 24.012.0 30.028.0 16.1-43.9 Gr. beta 49.3215.6 50.015.0 41 .3- 58.7 STW-573 Water Jun 1989 Ba-133 50.711.2 49.025.0. 40.3-57.7 < Co-60 31.322.3 31.025.0 22.3-39.7 Zn-65 167t10 165117 135.6-194.4 Ru-106 12319.2 128213 105.5-150.5 Cs-134 40.3tl.2 3925 30.3-47.7 Cs-137 22.3*1.2 20t5 11.3-28.7 STW-574 Water Jun 1989 H-3 45131136 45032450 3724'5282 STW-575 Water Jul 1989 Ra-226 , 16.823.1 17.722.7 13.0-29 4 l Ra-228 13.823.7 18.322.7 13./. . 1. STW-576 Water Jul 1989 0 40.321.2 41.016.0 30 - STW-577 Water Aug 1989 I-131 84.7t5.8 83.028.0 69.1-$3.s l STW-579 Air aug 1989 Gr. alpha 6.0t0.0 6.025.0 0.0-14.7 l Filter Cs-137 10.312.3 10.025.0 1.3-18.7 l STW-580 Water Sep 1989 Sr-89 14.721.2 14.025.0' 5.3-22.7 Sr-90 9.7tl.2 10.021.5 7.4-12.6 l STW-581 Water Sep 1989 Gr. alpha 5.0t0.0 4.025.0 0.0-12.7 i Gr. Beta 8.722.3 6.025.0 0.0-14.7 i. l 104
e Table A-1.- (continued) - Concentration in pCi/lb _ Lab Sample Date TIML Result EPA Resulta _ Code Type Collected Analysis 22cc is, N=1 Control Limits STW-583 Water Oct 1989 Ba-133 60.3210.0 59.0:6.0 48.6-69.4 Co-60 29.0 4.0 30.0 5.0 21.3-38.7-Zn-65 132.3 6.0 129.0 13.0 106.5-151.5 Ru-106 155.326.1 161.0 16.0 133.3-188.7. Cs-134 30.7:6.1 29.0:5.0- 20.3-37.7 Cs-137 66.324.6 59.025.0 50.3-67.7 STW-584 Water Oct 1989 H-3 3407 150 3496:364 2866-4126 l' i, STW-585 Water Oct 1989 586 (Blind) Sample A Gr. Alpha 41.729.4 49.0212.0 28.2-69.8 Ra-226 7. 9:0. 4 8.421.3 6.2-10.6 - Ra-228 4.420.8 4.120.6 3.1-5.1 l U 12.0!0.0 12.0 6.0 1.6-22.4 1 Sample B Gr. 8 eta 31.7 2.3 32.0 5.0- 23.3-40.7 Sr-89 13.3 4.2 15.025.0 6.3-23.7 Sr-90 7.022.0 7.0 3.0 4.4-9.6 Cs-134 5.0 0.0 5.025.0 0.0-13.7. Cs-137 7.0 0.0 5.025.0 0.0-13.7 STW-587 Water Nov 1989 Ra-226- 7.9 20.4 8.7 1.3 6.4-11.0 . Ra-228 8.921.2 9.3!1.2 6.9-11.7 l STW-588 Water Nov 1989 U 15.0 0.09 15.026.0 4.6-25.4 a Results obtained by Teledyne Isotopes Midwest Laboratory as a participant in the environmental' sample crosscheck program operated by the Interccuparison and Cali-bration Section, Quality Assurance Branch,. Environmental Monitoring and Support Laboratory, U.S. Environmental Protection Agency (EPA), Las Ve b All results are in the pCi/1, except for elemental potassium (K) gas, Nevada. data;in milk, l which are in mg/1; air filter samples, which are in pCi/ filter; and food, which is i in mg/kg. l c Unless otherwise indicated, the TIML results are given as the mean i 2 standard . deviations for three detenninations. I' d USEPA results are presented as the known values and expected laboratory precision (1s,1 detennination) and control limits as defined by EPA. l e NA = Not analyzed, f ND = No data. Not analyzed due to relocation of the lab. 9 Sample was analyzed but the results not submitted to EPA because deadline was missed. I 4i 105 .-
Table A-2. Crosscheck program results, thermoluminescent dosimeters (TLDs)'.. Teledyne Average'12 od Lab TLD Result Known (all Code Type Measurement 12aa Valuec part ic ipants) 2nd International-Intercomparisonb 115-2 CaF2:Mn Fihld 17.011.9 '17.1 16.417.7 Bulb Lab 20.814.1 21.3 18.817.6-3rd International Intercomparisone 115-3 CaF2:Mn Field 30.713.2 34.914.8 31.5t3.0
- Bulb 8 Lab 89.616.4 91.7114.6 86.2124.0 4th International Interccmparisbnf 115-4 CaF2:Mn Field 14.111.1 14.111.4 16.019.0-Bulb Lab (Low) 9.311.3 12.212.4 12.017.6 Lab (High) 40.411.4 .45.819.2 43.9113.2 Sth International Ir.tercomparison9 ll5-5A CaF2:Mn Field 31.411.8- 30.016.0 30.2114.6 Bulb Lab at 77.415.8 75.217.6 -75.8140.4 beginning Lab at 96.6t5.8 88.418.8 90.7131.2 end da g C-ee p 9' e-% -
w T+4' _ L- '
-- - - --- v-- " - - t- - '32
Table A-2. (Continued) mR Teledyne ' Average'120 d Lab TLD Result Known '(all Code Type Measurement 12aa Valuec participants) 115-5B LIF-100 Field 30.314.8 30.016.0 30.2114.6 Chips Lab at 81.117.4 75.217.6 75.8140.4 beginning Lab at 85.4111.7 88.418.8 90.7131.2 the end 7th International Intercomparisonh 5 ll5-7A LiF-100 Field 75.412.6 75.816.0 75.1129.8 Chips Lab (Co-60) 80.013.5 79.914.0 71.9127.6 Lab (Cs-137) 66.612.5 75.013.8 73.0122.2 115-78 CaF2:Mn Fleid 71.512.6 75.816.0 75.1129.8 Bulbs Lab (C0-60) 84.816.4 79.914.0 77.9127.6 Lab (Cs-137) 78.811.6 75.013.8 73.0122.2 115-7C CaSO4 :Dy Field 76.812.7 75.816.0 75.1129.8 Cards
' Lab (Co-60) 82.513.7 79.914.0 77.9127.6 Lab (Cs-137 79.013.2- 75.013.8 73.0122.'2 h
o . .t.
..i a Table A-2. '(Continued) _
l "R l Teledyne Average'120.d. . I Lab TLD. .Resul t Known (all Code Type . Measurement. 12ca- Valuec participants) 8th International Intercomparisoni 115-8A LiF-100 Field Site 1 29.511.4 29.711.5 28.9112.4 -> Chips l Field Site 2 11.310.8 10.410.5' '10.119.06 , i Lab (Cs-137) 13.710.9 17.210.9 16.216.8 115-8B CaF2:Mn Field Site 1 32.311.2 29.711.5 28.9112.4 Bulbs Field Site'2 9.011.0 10.410.5 - 10.119.0 Lab (Cs-137) 15.810.9 17.210.9 16.216.8 115-8C CaSO4 :Dy Field Site 1 32.310.7 29.711.5 28.9212.4 Cards Field Site 2 10.610.6 10.410.5 10.119.0 , 8 Lab (Cs-137 18.110.8 17.210.9' 16.216.8. Teledyne Testingj 89-1 LiF-100 Lab 21.0t0.4 22.4 - Chips 89-2 Teledyr.e Lab 20.911.0 20.3 - CaSO4 :Dy Cards a Lab result given is the' mean t2 - standard deviations of three determinations.- b Second International Intercomparison of Environmental Dostmeters conducted in April of 1976 by the Health and Safety Laboratory (GASL), New York, New York, and the School of Public Health of the Uni-versity of Texas, Houston, Texas. . cd Value determined by sponsor of the intercomparison using continously operated pressurized' ion chamber. Mean 32 standard deviations of results obtained by .all laboratories participatin9 in the program.- ' _ . - . - _ . . __ ._. ~ _ -
A- . Table A-2. '(continu:d) E mR Teledyne ' Average-12o d' Lab TLD Resul t . Known (al1 Code Type Measurement ~ 2aa ValueC participants) Fora. notes continued e Third International Intercomparison of Environmental Dosimeters conducted in summer of 1977. by Oak Ridge National Laboratory and the School of Public Health of the University of Texas, Houston, Texas. f Fourth International Intercomparison of Environmental Dosimeters conducted in summer of'1979 by the - School of Public Health of the University of Texas, Houston, Texas. 9 Fifth International Intercomparison of Environmental Desimeter conducted in fall of 1980 at Idaho Falls, Idaho and sponsored by the School of Public Health of the University of Texas,~ Houston, Texas and n r noen al asurements Laboratory, New York, New York, U.S. Department of Energy. , h Seventh International Intercomparison of Environmental Dosimeters conducted in the spring and summer- of 1984 at Las Vegas, Nevada, and sponsored by the U.S. Departnert of' Energy, the U.S. Nuclear Regulatory
, Commission, and the U.S. Environmental Protection Agency.
g Eighth International Intercomparison of Environmental Dosimeters conducted in the fall and winter of e 1985-1986 at New York, New York, and sponsored by the U.S. Department of Energy. 3 Chips were submitted in September, 1989 and cards were submitted in November, 1989 to Teledyne Isotopes, Inc., Westwood, NJ for irradiation. b p
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'"'!AY
__.Z____.. m,._m
. .~- [ ,- , t Table A-3. In-house spiked samples. Concentration in pCi/1 Lab Sample Date TIML Result Known Expec ted Code Type Collec ted Analysis n=3 Ac tivity Prec ision 1s, n=3a QC-MI-6 Milk Feb. 1986 Sr-89 6. 0*1. 9 6.4i3.0 8.7 Sr-90 14.2*1.7 12.912.0 5.2' I-131 34.2*3.8 35.213.5 10.4 Cs-134 32.0tl.8 27.315.0 8.7 Cs-137 35.812.1 35.0t5.0 8.7 ! QC-W-14 Water Mar. 1986- Sr-89 1.6t0.4 1.611.0 7.1 Sr-90 2.410.2 2.412.0 4.2 QC-W-15 Water Apr. 1986 I-131 44.912.4 41.517.0 10.6 Co-60 10.6t1.7 12.115.0 7.lb Cs-134 30.2*2.4 25.818.0 7.lb Cs-137 21.911.9 19.915.0 7.lb QC-MI-7 Milk Apr. 1986 I-131 39.7t3.3 41.5t7.0 10.4 Cs-134 28.7i2.8 25.818.0- 8.7 Cs-137 21.212.8 19.915.0 8.7 SPW-1 Water May 1986 Gross alpha 15.811.8 18.015.0 5c QC-W-16. Water June 1986 Gross alpha 16.2i0.7 16.912.5 8.7 Gross beta 38.4t3.5 30.215.0 8.7 QC-MI-9 Milk June 1986 Sr-89 <1.0 0.0 7.lb Sr-90 12.6tl.8 13.3t3.0 4.2b I-131 38.917.0 34.817.0 10.4 Cs-134 33.0i3.4 36.115.0 8.7 Cs-137 38.512.8 39.015.0 8.7 SPW-2 Water June 1986 Gross alpha 16.811.8 18.015.0 Sc SPW-3 Water June 1986 Gross alpha 17.710.8 18.0t5.0 Sc QC-W-18 Water Sep. 1986 Cs-134 34.715.6 31.3t5.0 8.7 Cs-137 51.li7.0 43.318.0 8.7 QC-W-19 Water Sep. 1986 Sr-89 13.614.1 15.613.5 7.lb Sr-90 6.411.6 6.2t2.0 4.2D
.. 110 i
Table A-3.1 In-house spiked samples (continued) Concentration in pCi/1 Lab Sampl e Date _ TIML Result Known Expecti3' Code Type Collected Analysi s n=3 Activi ty Precision is, n=3a QC-W-21 Water Oct . 1986 C -60 19.2t2.2 18.523.0 8.7 Cs-134 31.7t5.2 25.618.0- 8.7 Cs-137 23.8tl.0 21.625.0 8.7 QC-MI-11 Milk Oct 1986 Sr-89 12.3tl.8 14.323.0 8.7 QC-W-20 Water Nov. 1986 H-3 38552180 39602350 520b QC-W-22 Water Dec. 1986 Gross alpha 9.821.4 11.224.0 8.7 Gross beta 21.722.0 23.825.0 8.7 QC-W-23 Water Jan. 1987 I-131 29.8t2.5 27.923.0 -10.4 QC-MI-12 Milk Jan. 1987 I-131 36.521.3 32.615.0 10.4 Cs-137 32.6t4.2 27.4 8.0 8.7 QC-MI-13 Milk Jan 1987 Sr-89 10.4 2.1 12.2t4.0 8.7 Sr-90 14.6t1.6 12.623.0 5.2 I-131 49.521.2 54.928.0 10.4 Cs-134 41.6 0.0 8.7 Cs-137 33.310.6 27.428.0 8.7 QC-W-24 Water Mar 1987 Sr-89 24.723.6 25.9 t5.0 8.7 Sr-90 23.923.8- 22.828.0 5.2 QC-W-25 Water Apr 1987 I-131 28.021.9 29.315.0 10.6 QC-MI-14 Mil k Apr 1987 I-131 '25.022.2 23.9 5.0 10.4 Cs-134 42.1 0.0 8.7 Cs-137 34.2t2.0 27.217.0 8.7 QC-W-26 Water Jun 1987 H-3 3422t100 33622300 520 Co-60 24.8tl.4 26.517.0 8.7 Cs-134 42.0 0.0 8.7 Cs-137 21.220.5 21.627.0 8.7 QC-W-27 Water Jun 1987 Gr. alpha 8.521.9 10.114.0 8.7 Gr. beta 22.611.9 21.2t5.0 8.7 QC-W-28 Water Jun 1987 Gr. alpha 8.7t1.3 10.124.0 8.7 Gr. beta 12.2t5.2 9.4t3.0 8.7 111
p v;,
'O-Table A-3.. In-house spiked samples (continued)
Concentration ~ in pCi/l Lab Sanple Date . TIML Result Known^ Expected L Code Type Collected Analysis n=3 Activity Precision
-1s, n=3a QC-W-29 Water Jun 1987 Gr. alpha 16.421.3 18.9 5.0 8.7 Gr. beta 15.9 4.0 11.814.0 8.7 l
QC-MI-15 Mil k Jul 1987 Sr-90 19.421.6 18.8 3.5 5.2 1-131 43.520.7 45.327.0- 10.4 Cs-134 17.922.2 16.025.3 8.7 " Cs-137 25.421.8 22.725.0- 8.7 l QC-W-30 Water Sep 1987 Sr-89 17.5*3.0 14.315.0 8.7 , Sr-90 18.4 2.2 17.522.2 5.2 QC-W-31 Water Oct 1987 H-3 20532939 20592306 520 QC-W-32 Water Dec 1987 Gr. alpha 8.611.0 10.125.0 8.7 Gr. beta 15.220.1 13.123.0 8.7 o QC-W-33 Water Dec 1987, Gr. alpha 7.711.4 10.115.0' 8.7 Gr. beta 10.921.0 '7.923.0 8.7 i
~
QC-W-34 Water Dec 1987 Gr. alpha 4.0 0.9 5.113.0 8.7 Gr. beta 9.420.9 7.923.0 8.7 QC-MI-16 Milk Feb 1988 Sr-89 31.814.7 31.726.0 8.7 Sr 25.512.7 27.823.5 5.2 I-131 26.420.5 23.225.0 10.4 Cs-134 23.822.3 24.226.0 8.7 Cs-137 26.520.8- 25.116.0 8.7 QC-MI-17 Mil k Feb 1988 I-131 10.621.2 14.321.6 10.4 QC-W-35 Water Feb 1988 I-131 9.721.1 11.621.1 10.4 QC-W-36 ' Water Feb 1988 I-131 10.511.3 11.621.0 10.4 QC-W-37 Water Mar 1988 Sr-89 17.122.0 19.828.0 8.7 Sr-90 18.720.9 17.325.0 5.2 QC-MI-18 Mil k Mar 1988 I-131 33.222.3 26.725.0 10.4 Cs-134 31.322.1 30.225.0 8.7 Cs-137 29.9 1.4 26.225.0 8.7 112
,r ' - Table A-3. In-house spiked samples (continued) I Concentration in pC1/1 ,
~
Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision 1s, n=3a QC-W-38 Water Apr 1988 1-131 17.121.1 14.2 5.0 10.4-QC-W-39 Water Apr 1988 H-3 4439 31 41762500 '24
/
i QC-W-40 Water Apr 1988 Co-60 23.720.5 26.124.0 8.7 : Cs-134 25.422.6 29.224.5 8.7 Cs-137 26.622.3 26.224.0 8.7
-QC-W-41 Water Jun 1988 Gr. alpha 12.320.4 13.115.0 8.7 Gr. beta 22.621.0 20.125.0 8.7 QC-MI-19 Mil k Jul 1988 Sr 15.121.6 16.425.0 8.7 Sr-90 18.0t0.6 18.325.0 5.2 I-131 88.424.9 86.628.0 10.4 Cs-137 22.720.8 20.826.0 8.7 QC-W-42 Water Sep 1988 Sr-89 48.523.3 50.818.0 8.7 Sr-90 10.921.0 11.423.5 5.2 QC-W-43 Water Oct 1988 Co-60 20.913.2 21.4 3.5 8.7 Cs-134 38.721.6 38.026.0 8.7 Cs-137 19.022.4 21.023.5 8.7 -QC-W-44 Water Oct 1988 l-131 22.220.6 23.323.5. 10.4 QC-W-45. Water Oct 1988 H-3 4109 43 41532500 724 QC-MI-20 Mil k Oct 1988 I-131 59.820.9- 6'0.629.0 10.4 Cs-134 49.621.8 48.627.5 8.7 Cs-137 25.824.6 -24.724.0 8.7 QC-W-46 Water Dec 1988 Gr. alpha 11.522.3 15.225.0' 8.7 Gr. beta 26.522.0 25.725.0 8.7 QC-MI-21 Milk Jan 1989 Sr-89 25.5210.3 34.0210.0 8.7 Sr-90 28.323.2 27.123.0 5.2 1-131 540 13 550 20 10.4 Cs-134 24.522.6 22.6 5.5 8.7 Cs-137 24.020.6 20.5 5.0= 8.7 113
q
; l Table ~ A-3 _ In-house spiked samples (continued) i Concentration in pCi/1 l Lab' Sample Date 'TIML Result Known Expected-Code Type Collected Analysis n=3 Activity ._ Precision 1s, n=3a 1
QC-W-47 Water Mar 1989 Sr-89 15.223.8 16.115.0 8.7 Sr-90 16.421.7 16.923.0 5.2 QC-MI-22 Milk Apr 1989- I-131 36.321.1 37.225.0 10.4 Cs-134 20.822.8 20.728.0 8.7 Cs-137 22.222.4 20.418.0 8.7 3' QC-W-48 Water -Apr 1989 Co-60 23.522.0 '25.128.0 8.7 Cs-134 24.211.1 25.918.0 8.7 Cs-137 2.1.621.2 23.028.0 8.7 QC-W-49 Water Apr 1989 I-131 37.223.7 37.225.0 10.4 QC-W-50 Water Apr 1989 H-3 3011259 30892500 724 QC-W-51 Water Jun 1989 Gr. alpha - 13.021.8 15.0 5.0 8.7 Gr. beta 26.011.2 25.528.0 8.7
-QC-MI-23 Milk Jul 1989 Sr-89 19.426.5 22.0210.0 8.7 Sr 27.613.5 28.623.0 5.2 1-131 46.823.2 43.415.0 10.4 Cs-134 27.411.8 28.3t6.0' 8.7 Cs-137 24.121.8 20.826.0 8.7 QC-MI-24 Mil k Aug 1989 Sr-89 25.422.7 27.2210.0 8.7 Sr-90 46.011.1' 47.829.6 8.3 QC-W-52 Water Sep 1989 I-131 9.620.3 9.721.9 10.4 QC-W-53 Water Sep 1989 I-131 19.020.2 20.9 4.2 10.4 QC-W-54 Water Sep 1989 Sr-89 25.824.6 '24.724.0 8.7 l Sr-90 26.515.3 29.725.0 5.2 i
1~ a n=3 unless noted otherwise. l b n=2. L c n=1.
, 114 <
Table A-3. In-house spiked samples (continued)
- Concentration in pC1/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis -n=3 Activity Precision 1s, n=3a
-QC-MI Milk Oct 1989 I-131 70.023.3 73.5220.0 10.4 Cs-134 22.122.6 22.628.0 8.7 Cs-137 29.411.5 27.528.0 8.7 QC-W-55 Water Oct 1989 I-131 33.321.3 35.3210.0 10.4 QC-W-56 Water Oct-1989 Co-60 15.220.9 17.415.0 8.7 Cs-134 22.1 4.4 18.928.0 8.7 -
Cs-137 27.221.2 22.918.0 8.7 QC-W-57 Water Oct 1989 H-3 3334122 3379 500 724 QC-W-58 Water Nov 1989 Sr-89 10.9 1.4d 11.121.0d 8.7 Sr-90 10.421.0d 10.3 1.0d 5.2
.QC-W-59 Water Nov 1989 Sr-89 101.026.0d 104.li10.5d 17.5 Sr-90 98.023.0d 95.0210.0d 17,0 QC-W-60 Water Dec 1989 Gr. alpha 10.811.1 10.614.0 8.7 Gr. beta 11.6 0.5 11.4 4.0 8.7 I
a n=3 unless noted otherwise. b n=2. c n=1. d Concentration in pCi/ml c 4
)
115
i 1' l -. Table A-4. In-house " blank" samples.- r; Concentration in pCi/1 Acceptance Lab Sample Date Resul ts Criteria Code Type Collected Analysi s (4.66o ) (d.66o ) y BL-1 0.I. Water Nov. 1985 Gross alpha <0.1 <1 Gross beta <0.4 <4 BL-2 D.I. Water Nov. 1985 Cs-137 (gamma) '<1.9 <10
,, BL-3 0.I. Water Nov. 1985 Sr <0, 5 <5 Sr-90 <0.6 <1 BL-5 D.I. Water Nov. 1985 Ra-226 <0.4 <1 Ra-228 <0.4 <1 SPW-2265 D.I. Water Apr. 1985 Gross alpha <0.6 <1 Gross beta <2.2 <4 Sr-89 <0. 2 <5 Sr-90 <0.4 <1 I-131 <0.2 <1 Cs-137 (gamma) <7.4 <10 BL D.I. Water Apr. 1986 Gross alpha <0.4 <1 BL-7 D.I. Water Apr. 1986 Gross alpha <0.4 <1 BL-8 D.I. Water June 1986 Gross alpha <0.4 <1 a
BL-9 0.I. Water June 1986 Gross alpha <0.3 <1 SPW-3185 D.I. Water Jan 1987 Ra-226 <0 .1 <1 Ra-228 <0.9 <1
< SPS-3292 Milk Jan 1987 I-131 <0.1 <1 Cs-134 (6. 2 <10 Cs-137 (6 . 4 <10 SPW-3554 D.I. Water Feb 1987 H-3 <180 <300
, Gross beta <2.6 <4 SPS-3555 Milk Feb 1987 Sr-89 <0.6 <5 Se-90 1.9 0.4a <1 SPS-3731 Milk Mar 1987 Cs-134 <2.2 <10 Cs-137 <2.5 <10 a low level (1 - 5 pC1/1) of Sr-90 concentration in milk is not unusual.
116
= =._ = _- = _ ___ ___:_ ___-___- _ - - - - _= - _ _ _ - _-__:==___ _ _ _ _ _ _ _ _
.+
1 1 g
+ .
In-house " blank" samples (continued). Table A-4. Concentration in pC1/1 c Acceptance Lab- Sampl e Date Resul ts Criteria Code Type Coll ected Analysi s : (4.66a ); (4.663 ) SPS-3732 0.I. Water Mar 1987 Sr-89 <0 . 9 <5 Er-90 (0.8 <1 1-131 (0. 3 <1 Co-60 <2.3 <10 Cs-134 <2.2 <10 Cs-137 <2.4 <10 Ra-226 c0.1 <1 Ra-228 <1.0 <1 Wp-237 <0.04 <1 Th-230 c0.05 <0.1 Th-232 (0.02 <0.1 U-234 c0.05 (0.1 U-235 (0.03 <0.1 U-238 <0.03 - <0.1 SPS-4023 Mil k - May 1987 I-131 <0.1 <1 SPS-4203 D. I.- Water May 1987 Gross alpha <0.7 <1 Gross beta <1.7 <4 lSPS-4204 Milk May 1987 Sr-89 <0. 5 <5 Sr-90. 2.4 0.6a <1 SPS-4390 Mil k Jun 1987 Cs-134 <4.7 <10 Cs-137 (5.2 (10 SPS-4391 D.I. Water Jun 1987 Sr-89 <0 . 4 <S Sr-90 <0.4 <1 1-121 (0.1 <1 Co-60 <3.8 <10 Cs-137 <5.7 <10 Ra-226 (0.1 <1 Ra-228 <0.9 <1 SPW-4627 D.I. Water Aug 1987 Gross alpha <0.6 <1 Gross beta <1.4 (4 Tritium <150 SPS-4628 Mil k Aug 1987 Sr-89 <0.6 <5 Sr-90 2.410.6a <g SPS-4847 Mil k Sep 1987 Cs-134 <4.4 <10 Cs-$37 <5.3 <10 a Low level (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual. 117
~ ~ ~
~
!:jj{ j ,
1c;
.Tabl e A-4. In-house. " blank" samples (continued). j i
Concentration in pC1/1 ~ Acceptance i i Lab Sample Date Re:Gits- Criteria J Code Type Collected Analysis (4.66a ) (4.660 ) SPS-4848 0.1. Water Sep 1987 I-131 <0.2 <1 SPW-4849 0.I. Water Sep 1987 Co-60 <4.1 <10 Cs-134 <4.8 <10 Cs-137 <4. 0 <10 Sr-89 c0.7- <5 l Sr-90 <0.7 <1 -{ SPW-4850 D.I. Water Sep 1987 Th-228 <0.04 <1 Th-232 c0. 8 <1 L U-234 <0.03 <1 U-235 <0.03 <1 U-238 <0.02 <1 Am-241 <0.06 <1 Cm-242 <0.04 <1 Ra-226 <0.1 <1 Ra-228 <1.0' <2: SPW-4859 =D.I. Water Oct 1987 Fe-55 <0, 5 - <1 I SPS-5348 Milk Dec 1987 Cs-134 <2.3 <10-Cs-137 <2.5 <10 SPW-5384 0.I. Water Dec 1987 Co-60 <2.8 <10 , Cs-134 <2.6 <10 Cs-137 <2.8 <10 o ui I-131- <0. 2 <1 f) Ra-226 <0.1 <1 4 ' Ra-228 <1.2 <2 Sr-89 <0.5 <1 Sr-90 <0.4 <1 SPW-5385 D.I. Water Nov 1987 Gr. alpha <0.4 <1 Gr. beta (2. 2 <4 Fe-55 <0.3 <1 SPS-5386 Milk Jan 1988 I-131 <0.1 <1 SPW-5448 " Dead" Water Jan 1988 H-3 <177 <300
., 118
e s Table A-4. In-house ' blank' samples (continued). '
- Concentration in pCi/1 L:ceptance I Lab Sampie Date Resul ts Criterta l Code Type Collected Analysis (4.660 ) (4.660 )
I SPS-5615 Milk Mar 1988 Cs-134 <2.4 <10 Cs-137 <2.5 <10 . 1-131 <0. 3 <1 1 Sr-89 <0 . 4 <5 Sr-90 2.4 0.5a <1 SPS-5650 D.I. Water Mar 1988 Th-228 <0. 3 . <1 Th-230 <0.04 <1 Tli-232 <0.05 <1 U-234 <0.03 <1 U-235 <0.03 (1-
. U-238 <0.03 <1 -
An-241 <0.05 <1
, Cm-242 <0.01 <1 Pu-238 <0.08. <1 Pu-240 <0.02 <1 SPS-6090 Milk Jul 1988 Sr-89 <0 . 5 <1 i Sr-90 1.8 0.Sa <1 1-131 <0.4 <1 l Cs-137 <0. 4 <10 ,
1 L SPW 6209 Water Jul 1988 Fe-55 <0.8 <1 I, SPW-6292 Water Sep 1988 Sr-89 <0.7 <1-L. Sr-90 <0. 7 <1 fg' i' SPS-6477 Milk Oct 1988 I-131 e0.2 <1 Cs-134 <6 .1 <10 Cs-137 <5.9 <10 p SPW-6478 Water Oct 1988 I-131 <0. 2 <1 l L SPW-6479 Water Oct 1988 Co-60 <5.7 <10- l Cs-134 <3.7 <10 - Cs-137 <4. 3 <10 SPW-6480 Water Oct 1988 H-3 <170 <300 SPW-6625 Water Dec 1988 Gr. alpha <0.7 <1' Gr. beta <1. 9 <4 a Low level (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual. ! s 119
-1
i
- 4;- Table A-4. .In-house ' blank" samples (continued).
Concentration in pCi/l Acceptance Lab Sample Date Resul ts Criteria-Code Type Collected Analysi s (4.66o ) (4.660 )- i
.SPS-6723 Milk Jan 1989 Sr <0.6 <5 Sr-90 1.920.5a <1 I-131 <0.2 A
<1 Cs-134 <4. 3 <10 >
Cs-137 <4.4 <10 i SPW-6877 Water Mar 1989 Sr-89 <0.4 <5 Sr-90 <3. 6 <1=
/ SPS-6963 Milk Apr 1989 I-131 <0. 3 <1 Cs-134 <5.9 <10 '
Cs-137 <6.2 <10 L SPW-7561 Water Apr 1989 H-3 <150 <300 l SPW-7207 Water Jun 1989 Ra-226 , <0. 2 <1 ( Ra-228- <0.6 <1-SPS-7208 Milk Jun 1989 Sr-89 (0.6 <5 Sr-90 2.1 0.Sa <1 1-131 <0.3 <1 Cs-134 <6.4 <10 Cs-137 <7. 2 <10'
, SPW-7558 Water Jun 1989 Gr. alpha <0.2 <1 .l Gr. beta <1.0 <4 !
SPS-7322, Milk Aug 1989 Sr-89 ><1.4 <5 Sr-90 4.8 1.0a <1_
. 1-131 <0.2 <1 Cs-134 <6.9 <10
' -- s Cs-137 <B .' 2 <10 i SPW-7559 Water Sep 1989 Sr-89 <2.0 <5 Sr-90 <0 . 7 <1 SPW-7560 Water Oct 1989 I-131 <0.1 <1.0 l SPW-7562 Water- Oct 1989 H-3 <140 <300 l SPS-7605 Milk Nov 1989 I-131 <0.2 <1 Cs-134 <B . 6 <10 Cs-137 <10 <10 SPW-7971 Water Dec 1989 Gr. alpha <0.4 <1 ,
Gr. beta <0.8 <4 i i= a Low level (15 pCf/1) of Sr-90 concentration in milk is not unusual.- 120
t 1 j
= TIML -BL INU-01 Revision 0, 12-29-86 -
1 ATTACHMENT B 3. l ACCEPTANCE CRITERIA FOR " SPIKED" SAMPLES j
)
LABORATORY PRECISION:. ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSES 4 1 1 One Standard Deviation Analysis level for Single Determinatio'n l Gama Emitters 5 to 100 pC1/ liter or kg 5 pCi/ liter i
>100 pC1/ liter or kg 5% of known value l Strontium-896 5 to 50 pCi/ liter or kg 5 pCi/ liter j'
>50 pCi/ liter or kg 10% of known value Strontium-90b 2 to 30 pCi/ liter or kg ,
3.0 pCi/ liter l
>30 pCi/ liter of kg 10% of known value !
Potassium >0.1 g/ liter or kg , 5% of known value I Gross Alpha <20 pCi/ liter 5 pCi/ liter 1
>20 pCi/ liter 25% of known value Gross Beta <100 pC1/11ter 5 pCi/ liter l
>100 pCi/ liter 5% of known value -1 Tritium <4,000 pCi/ liter is = (gC5/11ter) =
l 169.85 x (known).0933
>4,000 pC1/ liter 10% of known value l Radium-226, <0.1 pCi/ liter 15% of known value '
Radium-228 i Plutonium 0.1 pCi/ liter, gram, 10% of known value 3 or sample j Iodine-131, b
- <55 pCi/ liter 6 pCi/ liter ;
Iodine-129 >55 pCi/ liter 10% of known value i Uranium-233, <35 pCi/ liter 6 p / liter l Nickel-630, >35 pCi/ liter 15% of known value Technetium-990
)
Iron-55b 50 to 100 pCi/ liter 10 pC1/ liter 10% of known value l 1 a L From EPA publication, " Environmental Radioactivity Laboratory Intercompari-I D son Studies Program, Fiscal Year 1981-1982 EPA-600/4-81-004. l: TIE ' limit. 121 l
1 4 A00EtlDuti TO APPEtlDIX A 1
- The following is an explanation of the reasons why certain samples were outside the control limit specified by the Environmental Protection Agency for the Interlabora. - l tory Comparison Program starting January 1987. .
EPA Lab Code Analysis Titit Result Control Limit Explanation i STri-504 Sr-89 57.024.3 60.3-77.7 tiilk had high fat content which Sr-90 32.02).0 32.4-37.6 made analyses difficult. Ad-dition of errors to TIttL result would put values within EPA control limits. EPA also had the same problem -in analyzing its own sample. STW-511 Ra-228 8.l!!.4 4.6-8.0 TIllt results are usually within EPA control. limits. Analysis of the next - sample was within EPA control limits, flo further action is planned. STW-516 Cr-51 80.3217.5 61.3-78.7 Results in the past have been , within EPA control limits and TItil will monitor the situation in the future. 1 L ST F-524 K 1010.72158.5 1123.5-1336.5 Error in transferrance of data. Correct data was 1105233. Results in the . past have been~ ' within the limits and TIllt will ; monitor the situation in the future. STW-532 I-131 9.022.0 6.2-8.8 Sample recounted after 12 days. The average result was -8.821.7-- , (within EPA control limits). , The sample was recounted in order to check the decay.
- - Results in the past have been within the limits and TIhL will l,
continue to monitor the situ-ation in the future. 1 STW-534 Co-60 63.321.3 41.3-58.7 High level of Co-60 was due to contamination of beaker. l Beaker was discarded upon dis-c ove ry of contamination and I sample was recounted. Recount ' results were 53.223.6 and 50.922.4. I: 122
u V . L. ADDENDUM TO APPENDIX A (continued) l L EPA Lab Code Analysis TIML Result Control Limit Explanation 1: 1 o STM-554 Sr-90 51.0:2.0 54.8-65.2 The cause of low result is not-known and is under investi-gation. It should be noted' . that 63% of. all participants i failed this test. Also, the
. average for all participants .
was 54.0 pCi/1 before the Grubb ' ! and 55.8 pC1/1 after the Grubb. STW-560 'Pu-239 -t ! 5.8 1.1 3.5-4.9 The cause of high results is not known (suspected contasi-nated standard) and is under-investigation. New Pu-236 standard was obtained and will be used for the next test. 6 STW-568 Ra-228 2.6 1.0 2.7-4.5 The cause of low results is under investigation. New i dilution was prepared and sample is being reanalyzed. Sample was used up during testing. Next EPA crosschecks with the control .11mits. STM-570 Sr-89 26.0 10.0 39.0 5.0 The cause of ' low results is Sr-90 45.724.2 55.0 3.0 . under. investigation. New-
" spike" milk sample was pre-1 pared and being. analyzed.
Results of analysis: See 4 Table A-3, sample QC-Mi-24. t e 123
1
+
Table A-1. (continued) cs Concentration in pCi/lb , Lab Sampl e Date TIML Result _ EPA Resule.d Collected Analysi s 15, N=1 Control Limits Code Type 2 2ac STM-554 Milk Oct 1988 Sr-89 40.327.0 40.025.0 31.3-48.7 i Sr-90 51.022.0 60.023.0 54'. 8 -6 5.2 ; I-131- 94.0t3.4 91.029.0 75.4-106.6 Cs-137 45.014.0 50.025.0 41.3-58.7' K 1500245 1600280 1461-1739 , STU-555 Urine Nov 1988 H-3 30302209 3025t359 2403-3647 l STW-556 Water 'Nov .1988 Gr. alpha 9.0t3.5 9.015.0 0.3-17.7 3i Gr. beta 9.711.2 9.015.0 0.3-17.7 ! STW-557 Water Dec 1988 I-isi 108.723.0 115.0212.0 94.2-135.8 STW-559 Water Jan 1989 Sr-89 40.028.7 40.015.0 31.3-48.7 Sr-90 24.3 3.1 25.021.5 - 22.4-27.6 STW-560 Water Jan 1989 Pu-239 5.821.1 4.220.4- 3.5-4.9 STW-561 W ater Jan.1989 Gr. alpha 7.3tl.2 8.025.0 0.0-16.7
- Gr. beta 5.321.2 4.025.0 0.0-12.7' STW-562 Water Feb 1989 Cr-51 245t46 235t24 193.4-276.6-Co-60 10.022.0 10.025.0- 1.3-18.7-Zn 170210 159t16 139.2-186.7 Ru-106 181t7.6 178t18 146.8-209.2 '
Cs-134 9.723.0 10.025.0 .1.3-18.7 Cs-137 11.721.2 10.025.0 1.3-18.7 1 . 1
; e i
l" 1' ! i l l I 102
+
,f 4:
Table A-1. (continued) Concentration in pCi/lb Lab Sample Date TIML Result -EPA Resultd Code Type ~ Collected Analysis 12cC 13, N=1 Control Limits STW-563 Water Feb 1989 I-131 109.024.0 106.0211.0 86.9-125.1
.!TW-564 Water Feb 1989 H-3 2820 20 27542356 2137-3371 STW-565 Water Mar 1989 Ra-226 4.220.3 4.9 0.7 3.7-6.1 Ra-228 1.9 1.0 1.720.3~ 1,2-2.2 STW-566 Water Mar 1989 U. 5.0 0.0- 5.0t6 t 0.0-15.4 -/ STW-567 AirFilter Mar 1989 Gr. alpha 21.721.2 21.025.0 '12.3-29,7 Gr. beta 68.3 4.2 62.0 5.0 53.3-70.7 Sr-90 20.0 2.0 20.021.5 17.4-22.6 Cs-137 21.321.2 20.0 5.0' 11.3-28.7 STW-568 Water Apr 1989 569 (Blind)
Sample A Gr. alpha 22.7*2.3 29.027.0 16.9-41.2 Ra-226 3.6 0.6 3.St0.5 2.6-4.4 Ra-228 2.6 1.0 3.6t0.5 2.7-4.5 U 3.0t0.0 3.0t6.0 0.0-13.4 Sample B Gr. beta 52.316.1 57.0 5.0 43.3-65.7 Sr-89 9.3 5.4 8.025.0 0.0 16.7 8.0 1.5 Sr-90 7.020.0 5.4-10.6 Cs-134 21.0 5.2 20.0 5.0 11.3-28.7 Cs-137 -23.0 2.0 20.0t5.0 11.3-28.7 STM-570 Milk Apr 1989 Sr-89 26.0210.0 39.0 5.0' 30.3-47.7 Sr-90 45.7 4.2 55.0 3.0 49.8-60.2 Cs-137 54.0 6.9 50.025.0 41.3-58.7 K-40 1521 208 1600 80 1461-1739. 103
'd' 1
. l Table A-1. (continued) , I Concentration in pCi/lb Lab Sampl e Date TIML Result ,,
EPA Resultd ) Code Type Cellected Analysis :2cc Is, N=1 Control Limits l 9 STW-571 Water May 1989 Sr-89 40.7 6.025.0 0.0-14.7 Sr-90 5.0*1.0 6.021.5 3.4-8.6 STW-572 Water May 1989 Gr. alpha 24.022.0 30.018.0 16.1-43.9 Gr. beta 49.3215.6 50.015.0 41.3-58.7 STW-573 ' Wat.er Jun 1989 Ba-133 50.7tl.2- 49.025.0. 40.3-57.'7 Co-60 31.312.3 31.0t5.0 22.3-39.7. 2n-65 167t10 165117 135.6-194.4 2
. Ru-106 12319.2 128213 105.5-150.5 Cs-134 40.3tl.2 3915 30.3-47.7 Cs-137 22.3 1.2 -2015 11.3-28.7 STW-574 Water Jun 1989 H -3 4513t136 45031450 3724'5282 STW-575 Water Jul 1989 Ra-226 16.823.1 17.722.7 13.0-22.4 Ra-228 13.823.7 18.322.7 13.6-23.0 i STW-576 Water Jul 1989 U 40.321.2 41.026.0 .30.6-51.4-STW-577 Water Aug 1989 I-131 84,7t5.8 83.028.0 69.1-96.9 STW-579 Air Aug 1989 Gr. alpha 6.010.0 6.025.0 0.0-14.7 Filter Cs-137 10.312.3 10.025.0 1.3-18.7 STW-580 Water Sep 1989 Sr-89 14.721.2' 14.025.0 5.3-22.7 Sr-90 9.711.2 10.0tl.5 7.4-12.6 ;
STW-581 Water Sep 1989 Gr. alpha 5.020.0 4.025.0 0.0-12.7 Gr. Beta 8.7t2.3 6.025.0 0.0-14.7 l i i 104 L ,
. .c . . , - .
Table A-1. (continued)
- Concentration in pCi/lb Lab Sampl e Date TIML Result EPA ResuTti---
Code Type Coll ected Analysi s 22cc Is, N=1 Control Limits STW-583 Water Oct 1989 Ba-133 60.3:10.0 59.0!6.0 48.6-69.4 Co-60 29.014.0 30.0:5.0 21.3-38.7 I Zn-65 132.3 6.0 129.0:13.0 106.5-151.5 Ru-106 155.32 6.1 161.0:16.0 133.3-188.7 Cs-134 30.7 6.1 29.025.0 20.3-37.7 Cs-137 66.3 4.6 59.0:5.0 50.3-67.7 STW-584 Water Oct 1989 H-3 3407:150 3496:364 2866-4126 STW-585 Water Oct 1989 586 (Blind) Sample A Gr. Alpha 41.7 9.4 49.0 12.0 28.2-69.8 Ra-226 7.920.4 8.4:1.3 6.2-10.6 Ra-226 4.4:0.8 4.120.6 3.1-5.1 U 12.0 0.0 12.0 6.0 1.6-22.a Sample B Gr. Beta 31.7:2.3 32 0:5.0 23.3-40.7 Sr-89 13.324.2 1 r, . 0 :5 . 0 6.3-23.7 Sr-90 7.022.0 7.0 3.0 4.4-9.6 Cs-134 5.0 0.0 5.025.0 0.0-13.7 Cs-137 7. 0 20 .0 5.0 5.0 0.0-13.7 STW-587 Water Nov 1989 Ra-226 7. 9 :0. 4 8.7 1.3 6.4-11.0 Ra-228 8.9 1.2 9.3 1.2 6.9-11.7 STV-588 Water Nov 1989 U 15.0:0.09 15.0:6.0 4.6-25.4 a Results obtained by Teledyne Isotopes Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Intercomparison and Cali-bration Section, Quality Assurance 8 ranch, Environmental Monitoring and Support Laboratory, U.S. Environmental Protection Agency (EPA), Las Ve b All results are in the pCi/1, except for elemental potassium (K) gas, dataNevada, in milk, which are in mg/1; air filter samples, which are in pCi/ filter; and foed, which is in mg/kg. c Unless otherwise indicated, the TIML results are given as the mean 2 2 standard deviations for three determinations, d USEPA results are presented as the known values and expected laboratory precision (1s,1 determination) and control limits as defined by EPA.
- NA = Not analyzed.
f ND = No data. Not analyzed due to relocation of the lab. 9 Sample was analyzed but the results not submitted to EPA because deadline was missed.
,_i 105
= . _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ . . . _ _ _ . . . . . . . . . _ _ _
;, , 'ti -
.L L
Table A-2. Crosscheck program results, thermoluminescent dosimeters (TLDs). mR , Teledyne Average 12 o d Lab TLD Result Known (all
- Code Type Measurement 1 20a Valuet partic ipants) 2nd International Intercomparisonb 115-2. CaF2:Mn Field 17.011.9 17.1 16.417.7 Bulb -
Lab 20.814.1 21.3 18.817.6 3rd International Intercomparisone 115-3 CaF2:Mn Field 30.713.2 34.914.8 31.5t3.0 - Bulb 8 Lab 89.616.4 91.7114.6 86.2124.0-4th International Intercomparisonf
, 115-4 CaF7:Mn Field 14.111.1 - 14.111 4 16.019.0 Bulb Lab (Low) 9.311.3 12.212.4 12.017.6 Lab (Iligh) 40.411.4 45.819.2 43.9113.2 5th International Intercomparison9 115-5A CaF2:Mn Field 31.411.8 30.016.0 30.2114.6 Bulb Lab at 77.415.8 75.217.6 75.8140.4 beginning Lab at 96.615.8 88.418.8 90.7131.2 end e
P--- _;._
- - - i,%- w.ma .mgy .p- e-as_. __.m .une.,m
._ mN:.. -mm-ssm* u.w-sms.m"ie -
E Table A-2. (Continued) mR Teledyne Average 120 d Lab TLD Result Known (all Code Type Measurement 12aa Valuec participants) 115-58 LiF-100 Field 30.314.8 30.016.0 30.2114.6 Chips Lab at 81.117.4 75.217.6 75.8140.4 beginning Lab at 85.4111.7 88.418.8 90.7131.2 the end 7th International Intercomparisonh
$; 115-7A Lif-100 Field 75.412.6 75.816.0 75.1129.8 1
" Chips Lab (Co-60) 80.013.5 79.914.0 71.9127.6 Lab (Cs-137) 66.612.5 75.013.8 73.0t22.2 115-78 CaF2:Mn Field 71.512.6 75.816.0 75.1129.8 Sulbs Lab (Co-60) 84.816.4 79.914.0 77.9127.6 Lab (Cs-137) 78.811.6 75.013.8 73.0122.2 l 115-7C CaSO4 :Dy Field 76.812.7 75.816.0 15.1129.8 Cards Lab (Co-60) 82.513.7 79.9t4.0 77.9127.6 tab (Cs-137 79.013.2 75.013.8 13.0t22.2 4
' " - - ' ' - - - ' ' ' ' ~ " "
Table A-2. (Continued) - udt Teledyne Average 220 d Lab TLD Result Known (al1 Code Type Measurement 12 04 ValueC participants) 8th International Intercomparisoni < 115-8A LiF-100 Field Site 1 29.511.4 29.711.5 28.9t12.4 Chips Field Site 2 11.2t0.8 10.420.5 10.119.06 Lab (Cs-137) 13.710.9 17.210.9 16.2t6.8 115-8B CaF2:Mn Field Site 1 32.3t1.2 29.711.5 28.9112.4 Bulbs Field Site 2 9.011.0 10.420.5 10.119.0 Lab (Cs-137) 15.810.9 17.220.9 16.226.8 115-8C CaSO4 :Dy Field Site 1 32.310.7 29.711.5 28.9112.4 Cards Field Site 2 10.610.6 10.410.5 10.119.0
' b Lab (Cs-137 18.110.8 17.220.9 16.2t6.8 Teledyne Testingf 4
89-1 L1F-100 Lab 21.0t0.4 22.4 - Chips 89-2 Teledyne Lab 20.921.0 20.3 - CaSO4 :Dy Cards i a Lab result given is the mean 22 standard deviations of three determinations. b Second International Intercomparison of Environmental Dosimeters conducted in April of 1976 by the Health and Safety Laboratory (GASL), New Yort, New York, and the School of Public Health of the Uni-versity of Texas, Houston, Texas. c d Value determined by sponsor of the intercomparison using continously operated pressurized ion chamber. Mean 22 standard deviations 0f results obtained by all laboratories participating in the program.
Tcble A-2. (continued) mR Teledyne Average 12o d Lab TLD Result Known - (all Measurement 2aa y jgec participants) Code Type Footnotes continued
- Third International Intercomparison of Environmental Dosimeters conducted in swumer of 1977 by Oak Ridge National Laboratory and the School of Public Health of the University of Texas, Houston, Texas.
f Fourth International Intercomparison of Environmental Dosimeters conducted in -r of 1979 by the School of Public Health of the University of Texas, Houston, Texas. 9 Fifth International Intercomparison of Environmental Dosimeter conducted in fall of 1980 at Idaho Falls, Idaho and sponsored by the School of Public Health of the University of Texas. Houston, Texas and nvironmental kasurements Natory,- New M, h M, U.S. MarWnt of Energy. i h Seventh International Intercomparison of Environmental Dosimeters conducted in the spring and maner of 1984 at Las Vegas, Nevada, and sponsored by the U.S. Department of Energy, the U.S. Nuclear Regulatory
, Commission, and the U.S. Environmental Protection Agency.
g Eighth International Intercomparison of Environmental Dosimeters conducted in the f-11 and winter of e 1985-1986 at New York, New York, and sponsored by the U.S. Department of Energy. Chips were submitted in September,1989 and cards were submitted in November,1989 to Teledyne Isotopes, Inc., Westwood, NJ for irradiation. m 4
o s Table A-3. In-house spiked samples. _ Concentration in pCi/1
~
Lab Sample Date TIML Result Known Expec ted Code Type Collec ted Analysis n=3 Ac tivity Precision [ 1s. n=3a QC-MI-6 Milk Feb. 1986 Sr-89 6. 0tl . 9 6.413.0 8.7 Sr-10 14.2tl . 7 12.922.0 5.2 -__ l-131 34.2t3.8 35.2t3.5 10.4 Cs-134 32.011.8 27.3t5.0 8.7
.- Cs-137 35.8t2.1 35.0 5.0 8.7 L
QC-W-14 Water Mar. 1986 Sr-89 1.610.4 1.6tl.0 7.1 Sr-90 2.4t0.2 2.412.0 4.2 QC-W-15 Water Apr. 1986 !-131 44.9t2.4 41.St7.0 10.6 Co-60 10.611.7 12.lt5.0 7.lb Cs-134 30.2t2.4 25.8t8.0 7.lb Cs-137 21.9tl.9 19.9*5.0 7.lb QC-MI-7 Milk Apr. 1986 1-131 39.713.3 41.5*7.0 10.4 Cs-134 28. 7t2. 8 ' 25.818.0 8.7 Cs-137 21.2t2.8 19.915.0 8.7 SPW-1 Water May 1986 Gross alpha 15.811.8 18.015.0 Sc QC-W-16 Water June 1986 Gross alpha 16.2*0.7 16. 9t2. 5 8.7 Gross beta 38.413.5 30.225.0 8.7 QC-MI-9 Milk June 1986 Sr-89 <1.0 . 0.0 7.lb E Sr-90 12.611.8 13.3t3.0 4.2b l-131 38.917.0 34.817.0 10.4 Cs-134 33.0t3.4 36.115.0 8.7 Cs-137 38.512.8 39.015.0 8.7 SPW-2 Water June 1986 Gross alpha 16.811.8 18.015.0 Sc SPW-3 Water June 1986 Gross alpha 17.7t0.8 18.0*5.0 Sc QC-W-18 Water Sep. 1986 Cs-134 34.715.6 31.315.0 8.7 Cs-137 51. lt7. 0 43.3t8.0 8.7 QC-W-19 Water Sep. 1986 Sr-89 13.614.1 15.6t3.5 7.lb Sr-90 6. 4tl . 6 6.2*2.0 4.2b i
. 110
l , Table A-3. In-housn spiked samples (continued) Concentration in pC1/1 , Lab Smapl e Date TIML Result Kno'n w ExpecteB~ Code Type Collected Analysi s n=3 Activity Precision 1s, n=3a QC-W-21 Water Oct. 1986 C -60 19.2t2.2 18.523.0 8.7 Cs-134 31.7t5.2 25.628.0 8.7 Cs-137 23.821.0 21.625.0 8.7 QC-MI-11 Milk Oct 1986 Sr-89 12.321.8 14.323.0 8.7 QC-W-20 Water Nov. 1986 H-3 38552180 3960t350 520b QC-W-22 Water Dec. 1986 Gross alpha 9.821.4 11.224.0 8.7 Gross beta 21.712.0 23.825.0 8.7 QC-W-23 Water Jan. 1987 I-131 29.8t2.5 27.923.0 10.4 QC-M1-12 Milk Jan. 1987 I-131 36.521.3 32.615.0 10.4 Cs-137 32.6t4.2 27.428.0 8.7 QC-MI-13 Milk
- Jan 1987 Sr-89 10.4t2.1 12.214.0 8.7 Sr-90 14.Gtl.6 12.6t3.0 5.2 1-131 49.5t1.2 54.928.0 10.4 Cs-134 41.6 0.0 8.7 Cs-137 33.3t0.6 27.428.0 8.7 QC-W-24 Water Mar 1987 Sr-89 24.7t3.6 25.915.0 8.7 Sr-90 23.923.8 22.818.0 5.2 QC-W-25 Water Apr 1987 I-131 28.021.9 29.325.0 10.6 QC-MI-14 Mil k Apr 1987 1-131 25.022.2 23.925.0 10.4 Cs-134 42.1 0.0 8.7 Cs-137 34.222.0 27.217.0 8.7 QC-W-26 Water Jun 1987 H-3 3422t100 33622300 520 Co-60 24.821.4 26.5t7.0 8.7 Cs-134 42.0 0.0 8.7 Cs-137 21.220.5 21.6*7.0 8.7 QC-W-27 Water Jun 1987 Gr. alpha 8.511.9 10.114.0 8.7 Gr. beta 22.621.9 21.225.0 8.7 QC-W-28 Water Jun 1987 Gr. alpha 8.7tl.3 10.114.0 8.7 Gr. beta 12.215.2 9.4t3.0 8.7 111
O Table A-3. In house spiked samples (continued)
, Concentration in pCi/l Lab Sample Date TIML Result Known Expect ed Code Type Collected Analysis n=3 Activisy Precision 1s, n=3a
~QC-W-29 Water Jun 1987 Gr. alpha 16.421.3 18.925.0 8.7 Gr. beta 15.924.0 11.814.0 8.7 QC-MI-15 Mil k Jul 1987 Sr-90 19.421.6 18.823.5 5.2 1-131 43.520.7 45.327.0 10.4 Cs-134 17,922.2 16.025.3 8.7 Cs-137 25.421.8 22.715.0 8.7 QC-W-30 Water Sep 1987 Sr-89 17.523.0 14.325.0 8.7 Sr-90 18.412.2 17.512.2 5.2 QC-W-31 Water Oct 1987- H-3 20531939 20592306 520 QC-W-32 Water Dec 1987 Gr. alpha 8.611.0 10.115.0 8.7
. Gr. beta 15.220.1 13.113.0 8.7 QC-W-33 Water Dec 1987 Gr. alpha 7.721.4 10.115.0 8.7 Gr. beta 10.921.0 7.9 3.0 8.7 QC-W-34 Water Dec 1987 Gr. alpha 4.010.9 5.113.0 8.7 Gr. beta 9.410.9 7.913.0 8.7 QC-MI-16 Milk Feb 1988 Sr-89 31.814.7 31.716.0 8.7 Sr-90 25.522.7 27.823.5 5.2 1-131 26.410.5 23.215.0 10.4 Cs-134 23.822.3 24.226.0 8.7 l
Cs-137 26.520.8 25.126.0 8.7 QC-MI-17 Milk Feb 1988 1-131 10.611.2 14.321.6 10.4 QC-W-35 Water Feb 1988 I-131 9.711.1 11.621.1 10.4 g QC-W-36 Water Feb 1988 I-131 10.511.3 11.611.0 10.4 l l QC-W-37 Water Mar 1988 Sr-89 17.112.0 19.818.0 8.7 Sr-90 18.720.9 17.325.0 5.2 QC-MI-18 Milk Mar 1988 I-131 33.212.3 26.715.0 10.4 Cs-134 31.312.1 30.215.0 8.7 Cs-137 29.911.4 26.215.0 8.7
\
l 112
Table A-3. In-house spiked $4mples (continued) Concentration in pC1/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision 15, n=3a QC-W-38 Water Apr 1988 1-131 17.121.1 14.225.0 10.4 QC-W-39 Water Apr 1988 H-3 4439231 41762500 724 QC-W-40 Water Apr 1988 Co-60 23.720.5 26.114.0 8.7 Cs-134 25.422.6 29.224.5 8.7 Cs-137 26.612.3 26.224.0 8.7 QC-W-41 Water Jun 1988 Gr. alpha 12.320.4 13.115.0 8.7 Gr. beta 22.611.0 20.125.0 8.7 QC-MI-19 Milk Jul 1988 Sr-89 15.111.6 16.415.0 8.7 Sr-90 18.020.6 18.315.0 5.2 1-131 88.414.9 80 618.0 10.4 Cs-137 22.720.8 20.816.0 8.7 QC-W-42 Water Sep 1988 Sr-89 48.513.3 50.818.0 8.7 Sr-90 10.921.0 11.413.5 5.2 QC-W-43 Water Oct 1988 Co-60 20.913.2 21.4*3.5 8.7 Cs-134 38.711.6 38.016.0 8.7 Cs-137 19.012.4 21.013.5 8.7 QC-W-44 Water Oct 1988 1-131 22.220.6 23.323.5 10.4 QC-W-45 Water Oct 1988 H-3 4109143 41532500 724 QC-MI-20 Mil k Oct 1988 1-131 59.810.9 60.629.0 10.4 Cs-134 49.621.8 48.617.5 8.7 Cs-137 25.814.6 24.724.0 8.7 QC-W-46 Water Dec 1988 Gr. alpha 11.512.3 15.225.0 8.7 Gr. beta 26.512.0 25.725.0 8.7 QC-MI-21 Milk Jan 1989 Sr-89 25.5110.3 34.0110.0 8.7 Sr-90 28.313.2 27.123.0 5.2 1-131 540213 550 20 10.4 Cs-134 24.512.6 22.6 5.5 8.7 Cs-137 24.020.6 20.515.0 8.7 1 113
O Table A-3. In-house spiked samples (continued) i Concentration in pC1/1 Lab Sample Date TTRCResult Known Expected Code Type Collected Analysis n=3 Activity Precision 1s, n=3a QC W-47 Water Mar 1989 Sr-89 15.213.8 16.115.0 8.7 ! Sr-90 16.411.7 16.923.0 5.2 QC-MI-22 Mil k Apr 1989 l-131 36.321.1 37.225.0 10.4 Cs-134 20.812.8 20.718.0 8.7 Cs-137 22.212.4 20.428.0 8.7 Apr 1989 23.522.0 25.118.0 QC-W-48 Water Co-60 8.7 Cs-134 24.211.1 25.928.0 8.7 Cs-137 23.611.2 23.018.0 8.7 QC-W-49 Water A'pr 1989 l-131 37.213.7 37.215.0 10.4 QC-W-50 Water Apr 1989 H-3 - 3011159 30891500 724 QC-W-51 Water Jun 1989 Gr. alpha 13.011.8 15.015.0 8.7 Gr. beta 26.011.2 25.518.0 8.7 QC-MI-23 Milk Jul 1989 Sr-89 19.426.5 22.0210.0 8.7 Sr-90 27.623.1 28.623.0 5.2 1-131 46.813.2 43.425.0 10.4 Cs-134 27.411.8 28.326.0 8.7 Cs-137 24.121.8 20.816.0 8.7 QC-MI-24 Milk Aug 1989 Sr-89 25.422.7 27.2210.0 8.7 Sr-90 46.011.1 47.819.6 8.3 QC-W-52 Water Sep 1989 l-131 9.620.3 9.721.9 10.4 QC-W-53 Water Sep 1989 l-131 19.020.2 20.924.2 10.4 QC-W-54 Water Sep 1989 Sr-89 25.824.6 24.724.0 8.7 Sr-90 26.515.3 29.725.0 5.2 a n=3 unless noted otherwise. b n=2. c nal. l 114
L " Table A-3. In-house spiked samples (continued) L Concentration in pCi/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision 1s, n=3a QC-M1-25 Milk Oct 1989 I-131 70.023.3 73.5220.0 10.4 Cs-134 22.112.6 22.628.0 8.7 Cs-137 29.421.5 27.528.0 8.7 QC-W-55 Water Oct 1989 I-131 33.321.3 35.3210.0 10.4 QC-W-56 Water Oct 1989 Co-60 15.220.9 17.425.0 8.7 Cs-134 22.114.4 18.928.0 8.7 Cs-137 27.221.2 22.928.0 8.7 QC-W-57 Water Oct 1989 H-3 3334222 33792500 724 d QC-W-58 sater Nov 1989 Sr-89 10.921.4d 11.121.0d 8.7 Sr-90 10.421.0d 10,321,od 5.2 QC-W-59 Water Nov 1989 Sr-89 101.0$5,0d 104.1210.5d 17.5 Sr-90 98.023.0d 95.0210.0d 17,o QC-W-60 Water Dec 1989 Gr. alpha 10.821.1 10.614.0 8.7 Gr. beta 11.610.5 11.424.0 8.7 a n=3 unless noted otherwise, b n=2. c n=1. d Concentration in pCi/ml 115
Table A-4. In-house " blank" suples. , Concentration in pCk/1 Acceptance " Lab Suple Date Resul ts Criteria Code Type Collected Analysi s (4.66o ) (4.66o ) , BL-1 0.1 Water Nov. 1985 Gross alpha <0.1 <1 Gross beta (0.4 <4 BL-2 D.I. Water Nov. 1985 Cs 137 (gama) <1.9 <10 , BL-3 D.I. Water Nov. 1985 Sr-89 <0.5 <5 Sr-90 <0.6 <1 BL-5 D.I. Water Nov. 1985 Ra-226 <0.4 <1 Ra-228 <0.4 <1 SPW-2265 D.I. Water Apr. 1985 Gross alpha <0.6 <1 Gross beta (2.2 <4 Sr-89 <0. 2 <5 Sr-90 <0.4 <1 1-131 (0.2 <1 Cs-137 (gama) <7.4 <10 BL-6 D.I. Water Apr. 1986 Gross alpha <0.4 <1 , BL-7 D.I. Water Apr. 1986 Gross alpha (0.4 <1 BL-8 D.I. Water June 1986 Gross alpha <0.4 <1 BL-9 D.I. Water June 1986 Gross alpha <0.3 <1 SPW-3185 D.I. Water Jan 1987 Ra-226 <0.1 <1 Ra-228 <0.9 <1
-SP3-3292 Milk Jan 1987 I-131 <0.1 <1 Cs-134 (6. 2 <10 Cs-137 <6.4 <10 ,
SPW-3554 D.I. Water Feb 1987 H-3 (180 <300 Gross beta <2.6 <4 SPS-3555 Milk Feb 1987 Sr-89 (0.6 <5 Sr-90 1.920.4a <1 SPS-3731 Milk Mar 1987 Cs-134 <2. 2 <10 Cs-137 <2.5 <10 a low level (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual. 116
.-- .- =. , - - ,
t Table A-4 In-house " blank" samples (continued).
- s Concentration in pCi/1 Acceptance Lab Sampl e Date Resul ts Criteria Code Type Collected Analysi s (4.663 ) (4.663 )
SPS-3732 0.1. Water Mar 1987 Sr-89 (0.9 <5 Sr-90 <0.8 <1 1-131 (0.3 <1 Co-60 <2.3 (10 Cs-134 <2.2 <10 Cs-137 <2.4 <10 Ra-226 <0.1 <1 Ra-228 <1.0 <1 Np-237 <0.04 <1 Th-230 (0.05 <0.1 Th-232 (0.02 <0.1 U-234 <0.05 <0.1 U-235 <0.03 <0.1 s U-238 <0.03 <0.1 SPS-4023 Milk May 1987 I-131 <0.1 <1 SPS-4203 0.1. Water May 1987 Gross alpha <0.7 <1 Gross beta < L,7 <4 SPS-4204 Milk May 1987 Sr-89 <0.5 <5 Sr-90 2.4 0.6a <1 SPS-4390 Milk Jun 1987 Cs-134 (4.7 <10 Cs-137 <5.2 <10 SPS-4391 D.I. Water Jun 1987 Sr-89 (0.4 <5 ' Sr-90 <0.4 <1 I-121 (0.1 <1 Co-60 <3.8 <10 Cs-137 (5.7 <10 Ra-226 <0.1 <1 Ra-228 <0.9 <1 SPW-4627 0. I. Water Aug 1987 Gross alpha <0.6 <1 Gross beta <1.4 (4 Tritium <150 SPS-4628 Mil k Aug 1987 Sr-89 (0.6 (5 Sr-90 2. 410. 6 a <1 SPS-4847 Milk Sep 1987 Cs-134 <4.4 (10 Cs-137 <5.3 <10 a tow leye) (1 - 5 pCi/1) of Sr-90 concentration in milk is not unusual. t 117
Table A-4 In-house " blank' samples (continued). Concentration in pC1/1 Acceptance Lab Sample Date Resul ts Criteria Code Type Collected Analysis (4.66c ) (4.66c ) SPS-4848 0.t. Water Lep 1987 1-131 -
<0.2 <1 SPW-4849 0.1. Water Sep 1987 Co-60 <4.1 <10 Cs-134 (4.8 <10 Cs-137 (4.0 <10 Sr-89 cD . 7 <5 Sr-90 <0.7 <1 SPW-4850 D.I. Water Sep 1987 Th-228 <0.04 <1 Th-232 (0. 8 <1 U-234 <0.03 <1 U-235 <0.03 <1 U-238 (0.02 <1 Am-241 (0.06 <1 Cm-242 <0.04 <1 Ra-226 (0.1 <1 Ra-228 (1.0 (2 SPW-4859 0.1. Water Oct 1987 Fe-55 <0.5 <1 SPS-5348 Milk Dec 1987 Cs-134 <2.3 (10 Cs-137 <2.5 (10 SPW-5384 D.I. Water Dec 1987 Co-60 (2.8 (10 Cs-134 <2.6 (10 Cs-137 <2.8 <10 1-131 c0. 2 <1 Ra-226 <0.1 <1 Ra-228 <1.2 <2 Sr-89 (0. 5 <1 Sr-90 <0.4 <1 SPW-5385 D.I. Water Nov 1987 Gr. alpha <0.4 <1 Gr. beta (2. 2 <4 Fe-55 <0. 3 <1 SPS-5386 Milk Jan 1988 1-131 (0.1 <1 SPW-5448 " Dead" Water Jan 1988 H-3 (177 (300 1
118
Table A-4. In-house " blank' samples (continued). Concentration in pC1/1 Acceptance Lab Sample Date Resul ts Criteria Code Type Collected Analysis (4.660 ) (4.660 ) SPS-5615 Milk Mar 1988 Cs-134 <2.4 <10 Cs-137 <2.5 <10 1-131 (0. 3 <1 Sr-89 (0. 4 <5 Sr-90 2.420.Sa <1 SPS-5650 0.1. Water Mar 1988 Th-228 <0. 3 <1 Th-230 (0.04 <1 Th-232 c0.05 <1 U-234 (0.03 <1 U-235 (0.03 <1 U-238 <0.03 <1 An-241 (0.06 <1 Ca-242 (0.01 <1 Pu-238 (0.08 <1 Pu-240 <0.02 <1 SPS-6090 Milk Jul 1988 Sr-89 <0. 5 <1 Sr-90 , 1.810. 5a <g 1-131 (0. 4 <1 Cs-137 (0. 4 <10 SPW-6209 Water Jul 1988 Fe-55 <0.8 <1 SPW-6292 Water Sep 1988 Sr-89 (0. 7 <1 Sr-90 <0. 7 <1 SPS-6477 Milk Oct 1988 I-131 (0. 2 <1 Cs-134 (6.1 <10 Cs-137 <5.9 <10 SPW-6478 Water Oct 1988 I-131 <0. 2 <1 SPW-6479 Water Oct 1965 Co-60 <5.7 <10 Cs-134 <3.7 <10 Cs-137 (4. 3 <10 SPW-6480 Water Oct 1988 H-3 <170 <300 SPW-6625 Water Dec 1988 Gr. alpha <0.7 <1 Gr. beta (1.9 <4 a low level (1 - 5 pC1/1) of Sr-90 concentration in milk is not unusual. 119
e
, Table A-4. In-house " blank' samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Resul ts Criteria Code Type Collected Analysis (4.66o ) (4.660 ) SPS-6723 Milk Jan 1989 Sr-89 <0. 6 <5 ' Sr-90 1.920.Sa <1 I-131 <0.2 <1 Cs-134 <4 . 3 (10 Cs-137 (4.4 (10 SPW-6877 Water Mar 1989 Sr-89 <0.4 <5 Sr-90 c0.6 <1 SPS-6963 Milk Apr 1989 - I-131 <0. 3 <1 Cs-134 <5.9 <10 Cs-137 (6. 2 <10 SPW-7561 Water Apr 1989 H-3 <150 <300 SPW-7207 Water Jun 1989 Ra-226 c0. 2 <1 Ra-228 <0.6 <1 SPS-7208 Milk Jun 1989 Sr-89 <0.6 <5 Sr-90 2.lto.Sa <1 1-131 <0. 3 <1 Cs-134 <6. 4 <10 Cs-137 <7. 2 <10 , SPW-7558 Water Jun 1989 Gr. alpha (0.2 <1 Gr. beta <1.0 <4 SPS-7322 Milk Aug 1989 Sr-89 41 . 4 (5 Sr-90 4.821.0a <1
. 1-131 <0. 2 <1 Cs-134 c5. 9 <10 Cs-137 (8. 2 <10 SPW-7559 Water Sep 1989 Sr-89 <2.0 <5 Sr-90 <0 . 7 ' <1 SPW-7560 Water Oct 1989 I-131 <0.1 <1.0 SPW-7562 Water Oct 1989 H-3 <140 <300 SPS-7605 Milk Nov 1989 I-131 <0.2 <1 Cs-134 <B . 6 <10 Cs-137 <10 <10 SPW-7971 Water Dec 1989 Gr. alpha <0.4 <1 Gr. beta <0.8 <4 a low level (1-5 pCi/1) of Sr-90 concentration in milk is not unusual.
120
TIML -8t !No-01 Revision 0, 12-29-86 - ATTACHMENT B ACCEPTANCE CRITERIA FOR ' SPIKE 0" SAMPLES LABORATORY PRECISION: ONE STANDAP;0 DEVIATION VALUES FOR VARIOUS ANALYSESa One Standarc Deviation Analysis Level for Single Determination Ganna Emitters 5 to 100 pCi/ liter or kg 5 pC1/ liter
>100 pCi/ liter or kg 5% of known value Strontium-89b 5 to 50 pCi/ liter or kg 5 pCi/ liter
>50 pCi/ liter or kg 10% of known value Strontium-90b 2 to 30 pCi/ liter or kg 3.0 pCi/ liter I
>30 pCi/ liter of kg 10% of known value l l
Potassium >0.1 g/ liter or kg 5% of known value ; Gross Alpha <20 pCi/ liter 5 pCi/ liter
>20 pCi/ liter 25% of known value Gross Beta <100 pC1/ liter 5 pCi/ liter
>100 pCi/ liter 5% of known value Trit tuin <4,000 pCi/ liter is = (pci/ liter) =
169.85 x (known).0933
>4,000 pCi/ liter 10% of known value Radium-226, <0.1 pCi/ liter 15% of known value I Radium-228 i Plutonium 0.1 pCi/ liter, gram, 10% of known value :
or sample Iodine-131, b <55 pCi/ liter 6 pCi/ liter - Iodine-129 >55 pCi/ liter 10% of known value Uranium-238, <35 pCi/ liter 6 pCi/ liter Ni c kel-630, >35 pCi/ liter 15% of known value Technetium-99D Iron-55b 50 to 100 pCi/ liter 10 pC1/ liter 10% of known value a From EPA publication, " Environmental Radioactivity Laboratory Intercompari-b son Studies Program, Fiscal Year 1981-1982, EPA-600/4-81-004. ; TIML limit. 121 1
I ADDEtiDUM TO APPENDIX A The following is an explanation of the reasons why certain samples were outside the l control limit specified by the Environmental Protection Agency for the Interlabora- i tory Comparison Program starting January 1987. EPA Lab Code Analysis T!til Result Control Limit Explanation STit-504 Sr-89 57.024.3 60.3-77.7 tiilk had high fat content which Sr-90 32.021.0 32.4-37.6 made analyses difficult. Ad. dition of errors to TIttL result would put values within EPA control limits. EPA also had the same problem in analyzing its own sample. , STW-511 Ra-228 8.121.4 4.6-8.0 T!flL results are usually within EPA control limits. Analysis of the next sample was within EPA control limits. No further action is planned. STW-SIC Cr-51 80.3217.5 61.3-78.7 Results in the past have been within EPA control limits and TIfit will monitor the situation in the future. ST F-524 K 1010.72158.5 1123.5-1336.5 . Error in transferrance of data. Correct data was 1105 33. Results in the past have been within the limits and TIllt will monitor the situation in the future. STW-532 1-131 9.022.0 6.2-8.8 Sample recounted af ter 12 days. The average result was 8.821.7 (within EPA control limits). The sample was recounted in order to check the d ec ay. Results in the past have been within the limits and T!hl will continue to monitor the situ-ation in the future. STW-534 Co-60 63.321.3 41.3-58.7 High level of Co-60 was due to contamination of beaker. Beaker was discarded upen dis-c ove ry of cont ami nat ion and sample was recounted. Recount results were 53.22 3.6 ana 50.922.4 , 122
ADDEWOUM TO APPENDIX A (continued) EPA Lab Code Analysis TIML Result Control Limit Explanation STM-554 I Sr-90 51.022.0 $4.S-65.2 The cause of low result is not known and is under investi-pation. It should be noted that 63% of all participants failed. this test. Also. ! the average for all participants was 54.0 pC1/1 before the Grubb I and 55.8 pCi/1 af ter the Grubb. STW-560 Pu-239 5.821.1 3.5-4.9 The cause of high results is not known'( suspected contasi-nated standard) and is under investigation. New Pu-236 standard wat obtained and will be used for the next test. STW-568 Ra-228 2.611.0 2.7-4.5 The cause of low results is under investigation New dilution was prepare.d and sample is being reanalyzed. Sample was used up during testing. Next EPA crosschecks ' with the control limits. STM-570 Sr-89 26.0210.0 39.015.0 Sr-90 45.714.2 55.013.0 The cause of low results is i under investigation. New
" spike" milk sample was pre-pared and being analyzed.
Results of analysis: See Table A-3. sample QC-Mi-24, i e 123
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,f o !
r i e I t APPENDIX IV l P REVISIONS TO THE ODCM RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SINCE 1986 ; r P l a k': f 7 124
g . REVISIONS TO THE RADIOLOGICAL ENVIR0"M ETAL MONITORING PROGRAM BYRON STATION DATE (00CM Revision) SAMPLE M0!!ITORING ComENTS TYPE LOCATION
'86 (IIA) Airborne All Revision Established monitoring locations identification numbers.
All Addition Sr-89 and 90 analysis on a quarterly composite. BY-22 Revision CECO Real Estate was retitled to CECO Property. Ground /Well Water All Addition Gross beta, Sr-89, and 90 analyses, quarterly. BY-14 Revisien CECO Real Estate was retitled to Ceco Property. BY-18 Revisien Station's Onsite Well was changed to the McCoy Farmstead Well, 1.25 mi SW. Surface Water All Addition Gross beta analysis weekly and Sr-89, 90 analyses on a quarterly composite.
~
BY-13 Revision Oregon Pool of Rock River, Upstream of Intake, 4.3 mi, SSW was changed to Rock River, Upstream of Intane, 2.6 mi, WNW. Cooling Water All Addition . Gross beta analysis weekly. Genna isotopic, tritium, Sr-89 and 90 analyses on a composite, monthly. M BY-10 Revision Byron Intake Pipe / River, at the station.
, Initially, this monitoring location was considered surface water exposure patNsay.
BY-11 Revision Byron Discherge Pipe / River, at the station. Initially, this monitoring location was corni4ered surface water exposure pathway. Sediments All Addition Gross beta analysis three times a year, not semiennually. BY-13 Revision Oregon Pool of Rock River, Upstream of Intake, 4.3 mi, SSW was changed to Rock River, Upstream of Intake, 2.6 mi, WWW. Precipitation All Addition Gross beta analysis monthly. Gansna isotopic, tritium, Sr-89 and 90 analyses on a quarterly composite at all the milk monitoring locations.
~ - .- _ _- - . - . . . . -_- ---_ . -- - -- -- -_.
REVISIONS TO THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM BYROM STATION Cont'd SAMPLE MONI!ORING COMMENTS DATE (00CM Revision) TYPE LOCATION Aquatic Plants All Addition Ganna isotopic and gross beta analyses, three times a year.
'86 (11A) Cont'd ' Oregon Pool of Rock River Downstream of Discharge, BY-12 Addition 4.5 mi SSW.
BY-13 Addition Rock River, Upstream of Intake, 2.6 mi WNW. Fish / Invertebrates All G .idi tion Gross beta, Sr-89 and Sr-90 analysis three times a year. BY-13 Revision Oregon Pool of Rock River, Upstream of Intake 4.3 mi, SSW was ch&nged to Rock River Upstrees of Intake,2.6 mi, idNW. Milk All Addition Sr-89, 90 analysis biweekly when milch animals are on
~
pasture, monthly at other times. BY-15 Revision Groenhagen/01tmann Fam, 2.0 mt 5 was changed to
- J.A. Reeverts Pine Hill Dairy, 3.2 at ESE.
BY-16 Revision Asbelford Fam, 2.7 mi W was changed to Kenneth Durien Fam, 3.3 al SE. BY-20 Revision Meyers Fam, 5.0 mi SE was changed to ~ Ed Seabold Fam, 2.5 mi NE. m" Ga ma isotopic, gross beta. Sr-89 and 90 analyses Cattle Feed / Grass All Addition quarterly at all the milk monitoring locations. Vegetables All Deletion Collection frequency is annually and the following 00CM statement is deleted:
"If harvest occurs more than once a year, saspilng shall be performed during each discrete harvest. If harvest occurs continuously, sampling shall be monthly. Attention shall be paid to including samples of tuberous and root food products.*
BY-19-1,2 Addition Gauna isotopic, gross beta, Sr-89 and 90 analyses annually. 1-131 analysis on leafy vegetables annually. Both locations are Oregon Vegetable Stands, 5.1 mi 55W.
REVISIONS TO THE RADIOLOGICAL ENVIRONi4 ENTAL MONITOBING PROGRAM BYRON STATION Cont'd SAMPLE MONITORING COMMENTS i DATE (00CM Revision) TYPE LOCATION
'87 (11B) All All Addition Listed distances from the center of the station in kilometers and listed sectors.
Airborne All Deletion Sr-89 and 90 +nalysis BY-21 Revision Onsite W, was retitled to BY Nearsite, N. BY-22 Revision CECO Property W, was retitled to BY Nearsite ESE. BY-23 Revision Onsite, 5, was retitled to BY Nearsite..S. BY-24 Revision The Meteorological Tower was retitled to BY Nearsite, SU. Direct Radiation All Addition The dation code BY proceeds the identification number. ~ Ground /Well Water All Deletion Sr-89 and 90 analysis All Revision Collection to occur biweekly, not quarterly. All Addition Analysis frequency is clarified the following ODCM statement:
"I-131 analysis to occur biweekly j
when dose rate calculations from water consumption exceeds >l wres/yr.* BY-14 Revision CECO Property was retitled Offsite Well. BY-18 Addition McGoy Farm Well is identified as CECO owned. Surface Water All Deletion Gross beta Sr-89 and 90 analyses
% Cooling -Ater All Deletion Sediments All Deletion Grcss beta analysis.
Ali Revision Collection frequency wes thanged to semiennually, not three times a year. Precipitation All Deletion Aquatic Plants All Deletion Milk All Deletion Sr-89 and 90 analysis Cattlefeed and Grass All Deletion Vegetables All Deletion Gross beta, I-131, Sr-89 and 90 analyses annually. Food Products Addition Analysis frequency is clarified with the l following ODCM statement:
"Gasuna isotopic and I-131 analyses shall occur at two different offsite monitoring locations and a location that is 15-30 km from the station having the highest predicted annual average ground level O/Q if milk sampling is not performed."
mm mun n ~~ ,~~ n,~.u,-----~~~,,-- ~n , M.
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\
l APPENDIX V e ADDENDA t
. . tc e ,
s U rs e r e 4 L C F 5 l i f'. . l L+,..<-v, a m. .. . 128 2
m f: BYRON NUCLEAR POWER STATION EFFLUEST AND WASTE DISPOSAL SEMI-ANNUAL REPORT JANUARY TO JUNE 1989 ADDENDUM A. The following is the breakdown for the continuous releases for gaseous effluents: 1st quarter Xe-133 19.8 Curies Xe-135 0.077 Curtes TOTAL = 19.88 Curies 2nd quarters No continuous releases
. B. The following data is the estimated composition of Byron's solid waste streams: ,
- 1. Dry Active Waste (DAW) 2. Primary Resin 3. Radwaste Rosin C-14 7.7% Mn-54 1.54% Mn-54 2.7%
Mn-54 4.0% Co-58 60.9% Co-58 30.6% re-55 46.6% Co-60 4.3% Co-60 6.8% Co-58 12.24 Cs-134 8.7% Cs-134 17.8% co-60 12.0% Cs-137 7.54 Cs-137 24.3% Cs-134 3.3% B-3 0.6% U-3 9.0% Cs-137 5.8% C-14 1.2% C-14 0.45% Ni-63 8.4% Fe-55 14.3% Fe-55 6.8% Ni-63 0.9% Tc-99 0.05% Sr-90 0.02% I-129 0.1% Tc-99 0.03% Pu-239 0.01% I-129 0.001% Pu-238 0.01% Pu-239 0.001% Am-241 0.04% Pu-238 0.001% Cm-244 0.04% Am-241 0.001% Ni-63 1.3% CM-244 0.001% Pu-241 0.005L 129
- i i
i i C. Per Technical Specifications 3.3.3.9 and 3.3.3.10, the following is a summary of effluent monitoring instrumentation inoperable for a period of time greater than specified in the Technical Speci- j s fications
- 1. Unit 1 Reactor Containment Fan Cooler Essential Service Water Outlet Monitor was inoperable for greater than 30 l days. The extended period of inoperability was due to a faulty sample pump.
j D. During this period', there were no major changes to the liquid, gaseous, or solid rsdwsste treatment systems. There were no major changes to l the Process Control Program (PCP). Byron Station continues to utilize the services of Westinghouse-Hittman for dewatering and solidification ] services. I E. Error Analysis S The following is an estimate of the errors associated with effluent j monitoring and analysis. The estimate is calculated using the square root of the sum of the squares methodology. I
- 1. Gaseous Effluents Sampling error = 1 to 3.5%
Calibration error 1
= 104 Counting Statistics error = 5%
Vent Stack flowrates error = 1.5% Total error = 11 - 124
- 2. Liquid Effluents Sampling error = lt Calibration error e 104 Sample volume error = lt Discharged volume error = 24 Total error = 104 l P. Meteorological and environmental impact information is reported in the l
Station Annual Radiological Environmental Operating Report as required by Technical Specification 6.9.1.6. 1 130
,, m . .- . . , , ..
BYRON NUCLEAR POWER STATION . EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT JULY TO DECEMBER 1989 ADDENDUM A. The following is the breakdown for the continuous releases for gaseous effluents: 3rd quarter No continuous releases. i 4th quarter Xe-133 36.1 Curies B. The following data is the estimated composition of Byron's solid waste s tre ams :
- 1. Dry Active Waste (DAW) 2. Primary Rosin 3. Radwaste Rosin C-14 4.3% Mn-54 20.79% Mn-54 7.1%
Mn-54 1.5% Co 58 11.14% Co-58 51.95% l Fe-55 60.6% Co-60 9.28% Co-60 9.97% l Co-58 13.3% Cs-134 7.05% Cs-134 9.90% ! Co-60 15.5% Cs-137 15.22% Cs-137 9.01% Cs-134 1.3% H-3 1.15% H-3 0.022% Cs-137 1.4% C-14 2.49% C-14 0.419% Ni-63 2.06% Te-55 30.80% To-55 9.69% Sr-90 0.038% Ni-63 1.97% Tc-99 1.89% Tc-99 0.005% Sr-90 0.048% I-129 0.004% I-129 0.0001% Tc.99 0.052% Pu-239 0.004% I-129 0.001% Pu-238 0.002% i Pu-239 0.0004% Am-241 0.005% Pu-238 0.0003% Cm-244 0.014% Am-241 0.0002% Ni-63 0.016% CM-244 0.0002% Pu-241 0.012% C. Per Technical Specifications 3.3.3.9 and 3.3.3.10, there were no effluent monitoring instrumentation inoperable for a period of time greater than specified in the Technical Specification. D. During this period, there were three changes to the liquida gaseous, or solid radwaste treatment systems. There were no major changes to the Process Control Program (PCP). Byron Station continues to utilize the services of Westinghouse-Hittman for dewatering and solidification services. The three radwaste treatment systems changes are as follows: Radwaste Changes For 89
- 1) MOD 0-87-116: Installed bypass line around the Spent Resin Storage Tank to allow transferring a low activity bed for disposal and i holding a high activity bed in the SRST. j l
l l (2308t/45) 131 l
l 9
- 2) MOD 0-88-012 Installed separate control switches for the WK monitor inlet valves. This allows both valves to be open at the same time and reduces radwaste processing time by half.
- 3) MOD 0-89-034: Converted from dry cleaners to wet wash. This prevents the production of a mixed hasardous waste (Freon).
4 E. Error Analysis I The following is an estimate of the errors associated with effluent monitoring and analysis. The estimate is calculated using the square root of the sum of the squares methodology.
- 1. Gaseous Effluents Sampling error = 1 to 3.5%
Calibration error = 10% Counting Statistics error = 5% Vent Etack flowratts error = 1.5% Total error = 11 - 12%
- 2. Liquid Effluents Sampling error = 1%
Calibration error = 10% Sample volume error = 1% Discharged volume error = 2 h_, Total error = 10%
- 3. Waste Resin Sampling error = 5%
Counting Statistics error = 7% weight error = 1% Egluge error = $% Total error = 10%
- 4. DAW Counting Statistics error = 7%
Calibration error = 10% ; Egight_ error = 2% , Total error = 12.4%
- r. Meteorological and environmental impact information is reported in the Station Annual Radiological Environmental Operating Report as required by Technical Specification 6.9.1.6.
G. No limits were exceeded in 11guld hold up tanks as stated in Technical Specifications 3.11.1.4 or in waste gas decay tanks as stated in Tnchnical Specifications 3.11.2.6.
+
l l (2308 /45) 132
O H. There were ao irradiated fuel shipments during this peridd. . I. Lower Limits of Detection are defined in Technical Specifications Tabic 4.11-1 for 11guld and Table 4.11-2 for gaseous waste. The Lower Limits of Detection are as follows:
- 1. Liquid Waste -
- a. Principal Gamma Emitters 5X10-7 pC1/ml
- b. 1-131 1X10*6 C1/mi
- c. Dissolved and Entrained Gases (Gama Emitters) 1X10-5 pC1/M1 ,
- d. H3 l'X10-5 C1/ml
- e. Gross Alpha 1410-7 pC1/ml ,
- f. Sr 89-90 SX10-8 C1/ml
- g. Te 55 1X10-6 pcl/ml
- 2. Gaseous Waste
- a. Waste Gas Decay Tanks and Containment Purge
- 1. Principal Gamma Emitters IX10-4 pC1/ml
- 2. H3 1X10-4 pC1/ml
- b. Ausillary Building Vent Stack Grab
- 1. Principal Gamma 1X10-4 pC1/ml
- 2. H3 1X10-7 pCi/ml
- c. Auxiliary Building Vent Stack Continuous
- 1. I-131 1X10-12 pC1/ml
- 2. 1-133 1X10-10 pCi/mi
- 3. Principal Gamma Emitter 1X10-Il pC1/ml
- 4. Sr 89-90 1X10-Il pC1/ml
- 5. Noble Gas Gross Beta or Gamma 1X10-6 pC1/ml (2308s/45) 133
7,,- c Q' e-
?
l. g,l a I t. APPENDIX VI , 1989 REMP SAMPLE RESULTS s. 6 a s t 5 t' b 134
' i s ' e(
t
'4 .
O SPTEUEDYNE? ISOTOPES MIDWEST LASCAATORY. 700 LANDWEMA ROAD - NORTMSROOK, ILLINOIS 60082 23to 90s 944 0700 FAX FOS 8444617 C FINAL PROGRESS REPORT
- TO COMMONWEALTH EDISON COMPANY 1AD10 LOGICAL ENVIRONMENTAL MONITORING PROGRAM (REMP)
FOR BYRON NUCLEAR POWER STATION BYRON, ILLINOIS PREPARED AND SUBillTTED BY TELEDYNE ISOTOPES MIDWEST LABORATORY Reporting Period: ' January - December,1989 Reviewed and [j Approved by: m V[/ //J M t'1A
/ Date ~5 -/9 - 9/S U' 6 G. huebner
$ deneral Manager 3
p'< r.A o.. .;. (> j% .. , $ 1 BYRON
-7 l
s. TABLE OF CONTENTS t Section Page Li st of -Tabl es . . . . . . . . . . . . . . . . . . . - . . . . . .. . iii. N- 1.0 I NTR ODUCTI ON . . . . . . . . . . . . . . . . . . . . . . . . . I 2.0 LISTING OF MISSED SAMPLES .................. 2
.c, k
( l l 4 : I 11
t BYRON LIST OFLTABLES No. Title Page 1 Airborne Particulates and Iodine-131, locations By-01, 02, 03, 04 . . . . . . . . . . . . . . . 4-2 Airborne Particulates and Iodine-131, locations By-05, 06, 07, 08 . . . . . . . . . . . . . . . 6 3 Airborne Particulates and Iodine-131, locations By-21, 22, 23, 24 . . . . . . . . . . . . . . . 8 4 Airborne Particulates, Quarterly Composites of Weekly Collections ................... . 10 5 - Gamma Radiation, as Measured by TLDs . . . . . . . . . . . . . 12 6 , Milk . . . . . . . . . . . . . . . . . ... . . . . . . . . . . 15 7 Fish, Edible Portions ..-.................. 17 8 Vegetables . . . . . . . . . . .:. . . . . . . . . . . . . . . 18 9- Surface Water ................-......... 19 10 Wel l Wa t e r . . . . . . . . . . . . . . . . . . . . . . . . . . 21 11 Bottom Sediments . . . . . . . . . . . . . . . . . . . . . . . 23 1 Milch Animal and Nearest Residence Census .......... 24 I 111
B4RON
1.0 INTRODUCTION
The following constitutes the final Protcess Report for the Environmental Radiological Monitoring Program conducted at the Byron Nuclear Power Station, Byron, Illinois. Results of completed analyses are presented in the attached tables. Missing entries indicate analyses ' that are not completed and the results will appear in subsequent reports. Data obtained in the program are well within the ranges previously encountered in the program and to be expected in the environmental media sampled. For all gamma isotopic analyses, spectrum is computer scanned from 80 to 2048 kev. Specifically included are Mn-54, Co-58, Fe-59, Co-6n , In-65, I r-95, . Nb-95, Ru-103, Ru-106, I-131, Ba-La-140, Cs-134, Cs-137, Cc-1'1, and Ce-144. Haturally occurring gamma-emitters, such as K-40 and Ra daughters, are fre-quently detected but not listed here. Data listed as "<" are at the 4.66 sigma -level,- others are 2 sigma. Cs-134 and Cs-137 are listed . separately. All other gamma emitters are listed under "Other Gammas". Unless noted otherwise, the less than value ("<") reported under "Other Gammas" is for Co-60 and may be higher or lower for other radionuclides. All concentrations, except gross beta, are decay corrected to the time of collection. Deviations from Scheduled,5cmpling and Corrective Actions Taken All samples were col'".;ted within the scheduled period unless noted otherwise in the Listing of Missed Samples. l 1 ,
BYRON LISTING OF MISSED SAMPLES Expected Collection Sampl e ~ Type Location Date Reason Well Water BY-14 51-23-89. NoLpower to pump. BY-14 01-30-89 No power to pump.' Milk BY-20 '01-02-89 No sample available.
. Surface Water BY-09 01-02-89 River frozen.
BY-09 01-09-89 River frozen. BY-09 01-16-89 River frozen. BY-09 01-23-89 River frozen. , BY-12 01-02-89 River frozen. BY-12 01-09-89 - River frozen. BY-12 01-16-89 River frozen. BY-12 01-23-Et River frozen. BY-13 01-02-89 River - frozen. BY-13 01-09-89 River frozen. BY-13 01-16-89 River frozen. BY-13 01-23-89 River frozen. Surface Water BY-09 02-06-89 River frozen. BY-09 02-13-89 River frozen. BY-09 02-20-89 River frozen. BY-09 02-27-89 River frozen.- BY-09 03-06-89 River frozen. BY-12 02-06-89 River frozen. BY-12 02-13-89 River frozen. - BY-12 02-20-89 River frozen. BY-12 02-27-89 River frozen. BY-12 03-06 River frozen. BY-13 02-06-89 River frozen. BY-13 02-13-89 River frozen. BY-13 02-20-89 River frozen. BY-13 02-27-89 River frozen. BY-13 03-06-89 River frozen. BY-09 12-26-89 River frozen. , BY-13 12-26-89 River frozen. NOTE: Page 3 is intentionally left out. 2
(* !
* ' BYRON ,
- Table 1. Airborne Particulates and Iodine-131a ,
Collection:2 Units: Weeki 10- pCi/m Byron Stillman Valley Near Site E Paynes' Point BY-01 BY-02 (C) BY-03 BY-04 Week Volyme Gross Vol e Gross Volyme Gross Volyme Gross Ending (m3) Beta (m) Beta (m?) Beta (m9) Beta 01-09-89 284 5. 3i0. 5 274 5.60.5 2 282 4.7 0.5 282 4.6*0.5 ' 01-16-89 286 2.9 0.4 286 <0. 4b 286 3.1 0.4 285 2.8r0.4 01-23-89 286 2.0 0.4 285 2.320.4 285 2.020.4 285 2. 1 20. 4 01-30-89 .285 3.6t0.4 285- 3.520.4 285 4.0 0.4 285 '3.3 0.4 02-06-89 286- 5.0 0.5 296 4.320.5 289 4.520.5 288 4. 320. 5 02-13-89 284 2.5t0.4 275 2.9 0.4 282 3.0 0.4 283 2.6 0.4' 02-20-89 286 2.1 0.4 286 2. li0. 4 286 2.420.4 286 1.6t0.4 02-27-89, .285 3.520.4 285 3.6 0.4 284 3.50.4- 284 3.4*0.4. 03-06-89 284 2.5 0.4 291 3.2t0.4 286 2. 6 t0. 4 286 2.9 0.4 03-13-89 285 3.410.4 278 3.3 0.4 285 2.7 0.4 285 3.0t0.4 03-20-89 283 3. 0 t0. 3 283 3.0 0.3 284 2.9 0.3 283 2. 7 20. 3 03-27-89 285 2.7i0.4 285 2.820.4 206 3. 0i0. 4 286 3.1 0.4 04-03-89 286 2.5 0.4 2 96 2.220.4 289 2. 0 t0.4 2 88 1.9 0.4 1st Qtr meants.d. 3.221.0 3.221.0 3.li0.9 2.9 0.9 04-10 284 1.810.4 274 1.710.4 283 1.5i0.4 283- 1.6 0.4 ; 04-17-89 285 3.4 0.4 285 3.5 0.5 283 3.Si0.5 283 3.3 0.4 04-24-89 285- 2.220.4 285 1.8 0.4 285 2. 0t0. 4 285 2.2 0.4 05-01-89 288 1.8t0.4 294 2.0 0.4- 288 2.4t0.4 288 1.8 0.4 05-08-89 285 1.1 0.4 278 1. 5 t0. 4 285 1.420.4 285 '1.420.4 05-15 284 1.2 0.3 284 1.6t0.3 284 1.6 0.3 284 1. 0t0. 3 ' 05-22 285 2.8i0.3 278 3.1 0.3 284 2.920.3 .284 2.3 0.3-05-29-89 289 1.6 0.3 286 2.320.3 290 2.1 0.3 288 1.6 0.3 06-05-89 280 2.0$0.2 281 2.4t0.2 274 2.0 0.2 280 1.820.2 06-12-89 283 1.410.3 286 2.1 0.4 290 1. 6 t0. 3 283- 1.4-0.3 06-19-89 289 2.3 0.4 295 1.8t0.4 290 1. 7 t0. 4 290 1.720.4 06-26-89 288 2.6 0.4 287 2.3 0:4 287 2.0 0.3 287' 2.420.4 07-03-89 288 2.0t0.3 2 90 2.1 0.3 .290 1.9 0.3 289 1.9t0.3 , 2nd Qtr meants.d. 2.0 0.6 2.2 0.6 2.010.6 1. 9!0. 6 a Iodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. b Filter paper very light. 4
l e. i BYRON Table 1. Airborne Particulates and Iodine-131a (continued) ; Byron Stillman Valley Hear Site E- "Paynes Point BY-01 BY-02 (C) BY-03 BY-04 Week Volyme Gross Vol e Gross Volyme Gross Volume Gross Ending (m3) Beta (m ) Beta (m4) Beta (md) Beta 07-10-89 284 3.110.3 272 2.910.3 281 1.410.2 272 2.820.3 07-17-89 285 2.010.2 292 1.820.2 284 2.120.2 285 2.0t0.2 07-24-89 284 1.910.2 278 1.9t0.2 284 2.0t0.2 284 1.920.2 07-31-89 286 1.4 0.3 286 1.6*0.3- 286 1.320.3 286 1.4t0.3 08-07-89 288 2.0t0.3 298 1.810.3 290 1.910.3 290 1.810.3 08-14-89 281 2.210.3 272 3.0t0.4 279 2.6 t0.4 279 2.410.3 08-21-89 286 2.210.3 292 2.520.3 286 2.420.3 286 2.210.3 , Q8 '28-89 293 1.7t0.3 288 1.8t0.3 294 2.410.4 294 1.610.3 09-04-89 279 1.310.3 286 1.810.3 280 1.220.3 280 1.5t0.3 09-11-89 285 1.620.3 277 1.8t0.4 284 1.220.3 284 1.4t0.3 . 09-18-89 285 1.5t0.3 285 1.820.3 285 2.120.3 285 1.620.3 09-25-89 286 2.310.3 277 2.9tQ,4 284 2.910.4- 283 2.420.3 10-02-89 288 2.910.4 297 3.0t0.4 290 3.4*0.4 29 0 3.0t0.4 3rd Qtr meants.d. 2.020.5 2.2i0.6 2.110.7 2.0t0.5 l 10-09-89 285 1.910.3 274 1.920.3 283 2.5t0.3 '283 1.7t0.3 10-16-89 282 2.920.4 290 3.920.4 281 3.520.4 281 3.5t0.4 10-23-89 286 2.0t0.3 281 2.410.3 286 2.0t0.3 286 1.810.3 10-30-89 288 3.8t0.4 287 4.010.4 288 1.8t0. 3 288 4.210.4 11-06-89 287 2.0t0.3 294 2.320.3 287 1.120.3 287 2.420.3 11-13-89 284 1.5t0.3 277 1.510.3 283 0.820.3 283 -1.6t0.3 < 11-20-89 287 2.7t0.4 286 3.010.4 286 1.6t0.3 288 3.020.4 11-27-89 285 3.4t0.4 285 2.910.4 284 2.120.3 284 3.0t0.4 12-04-89 285 2.820.4 291 2.820.4 286 3.0t0.4 286 3.220.4 12-11-89 288 2.7t0.4 280 2.810.4 287 3.0t0.4 287 3.020.4 12-18-89 282 4.320.4 283 4.4t0.4 283 4.8t0.4 283 4.210.4 12-26-89 329 3.620.4 329 3.4t0.4 329 3.810.4 329 3.6t0.4 01-02-90 285 1.920.3 296 2.410.3 288 2.0t0.3 288 2.410.3 4th Qtr meants.d. 2.7t0.8 2.910.8 2.Stl.1 2.910.9 a Iodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. 5 i 5
4 BYRON I Table 2. Airborne Particulates and Iodine-131a i Week 1 Collection:2 Units: 10- pC1/m Near Site S Oregon Mt. Morris Leaf River-BY-05 BY-06 BY-07 (C) BY-08 (C)> Week Volyme tross Volyme Gross Vol yme Gross Volyme - Gross o Beta Beta Ending (m4) Beta (m) (m3). . Beta (m3)
^
01-09189 282 5.5 0.5 284 5.6 0.5 284 5.3 0.5 2 84 5.310.5 01-16-89 286 3.3:0.4 286 3.120.4 286 3.110.4 2 86 3.010.4 01-23-89 285 2.220.4 285 2.420.4 285 2.2 0.4 285 2.410.4: 01-30-89 285 3.510.4 285 3.710.4 285- 3.020.4 285 3.420.4 02-06-89 287 4.620.5 286 4.4 0.5 2 86 4.2 0.5 286- '4.7t0.5 02-13-89 284 3.6 0.5 285 3.020.4 285 2.4 0.4 285 2.7 0.4 02-20-89 286 2.3 0.4 286 2.4t0.4 286 2.8 0.4 286 1.5 0.4 02-27-89 284 3.820.5 285 3.0 0.4 285 3.4i0.4 285- 3.2 0.4 03-06-89 286 3.020.4 286 3.620.4, 286 3.0i0.4 284 3.520.4 03-13-89 285 3.820.5 285 3.110.4 285 3.520.4 285 2.820.4 03-20 2 83 '2.9i0.3 283 2.9i0.3 285 2.320.3 '284 2.510.3 03-27 285 2.9 0.4 285- 2.420.4 286 2.7 0.4 286 2.410.4 . 04-03-89 2 88 -1.910.4 285 2.420.4 285 1.920.4 285 2.2t0.4 1st Qtr meanis.d. 3.321.0 3.220.9 3.120.9 3.021.0 04-10 282 1.4i0.4 284 2.120.4 2 84 1.4i0.4 284. 1.8 0.4 04-17-89 285 3.410.4 285 4.210.5 285 3.210.4 285 3.110.4 04-24-89 285 2.510.4 285 2.820.4- 285 1.6 0.4 285 2.1 0.4 05-01-89 2 88 2.520.4 287 2.320.4 286 1.910.4 286 1.920.4 05-08-89 284 1.4 0.4 285 1.520.4 286 1.020.4 286 1.220.4 05-15-89 285 1.810.3 284 2.0 0.4- 283 1.7t0.3 283 1.5 0.3 05-22-89 284 2.610.3 284 3.2i0.3- 286 2.6i0.3 286 2.7 0.3 05-29-89 287 1.910.3 286 2.020.3 288 1.720.3 288 2.010.3 06-05-89 280 2.110.2 281 2.420.2 282 2.220.2 282 2.2 0.2 06-12-89 283 1.720.3 283 1.7 0.3 2 83 1.8 0.3 283 1.6 0.3-06-19-89 290 1.5t0.4 289 1.8 0.4 289 1.620.4 289 1.620.4 06-26-89 287 2.420.4 287 2.610.4 288 2.210.4 288 2.2 0.4 07-03-89 289 1.920.3 288 2.1 0.3 286 1.6 0.3 286 1.810.3 2nd Qtr meaants.d. 2.10.6 2.4 0.7 1.910.6 2.0 0.5 a lodine-131 concentrations are <0.07 pCi/m 3 unless noted otherwise. 6
o BYRON .
.c Table 2. Airborne Particulates and Iodine-131a (continued)
Near Site S Oregon Mt. Morris Leaf River BY BY-06 BY-07 (C) BY-08 (C) Week Volyme Gross Volpe Gross Volume Gross Volume Gross-Ending (mJ) Beta (m4) Beta (mJ) Beta (mJ) Beta 07-10 282 2.720.3 272 3.0*0.3 284 2.6 t0. 3 284 2.6t0.3 07-17-89 285 1.920.2 284 2.210.2 285 1.920.2 285 1.920.2 1 07-24-89 284 2.210.2 285 2.220.2 285 1.820.2 285 1.620.2 : 07-31-89 286 1.6t0.3 286 1.410.3 286 1.520.3 286' 1.120.3 ;
~
08-07-89 290 2.320.4 286 1.620.3 280 1.820.3 288 1.620.3 08-14-89 281 2.6t0.4 283 2.7t0.4 283 2.7 t0.4 283 2.7t0.4 08-21-89 286 2.7t0.3 286 2.2 0.3 286 2.2 0.3 2d6 1. 9 t0. 3 - a' 08-28-89 294 2.210.3 294 2.010.3 294b 1.720.3 293 1.7 0.3 09-04-89 279 1.810.3- 279 1.820.3 279 0.7t0.3 279 1.6t0.3 09-11-89 284- 2.6t0.4 286 1.810.3 286 1.620.3 285 1.7t0.3 09-18-89 285 2.320.3 284 2.420.3 285 2.4t0.3 285 2.320.3
.09-25-89 283 2.510.3 ~286 3.120.4 286 2.6't0.3 285 3.0t0.4 10-02-89 290 2.810.4 286 3.010.4 294 2.7t0.4 293 3.420.4 3rd Qtr meants.d. 2.310.4 2.310.6 2.lt0.6 2.1 0.7 ,
10-09-89 283 1.720.3 286 1.820.3' 286 1.7t0.3 285 2.210.3 10-16-89 282 3.7t0.4 283 3.920.4 283 2.9t0.4 284 3.6t0.4 10-23-89 286 0.710.2 286 2.310.3 286 1.910.3 286 2.310.3 10-30-89 288 4.7t0.4 289 4.3t0.4 287 4.0t0.4 287 3.910.4 11-06-89 287 2.420.3 285 1.910.3 287 1.6t0.3 286 2.520.4 11-13-89 283 1.920.3 285 1.4*0.3 285 1.420.3 :285 1.7t0.3-11-20-89 287 3.310.4 287 3.220.4 286 2.620.4 286 3.010.4 11-27-89 285 3.320.4 285 3.210.4 285 2.810.4 285 3.5t0.4 12-04-89 285 3.610.4 284 3.310.4 284 3.120.4 284 2.720.4 12-11-89 287 2.4t0.4 288 3.110.4 288 3.110.4 288 2.6t0.4 12-18-89 283 4.510.4 283 4.7t0.4 283 4.120.4 283 4.210.4 12-26-89 329 3.4i0.4 329 4.4t0.4 329 4.0t0.4 329 4.5t0.4 01-02-90 296 2.520.3 284 2.320.3 284 2.110.3 284' 2.420.3 4th Qtr meants.d. 2.911.1 3.121.1 2.7t0.9 3.010.9 a Iodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. b- Timer out of order, volume is assumed. l . 1. 7
~
L ! r
' BYRON s l\
Table 3. Airborne Particulates and Iodine-131a Collection: lleekig - Units: 10- pCi/m BY-21' BY-22 BY-23 BY-24 Week Volyme Gross Volume Gross Volyme Gross _ Volume Gross
.Ending (m4) Beta (m3) Ceta (m3) Beta (m3) Beta
^
01-09-89 284 5.720.5 284 4.3 0.5 284 1.220.3 284' 6.620.5~ 01-16-89 2 86 3.5 0.4 286 3.420.4 286 3.610.4 286 3.2 0.4 01-23-89 285 2.920.4 285 2.420.4 286 3. lt0. 4 286 2.720.4-4.0 0.4 01-30-89 285 3.620.4 285 4.020.4 285 4.220.4 285 02-06-89 287 4.920.5 287 5.520.5 287 5.4t0.5 287 5. 0!0. 5 - 02-13-89 :284 2.620.4 284 2.820.4 284 4.2 0.5 284 3.220.4 02-20-89 '286 2.2 0.4 286 2.0 0.4 286 2.7t0.4 286 -2.320.4 02-27-89 285 3.2 0.4 285 3.7i0.5 285 3.620.4 2 84_ 3.520.4 03-06-89 287 3.520.4 286 3.120.4 286 3.3i0.4 286- 3.110.4 03-13-89 285 4.0 0.5 285 3.220.4 285 3.020.4 285 3.5 0.4 03-20-89 285 3.110.3 283 3.0i0. 3 283 3.0 0.3 283 3.0 0.3 03-27-89 286 2.710.4 286 3.420.4 286 3.020.4 285 3.3 0.4 L 04-03-89 287 2.220.4 ~286 2. li0. 4 287 2.410.4, 287 2.5 0.4 1st Qtr mean s.d. 3.4 1.0 3.321.0 3.3tl.0 3.511.1- t 04-10-89 284 1.320.3 284 1. 4 A0. 4 283 1.5 0.4 283 1.720.4 04-17-89 285 4.1 0.5 285 3.4 0.4 285~ 4.110.5 285 3.4 0.4 . 04-24-89 285 2.110.4 285 2.620.4 285 2.4i0.4 285 2.5 0.4 ? 05-01-09 2 88 2.4 0.4 P39 2.1 0.4 288 2.420.4 288 2.220.4 05-08-89 285 0.810.4 2o5 0.620.4 285 0.520.4 285 <0.6 05-15-89 283 1.6 0,3 283 1.Si0.3 284 1.6t0.3 284 1.520.3 05-22-89 285 2.720.3 285 2.7 0.3 285 2.4 0.3 285. 2.7 0.3 05-29-89 288 2.0i0.3 -286 2.020.3 287 2.3 0.3 272 2.4 0.4 06-05-89 282 2.420.2 187 3.5 0.4 -282 2.3t0.2 280 2.6t0.3 ', 06-12-89 283 1.9 0.3 283 2.1 0.4 2 83 _1.720.3 283 2.010.3 4 06-19-89 289 1.810.4 289 1.7 0.4 289 1.9 0.4 290 1.920.4 06-26-89 287 2.4i0.4 288 2.2 0.4 287 2.5t0.4 287 2.8 0.4- ' 07-03-89 288 1.1 0.3 288 1.8 0.3 288 2.220.3 288 2.3 0.3 2nd Qtr meanis.d. 2.0 0.8 2.lt0.8 2.1 0.8 2.3 0.5 a Iodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise.
-t 8
v
o.
,5 BYRON Y
Table 3. Airborne Particulates and Iodine-131a (continued) BY-21 BY-22 BY-23 BY-24' Week Volyme Gross Volyme Gross Volyme Gross Volyme Gross Ending (m3) Beta (mJ) Urta (mJ) Beta (md) Beta 07-10-89 283 3.820.3 283 3.0t0.3 '283 2.820.3 283 2.7t0.3 ' 07-17-89 285 2.0t0.2 285 2.1 0.2 285 2.020.2 285 1.920.2 07-24-89 284 2.120.2 284 2.020.2 284 2.110.2 284 2.120.2 07-31-89 286 1.810.4 286 1.810.4 286 1.620.3 286 1.9 0.4 08-07-89 272 2.020.4 272 2.lt0.4 289 1.9t0.3 284 1.720.3 08-14-89 281 3.520.4 281 3.1t0.4 280 3.120.4 280 3.120.4 08-21-89 286 '3.220.3 286 2.6 t0. 3 286 2.4t0.3 287 2.7t0.3 08-28-89 294 2.4t0.4 294 1.7t0.3 294 1.920.3 294 1.920.3 09-04-89 278 1.910.3 279 1.8t0.0 279 1.810.3 279- 2.020.3 09-11-89 285 2.010.4 285 2.0t0.4 285 1.810.3 285 2.110.4. 09-18-89 284 2.0t0.3 285 1.820.3 285 1.920.3 285 2.6*0.4 ' 09-25-89 284 3.020.4 283 2.9t0.4 283 2.620.3 283 2.6t0.3 10-02-89 284 2.420.4 293 0.620.3 285 2.720.4 285 4.lt0.5 ,. 3rd Qtr meants.d. 2.510.7 2.110.7 2.220.5 2.420.7: 10-09-89 284 2.120.3 284 2.5 0.3 284 1.6 0.3 284 2.0t0.3 10-16-89 281 3.9'20.4 282 4.010.4 282 3.820.4 282 3.620.4 10-23-89 286 2.3t0.3 286 2.2 0.3 286 2.220.3 286 2.220.3 10-30-89 288 4.4t0.4 288 4.210.4 288 4.4t0.4 288 4.8t0.4 11-06-89 287 2.6t0.4 287 2.3t0.3 287 2.410.3 287 3.120.4 11-13-89 283 1.910.3 283 2.0 0.3 283 2.0i0.3 283 2.120.4 11-20-89 287 3.210.4 287 3.710.4 287 2.920.4 287 3.510.4 11-27-89 282 1.210.3 .284 3.0t0.4 284b <o,04 285 3.1t0. 4 12-04-89 285 3.320.4 285 3.320.4 285 3.120.4 285 3.0t0.4 12-11-89 288 3.320.4 287 3.220.4 287 2.320.4 287 3.520.4 12-18-89 282 4.720.4 282 3.6t0.4 283 4.7t0.4 283 5.120.4 12-26-89 328 4.120.4 328 4.510.4 328 4.220.4 329 4.0t0.4 01-02-90 285 2.720.4 286 2.420.3 286 2.7t0.4 286 2.320.3 4th Qtr meants.d. 3.121.0 3.120.8 3.0tl.0 3.221.0-a Iodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. b filter paper very light, probably due to improper seating of filter in housing. < 9
} f, BYRON Table 4. Airborne Particulates Collection: - Quarterly composites of weekly collections Units: pCi/m3 . Volume Other " Location Lab Code (m3) Cs-134 Cs-137 Gammasa 1st Quarter 1989 s BY-01 BYAP-1459 3705 <0.01 <0.01 <0.01 BY-02 1460 3705 <0.01 <0.01 <0.01 BY-03 1461 3709 <0.01 <0.01 <0.01 BY-04 1462 3706 <0.01 <0.01 <0.01 BY-05 1463 3706 <0.01 <0.01 <0;01 BY-06 1464 3706 <0.01 <0.01 <0.01 BY-07 1465 3709 <0.01 <0.01 <0.01 BY-08' 1466 3706 <0.01 <0.01 <0.01 BY-21 1467 3712 <0.01 <0.01 <0.01 BY-22 1468 3708 <0.01 <0.01 <0.01 BY-23 1469 3710 <0.01 <0.01 <0.01 BY-24 1470 3708 <0.01 <0.01 <0.01 2nd Quarter 1989-BY-01 BYAP-1568 3713 <0.01 <0.01 <0.01 BY-02 1569 3703 <0.01 <0.01 <0.01 BY-03 1570 3713 <0.01 <0.01 <0.01 BY-04 1571 3709 <0.01 <0.01 <0.01 BY-05 -1572 3709 <0.01 <0.01 <0.01 BY-06 1573. 3708 <0.01 <0.01 <0.01 BY-07 1574 3711 <0.01 <0 . 01 - <0.01 BY-08 1575 3711 <0.01 <0.01 <0.01-BY-21 1576 3712 <0.01 <0.01 <0.01 BY 1577 3616 <0.01 <0.01 <0.01 BY-23 1578- 3711 <0.01 <0.01 <0.01 BY-24 1579 3695 <0.01 <0.01 <0.01 a See Introduction.
10
BYRON . Table 4. Airborne Particulates Collection: Qyarterly composites of weekly collections Units: pCi/m3 Volyme 0ther Location Lab Code (m4) 'Cs-134 Cs-137 Gammasa 3rd Quarter 1988 BY-01 BYAP-1672 3710 NA <0. 01 <0. 01 - <0.01 BY-02 1673 3700 <0. 01 <0.01 <0. 01 BY-03 1674 3707 <0.01 <0.01 <0.01. BY-04 1675 3698 <0.01 <0.01 <0.01 BY-05 1676 3709 <0.01 <0.01- <0.01 BY-06 1677 3697 <0.01 <0. 01 <0.01 BY-07 1678 3713 (0.01 <0.01 <0.01 BY 1679- 3717 <0.01 ,<0. 01 <0.01 BY-21 1680 3686 <0. 01 <0.01 <0.01' BY-22 1681 3696 <0.01 <0.01 <0 . 01. BY-23 1682 3704 .<0 . 01 <0. 01 (0.01' BY-24 1683 3700 <0. 01 <0.01- <0.01 4th Quarter 1988 BY-01 BYAP-1779 3753 <0 . 01 - (0.01 <0.01-BY-02 1780 3753 <0.01 <0.01 <0.01 BY-03 1781 3751 <0.01 <0.01 <0.01 BY-04 1782 3753 <0.01 <0.01 <0.01 BY-05 1783 3761 <0.01 <0.01 <0.01 BY-06 1784 3754 <0. 01 - <0.01 <0. 01 BY-07 1785 3753 <0.01- <0.01 <0.01. BY-08 1786 3752 (0.01 <0. 01 <0.01 BY-21 1787 3746 <0.01 <0.01 <0.01-BY-22 1788 3749 <0.01 <0. 01 <0.01 BY-23 1789 3750 (0.01 <0.01 <0.01 BY-24 1790 3752 <0.01 <0.01 <0.01 a See Introduction.
)
11
4-l. I .' BYRON Table 5. Gamma Radiation, as Measured by Thermoluminescent Dosimeters (TLDs)- STANDARD RADIOLOGICAL MONITORING PROGRAM 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 01-02-89 04-03-89 07-03-89 10-02-09 Date Removed: 04-03-89 07-03-89 10-02-89 01-02-90 4 Days in the Field: 91 91 91 91 Location Average mR/Qtr. Offsite Indicator Locations 8Y-01 Byron 13.5 0.9 12.620.9 12.6 1.3 13.020.8 BY Nearsite East 12.3 0.9 16.621.2 16. 0 t0.9 . 15.9 0.9 BY Paynes Point 11.9:0.9 16.83 1.3' 14.820.9 16.2 0.8 BY Nearsite South 13.9 0.8 19.0 1.3 17 .0 0.9 17.6:1.3 BY Oregon 12.1 1.0 14.8 1.5 13.9 1.0 13.6 0.8 Mean i s.d. 12.7 0.9 16.022.4 14.9 1.7 15.3 1.9 Onsite Indicator Locations BY Onsite North 9.6 1.0 11.020.8 11.4 0.9 11.520.7 BY Onsite ESE 15.3 1.2- 18.820.8 18.011.1 18.5tl.1 BY Onsite South 14.0!1.3 17.520.8 16.721.4 16.9 0.9 BY Met. Tower 12.3 1.2 16.811.0 '15.811.4 16.7 0.9 Mean s.d. 12.8r2.5 16.013.4 15.522.9 15.92 3.0 Background Locations BY Stillman Valley 10.9 0.9 13.320.8 13.311.0 14.0t0.8 BY Mt. Morris 11.6 0.8 15.821.0 14.411.1 15. 6t 0. 8 BY Leaf River 12.0 0.9 14.6tl.1 14.411.3 14.1 0.7 Mean s.d. 11.St0.6 14.611.2 14.0t0.6 14. 6t 0.9
.~
12
4 0-BYRON . Table 5. Gamma Radiation, as Measured by TLDs-(continued) SPECIAL PROGRAM Innce Ring, Near Site Boundary, Indicator Locations 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 01-02-89 04-03-89 07-03-89 10-02-89 Date Removed: 04-03-89 07-03-89 10-02-89 01-02-90 Days in the Field: 91 91 91 91 Location Average mR/Qtr.- BY-101-1 13.221.3 17,920.8 17.2tl.6 17.4t0.7 BY-101-2 15.9t0.9 18.6t0.8 16.810.8 18.020.7 BY-102-1 13.911.0 19.120.8 17.111.1 19.4tl.3 BY-102-2 15.811.0 18.211.0 17.511.0 17.8t0.8 BY-103-1 12.6t0.9 17.120.8 15.6*1.2 16.520.9 BY-103-2 14.110.9 17.4t0.8 15.3t0.8 16.410.6 BY-104-1 13.4t0.9 18.220.0 16.310.8 18.3t1.2 BY-104-2 15.021.0 17.6t0.8 16.521.1 17.6t0.7 BY-105-1 14.410.9 18.7t0.9 17.310.8 18.3t0.7 BY-105-2 15.3t0.9 17,910.8 16.521.0 17.8t0.9 BY-106-1 13.310.9 18.220.8 16.9 0.9 17.610.7 BY-106-2 14.111.1 16,811.0 15.010.9 16.310.8 BY-107-1 14.4t1.2 21 lil.1 17.421.0 19.810.9 BY-107-2 16.4t0.9 18.621.1 17.620.9- 18.0t0.9 BY-108-1 14.920.9 19.4t0.8 18.0t1.0 18.510.7 BY-108-2 13.0t0.9 14.420.9 14.3t0.9 14.920.8 BY-109-1 12.810.8 17.421.0 15.910.9 17.210.7 BY-109-2 14.621.1 14.7tl.0 16.1tl.0 16.811.0-BY-110-1 15.0t0.8 16,910.9 14.821.0 16.320.7 BY-110-2 14.4tl.2 15.421.1 16.121.0 15.420.9 BY-111-1 16.011.1 18.3t0.8 16.0t0.7 17.6t0.7 BY-111-2 15.721.1 16.310.9 17.020.9 16.120.8 BY-112-1 14.6tl.0 17.520.9 15.811.0 16.810.6 BY-112-2 14.210.9 15.521.0 16.0 0.8 15.310.8 BY-113-1 13.9 0.9 16.821.1 15.110.9 16.4t0.7 BY-113-2 12.8t0.9 13.620.9 13.9t0.8 14.5tl.0 BY-114-1 11.620.8 13.8tl.1 12.7 t0.8 14.011.0 BY-114-2 14.110.9 16.310.9 15.7 t0.9 15.920.7 BY-115-1 14.311.0 16.321.2 15.3t1.0 16.2t1.0 BY-115-2 13.8tl.0 15.6t1.2 14.021.0 15.4t0.8 BY-116-1 12.310.9 14.0t0.9 15.311.2 14.120.7 BY-116-2 14.921.1 15.8t1.1 15.4tl.0 15.611.3 Mean t s.d. 14.211.1 17.011.8 16.021.2 16.821.4 13
.i . ,
s BYRON N ,
,g Table 5. Gamma Radiation, as Measured hy TLDs (continued)-
SPECIAL PROGRAM Outer Ring, Near 5 Mile Radius, Indicator Locations t ist Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 01-02 04-03-89 07-03-89 10-02-89 Date Removed:- 04-03-89 07-03-89 10-02-89 ' 401-02-90 Days in the Field: .91 91 91 91 1 Location Average mR/Qtr. BY-201-1 13.111.1 16.621.1 14.011.4 .16.520.8 BY-201-2 16.2tl.0 18.410.9 17.821.0 17.9i0.7 O BY-202-1 13.420.9 15.620.9 14.0t0.8 15.320.8 BY-202-2 15.120.8 16.8tl.3 16.7tl.2 17.510.8 ' BY-203-1 10.820.9 11.711.0 11.610.7 12.510.9 BY-203-2 14.7t1.5 16.1tl.0 15.7tl.3 16.210.9 BY-204-1 -11'.210.8 13.020.9 12.620.8 13.5t0.7-BY-204-2 15.410.9- 18.410.8 17.0t0.8 17.520.8 BY-205-1 15.610.9 18.2*1.6 17.211.1 17.310.9 BY-205-2 14.6 1.0 16.8t0.9- 15.6t0.9 16.521.0 BY-206-1 16.611.2 18.5:1.0 17.611.0 17.920.8 BY-206-2 15.810.9 17.510.9 17.110.8 16'.920.8' BY-207-1 15.7t0.9 19.0t0.9 17.8tl.1 18.720.9 -, 17.4 1.0 16.4tl.0
~
BY-207-2 15.120.8 16.220.8 BY-208 17.410.9 20.510.9 19.920.8 19.420.9 BY-208-2 15.821.0 17.510.9 16.8t0.8 17.220.8 " BY-209-1 17.5t1.5 19.521.9 19.0tl.2 18.7tl.4 BY-209-2 13.021.0- 15.120.9 14.610.9 14.720.8 ; BY-210-1 15.120.8 19.2t0.8 17.511.0 18.2t1.0 - BY-210-2 15.2tl.1 16.811.1 17.0t0.8 17.1tl.0 BY-211-1 15.3t0.8 16.420.9 16.611.1 17.121.1 ' BY-211-2 15.6t1.7 19.011.1 17.821.3 18.620.9 BY-212-1 15.620.8 18.3t0.8 17.520.9 18.221.5 ' BY-212-2 14.7t0.9 20.4tl.0 17.7t0.9 19.511.0 BY-213-1 15.6t0.8 16.721.1 17.420.9 16.520.9 BY-213-2 15.211.0 19.721.1 18.120.9 19.0t0.7 BY-214-1 14.521.0 16.0 tl .0 16.221.0 16.120.9 BY-214-2 15.011.4 17.810.8 16.920.8 17.820.8 BY-215-1 15.8tl.0 17.610.8 17.120.9 17.7t0.8 BY-215-2 14.120.9 18.721.1 16.910.9 18.120.7 BY-216-1 17.121.0 17.821.0 18.3tl.6 17.421.0 BY-216-2 16.511.1 19.610.9 18.121.2 18.St0.8 l, Mean t s.d. 15.1t1.5 17.521.9 16.711.7 17.2tl.6 l
, 14
j .._ BYRON Table 5. Gamma _ Radiation, as Measured by TLDs (continued) RESTRICTED AREA MONITORING PROGRAM 3rd Quarter 4th Quarter
-Date Placed: 107-03-89 10-02-89 Date Removed: 10-02-89 01-02-90 Days in the Field: 91 91 Location Average mR/Qtr.
B-1 Security Gatehouse (Parking Lot) 14.5t0.8 16.8 1.4
.i J
d 14A 1 1
o-BYRON
I Table 6.
Milk Collection: Monthly; semimonthly durin9 grazing season (May-October) Units: pCi/l ! Collection Other Date Lab Code 1-131 Cs-134 Cs-137 Gammasa Warren Danakas Farm BY-15 01-02-89 BYMI-2968 <0.5 <5 <5 <10 02-06-89 3072 <0.5 <5 <5 (10 03-06-89 3139,40 <0.5 <5 <5 <10 04-03-89 3214 <0.5 <5 <5 <10 05-01-89 3288 <0.5 <5 <5 <10 05-15-89 3365 <0.5 <5 <5 <10-06-05-89 3465 <0.5 <5 <5 <10 06-19-89 3544 <0.5 <5 <5 <10 07-03-89 3609 <0.5 <5 <5 <10 07-17-89 3676 <0.5 <5 <5 <10 08 07-89 3792 <0.5 <5 <5' <10 08-21-89 3870 <0.5 <5 - <5 <10 09-04-89 3933 <0.5 <5 <5 <10 09-18-89 4017- <0.5 <5 <5 <10 10-02-98 4083 <0.5 <5 <5- <10 10-16-89 4146,7 <0.5 <5 <5' <10 11-06-89 4233 <0.5' <5- <5 <10 l' 12-04-89 4298 <0.5 (5 <5 <10 Bill Leupkes Farm BY-25, 01-02-89 BYMI-2970 <0.5 <5 <5 <10 02-06-89 3074 <0.5 <5 <5 <10 03-06-89 3143 <0.5 <5 <5 <10 04-03-89 3217 <0.5 <5 <5 <10 05-01-89 3292 <0.5 <5 <5 <10 05-15-89 3368 <0.5 <5 <5 <10 06-05-89 3468 <0.5 <5 <5 <10 06-19-89 3547 <0.5 <5 <5 <10 07-03-89 3611 <0.5 <5 <5 <10 07-17-89 3679 <0.5 <5 <5 <10 08-07-89 3796 <0.5 <5 <5 (10 08-21-89 3873 <0.5 <5 <5 <10 09-04-89 . 3937 <0.5 <5 <5 <10 09-18-89 4020- <0.5 <5 <5 <10 10-02-89 4086,7 <0.5 <5 <5 <10 . 10-16-89 4150 <0.5 <5 <5 <10 11-06-89 4236,7 <0.5 <5 <5 <10 12-04-89 4301 <0.5 <5 <5 <10 a See Introduction. l l 15 9 e 4 y
BYRON Table 6. Milk (continued) }. - Collection Other Date Lab Code 1-131 Cs-134 Cs-137 Gammasa Whitten Holsteins BY-17 01-02-89 BYMI-2969 <0.5 <5 <5 <10 02-06-89 3073 <0.5 <5 <5 <10 03-06-89 3141 <0.5 <5 <5 <10 04-03-89 3215 <0.5 , <5 <5 <10 05-01-89 3289 <5 <5 <10 05-15-89 3366
<0.5/
<0.5 <5 <5 <10 06-05-89 3466 <0.5- <5 <5 <10 06-19-89 3545 <0.5 <5 <5 <10 07-10-89 363P <0.5 <5 <5 <10 07-17-89 3677 <0.5 <5 <5 <10-08-07-89 3793 <0.5 <5 <5 <10 08-21-89 3871 <0.5 <5- <5 <10 09-04-89 3934,5 <0.5 <5 <5 <10
, 09-18-89 4018 <0,5 <5 <5 <10 10-02-89 4084 <0.5 <5 <5 <10 10-16-89 4148 <0,5 <5 <5 <10 11-06-89 4234 <0.5 <S <5 <10 12-04-89 4299 <0,5 <5 <5 <10 Kenneth Reeverts Farm BY-20b 01-02-89 BYMI-NSc .. .. .. ..
02-13-89 3100 <0.5 <5 <5 <10 03-06-89 3142 <0.5 <5 <5 <10 s 04-03-89 3216 <0.5 <5 <5 <10 05-01-89 3290,1 <0.5 <5 <5 <10 05-15-89 3367 <0.5 (5 <5 <10 06-05-89 3467 <0.5 (5. <5 <10 06-19-89 3546 <0.5 <5 <5 <10. 07-03-89 3610 <0.5 <5 <5 <10' ' 07-17-89 3678 <0.5 <5 <5 <10 08-07-89 3794,5 <0.5 <5 <5 <10 08-21-89 3872 <0.5 <5 <5 <10 09-04-89 3936 <0.5 <5 <5 <10 09-18-89 4019 <0.5 <5 <S <10 10-02-89 4085 <0.5 <5 <5 <10 + 10-16-89 4149 <0.5 <5- <5 <10 t 11-06-89 4235 <0.5 <5 <5 <10 12-04-89 4300 <0.5 <5 <5 <10 a See Introduction, b On February 13, 1989, Ed Seabold Farm was replaced by K. Reeverts Farm, 5674 German Church -Road, Byron, IL. c NS = No sample available. I 16 n -- - - - . _ _ _ - - - _._._.-__._n,_....__-n.x_--_ - n . _ _ . . _ _ ._. _s n, . , _
4 4 BYRON Table 7. Fish, Edible Portions. Collection: 3 times per year
~ Unit: pCi/g wet'. weight Collection Other Date Lab. Code Type Cs-134 Cs-137 Gammasa -
Oregon Pool of Rock River BY-12
'05-08-89 BYF-659 Perch <0.10 .<0.10 <0.13 4 05-15-89 -
676 Bass <0.10 <0.10 <0.13 07-24-89 . 770 Catfish <0.10 <0.10 ~ <0.13 07-31-89 777 Carp <0.10 <0.10 <0.13 10-16-89 863' Catfish <0.10 <0.10 -<0.13 10-16-89 864 ' Walleye <0.10 <0.10 <0.13 Upstream BY-13
'05-15-89 BYF-677 Carp <0.10 <0.10 <0.13 05-15-89 678 Catfish <0.10 <0.10 <0.13 07-17-89 753 Carp <0.10 <0.10 <0.13 07-24-89 771 Catfish <0.10 <0.10 <0.13 10-30-89 902 Carp <0.10- <0.10 <0.13-11-06-89 907 Catfish <0.10 <0.10 <0.'13 ~
a See introduction. I 17 s . . .,
i {
.4
- BYRON , Table 8. Vegetables Collection: Annually Units: pCi/g wet weight Other Collection 'I-131a Cs-134 Cs-137- Gammasb ! Date tab Code Type ._ ___.____ BY-19-1 966 East Weld Park Road .
---- <0.1 <0.1 <0.2 08-07-89 BYVe-689,90 Cucumber Brussel Sprouts ---- <0.1 <0.1 -<0.2 08-07-89 692 <0.2
; ---- <0.1 <0.1 08-07-89 693 Zucchini. <0.1 <0.1 <G.2 816 Broccolli Leaves 0.02 10-09-89 Es BY-19-2 6993 North River Road Cucumber
---- <0.1 <0.1 <0.2 08-07-89 BYVe-695
<0.2
'696 Carrots ---- (0.1 <0.1 08-07-89 ---- <0.1 <0.1 <0.2 08-07-89 697 Corn Beets
~
---- <0.1 - <0.1 <0.2 08-07-89 698 Cabbage 0.03 <0.1 <0.1 <0.2 10-09-89 817
" Analysis for I-131 required for green leafy vegetation only.
See Introduction. s
3 r* BYRON Table 9. Surface Water
- Units
- pC1/1 MONTHLY COMPOSITES OF WEEKLY COLLECTIONS -
Composite Other Period Lab Code Cs-134 Cs-137 Gammasa Woodland Creek BY-09 January, 89 , BYSW-319b <10 <10 <15 February , 89 NSc .. .. .. March, 89 1282 <10 <10 <15 April,-89 1660 <10 (10 <15 May, 89 1862 <10 <10 <15 June, 89 2552 <10 <10 <15 July, 89 2884,5 <10 <10 <15 August, 89 3132 <10 <10 <15 September, 89 . 3677 <10 <10 <15 October, 89 4098 <10 <10 <15 November, 89 <10
<10 <15 42g0 -' ' December, 89 NS Downstream BY-12 January, 89 BYSW-617b <10 <10 <15 February, 89 NSc .. .. ..
March, 89- 1283 <10 <10 <15 April , 89 1661 <10 <10 <15 May, 89 1863 <10 <10 <15 June, 89 2553 <10 <10 <15 July, 89- 2886 <10 <10 <15 August, 89 3133,4 <10 <10 <15 September, 89 3678 <10 <10 <15 0etober, 89 4099,100 <10 <10 <15 November, 89 4291,2 <10 <10 <15 December, 89 4729 <10 <10 <15 Upstream BY-13 January, 89 BYSW-321b <10 <10 <15 February , 89 NSc .. .. .. March, 89 1284 <10 <10 <15
, Apri1, 89 1662 <10 <10 <15 May, 89 1868 <10 <10 <15 June, 89 2554 <10 <10 <15 July, 89 2887 <10 <10 <15 Au9ust, 89 3135 <10 <10- <15 September, 89 3679,80 <10 <10 <15 October, 89 4101 <10 <10 <15 November, 89 42g3
<10 <10 <15 December, 89 NS -- -- --
a See Introduction, b Grab sample, collected 01-30-89. I c NS = No sample available. River frozen. 19,
.. t
,L
= !
, BYRON Table 9. Surface Water (continued)
QUARTERLY COMPOSITES OF WEEKLY COLLECTIONS Concent' ration (pCi/1) Composite Period Lab Code Tritium Woodland Creek BY-09 1st Quarter, 1989 BYSW-1086 <200
- 2nd Quarter, 1989 2491 <200 3rd Quarter, 1989 3614' <200 4th Quarter, 1989 4724 <200 Downstream BY-12 -
1st Quarter, 1989 BYSW-1087 596 105 2nd Quarter,1989 2492 7902100 3rd Quarter, 1989 3615 5321113 4th Quarter, 1989 4725 14702136 Upstream BY-13(C) f 1st-Quarter, 1989 BYSW-1088 <200 2nd Quarter, 1989 '2493' <200 3rd Quarter, 1989 3616 <200 4th Quarter, 1989 4726- <200 1 20
. - . . _ . . . _ . .=...
^
'#. ,0-BYRON Table 10. Well Water Units: pC1/1 Collection: Composite of semimonthly collections.
MONTHLY COMPOSITE OF SEM1HONTHLY' COLLECTIONS BY-14 BY-18 ~ Collection Gross Other - Gross lither Beta Cs-137 Gammas a .d . Date Lab Code Beta Cs-134 Cs-137 Gammas - ~ Lab Code Cs-134 January, 89 NDb -- -- -- -- BYWW-572,3 1.310.6 <10- <10 <15 February, 89 BYWW-748 <1.7 <10 <10 <15 749 ' <1.8 <10 <10' <15 O! Harch, 89 1285 <1.5 <10 <10 <15 1286 <1.6 <10 <10 <15 April, 89 1663 2.211.3 <10 <10 <15 1664,5 1.8 1.3 <10 <10 <15 May, 89 1869 <2.4 < 10_ .<10 <15 1870 <2.3 <10 <10 <15 June, 89 2555,6 <1.6 <10 <10 <15 2557 <1.7 <10 <10 <15 July, 89 2888 <2.6 .<10 .<10 <15 2889 <2.3 <10 <10 <15 August, 89 3136 <2.2 <10. _<10 _<15 3137 <2.3 <10 <10 ~< 15 September, 89 3681 <1.8 <10 <10 <15 3682 <1.6 <10 <10 '
<15 October, 89 3757c <2.5 <10 <10 <15 4102 <2.5 <10 <10 <15 November, 89 4294 <1.8 <10 ' < 10 . <15 4295 <1.6 <10- <10 <15 Decenber, 89 4730 <1.6 <10 <10 <15 4731 2.211.1 <10' <10 ' <15
.m.r a See Introduction.
5 ND = No data. Sample not collected, pump out of order. c Grab sample only; pump out of order first part of October. d In monthly reports "other gammas" were reported as <20. The change to <15 was made to comply with Technical Specifications. Actual-LLD's obtained for.all samples were.much lower than " reported.
. - - . .,m., w -
. . ~ , , . ~ , ww g # s h. gor -
.fw...e - '%, . - , - - ,. , ..-y+ v _
( e BYRON l l
]
Table 10. Well Water Units:. pC1/1 i QUARTERLY GRAB SAMPLES Coll ection Date Lab Code Tritium
'1 Off-Site Well BY-14 ist Quarter, 89. BYWW-1089 <200 2nd Quarter, 89 2494 ,
<200 3rd Quarter, 89 3617 236 103 4th Quarter, 89 4727 .<200 McCoy Farmstead Well BY-18 1st Quarter, 89 BYWW-1090 <200 2nd Quarter, 89 2495,6 <200 3rd Quarter, 89 3618 .<200 4th Quarter, 89 4728 <200 ,
a See Introduction. r i 22
i,f BYRON Table 11. Bottom-Sediments Collection: Semiannually , Units : -pCi/g dry weight. Date Other Collected Lab Code Cs-134 Cs-137 _ Gammasa Oregon Pool of Rock River BY-12 05-01-B9 BYBS-510,1 <0.1 <0.1 <0.2 10-09-89 BYBS-623 <0.1 <0.1 <0.2 Upstream BY-13 05-01-89 -BYBS-640 <0.1 <0.1 <0.2
.10-09-89 BYBS-624 <0.1 <0.1 <0.2 a
See Introduction. 23
g . -
?l ; .. .
,o i'
1-4 l' el fl . n BYRON f h i HILCH ANIMALS AND NEAREST RESIDENCES CENSUS i
- h:
~! . . '
-)
9 24
7
,e .
-6:
4. BYRON BYRON DAIRY CENSUS 1989 5 A. Site Boundary to 7 mi. None B. 2'mi, to 5 mi. -; i
- 1. Reeverts Dairy Farm (BY-20) 5674 N. German Church Road Route 1-Byron, Illinois {
2.1 miles @ 037' Milks 40 cows
- 2. Whitten Dairy Farm (BY-17)
Didtown Road Route 1 , Byron, Illinois- 'i 8.5 miles @ 250' Milks 40 cows l
- 3. Warren Danakas (BY-15) 5845^ East Holcomb Road Route 1.
Oregon, Illinois ; 3.3 miles @ 110' !
?
Milks 14 cows 4.: 0ltmann Dairy Farm; Richard Oltmann, owner
'1858 N. German Church Road Route 1 gj Oregon, Illinois 2.2 miles @ 180' i Milks 15 cows u
25 v
, . , 73, .
. . .. ..v -
,~ ,-
, ~ 1, .- v - -
m , o- , 8 BYRON DAIRY CENSUS 1989 (continued) ; e . v rh
- 5. Bill Luepkes (BY-25) 2887 Brick Road '
Route 1 Oregon, Illinois l 3.7 miles @ 190' Milks 56 cows
- 6. Ashelford Dairy Farm 4210 IL Route 2 Ruute 3 Oregon, Illinois i 2.6 miles @ 275' Milks 12 cows :
- 7. CAM-DEE Farms, Gerald DeVries, owner 5213 N. Town Hall Road Route 3 ;
Oregon, Illinois 3.3 miles @ 290' l Milks- 35 cows
- 8. Duane Camling '!
50 East Camling Road t Route 3 Oregon,. Illinois 3.2 miles @ 305' Milks 26 cows C. Sampling Locations BY-15 Warren Danakas Milks 14 cows - Diet: ; May - October: Pasture 5 acres. Pasture, hay, corn, oats , protein / mineral supplement. ' November - April: Feedlot 1 acre. Hay, corn, oats and protein / supplement. ,. t 26 !
, .m . v.. . g y y , 7.., .
a k
*v i
BYRON DAIRY CENSUS 1989 (continued) BY-25 Bill Luepkes Milks 56 cows Diet: ; May - October: Pasture feedlot 2 acres. Haylage, corn, hay, and protein / mineral supplement. . November - April: Feedlot less than 2 acres. Haylage, hay, , corn, silage, oats, and protein / mineral s supplement . BY-17 Whitten Farm Milks 40 cows Diet: May - October: Pasture feedlot 5 acres. Green chop, hay, haylage, mineral supplement. - November - April: Feedlot 0.5 acres. Silage, haylage, corn, hay, mineral supplement. BY-20 hoeverts Dairy Milks 40 cows Diet: May - October: Pasture 7 acres. Pasture, Haylage, hay, i corn, protein / mineral supplement. November - April: Feedlot less than 2 acres. Hay, silage, corn, protein / mineral supplement. Census conducted by L. Coleman on August 21, 1989. i Y l 27
m o BYRON d i NEAREST RESIDENCE CENSUS,1989 Nearest residences of the Byron Station within a five (5) mile radius. N 1.9 miles NNE 1.5 miles NE 0.9 miles ENE 1.3 miles E
, 1.2 miles ESE 1.6 miles SE 1.1 miles SSE 1.2 miles S 0.7 miles SSW 0.6 miles SW 0.9 miles WSW 1.7 miles ,
W 2.0 miles l WNW 0.8 miles l l NW 1.2 miles l NNW 1.3 miles , l Census conducted by L. Coleman on August 21, 1989. l 28 i l}}