ML20073D004
| ML20073D004 | |
| Person / Time | |
|---|---|
| Site: | Byron  |
| Issue date: | 12/31/1990 |
| From: | Pleniewicz R COMMONWEALTH EDISON CO. |
| To: | Davis A NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III) |
| References | |
| BYRON-91-0260, BYRON-91-260, NUDOCS 9104260110 | |
| Download: ML20073D004 (69) | |
Text
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-~x C:mm:nw:alth Edison N Byron Nucl:ar Station . . .
, / 4450 North GGrmin Chusch Road
' 7 Byron, Illinois 61010 m../
h April 5, 1991 LTRI Byron 91-0260 FILE 9 2.12.1523 Mr. Bert Davis Administrator Nuclear Regulatory Commission Region III 799 Roosevelt Road Glen Ellyn, IL 60137 Dear Mr. Davis Enclosed is the 199C Byron Station Annual Radiological Environmental Operating Report Docket Numbers 50-454 and 50-455.
This report contains the results of the Radiological Environmental and Meteorological Monitoring Programs.
1 Two copies of the report are provided for your use. Two copies will be forwarded to the Document Centrol Desk and one copy to
-the Resident Inspector.
Sincerely yours, Rich Pleniewicz Station Manager Byron Nuclear Power Station RP/BM/dd 9104260110 9MR PDR R
ADOCK 0500 PDR 54
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BYRON ST ATION ANNUAL R A DIOLOGIC A L ENVIRONMENT AL OPER ATING REPORT I
1990 M A RCH 19 91
TABLE OF CONTENTS Page INTRODUCTION . . . . . ...................... 1
SUMMARY
............................. 2 10 EFFLUENTS ............................ 3 1.1 Gaseous . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 1.2 Liquid ........................... 3 2.0 SOLID RADI0 ACTIVE WASTE ..................... 3 3.0 DOSE-T0 MAN ........................... 3 3.1 Gaseous Ef fl uent Pathways . . . . . . . . . . . . . . . . . . 3 3.2 Liquid Effluent Pathways .................. 5 3.3 Direct Radiation ...................... 5 4.0 SITE METEORC!0GY . . . . . . . . . . . . . . . . . . . . . . . . . 6 5.0 ENVIRONMENTAL MONITORING . . . . . . . . .. . . . . . . . .-. . . . 6 5.1 Gamm a R ad i at i on . . . . . . . . . . . . . . . . . . . . . . . 6 5.2 Airborne 1-131 and Particulate Radioactivity ........ 7 5.3 Terrestrial Radioactivi ty . . . . . . . . . . . . . . . . . . 7 5.4 Aquatic Radioactivity . . . . . . . . . . . . . . . . . . . . 7 5.5 Mil k ........-.................... -
8 5.6 - Sample Collections ..-................... 8 5.7 Program Modi fi cat i ons . . . . . . . . . . . . . . . . . . . . 8 6.0 ANALYTICAL PROCEDURES ...................... 9 7.0 MILCH ANIMAL CENSUS ....................... 9 8.0 NEAREST RESIDENCES CENSUS .................... 9 9.0 INTERLABORATORY COMPARIS0N PROGRAM RESULTS . . . . . . . . . . . . 9 10.0 ADDENDA ............................. 9 i
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TABLE OF CONTENTS (continued)
Page APPENDIX 1 - DATA TABLES AND FIGURE S . . . . . . . . . . . . . . . . . . 10 Station Releases Table 1.1-1 Gaseous Ef fluents .................. 11 Table 1.2-1 Li qui d E f fl ue nt s . . . . . . . . . . . . . . . . . . .
- 19 Table 2.0-1 Solid Waste Shipments ................ 23 Figure 3.1 Figure 3.1-4 Isodose and Concentration Contours . . . . . . . . . . 35 Table 3.1-1 Maximum Doses Resulting from Airborne Releases . . . . 39 Table 3.2-1 Maximum Doses Resulting f rom Liquid Discharges . . . . 43 Environmental Monitoring Figure 5.0 Figure 5.0-4 Locations of Radiological Environmental Stations . . . 45
- Tabl e 5.0 Radiological- Environmental Monitoring Sampl i ng Si tes . . . . . . . . . . - . - . . . . . . . 49 Table 5.0-2 Radiological Environmental Fbnitoring Program .... 50 Table 5.0 Table 5.0-6 Environmental Summary Tables ...... .
56 APPENDIX 11 - METEOROLOGICAL DATA ..... ............. 63 APPENDIX 111 - 1990 REMP SAMPLE RESULTS ................ 92 APPENDIX IV - INTERLABORATORY COMPARIS0N PROGRAM RESULTS . . . . . . . . 125 APPENDIX V - ADDENDA . . . . . . . 1 ................. 163 I
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INTRODUCTION
.ByronL 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
' regul ations .- r Liquid Lef fluents: from Byron: Station _ are relecsed into the Rock River in controlled < batches .after redioassay of each batch. Gaseous effluents are-
- released toithe: atmosphere.'and are calculated on the basis of -analyses of .
daily; grab samplesLof. 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,1-131
. and; particulate 1 radioactivity in' offsite areas are calculated using isotopic
- composition-of effluents effluent and meteorological data.
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. En n ironmental monitoring is ~ conducted by sampling at indicator- and : reference (control) -. locations inithe. 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 1-131 in milk are the most critical pathways at- ,
this site;' however, an- environmental monitoring - program: is conducted wh'ich-
~
- includes. otherL pathways- of less importance. _
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SUMMARY
Gaseous and . liquid . effluents for the period'. remained at a - fraction of 'the
- Technical SpecifMtiqn limits. Calculations of environmental concentrations based on efficent, Rock River flow, and meteorological data for the period indicate thcc- consumption by - the public- of radionuclides attributable to the. plant are well below the regulatoryi limits. ' Radiation exposure from
. radionuclides released to the atmosphere ' represented the critical pathway _ for
- the period with a maximum individual dose estimated to be 1.14E-03 mrem for
--the year, when'a shielding and occupancy _ factor of 0.7 is assumed.
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The assessment of radiation doses -.is performed -in accordance with the:0ffsite Dose
- Calculation Manual- '(0DCH)~. The results of analysis confirm that the station ',
is operating in compliance with 10CFR50 and 40CFR190.
An ~ assessment of radiation do'ses from liquid - and gaseous effluents to mem--
.bers of_ the public -due to their- activities inside the site boundary during -
i theFreporting period is not included because it is not applicable to Byron 1 Station.
There were :no additional operational controls _ implemented -which affected thel :i
- areas of . radiological effluents in _1990.
There were. no measurements which exceeded the- reporting levels, including any
?
unich would_.not have been attributable to plant effluents.
The 'results nof -the . current ' radiological environmental monitoring program
- approximate 7those . found- during - the preoperational studies conducted at Byron Station.
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1.0 EFFLUENTS 1.1 Gaseous Effluents to the Atmosphere Measured concentrations and isotopic composition of noble gases, radioiodine, and particulate radioactivity released to the atmos-phere during the year, are listed in Table 1.1-1. A total of 1.24E+03 curies of fission and activation gases was released with a maximum monthly release rate of 2.51E+04 uC1/sec.
A total of 4.41E-03 curies of I-131 and I-133 was released during the year.
A total of 3.80E-05 curies of beta-gamma emitters and 6.13E-06 curies of alpha emitters were rel eased as airborne particulate matter, A total of 1.07 curies of tritium was released.
1.2 Liquids Released to the Rock River A total of 6.37E+07 liters of radioactive liquid waste (prior to dilution) containing 1.16 curies (excluding tritium, gases, and alpha). were discharged after dilution with a total of 2.66E+10 liters of water. These wastes were released at a monthly average concentration of 4.92E-08 uCi/ml, discharged on an unidentified nuclide basis. An undetectable amount of alpha radioactivity and 9.98E+02 curies of tritium were released. Monthly release estimates and principal radionuclides in liquid effluents are given in Table 1.2-1.
2.0 SOLID RADI0 ACTIVE WASTE Solid radioactive wastes were shipped to Barnwell Nuclear Center, South Carolina and Richland, Washington. The record of waste shipments is sumarized in Table 2.0-1.
3.0 DOSE TO PAN 3.1 Gaseous Effluent Pathways Gama Dose Rates Gamma air and whole body dose rates offsite 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.
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Based on ' measured effluents and meteorological data, .the maximum idose to an- individual would be 1.14E-03 mrem for the year,~ with 'an *
, occupancy or_ shielding - factor of 0.7 included. The maximum gamma air dose was 4.24E-03 mrad.
Beta Air and Skin Rates The range of beta particles in air is relatively small (on the order '
.of a few meters or less); consequently, plumes of-gaseous effluents may be considered " infinite" for purpose of- calculating the dose from beta radiation incident on the skin. However, the actual dose to sensitive . skin tissues is difficult to calculate because this L 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 i for the year was 8.78E-03 mrem.
The - air- concentrations of radioactive noble gases at the offsite
. recepto- locations -are given in Figure 3.1-2. The maximum offsite
- beta ' air dose for the year-was 1.64E-02 mrad.
e Radioactive Iodine
- The - human thyroid . concentrates ingested or inhaled iodine end the radionuclide I-131. Minimal levels released during routine opera-
' tion of. the p1 ant.-may-be made available to-man thus resulting in -a
- dose to the thyroid. The pathway = of interest _ for this -radionuclide is.-ingestion of radioiodine -in milk byL an infant. Calculations are performedEannually but . the --levels released from the station in previous _ years indicate that contributions to doses--from inhalation zof 1-131 and'I-133, and I-131 in milk, are negligible.
l? Iodine-131 Concentrations in Air 4,
I o .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 L phenomenon of elemental l iodine deposition on the ground. The maximum offsite- concentration p
H is estimated--to -be S.23E-04 pC1/m3 for the year.
~00se to Infant's Thyroid
- 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 1.34E-02 mrem during the year (Table 3.1-1).
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1-Concentrations of Particulates in Air Concentration contours of radioactive airborne particulates are shown in Figure .1- 4 . The maximum offsite level is estimated to be 4.48E-06 pC1/m}0 Summary of Doses Table 3.1-1 summarizes the doses resulting from releases of airborne radioactivity via the dif f erent exposure pathways.
3.2 Liquid Effluent Pathway,ss The three principal pathways through the aquatic environment for potential doses to man from liquid waste are ingestion of potable water, eating aquatic foods, and exposure while walking on the shoreline. Not all of these pathways are applicable at a given time or station but a reasonable approximation of the dose can be made by adjusting the dose formula for season of the year or type and degree of use of the aquatic environment. NRC* developed equations were used to calculate the doses to the whole body, lower G1 tract, thyroid, bone and skin; specific parameters for use in the equations are given in the Commonwealth Edison Offsite Dese Calculation Manual . The maximum whole body dose for the year was 2.30E-02 mrem and no orgen dc:a exceeded 8.12E-02 mrem.
3.3 Direct Radiation In Section 3/4.11 of the Byron Technical Specifications, 40CFR190 calculations of total dose due to the Uranium Fuel Cycle are re-quired only when calculated doses from liquid or gaseous releases of radioactivity exceed certain levels. These levels are twice the following limits:
a 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 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).
Nuclear Regulastory Commission, Reguitory Guide 1.109 (Rev . 1 ) .
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i a The RETS limits.on air dose in noble gases released in gaseous effluents to a Member of' the 1 Public from each reactor unit' (5 mrad for gamma "
- radiation or 10 mrad- for-- beta radiation during any calendar _ quarter; 10 mrad for gamma' radiation R or 20 mrad for beta radiation during any calendar l year). l
- radionuclides in- particulate form with half-lives
- greater than 8 days in gaseous effluents' released 1 from each reactor unit (7.5 mrem to any organ i during any calendar quarter; 15 mrem to any organ !
during any calendar year).
During the period January to December 1990,' Byron Station did not exceed these criteria; offsite and-members of the public-(occasional visitors to the. site) did not exceed these criteria either when-onsite.
~4'.01 SITE METEOR 0 LOGY. ,
A- suninaryi of? the ' site meteorological measurements taken -during _ each Equarter 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 difference between the L250' and 30' levels.
Date recovery.
for these measurements -was -about 99,8%. -
i 5.0 ENVIRONMENTAL MONITORING Tables 5.0-1< and --5.0-2 provide -an: outline of the Radiological Environ -
- 1 mental Monitoring; Program -as required in.- the Technical J Specifications. -
Sampling" locations- are shown in Figures 5.0-1 through 5.0-4. Concentra-
' tions of radioactivity in various media are summarized in . Tables 5.0-3 through15.0-6=, Tables listing all- data are presented 'in Appendix - III.
. Specific findings for various environmental media' are discussed below.
-5.1 Gamma Radiation- q External: radiation dose was measured at- _nine. indicator and three ,
reference (control) : locations using CaSO4 :Dy thermoluminescent
. : September 28, 1981, such that each sector was covered at both five miles and the site -boundary, Quarterly external radiation -dose at _ twelve' air sampling locations averaged (14.512.0) -mR and was R
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similar to that measured in 1985 (14.4 mR),1986 (14.9 mR),1987 (15.3 mR),1988 (15.2 mR), and 1989 (14.6 mR). The differences are not statistically significant.
5.2 Airborne 1-131 and Particulate Radioactivity Locations of air samplers are shown in Figures 5.0-1 and 5.0-2.
Airborne I-131 concentration remained below the LLD of 0.07 pC1/m3 throughout the year in all samples.
Gross beta concentrations ranged from 0.004 to 0.049 pC1/m3 and averaged 0.021 pCi/m3, which was slightly lower than the average concentrations in 1985 (0.026 pC1/m3),1986 (0.026 pCi/m3, except for the period from May 12 through June 9 when it was influenced by the reactor accident at Chernobyl), 1987 (0.027 pCi/m3), 1988 (0.031 pC1/m3), and 1989 (0.026 pCi/m3).
All gamma-enitting isotopes activities were below their respective LLD levels. No radioactivity attributable to plant operation was detected in any of the samples.
5.3 Terrestrial Radioactivity Vegetables were collected in August and analyzed for gamma-enitting isotopes. _ In_ addition, green leafy vegetables were analyzed for iodine-131. All isotopes were below-the limits of detection, indicating that there was no measurable amount of radioactivity attributable to the station releases. Identical results were obtained during the period 1985 through.1289.
Well water was collected monthly from two offsite wells and analyzed for gross beta, and gemma-emitting isotopes. Quarterly composites were analyzed for tritium. Gross beta concentration averaged 2.7 pCi/L and-was similar to that measured in 1988 (2.0 pC1/L) and lower than in 1985 (7.3 pCi/L),1986 (7.5 'pCi/L), and 1987 (7.5 pC1/L).
Tritium was below the LLD level of 200 pC1/L in all samples and was similar- to that in 1985 (232 pCi/L),1986 (<200 pCi/L),1987 (<200 pCi/L),1988 (260 pCi/L), and 1989 (236 pCi/L). All- other results were below the lower limits of detection. The results were similar to those obtained in 1988 and 1989.
5.4 gugicRadioactivity 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
-134 and -137 concentrations were below the LLD level of 10 pCi/L.
Tritium concentration was below the LLD of 200 pCi/L in 611 samples collected from Woodland Creek (BY-09) and Upstream (BY-13). These levels were similar to those obtained in 1985 through 1989.
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i Downstream from ' discharge, tritium averaged 675 pCi/L,- ranging from less than 200 to 1231-. pCi/L. Cs-134 and Cs 137 levels were below
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the LLD level of 10 pC1/L. All other gamma-mitters were below their respective - LLDs. Elevated levels of tritium downstream from discharge: pipe are _ attributable ' to the station operation.- These
. levels were similar to .those obtained in 1905 through 1989.
. Sediment sampies . were coilected twoice, from one control and one 1 indicator location, and. analyzed for gamma-mitters.
Cesium-134 wass below: the -LLD level of 0.1 pCi/g dry weight in all. samples.
Cesium-137 was detected in two samples (one control and one indica-tor) .and ' averaged 0.36 pCi/g dry weight. All other gaina-mitting .,
isotopes, except naturally occurring gamma-emitters, were below ]
detection limits.' q l
' Levels of gamma radioactivity in fish were measured and found in
- all~ cases- to be below the lower limits of detection for the program. .
e The results were identical to those obtained in 1985 through 1989. 1
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- Milk samples were collected monthly from November through April and ]
~bi-weekly from May through~' October and analyzed for iodine-131 and j
, gamma-emitting isotopes. Iodine-131 level was below -the LLD -level ;
of: 0.5 pCi/L in all samples. !
Cs-134s and Cs-137 were below the LLD-level- of 5 pCi/L. . All = other $
gamma-emitting. isotopes, except- naturally-occurring K-40, were below j their respective Lt0s. :There was no tadication of the effect on the j '
environ _ ment due; to station operation. _ : The results for 1-131,' Cs-134 '
and :Cs-137' were -identical to. those obtained during the period 1985 -
through4 1989,L except during several months ~ following accident at- .
Chernobyl , which ' occured on - April 26, 1986. During those: months- _!
.1-131? ranged from-0.9 to 58.6 pC1/L, Cs-134 ranged from !.8 to 10.7 -
2 pCi/L and'Cs-137-ranged from 5.3 to .17.8 pCi/L. !
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5.6C Sample Collections
, m L All samples were collected as scheduled except those listed in -
Listing . of Missed Samples, Appendix _-III.
5.7 Program Modifications -
- In March of 1990, the milk farm at Location BY-25.(0. Leupken Farm, 3.7 miles 8190*) which was destroyed by fire was replaced by R. Oltman Dairy, 24 miles 8 180". In June 1990, Witten Holstein Dairy (BY-17), locatt'd '8.5 miles at 250*, went out of business and was replaced by Hazard Dairy (BY-26), located 13.5 miles 6 355*.
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In October 1990, Druien Dairy (BY-27), located 5.3 miles 0 236',
was added to the program. The sampling of milk at this dairy is not required by the Technical Specifications.
6.0 ANALYTICAL PROCEDURES Procedures used ouring the period covered by this report remained essentially unchanged. A summary of the procedures used for analyzing radioactivity in environmental samples is given in Appendix V of the report for the period January-December 1988.
7.0 MILCH ANIMALS AND NEAREST CATTLE CENSUSES A census of milch animals was conducted within five miles of the Station.
The survey was conducted by " door-to-door" canvas and by information from Illinois agricultural agents. The censuses were conducted by L. Coleman on July 2 and 9, 1990.
8.0 NEAREST RESIDENCES CENSUS The census of nearest residences within a five (5) mile radius was conducted by L. Coleman on July 9,1990.
Results of the milch animals, nearest cattle, and nearest residence censuses are presented in Appendix Ill.
9.0 INTERLABORATORY COMPARIS0N PROGRAM RESULTS Interlaboratory Comparison Program Results are presented in Appendix IV.
10.0 ADDENDA Addenda for January - December,1990 Effluent and Waste Disposal Semi-annual Reports are presented in Appendix V.
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APPENDIX 1 DATA TABLES AND FIGURES 4
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TABLE 1.1-1 tap tiet.tf U l Ontet the $14 50 444 8'''
6flom sAEttad 704 0 $1 allot (ff tutul De unit ( til#0%AL StalAJe4ent alPott f 00 Je* hae 1910 645(0V% ttf LLEstl . kreuttem 6f &LL tittatil 1 imili 1 an 1 P ett i mar J _ gyggligt april j ~ ng gga, 1 gg
- 4. fissies ead actl.ettea 64 tete ies
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a_ mia tam fino arMaart i 1 1 0.07 1
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e, leeine seidaies
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- 1 el 190824 lients in lated ea the easima rolesie rete for the pecied seatisered.
Iodine, pettitelete, 84e tilite IISill era estrelled et e tetel llett. See lle$ E, 11
TABLE 1.1-1 (continued)
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TABt.E 1.1-1 (continued)
De, ii .n U 1 LO(E(I NuM8(R Sf N-50 454 '"'""'
evD0m aaKilat POWtt $tattom (f f tutul Aae wallt 61180$at $tmitsonal 4tPO41 f 04 J9I t *O*C 1990 GA%ttw) If f!Utuf t * $w994flom Of. Att etttatt) i tanL _1.hn Y I AMP. 1 (f p f _ t_ Ted euangt act i Nnv s
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- a. . **14.34(54Larandssatt i 1
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- n. t n nn i o_nn utaAteLacandaari I '1 - I n n> I n_ni I n n1 I n_n> I n nn I n:nn a Jma- o nn
___; a. 1 af IK!!St.Usit a I n nn 1 n.nn m; _ W Outiatis.fi.ataan 1 .n nn n nn n nn_ 2 1 n nn n nn n nn n nn m.
a.ta awrtati:Eimai 1 n nn n nn n nn n nn n nn n nn n.
--- -- .Litt.aun 1 n nn n nn n nn J nn _. n.nn n nn n nn . n nn n nn n nn nJua. Annual f 2e .,ai t n nn n nn n nn n nn n nn n nn n nn n nn
. 4. leelee Releetet i i: Igulh11 Lana 1.111 Artigit. I ri
?
- 2. t af ist[jggigiu ti ite** f$.07F.4ll 1M-419.69 M J 7.16f.4 1 0 nnfe Q 0.norin t 0 not .01 0.QnM I a-t y
1 e' 1 of .10(f th lients in tesed on 14e masseus roleete rete for the period seasidered, 1edeae, portteelete, and tritiva lletts are espeessed es e tetel leett. See Step (,
1 e
I 13
- ~. . . - . . , , . _ - _ . . .- . --
-a m
+
TABLE 1.1-1 (continued) eee lies.t.
U 100CKtt NUMBER $1N $0 454 Ovoom sagttaa pewte Station .
.a (f f tutti amp wallt St190$4L $(alamt 9(P0ef f ee Julv. Bee 1990 ~~
GaSt0U1 (f f twutt . lumell> Of att etttattl~ I l
1 ta t ti 1.It ti Y l A!!r. . 1-(Jpf I .irdnuanity fr f I kog I hrf 1 Jgggggjg3 'I
- t. Pa,tNelett 18 8 6ef hell *lif el 8eleonet
- t. r.r.an asti.it. t et ti g M O,00ftQ d.QQf,1Q1 EM .6 1 0. 0nf tA._
. L . Ersa&43h4. art t u t t. I
) 6.164.Ity 4. it,t .19 F 4 141 191 d MF .19l d .1l_fsf .13,(M[.AL%CQf O_nnr t
.19 L6.16F .19 a d et L ..Lallt(It21/lKf1MEmiti" l 6.16f (6_ lf f . 9 0 ' ltittus Aelestes *
- 1. Igdal141a Artlette i T 1,19E 1 i 4.0tt-2 i 3.16E-2
- 2. 'I af IMfEgf3([1MMalti" ft 15.06E 2 3.42E-2t 3.44(-h 1 4. 34E-2 i 1.16F 1
.(. %e of ledlae, tattleviate {s 8 der ha)f Ilfe), aad frillem Seleatti l
I.'
f atal art t ite i et
-t. i aug(Igmit l i .15 E -213. 4 3E 213. 4 $E -2i 1.20E -1 i 4.01E-2 e 3.16E 2 e4. 39(-2 i 1. t6E 1
.. n.. e, e naa .,
' 1. I af IKf tia Ligit f..u i , u i 0.00 s 0.00 1 0.00 1 0.00 1 0.00 i 0.00 -0.00 1 0.00 ;
.. a utad Aa. ersa. <Lt ., i i t i 0.05_ 10.0i i n.at i 0.07 i 0.00
-a i 0.00 i m - t a. iT I i 0 00 L O.00 ar . i ns.e .r i 1 0.02 I0.00 l A.Qi I 0.03 l 0.00 1 0.00 17M I Do a t . i.)
i......ui.i.i..-.4 o m . u.o ......,... 4..i.t.i u.u, 5,. ii., e ,
f 1
l
- i V
9 a
(
i 14
N TABLE 1.1-1(continued)
,o.,
v., wiei .., si. so..n . 'a'""'
. to., uisi, w e si n.,
(ff LIAai ase esa$1( 01$80$At MaiasesA6L tt70.I f te . lea luns t9to 6AHeul (titwatt .16seintion Of att Attga5()
I tai t t . 1. Jea e fet i 8te
- I fana f f a t Aem b I mas i Jeae I tantu
~ Ai f eesten and Act6 s46ee Gas teleases
- 1. f aul talana Ar tielte l 2.
ft iM21'? l 2.10f *l l P. #2f el i 1. %[ * ? I 4 22t e l 1 . I OR( *? t 1 Ot(*? I I %ftet m.hu am} gat.ta I Jt/ur I 2 Alf *4 I 1.11t e] ] 7.01t sf l 2 31f et I 1. 2 4f *1 I'2.Mf+]
- 1. 1 af taffA1A Liattae I P 0?f *) I ? %te)
- a. mia ham. # as arma/ aart 1 1 fi o 1 0 01 1 1 0.01 1 0 02 l 0 01 1. 0 01 0 01 h ea_ tMWaalgaar n 1 i. 0 0>
- h. _
l 1 l 0 02 1 0.01 1 0.01 l 0.07 I O Ot ~l 0 of l 0 01 1 0 67
- 4. I af Ig(flia ttatta a r-Lafidfis h Mt 1 0.02 0.00 0.00 _ __ LgL , 0.00 k.
ht2 Aartaste f ilafMt
_OJi 0.01 0 02 1 0.04 0.00 0.00 0 04 0.01 0.01
- n. r-=*- 1116,midt 0.01 0 01 1 0.01 0.00 o to D 01 0.00
- m. h ta a-- -I 12e araal 0 00 0.00 0 00 1 0 02 0.30 0.00 0 of 0.00 0.01 0.01 0.0?
- 4. ' ledese telestet
- 1. f aul f. i11 ama 1.111 1111 6 te i ft i G 90f.41 1 R9f.41 0 g(egl 13Af.1 1 0 Ocf *G f D OCf *0 t
- 2. 1 et 1&f f t?$116ffisa L lan ta** 0.00(+0 l Q 31 I of 19(f 32016 ells Il bened se the meaths releste rete for the perled teattdered.
'8 ledite, pef %ltelete, and LFilles llette are esprelled el 4 4etal 11014. See $lep (,
c 15
_...r...,.......---.;,... . . . . . . . . . . . . . . .
P TABLE 1.1-1 (continued)
De t 1144 03 U-l 0%tet 4v ater $14 S0 4% g ,,g i, g
$Y9CII ILgg(&A pohd(g gjag gg lif tIANI Aac alallt etts0%At StillNL t(Poel f ee Jan - Je ea 1990 f.AM0v% tif tUtsti - kawt10se Of Att ettlaug C. Partitelete to 4 seg half,11ren teneaseg
- t. far a t t Ar t t u tiv i fi IMt .01 0 Mt.01 0.00f*0 1 0 00t*0 1 0 00(*0 1 4 90t*0 1 0 Oct eG
_.J 1rsagAntigite I fi I dold t I ca IM.13,ga. Q0t *0 1<n. tu . a I tt 16r.19 l (Utf M l lu.HI 6 nt.M I int.n
- 1. 1.3t.J Uj2t[190 1M tialtt**
- 9. lettive teleenes
- 1. f atal talggna ar ti.it s t ri 3 % 40( .? 3 3 g }( .p g 3 pag.pl I lit l l 4 10(.? t e all.) g g es( . ; g g go( . i
- 2. 1.gl )$Ulli/IKIRM t taiit**
I. 5.m of ledise, particolate O 8 det helf. life), a4 lrttle teleases
- 1. f atal Artggt te t rg ig gc(.? l 3 $9(*ll 3 ICE *ll 1 26t 1 1 % 10( ? I e 8112 i s ogg.; i i gog.:
- 2. 1 g W {li tient a- 14. grum iMai aram/_naAtt i 1 10.0LM.00 1 0.00 1 0 00 1 0 00 t 0.00 1000 1 0 (c
- 1. 1 af IEf bo Limit
- 2. cua r t a r l e aa. Gr um 17.1 ar ea t
~
i 1 10 00 1 0.00 1 0.00 1 0 00 1 0 00 1 0 QQ t0M 1 0 00
- m. aanmat Am. 8rna tii.e ar eal % I 1 I 0 00 l 0.00 1 0.00 l 0.00 l 0 00 l 0.00 I O On I O 00
" lediu particeiete. as trini. i.. i e,e e.,,e..ee e. e isiei ii.,i, g,, gg,, g ,
16
a 1
1 I
1 1
1 i
1 TABLE 1.1-1 (continued) l see sioe.tf U 2 DOCKET NUH8tt $TNa$0 4)$ 'e'it'*a 0 gveces auttt64 pow (g $ tai 30m (if tuluf A40 ut$ft DtlPOSAL $(MiassaaAL stP048 f 0s JULY DEC 1990 J a
Cs lt0I/1 tiflututt
- Sumallem Of ALL e(L(AMS l
8 tatti i JULY l A t'C l $EPT I ) f d ou1A f f a l i NOV net t DEC 34h qgg A.., fittlee sad Activelloa Get telestes ~
- l. f atal$gigata Activits i ft i 1 tate] l 4.ggtet l} t)(et i
- 1. 1. ?!( *i 1 0.00( *0 t 1 44(.7 1 7 N( *C 1 l A4L *C Ita*1amaltlaut_ Rata
..J. 1.af Ietf Ele .Malin' I di/ ar A I 2 Iff *3 I 9 71t e2 Il ellel I 7.17( * ) 1-0 00(*0 l 1.16tal I 4.7M el P.7M
- 6 a.
whaldegdggpam/s earl . I 1 1 a.M 1 0.01 1 0.61 1 0 of f 9 00 1_. 0 00 . tag 1 0.00 p' bdkla fl060 MatlJeati I 1 IoM I n of I o of I oM I D en I - 0.00
- 4. 1 af taf f A%Qg{tt l 0 00 : IMO ,
a: 'Nbettarla f1 aragt i nm n at nM n ni em . Q.co y_ g,go h __ Rata hartarle f 18 ar ad t i a at a ni nM AM nM o on 0.00 0.00
-r.
r -- a -- -1 f tam an 1' nm nm -oe am s r!o 0.00 0.00 0,00
- d. . Agta Aaaal f 74 gad t 1- a ni nM nM SM
. e at JS _ 3 09 0 00
- 8.
ledL44 teleanet i
' 11 fgtal 1,111 and 1-111 Artigtg i fl- 1 A.tAF .4 1 7.7&f.4 1 %.0 f f .e i 1 CM.1 1 0.Mt +0
- f. I af taf fjlgf,jggg}8 timit t** 1 0 00t*0 1 0.00(*0 1 0 00( *0 I el 10(f B76 lleilt il 44144 'sa the see6ew release rate fee the perled goatidored.
ledtae, p4F%itt l ete, and (Fillge Iloill art Geffelled 49 4 Letal llett. 149 $40$ (*
i <
l.~'
f
- 1. .t 4
l 17
, . .. . ... ~ . . - - . - . . - . . . - . .-.- .-.- ~ . . - - . . .
r1
-TABLE 1.1-1(continued)
De* I ttg.f s W.7 DiXtti sitesett $14 M.tsg evtosi mWttae 90wt4 Stallosi -
if flut4f Aae lealt! Oll*0%At linlaassuat 4(poet ice EAf Ott 1990 ,
GAlttut fif tutull * $Ur** tion Di att ettf A)(1 -
)
- i.
f t.as t fi I JtA I I- AUG l_. 5( P t t 174 QuaJltt! Of f 1 ROV l Bf f 14 tit Guaa lit
' C.' Partitglets (p $ esp bellellfel ideleetet -
- _ L fornst Ar t ivile i ft
__ g _ farata Alaka At tleite i 1.101 5 t,gggM[Q l 1.10f.i i B Yt eo I a.Dof eo .. I a.mf eo I AgL '
I ft h 6J[dt h 6.16f.191<t 16f 19 l <t. lif.19 l '4.1&f.19 I v_ & _ l&f .14
't - ' t at 1erfila>1strasa timittu l $ 1kl.19 51 1hf.19 ,
, 0,' fritive teleetes *
- 1. - f atal telsace Ar t teils i
- 2. fl - 1 4.70f.2 l }. tit.? I 4.Mt.) I l _31t .1 l 4.6?f.2 1 7.141 2 i l _ {Q.1 1 2 4t[,1 [
~
1 af iagunnaggsg.uniti"
- 4. 52 .ej i e.,o .i.i. i. . .., n.u.io.3, . i,io . .i..... 1
- 1. IgtAI Arttwits l 2.
fl_ I4 Ill*2 1 } . 90f 2 l ' 4_ I}f *2 ] ' 1. 3(f ,1 - I a _ h7f.2 - l 7.341 2 1 1. e ti .1 - 1 2_ggf.1 7 1 C SCfile 11att
- m. Aa. Grama i1%Qg ggeljaar t i t IoM i aM i ft m i'nm t am -- 1 nm
- 1. t af tetta's t halt Inm inm
- a. euagiarli Aa. orea.s (f tmeal i 1 10.0% 1 0.01 I 0 06 I 0.li I O 00 1 0 00 t 0.00 1 0.00 l
'h. Anel Aan Grama I M e mig % I 1 l 032 I Ole l OM) I B $4 IeM I O _M IoM l9M r t
l64484,' portI(vlete. Sad (fillve I4*Ill 6tg taptegned at 4 total lleil. ' lef Step t.
e 4
M 4
s
-l
~l 1
l 18 l
5 TABLE 1.2-1 689 1164 8i ti l Omnet ownber 514 %0 4%4 '"'"'"'
eveoss taJf t(as pous a llallesi (88ttAet se malli etWOSAL %dalassamt atP9el #0a das * .Lae 1990 i tiQult (f f tututt . Summf 40ss of Att attlatti $
t taltt t Jaa i fe6 i ma r i gt Apsli i . Re y June
) g g gg
- 1. fission end 44tivettee Prod 4ts
- 1. IgLal Artigits talaa taa f ft 11 74(*l i ) 6ll*d 14 84(*) i 2 II('I t J 6Ile)
- 2. Aggragg fant aat ratina Aa1.ima t yg.g _ _ p , g yg ,p g p q.p I gal I201f.1 I438(6I964f.9l 9Ill.4 l 4 37(.9 I 4 ?st( .4
. . . . 1. 1.gLIKf1M i tan ti f I 0$(.8 ~ I ? . 441 8
'a.
(Lantme h mm1* maa fi t arani 1 0.0% 0 08 0.02 0.1% 0 02 0 02 0.0 L - 0 05
- a. f.,ggta r t s Aan Grama #1 a.armal 1 d_10 0.05 0 01 . 0.26
- c. **- .l g la 1.4. f1 e arant ___1 01 0.14 0 06 0.7) 1 0 01 0.04 0.01 0.08 0.01 Ojl Oji 00)
- d. in a l Aa e Graas ilA_t aran) 1 0 10 0 D1 0.00 0.11 0.00 0.07 0.04 0.11 J. f e s t itan -
f.
fatal Acttulla ta l a a t a a fi ; 3_ taf el 1 Mfol. 2 Alf*1
- 1. Ama taae furs aggggjaa Ralgggaa ll/m1 4.30( 1
- 9. tof el_J M et 4.0 4t s t ._$ 08161 1.31fe2 4.0ff.i 4.16(.S 4.lgt.$ 4,86( % _
i_ 1 af t sat t sla.1 J umin 1 ) . 4t( . %~ 4 5C( .$ 4 )l( %
4 . 34 i el 1. J9 1, J9 l.62 1,16 0.80 1.6i
- 5. Dettel e4 tesel, &assee L 1gtal Artigit s tal a taa et i 1. 7W. I 3.?9(.I 1.49(.1 6 64(.I
- 1. Anggagg raarmat rAtlaa talamina 4,18(.I 1. 4 %( . I 1 80( t LO3(
- L -
li/mi 1_9s t .) 199f . 7 1
1 af Lia!@d af t/ alt MQ 1 Alf.7 2 21(.f yg_. f _ _ l.10(.i 1.64(.7 1 O_!S 0 20 0.06 0.14 0.11 $ 06 0 08 f.44
- 4. 6 tent Alp 64 1- f at4Wgin t t e talia taa f ta 6 4 91( 14 F 4 19( 14 H4,19(.141 d e 19(.14 f (4 19( 14 i
- 2. Angrage f antaattatlan Aalg4&gg '4 14( . t 4 t
- 4 y{ Q4jdp(.14 I di/a) l 0 00(*0 10 00(*0 l 0 DQt*01 0.00(*0 1 0 00( *0 1 - 0 00(*0 1 0.00(+0 1 0 00(*4 ll.,,,.yalm a f t lktA Matt
- 18 .h t ' =*
I litata- . i e 49(*6 I ).8P(*4 t t . lit et t t ts(W 4 . tg(
- 6 t 1, f gt .6 t 5 16( *6 1 1 )?(*7
- E J41= $8.Atlattaa.li41** f 111agA f 8 60(*G i 82(1(16 tit *a i 2. 36(,9 i 8 iCt ed f 1.16t*9 f _ .1,M(*9 1 1.01(*9 1
19 i
l l
I
d
-i r
' TABLE 1+2-1 (continued) ,
C est ineg.tr W. t 00(tf f stpe(t ilt 50 454 GTt0N NU(t(at POW (6 $1all0m tritugal amo magtt ef tpotat Sensawn e(poet fee Jul *0ec F 1990 (19Ul0 (f f tutell a $tsessflou Of att ett(Alt $ ,
I tafft i JUL i auG I MPI i )*4 cuaaltal 0(1 I =0V 1 0(C Pth Guasd I. flatlea and activellee Prodects
- 1. Igu W 111 W egud I 1 l 06(al I 6.3/t.) t 1.11t *)
- 2. taggggg f aar amtrattaa talained fl [ 7.?tt.1 1 1.10(*? t 7. lit.2 t % . 74(. ) g 4 04(.1 1- 1 a Q gQ t1 W alla I dt/mi ) 9 64(.9 } 7 4B(.9 I i 60(.7 I 4 60t 0 I e 49( 4 l t 44(.4 l % 41(.9 l ? 4 H.4 ~
- a. fL.artarie mals_, jade f 1 1 me nat 1 0 79 - 0 11 0 07 0.47 0 04 0.04- 0 01 0 09
- h. Quietarl e am. Ornaa f t e araan 1 0 11
- e. *--
0.0% 00) Og 0.04 0.0% 0.0l' O.it
-1 mals _tede ti.e areal 1
__0 it 0.04 0.01 0.24 0 02 0.02
- d. *--
-1 Am. Graan f18.0 misal 0 01 e os 1 0.04 0 02 0.07 0.1% 0 04 0 02 0.01 - 0.01 J. tr\tte t.
fatal Arttelte f alsmd fl S 76(*1 2.61tel S.Mf el 1 19tet ] 74(*) S.tstet
- 2. .Avaraan raar. erattaajg}.asas 4 11(
- t - t,tg(et de/a) 5.241.s_. 1_04Eg e,00t.1
-t s.ftf.S 4.51t.1 S .gj[.Lyq[.3 . J,14[.1.;
1 at ttatt f L 1 utt/att 1. 1.7%
J.6?
l.02 i 44 1.52 f.96 .1 60 % 04 Re' etsseleed sette Gasses
,.; t. f atal AztivitnJg1ggggd fl- 2.i&f I ,J.,jj[:1
~
0 Mf.2_. 1. A l t .1 _ 9 ?it.( 1. Mt .1 1 11L jjlt .2 d a ArttAtt.ite&1ALIll14LItit&Ald MC14If*I I I9d Id1E * ? 1.16[.7 l _3 ? [ ._9 _. - 3 Of.9 I 97[.4
't. 1 af t imi t f 2f.4 af t /a11 e . 4 7t.9 1' O.12 0 01 0.06 0.j 7 0 00 0 00 0.01 0.01
- t. Getts AI P44 -
t
- 1. Igul Arttelte ggigaggd f ft 1 <4 91f.14f r 4.91[.14 (4.9)t.1 <
}{.14 t <g 9t[.14 ggj(( gg g eq 9tt,gg g ,4 ggg,gg
_ 2. . A*1 rams f ancangratlan telAAlta 'I dt/mi 10.00f *C I 0.00f ed I 0 Qgf *o I 0.00f=0 l e Mf ed - h 00t oo I 0.001 0 I O oct *0 _ _
- m. wel.ma ,g[,11ggitggsta Lg.J11thafst ! ' I t t *g1_ _ t l ' 9 7t *6 1 I . 54 t *6 f 1. 6 7[*6 1 $. 70f *6 . I 9 43f *S i 1. 38t *4 1 - 1:17(*6 I 3 44(*+
. L X41me af Bilatiaa.Matar i Itagt I l.19f *9 I 9.5?f *916 94t*8 1 2 65fet 1 7.l?[*8 I 8 80(*9 1 9 02t*4 t 2_49tet 1
j i ' .1 l-x 1
.k l;
20
i
,I J.
q i
-i 4
TABLE 1*2-1 (continued) tot 1sH.fi f
v.: ouiei ,m $,= so.m '"'"
Sve0m saJCttaa pow (4 5fallos '
(f f tut et Amo unit ( 9t%89Mt $1mlaastant st reet f 0s Jea + Jva e 1990 t t0 ult (ff tutult . $weintion of ait 8(t(A1(1 i taaf f t i Jea 1 8et t "de t gg Aartl Map 1
l Jeae
- 1. f attisa sad 4stivstlea Prodv4tt 1
i gg )
- 1. aul Art tutta Aalmataa 1 ft i l 74(=l 1 ) 6l(.? 16 841 3 i ?. lit 1 t 3 67(*) 1 4 96(.i
- 2. _ A yggt f u n mat eat t u Rajaaaaa l JUel l I Ol(*i I i 19( 4 I 4 9?t *9 I 4 %(-4 l 7 87(./ l 7 w('.7 L LaL1El&M_Llalta I i l6t+9 ~I i IS( 4 I i 0?f 4 ) I //t 4 a
fLar t a r t . mala and e f l _ t armal 1 0 0*> 0 04 0 02
- n. ~ tLa tar i n Aan Braam M e areal 1 0.1% 00? L 07 0 Ot 0 0%
- 0. ?O 0.0% 0.01 0.7% 0.01 0.14 r.
d.
a-a==-
a mais haddle armal d ?a s ornaa (10.9 aram) 1_ 0.02 0.04 Q _02 0.ua 6.01 _0.01 0 011 O_01 0
0 01 IC 1 0 10 00} 0.00 0.11 D_00 0.07 0.04 0.11 J. let t e.m -
- 1. latal Ar t isit s Ralm aiad 2_ A. ,ama f uimat eat ig,ggla mina ft 11/mi 3 41161 L Ml
- 1 MR ,J.9Cf *l 4 ilf el 4.04fel 5 Qg[*1 1 ]M *? _
f Sif i 2.14F . $ ) t_Af d j _SRf 5 }. 4 }f .i _ l,pf .3 1_
1 af tin 6L f if .1 J i /gt 1 0 AF e 77 e at 2.43f.i
__ gQQ o at 8 Al 0,ag a go f) 8, 96stelved me61e Gets:t l_ f aul Artiette talmaima _ ti i1 int.1 3. ?M . i 1 49(+1 6 64(.1 1.79(.1 L A erag (macantrat.lagf alsata, 1.4tt.l 4.G4(.! 4.0H.6 ll/al ! 9 88f 9 I 99f*! l 72I'I l 40l'i i Cif.i 6 ?R( 4 8 49t 4 L 1 at timit f 2f.4 d t /m{t , 1 Q.0% 0.10 0.07 J /ll 4
.._ . 0. 06 0 0', 0 01 0 04 0 v4
- t. Iwesi aien4 .
- 1. fanat Artigte Aalmatad I ft 2_
Awa rama_ f aat mat rat t aa tala mina kt 91f 141ce 19f 141191f.141 (4 91f 14,'g111 14 1 v 4 ti f .14 1 < 4 91( 14 i i 4 9lt 14 l Ji/al l 0 Mf *O l 0 OCI*0I & Sciso l 02[f ( 0 00t*0 I 0.00 Leg I O 00t *0 1 0 DCt *0
- ' RJabses af Lia-'LMe&lL,LLRAALAAL9t.
MittA - l 1 1We6 i .1 Ailes i F fj[gghtf]f ee i 2_ Hf eb 1 ? tit el 1 ] . 31t +6 1 91$f *4 m_
valm a f at].al.lat.XA' ** I liitti 1 I F2I *9 I I 44I i I NI t 4 #4I'9 1 3 #0E '9 f i III*I I ~ i l*'I ]
- I N
21 t
t.'-
TABLE 1*2-1(continued)
... n 00.o v a 00at .u . u. so.m . .. i u .a . .
titos %Cttaa rout a list (On (if tUtaf 140 WASIt Bil*0W italawuat etal 10e Julr+0*c.1990 tt0Ut3 (f f tututt . Syretation Of att att(astg i taal f t i M l A UG 3 st H ! )<e amenal O l
- E
- I, f lg s lea sag ag g 6 et t en Fredet t s -
8 I M MM -
- 1. fggAl Artig1Mlggasd 1 _ L1 Il fM F } l [,.,,( l y *
- 2. . Au11Aetlaguattat taa talgatad ,, {e {Mlh h]4M_ 4 l mtt/a1 b 64t+4 l1.4 t+9 3 . #s t1 8.64t- .= (*. g1,64t*M l5.811 9 gl.4}t+6 L 1 af tgG1$4Watta
- a. Quagtert e taale egde f1 3 areal 1 0.29 0.41 0.07 0.47 0.04 0.04 0,01
- b. 0.05 n,p9
~
Guarterle Ane Grama (Lhant 1 0. l_t 0.15 0.31 o.06 D5 0,01 o,te
- f. Annua! OaIn Sadt fl0 htaan 1 0.*5 0 06 00) 0--24 0.07 0,02 -_ _ _ _ _ 0 01 tot -
' d. Annual Aan Graan f lR.9 areal 1 0.06 0.02 0.07 0.15 0 04 0 0? O 01 0.0; T J. fritie 1.
f atal Activilt.111Hud ft 5.76tti 2.61t+1 5.55t+1 1.19t*2 1.14E+1 S.48t+1 4,3)(+l L,28t*2 1_ A..,2.n r am, ..t rai t am s. lanae ottimi 5.24t 5 1 061 5 ggd 5,25t $ S.89t 5 4.801 5 t_ t af ttatt # 1r .1 a t /an 1 f.7% 1.02 4.55t 5 1.lat*5
[+
2.67 5.44 1.52 1.96 - 1.60 5.08 K. 04stelved metle Gasses l- t. tag 4Wivit* Aslaatad - ti _ 2.66tal 1.49t-2 6.002 2 3,61t-1 9,75t 4 1.25t*)
l1 2. AnstattlaattairALitLitlAAtti _L . 69 t 2 -- 2.tlE*J
.u(.Unl 1.ilE2.L,l*Ulf_51.M.1;L,1.)6E-7 I.)7I 9 3.69E 9 I.87E a 1 ' t af timit r >f.d oc uan 1 0.12 0.01 0 06 a_.4IE 9 O_07 0 00 0.00 0.01 0.01 L. 6tets AI Ph4 -
l-
- 1. f atal Arti?lia.laltalad I fl I 4Mif fil111 - (4 911 141<4 91t 14 l< 4 91t 14 t re 911-14 $4 tit.no ite.9tt.se
..2. AvatAna f aar aattavian t'lAAud Iutt/mi b 00f *0 h 00[60 0.00t*0 lo 00(*0 10.00t *0 l0 00(*0 10500(*0 l 0.00( *C
- W&j;an, af Liguld Watta la 111ggggan i litect il 4?[*4 ff MM e6 ll &?fol ISEf *6 19 4t( * $ t l . Mte6 - tt,(2(e( ] L44(e4 M. Va l ues mLolluttaan' alt! I liiggt f1 10f et M $2f et 14 94[*e If.Hf ei 17.12(*9 16.80(*8 19 07t*4 1
- 12. 4M *9 i l: I l' I r- -1 I
l' l1 l
1 1
.- 1 I
l l
22 i
I 1
i b
I k
a TABLE 2.0-1
.e i i . . .
U+1 4 U-r Cet te t 44175 5ts 50 444 4 5ts so.4% '"""0 0flom ett(A4 W G $14 TION tIf LIAet a#c isantt ellM$At StalAmeAt etegel SOL 1014eltb4(ifvf inalti sonin je Ytaa h osip.sitt .# natertoi Mf ( Be it r ia l l aA _ flALL I n ad lahgdg g g at pk(g,,,3 Q ggggg Q,M[ { Aa g ina .J d C ar Shi m C 1 b _.hadatal amma at.
15 filter. Class A, nic tu, see teciesi.e ou se r.n l i ,5( 13.4 $ 57
!*ll Dewa tered teila, Clell A, Cast Lu, tone (stivitee Une 84 ramell, $( 18),2 6,3%
l ts tha r ,- Class a, prestu, we teciosi.e use ge rnw i t ,5C 62: 5 .re MafMtv f0f at$;
3 gig,g gg y
- Volwne seat te ve*44r. felt 11 not final bortal sol ne.
23 i
)
TABLE 2.0-1 (continued) i
.e , i i . . ,
N " ** 0 U l & U-2 bxtet 4mert $14 W 4t4 6 % 4% )
avecse antigas pode $latI0s: 1 tirinAuf ase w$tt estposat Stalawat esposs l 10tIO tapt6atttyt w$tt j 1
ein 116 vtas ,,127 9
etapeittlea of metectal BAtf f 6e s t r13(t aa _ f l a t t I nad hi gj((Jigg,.AgggLAO[,,,1g Agiggg,,,,, Agil AJil aa _gg d fg d igggg(((( g, g gjggjgg igg,,gggg 21 De=atered testa. Clain A. Cast LM. Soae (*(last.e use Barnwit. M 143.2 3n
{
7 16 Da m. (14tt A. Dres tM. Roa* E stivove Use lawll. M )$2.5 2.JI 7 il Filters. Class A. Radlet (sth lM. hoae [actestve use Sarawil. M 13.4 3 61
'1\
7 il Oe.atered net te. Class A. Cast LM. hoae (scluitve use laramil. M 181.2 1 91 J
1 t
I I
etat? fcf ats; gy_ y a
l g,3 l
t 24
i 4 5 TABLE 2.0-1(continued)
' ee, ....
vi i v.: o.ciet ... see w ase i w an se... .
.. w an =iesius. .
s (f#tutet ase witt 616899L Listassunt eteget -
10Ll4 SelentflW( tsall(
seule __she' vtaa _. lHO Stepositten of noteenet ..
ha ft bildi f n W M., hada af f f A&ataf L tranu# tauma f1Ain f ema hQAg.J&laggjaf ikimanal f f(3LM &g.jg d h g(
)6 De.eteres netta. (tens A. (e st.L M. Sene - teclettie Use Seramell. $( 11) 6 0.l6' A- 3 ft env. (Ins a, Dres tu, none factestee vie 6ernwit. SC tit 6 1.26
- 32) De. ieces aesia. Clett A. Ce nt *L $A . eene (aclettre vie 4ernmell. SC tt).i 0.8%
i P
l I
l - Ofsett f0f 4Lt!' ) 64 U l w i
l--
l' P
i
~]
i 4
5
-25
=%,-. , - . - , _ , , , , , , ,. , ,,.--.r.i..com...e,.mm--, .,.,,...,..,.-,.,,,,,....e , ,y, ., .., .- . , .<m,w,m,. .r,- m,
TABLE 2.0-1 (continued)
.., t. ...
U l 4 U i Dix t e t sete ct $14 %0 4%4 4 W- 4%%
N" '
Svtom stKital POWit Stolt0N littWLet asO us%f t Sl%#0Mt $satwt etpost
%0410 ta010a(flyt inanti suuta _Ag41., vtas ,_11gL 66 posittee of metecten klL,.tDautta t t aa - f1*** l a ma lalAs Lis tas.AataL_._fmaa afJiaatsatL._Da&Llaauta..161asuttst.AiastaLilb_..lat191.fst 1lklamaaL
. . i, .. (i.... .. .. . t u . .. s ui..... ... ... n $( io.o in 0
- ll Dree tt'f 4 Of t r#, (141% Ae C elt al %A . 40#f I8tIsll'8 Ulf $4Pavell . $( 19 ) t 0.9) 4 I) Doeti$'96 Itlle. (14%l 4, (4 t h
- L 54, 40nt ( .t IW1999 Vit $4t#e9II, $( LII.) 0.l$
4 1
k saminte totatt: ) 2.26 1400.6 l
. .., - ... t. ....... ,,,, ,, t .. 4, ... ., .., .
26
TABl.E 2.0-1 (continued) v.i i v. w<i i 6 - .. u. w..s w..ss ...... .
. uu. wesi.,,
lif tut h' he u.it t Dt %80'.At St at u. cat et pge t l MLIS t@l64(livt vatt(
0.ilm R.F ytas j990 l
... ..ii .e =i.,i.i '
MIf .lbtA&ll8LI C (likk IN - hll11[A184 A4pt& L.fheds.&l.l!#418tlL. .It & Ll&&LI A&,,JtImt.fadlAtt&iM L.1(lg&_ftf M[m&L
- s. i. we.......... ci.. c . c....i sa , t i.<i.. .. ... .. ..e. o . u ni 4 3,,.. 1
%. E b esiered ettes, (legt A. (e gl 4 %A , tong (s<lyllet Utt la awell, M ljf.4 [j,)
2 3 4_ g 3gg,7 1
l l
f 27
TABLE 2.0-1 (continued)
.e. ii .i e v.i i v.i wi.e . 9,s u w.es. : w.m '*"""'
Ottm Estl&A W 9 Slail0m lif Lutal we ual!( 915PO$at Malasmust Giront wilt 8410a(fivt malft Malm . . 1m staa ath
$ttpetitlM ef anstpfiel
.jlkil_..let&&lAA LAM iln - 11M. hllillaint Ass &L Jbet. tL11&akattL.Ja&Li&allaL..IslantJ4LJkl8 BEAL.llLL..$stl4&_ fat 314at&L 6 1% Drestettd Delta. (tell A. (e gt .t M , home [stlagtve y)$ RIghland, W l%9 4 f,g; I
M' h , f,hf l
28
TABLE 2.0-1 (continued)
..e ii... ,
v.i a u.i wiii .aies si. 50.m a sr. w.m ...... .
6f tCm eas(Llat POWt t Stall 0m (rflutet ase testit DitP0tal tininoajat etP0ef 10 LID ta016atilvt malit e ta JUL v ggae . Im Ottpelltl44 ef Ntettet haft JatAulaundinn f ase 9 iall411sikalsetL A46 al.114alestL Dantlaall4&_Jalma f111hisacaLL(LL..Lat.la1Jat.lblJetAL 7? Deestered testa. Clost A. Cast . L M . toae (sclellte Use althisat W 199 4 i 4) 1 12 DA v. Clatt A. Deves . (SA. tone tettelive use Barnwit SC 747 4.44 F.26 De.ateret Retin. Clast A. Cast . LM. tee Est tutt've Use Althtend. W 199 4 .19 l
l OTHtt totall' 3 641 4 43 1
29
I k
TABLE 2.0-1 (continued)
.., ii.....
p.18 U 7 00(t!I 9W(R) St4 50-8%e 4 %0 4%% "
Ottom auttles eWtt Statten fif tWitt De balt( Dl%80%at flotatedust tieget mit taDtea(ttvt inalt(
stmin ,$G ttat 1990 eis,eiste ee %ieciei
.AAIL..lattuisLlea 11ain hat klia11 stas AstaL._rinst_aLhaatsetL .taattaattet. JalumaJar_1hiamaaL11L,L ..Lutlat f ar SMament 8 16 k ettees sesia, (tesi A tait - Lu. naae (seleibe vie sichtaae, v 199 4 s 67 e 31 W.eteres seien, clasi s tain . tu, noe, t rivinetne stoi ne, v itt 4 t 44 Matmv fetatg; ; ),, y gg l
l 30
1 1
1 TABLE 2.0-1 (continued)
.e e .it v-i a v. nit t =m es v. w.c. w.m ee.'oea e l'60N MLlat etMt Stations Ef f twat a80 utlti St%P0ut Slatameauet stroet 10ttD taaleattivt walf t geen .MPt etas Mic esseesttlea of Niettet y
hit J9aattisusa.f tau time hudiistas. '= =t hea 4LitaatsuL .htausauna JalimmaJarlimosaL11L1_ .Latla&Jat 1hiamaat.
94 Fr. Class a. Dewns - ( SA , none (sitee , use te r w i t , y .;6 ) . t P . cit . 4 9 14 De.ettees tetia, tiesi a, (est . (ta, none teclep,e gge tipleng, y 399.4 p,p 2,70 othfMtv 10 tat 1' i 963 l
' Veliane test to ,enoor. inig is act f ene t g,riet vols.,,
31
TABLE 2.0-1 (continued)
.ee . .....
U l 4 U i (VXfll 4 Pt(95 514 W 444 4 %0 8%
tet:m attial PNs Italtta (f f tutet a@ welf t Dl%P0ial %f attesaual 6teget 10(19 Set 0Attivt uallt 8tmin ut vt at part . .. . .
$1tpetitita el Insterl4%
AIL .ibaattittlea Llau ..Jssa - MidilataaAse6L_ AstaLt:Atuer L .6stLinattaa. .tahme Jat. Ahlsem aLilb_ istaatJatalearnt 10 4 0 .ete,ve netin, tiest a, (ess . tsa, newe tet tvitet use Wit hiend, e att 4 F 67 10 4 Da g . Clett a. D'en 154, hoao lettettet Use le * *w i l , %( 3% = f 6 67 10 10 Dreatered besta. (18518. telt 19. hone let t vgle, gie serewil, %( lit 4 JO %
sone'MT 101sti: 3 "8 ~
- 4 69
=
1 32
TABLE 2.0 1 (continued)
... ii...t.
U 4 4 W l W 4(? #Mtti V4 50-8%4 4 so.6%
t?#Ce tuttf at SMS leatitus (tituint se waltt signeut gtnianuat tippet 40416 64Dl6&(lift shallt stelu.#M stan IN ,,,,
M/ -
hhhh $ h hk J! AIL JbantlettaA_ Lim.. ,Jun istidl(alas AsanL_,Ada.6Lisautett Jestination Jalune.f at.AhtmaL11b_ les '- - .
41 1 tiesetekee ses:n, pegs a, (ess tu, non, g n i,si,, Wie e,inid ae, e in a p4 ll*$ 049 (1849 0, D'upt a lu e hohe latletlet Une le'a me ll, $( ' BOO .
Il+II Ofoote?t$ hella, (l.nl te (e44 = ($8, 49ht (stivtlet Uge $ tt hleh(, t 49% 4 ) 70 stafHit f0tatl
- 3 M8 8 12 55 6 telwa w tent to vendor, thin is not finel burie l volume 33
TABLE 2,0-1 (continued)
...ii...
U l 4 U f tkX tti 6;s$(t) a W.a%. 4 bO 4tt 8"' O *" I 9,90ss ILE6f 60 #0 Wit tilfl6d (f ttuttf Aapp tuttg $ttpetAt 1(st(%gg p(ppst WL l0 tabl6A(f f tt sett,'
stimin 8(c vist 14e ei. ..iu.. .e a.ieriei
.AAllJDtnLilalt h.D.&it --- 8848 I Alifilal&$ lJe&L...A48 41.lf 4 Alp 6CL.,It&Llh&L134 ,J81asetJaf lklSeeklJjl. L, .lat latJEMisetAL, i,., .. i . . .. ., u . , c , . . , , c , . . t u , ... <, i.,i., o,, .......,,, ,,, , , 3, 17 17 dab. Clain A, D,ual . Lia , none f eilense use gerawil, st f 37.6 41 ti.o o...t....... ci. 4,c.ii.tu , nr. i.,i.o/,u,, ....i...,. i,, . i ,,
l
=me isiaa: im.
3 l 1,..
M i
t
. ._.. . . - . . . . _ - . . . - - _ . - . . . . _ _ - . - - - - - - - _ - . - _ ~ ..
FIGURE 3.1-1 Estimated Cumulative Gamma Dose (in mrom) from the Byron Station for the period January-December 1990
[f' "
mg \'lk
>150 ....' 50 lienleth tabels 25 ,!* 1 h Small figure - multiply by 10 s j l Latge figure - multiply by 10 8 4sy' M T 5 l
..._J' Y j/
50 -.
-. l w N m ' "'
/ ,_ f'
_00 50 *
+
f :-<
i i 250
- ,e /
10
) .,...... e,, I q v- ,- 6 N
E .
vi. .ees.
"" l 10 0 si or e.. l 7
) s+
r.i.
- f b* '
~ ....,,.
Dinon
,,/ /
xx \
/
35 0 $ 10 16 20 mi
% *~ w W-.. ..,. - ' 1
FIGUE 3.1-2 -
Estimated Total Concentrations (in p01/m3) 4 33 cf Noble Cases from the Byron Station -
~~
for the period January-Docember 1990 I JE pleth Lebeh ['? I Sr,4811 figure - multiply by 10*0 Lares figure - multiply by 10*' L
[ l 1
') k*
s I
% ,. , 10 0 9'
. a
/
\\ 25 t ! -
i f,.
N o m__ _
7 ,..
. ., . . . . . . . o,,,,a, 7_ ,,
t
/ 10 0 < t_ "
l1 \ \ e
)d '
1 s0 ,.
i 1
,, ...... W-, 25
\
-" \
.c
.. , . t ...
rs. e t ,,,
s s 3 s
u ( ....
. =-
)J "
A .. . '
,n, ..n.
^
.l0 1 7 Dino,n Ashi+* '3 x
36 is rp nii ww . 5 O
ip i
FIGURE 3.1-3 Estimated Total Concentrations (in pC1/m3) of lodine from the Byron Station for m N r l_ %
the period January-December 1990 _ _,
llooleth Lapolg 50 l' Small figure - multiply by 10 s ;
f
(
[
Large figure - multiply by 10 e ~, ,
N '
- h 100 /
p
- 7 7
%U t' L-.4__
' Pecotonice gneggng,
/ 0
~ to -
25
- o-
\ ..... ,
1,r sn.e n , ,,,,
~
re ~
10 0 I k ,,
,e ci .
\,
I I I
,..... gw -
=
j ,...
J .n.
oison 37
FIGURE 3,1-4 Estimated Total Concentrations (in pC1/m8) of /
100 w 300 Particulate Matter from the Byron Station for the period January-Decemter 1990 -
~,,
IsoDieth LAk311 [ 400; Small figure - multiply by 10-s 25 Large figure - multiply by 10-8 22 x 1
- j t '-
ROCkf0RD so- -
__ a a-25
/
e.....i.. e ,. .
J lv rs '
' N p q
- e =
tsYRN
' l s 4 --- "'," 1 50 N~ m
,q ..
2,5 10 - s j ,,,,n, 3
Dion Ai nj.*
38 0 5 to 16 to eni w=w=6 a >
1
TABLE 3.1 1
$YPON UN!T ONE 1990 ANNUAL REPORT MARIMUM D08t8 RESULTING FROM AIRDORNE RELEAtt8 PERIOD OF RtLEASE . 01/01/90 TO 12/11/90 CALCULAftD 01/16/91 INFANT RfCtPTOR 187 2ND 3RD 4TN TYPE QUARTtR QUARTER QUARTER QUARTER ANNUAL JAN. MAR APR.JUN JUL.8tP OCT.DEC CAMMA AIR 1.25t.03 2.08t.04 9.35t.06 6.195 06 1.56t.03 IMkAD)- (St ) (St ) (88 ) (88 -l ist )
SETA AIR 4.118 03 8.64t.04 3.135 04 1.238 05 6.96t 03
- ( M RAD) -(8t ) (8t I (82 )
707. B001 (82 ) (St )
3.41t.04 $.318 05 2.542 05 2.618 06 4.28t.04
- (MREMI (8t ($t )
't Ist I (88 ) (St- )
-$RIN .. 2.62t=03 4.392 04 1.945 04 1.018-06 3.26t.03 (MREM)' -(St ) ( 8 5 -- ) 18t ) (82 ) (8t I QRCAN 1.86t 04 6.34t.06 4.19t.03 3.10t.ol 4.ttt.03 (MREM) (8E ) (Nt ) (NC ) (NR ) (Nt )
THYRCID LIVER THYROID LIVtB THYR 0!D THYROID klDNEY LUNQ Gl.LLI THIS IS A REPORT POR THE CALENDAR YEAR 1990 COMPLIANCE STATUS . 10 CFR 60' APP. I INFANT RECEPTOR.
.............. g-Or AFP I, ............ --
QTRLY 187 QTR - 2ND QTR 3RD-QTR -4TH QTR YRLY % or OBJ JANaMAR APR JUN 'JUL*SEP OCT.NOV OBJ APP.!
G AM MA ' AI R ( M RAD ) 5.0 0.02 0.00 0.00 0.00 10.0 0.02 htTA. AIR ( M RAD ) = 10.0 0.05 0.01 0.00 0.00 20.0 0.03 TOT.-BODY (MREM) 2.5 0.01 0.00 0.00 0.00 S.0 0.01
-SRIN (MREMI T.S 0.03 0.01 0.00 0.00 15.0' O.02 ORCAN--(MREM) 7.5- 0.00 0.00 0.06 0.00 15.0 0 .03 THYR 01D LIVER THYR 0!D LIVER THYROID' THYROID ElDNEY LUNG GI.LLI +
i RESULTS BA$tD UPON l ODCM ANNEX REV!$10N 0.9 AUGUST 1990 I
39
_ _ . . . . . . . . . . . . . . . ~ . . . . _ _ _ . . . . . .
TABLE 3.1 1 (continued)
$YRON UNIT ONE 1990 ANNUAL REPopf MAtlMUM Dost8 atSULT!NG PROM AIP90RNE ptLtAst$
PERIOD OF RELEAst . 01/01/90 70 12/31/90 CALCULAttD 01/16/91 ADULT RECEPTOR IST 2ND 3RD (TH TYtt CUARTER QUARTta QUARTth QUARTtR ANNukL JAN.NAR APR.JUN JUL 8tP OCT.DtC CAMRA AIR 1.2$t.03 2.002 04 9.llt.05 $.79t 06 1.568 03 (MKADI {$t ) {$t ) ($t )
$tTA AIR (82 ) (8C 1 4.712 0) 6.58t.04 ).7)t+04 1.238 0$- 6.962 0)
(MRAD) (8t 1 (88 I !
707. 60DY (St ) (88 ) -(St )
3.47t.04 6.31t 05 2.64t.05 2.67t.06 4.28t 04 ;
(MRtM) (88 -) (St ) (82 ) (8t l- (St 1 '
SRIN 2.62t.03 4.392 04 1.94t.04 1.07t 06 3.24t.03 (MREM) (8t ) (St ) (8t I (8E i {$t )
ORGAN 1.47t.04 8.88E.05 2.3lt.03 4.112 05 2.58t.03 (MRtM) (88 ) (Elt ) (t88 ) (t88 ) (t88 )
THYROID THYR 0!D THYR 0!D L1VER THYROID -
THYR 0!D >
RIDNEY LUNC i GI.LLI l
THIS IS A REPORT POR THE CALENDAR YEAR 1990 !
COMPLIANCE STATUS . 10 CPR 50. APP. I ADULT RECEPT 0R
- . . ... ....... % O F A P P I . ............
QTRLY iST QTR . 2ND QTR 3RD QTR 4TH QTR- YRLY l 0F
.08J_ JAN. MAR APR.JUN JUL.StP. OCT.HOV-'0BJ APP.1-CAMKA AIR (MRAD) 5.0 0.02 0.00 0.00 0.00. '10.0 0.02 atTA AIR (MKAD) 10.0 0.05 0.01 0.00 0.00 0.0) 707. 80DY (MREM)- 2.5 0.01 'O.00 ' 20.0 0.00 0.00 $.0 0.01 SRIN (MREM) 7,5 0.03 0.01- 0.00 0.00 15.0; 0.02-ORGAN (MREM) 7.5- 0.00 -0.00 0.0) 0.00 16.0~ 0.02- .
THYR 0!D THYROID THYkotD LIVER THYPOID THYRotD-K!DNEY LUNQ CI.LLI RESULT 8 BASED UPON-ODCM ANNEX
' REV!810N 0.B.
AUGUST 1990 1
L .
40 ,
i n
~ . . ~ , . - ,---.,__-_...,.,,,_~--,,_.,,,-_m,,,w,_
i TABLE 3.11(continued) .
$YRON UNIT Two 1990 ANNUAL REPORT RAXIMUM DO$t$ RESULTINC FROM AIR $0RNE RtLEA$t$
.Ptl100 0F RtLEA$t . 01/01/90 TO 12/31/90 CALCVLAftp 02/22/91 INFANT RECEPTCR 18T 2ND 3RD 4TH TYPt QUARTER Q J' P.T E R QUARTER QUARTER ANNUAL r JAN MAR AP.,-JUN JUL $EP OCT.DCC gamna AIR 1.20t 03
- l. IMkAD) 8.255 04 5.68t-04 9.935 06 2.60t 03 (St I ($t ) ($t ) ($t )
ttTA AIR 4.02t-03 3.31t-03 2.20t-03 (St i
- (MRAD) (82 )
3.98t-05 1.04t 02 t (St ) (St ) ($t ) ist I '
707. SCDY 3.57t.04 2.112 04 1.45t-04 (MREM) (8t I 2.73t-06 7.15t 04 L (St ) (82 .) (8t ) (St )
' $ R I N - .- 2.60t.03 1.678 03 1.14t-03 2.14t+05 5.52t 03 (MREM)
ORGAN (St ) ($t ) (St 1 -- (St ) ($t )
3.06t-04 4.81t 05 0.115-03 8.445-05 6.41t-03 (MREM) (82 l- (We ) (NE ) (Nt ) (NE )
{
THYROID THYR 0lO THYROID LIVER THYR 0!D -
THYROIO '
RIDNEY LUNO-01-LLI ?
THIS !$ A REPORT POR-THE CALtNDAR YEAR 1990 j' COMPLIANCE STATUS . 10 CPR 50 APP. I r INFANT RECEPTOR '
............ g or APP t. ............
j,
.QTRLY IST QTR- 2ND OTR. 3RD CTR 4TH OTR YLLY % CP-OBJ JAN-RAR -APR-JUN JUL $tP- OCT NOV On J APP.! '-
CAMMA AIR (PRAD) 5.0 -0.03 0.02 0.01' O.00 10.0-
- StTA AIR (MRAD) 10.0 0.05 0.03 0.03 707. 80DY ' I MR EM I 2.5 0.02 0.00 20.0. -0.05 0.01 0.01 0.01 0.00 5.0' -0.01
$RIN (MREM) 7.5 0.04 0.02 0.02 ORGAN (MREM) 7.5' 0.00 15.0 0.04 0.00 0.00 0.11 0.00 15.0 0.06 !
TH'R0!D THYROID THYROID LIVER ~
, -THYR 010 THYROID RIDNEY LUNG 01.LLI
-RESULTS BASED UPON CDCM ANNEX-REVISION 0.8 AUGUST 1990 41
. , ~ - . - . - - . -.- . - . . . . . - - - . - . . - ~ - - . - - - . - - - - _ . - - - - .
TABLE 3.1-1 (continued)
SYRON UNIT TWO 1990 ANNUAL REPORT MAXIMUM DO$t$ RC$VLTING PROM AIRBORNE RELtAst$-
-PERIOD of atttAst . 01/01/90 TO 12/31/90 CALCULAttD 02/22/91 ADULT RECEPT 0R 187 2ND 3RD (TH TYPt QUARTER QUARTER QUARTER QUARTER ANNUAL JAN. MAR APR JUN JUL-SEP OCT.Dtc GAMMA AIR 1.282 0) 8.25t-04 5.68t (MAAD) 9.93t 06 2.68t 0)
(St- ) (St ) - (st 1- t$t )
stTA AIR 4.82t.03 1.31t.03 tst )
2.28t-03
( M AAD )
3.90E-05 1.04E 02 '!
(82 ) (88 1 (8E ) (St ) (8t )
TOT. BODY 3.57t-04 2.11t-04 1.45t-04 (MREP) (St )
2.73t.06 1.1$t-04 ?
ist ) (St ) 188 ) (St )
SRIN ' . 2.64t.03 1.67t-03 1.14t-03 2.14t.05 (MREM) (St -) 5.528 03 ORGAN (St ) ($t ) ist l' (at- 1 2.42t.04 8.76t.0$ ).92t 03 7.522 0$ 4.252 03 (MREMI. (St 1 (Est I (Est ) (NE ) (tSt=}
THYRO 1D THYROID THYR 0fD LIVtR ' THYROID THYROID !
E!DNEY- .
LUNO G1.LLI -
l THIS IS A REPCRT FOR THE CALENDAR YEAR 1990 .)
COMPLIANCE STATUS . 10 CPR 50 APP. I ADULT RECEPT 0R
............ g'Or APP !. ............
(TRLY 187 QTR 2ND QTR 3RD Q1R 4TH QTR YRLY % of SSJ JAN KAR APR=JUN' JUL.StP i OCT NOV 09J- APP.! :
- GAMMA A!R (MRAD)- 5.0 0.03 0.02 0.01- -0.00- 10.0 0.03 h - BETA AIR ( M RAD l ' 10.0 0. 0 5 .- -0.03 0.02 0.00 20.0 0.05 707.~ BODY (MREM) 2.5 0.01 0.01- 0.01' O.00- 5.0 0.01
$RIN (MREM) 7.5 0.04 0.02 0.02
- ORGAN (MREMi' 7.5 0.00- 15.0 0.04
.0.00' O.00 0.05 0.00- 16.0 0.03 i
THYPCID- THYROID THYROID LIVtR THYR 0!D
-THYROID RIDNEY LUNO G1.LLI
'$tSUL15 BA$tD UPON-ODCM ANNEX REVISION 0.8 AUGUST 1990 42
- v. r , s, , -, ,-%.., , _.,.,.-,.~.,_n.,,.mm.-- ..,~,.,,,e~-,.-,. --.-_-,m,,m....,...--%..m, . ..w~,... ., -
l TABLE 3.2-1 l SYRON UNIT ONE ADULT RECEPTOR 1990 ANNUAL REPORT MAXIMUM DOSE $ (MREM) RESULTING FROM LIQUID IFFLUENTS PERIOD OF REttAst - 01/01/90 70 12/31/90 CALCULAtt D 02/22/91 iST 2ND )RD 4TH D08t TYPt QUARTER QUARTER QUARTER QUARTER ANNUAL JAN RAR APR-JUN JUL-StP OCT-DEC TOTAL 2.23t-03 BODY 7.20t-04 7.03t-0) 1.47t 03 1.15t-02 INTERNAL 1.31E-02 ORGAN 1.16t-02 9.275-03 7.112 03 4.06t 02 G1-LL1 GI-LLI LIVER Cl-LL1 Gl.LLI THIS 15 A REPORT FOR THE CAttNDAR YEAR 1990 COMPLIANCE STATUS + 10 CFR $0 APP. 1
............ g or AFP 1, ............
QTRLY 1$7 QTR 2ND QTR 3F0 QTR 4TH QTR OBJ JAN-nAR APR JUN YRLY % 0/
JUL-SEP OCT NOV 08J APP.!
TOTAL BODY (MREM) 1.5 0.1$ 0.05 0.47 0.10 3.0 0.38 l
CRlf. ORGAN (MatM) $.0 0.26 0.23 0.19 0.14 10.0 0.41 !
GI-LL1 01-LLI Liven GI LLI Ct.LLI I
RESULTS BA$tD UPON ODCM ANNEX REVISION 0 MARCH 1989 i
\
l-1 43 I
l l
TABLE 3.2-1 (continued) 8yRON UN!T TWO ADULT RtCtPTOR 1990 ANNUAL REPORT MAXIMUM DO$t$ (MREM) RESULTING PROM LlQUID EPPLVENT$
PERIOD OP RELtAst - 01/01/90 to 12/11/90 CALCULAtt0 02/22/91 1ST 2ND 3RD 4TH Do$t TYPt QUARTER QUARTER QUARTER QUARTER ANNUAL JAN-MAR APR-JUN JUL-StP OCT-DEC TOTAL 2.23t-0) 7.20t 04 7.03t-03 1.47t-03 1.15t-02 80DY INTERNAL 1.31t-02 1.16t-02 9.27t-03 7.11t-0) 4.06t-02 ORGAN Cl-LL1 Cl-LLI LIVER Cl-LLI 01-LLI TH!$ !$ A REPORT POR THE CALENDAR YEAR 1990 COMPL1ANCE STATU$ - 10 CPR 50 APP. 1
.........--. ) 0F APP !. ------------
QTRLY IST QTR 2ND QTR 3RD QTR 4TH QTR YPLY ) 0F CBJ JAN-MAR APR JUN JUL-Str OCT-NOV CBJ APP.!
TOTAL 80DY (MPEM) 1.$ 0.15 0.05 0.47 0.10 3.0 0.38 .,
CRIT. OPGAN(MREMI 5.0 0.26 0.23 0.19 0.14 10.0 0.41 Cl-LL1 GI-LLI LIVER GI-LLI GI-LL1 RESULTS SAstD UFCN ODCM ANNEX PtVISION 0 MARCH 1989 44
1 l
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= =s es tactusione amca souwoamy ON$lTE AIR $AXPLING AND TLD LOCAf!0NS
....... assinictio nata sov oaar DY.21 Near Site N BY.22 Near Site ESE BY.23 Near Site S BY.24 Near Site SW 45
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E, ,,*vg? " STRON STATION is40cmstyth,uPsthtag 14 Cass#75 wiu watta 15 wAAAIN DANA 4$ QA.RY is Am t wo INGE$ TION ANOWATEPENE EXPOSURE PATHWAY SAMME LOCAT043 16AAA t evth MI8 A CAD SV Ac,eost 6 7mog 19 3 SOUTM OF AJA SAuptg h tv og 30 Et kNCTW mt tyt at$ # Apu 2$ AsCHAJC OLTMAN DA,4Y f AAW M HA2tARD OtARY 37 EINNfIM DAVi(N DAIRY
- Repued by MaJ44<W Dasy i4Y Mi A8r 16 '990 47
REVISION 0 MARCH 1989 FIGURE 5.04 a M, 7'~'_-LM m .,, - P ",# 7 SS ' pd ,y -g
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BYRON STATION INNER RING AND OUTER RING TLD LOCATIONS 48 l l i l
-- - . - . - - . . , _ , . , . , - . . .-_ 1
TABLE 5.0-1 L.
W Byron Statl0n o g e
Radiological Environmental Monitoring ; 3 % -
Locations -l: g b 1; . J ;
a e 1 - - 1 e a e a . .o d
e C 3 U e .c U e
.M ..* . m E g L C3 0
.e m 3 m
. x -.4 .o .- % &. C,
.m J
.O L D o O .M e .e4 3 e '.O 3 . L
.c s u u. s 2: n. oc o o > o BY.01 Byron 00...... . ............ ..
BY.02 Stillman Valley 00............. . ... . ..
BY.03 Nearsite. East 00........... .. . ...., .
BY.04 Paynes Point 00................... . .
BY.03 Nearsite. South 00...,....... . . . . . . . ..
BY.06 Oregon 00..... . .. . . .......
BY.07 Mt. Mo'.is 00...... . .. . . . . . . ..
BY.08 Lear River 00........ ..............
/ BY.09 Uloodland Cr ek BY.8; Oregon Pool of Rock River * .................O.......
.....O. ...... O.O..... .
P'.13 Rock RJver. Upstream .
...O....... .O.O.......
BY 14 Olisite Well Water ............. ....... . O.
bY.15 Warren Danakas Dairy ... . ....O... ...........
BY-17 Whitten iloisteins Dairy' ........ O.... ... . . . .
BY.18 McCoy Farmstand Well . ............. ........O.
BY.191 River Road Across from BY.01 . ................. O.....
BY.19 2 South of BY.05 . ...... ...........O. ..
BY.20 Kenneth Reeverts Dairy .........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 Richard Ottman Dairy .
.......O...............
BY.26 Ilazzard Dairy .........O. . ........ . .
BY.27 Kenneth Druien Dairy .. . . ..O......... . . . .
- Replaced by llazzard Dairy (BY 26) on July 16.1990.
CENSUS Dairy Cattle Residence 49 l
~. - .- . . _ - _ - .
TABLE 5.0-2 BYRON STATION ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM, SAMPLING LOCAT10).!
- 1. AIR SAMPLERS Distance Direction Site Code 8 Location (miles) (*)
'BY-01 Byron 3.5 25 BY-02 (C) Stillman Valley 6.2 56 DY-03 Nearsite - East -
3.8 85 BY-04 Paynes Point 4.5 140 BY Nearsite - South 3.6 180 BY-06 Oregon 4.6 213 L
BY-07 (C) Mt. Morris 7.8 24 0 BY-08 (C) Leaf River 7.0 315 BY-21 Nearsite North 0.3 9 SY 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 No. 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 i
a Control (reference) locations are denoted by a "C" after site code. All-other locations are indicators.
I' 50
l 1
TABLE 5.0-2 (continued)
BYRON STATION ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM, SAMPLING LOCA110NS
- 2. TLDs
- b. Special TLD Samplers (continued)
Distance Direction Site Code (miles) (*)
BY-113-1,2 0.7 270 i BY-114-1,2- 0.8 298 BY-115-1,2 1.0 314 BY-116-1,2 - 1.4 329 Outer-Ring BY-201-1,2 -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-),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 i ~3. MILK l' .
Distance Di rection -
Site Code a Location (miles) (*)-
BY-15 -. Warren Danakas Dairy Fann- 3.3 110 ;
-BY-17.(C)-
=
Whitten Holstein Dairy Farmb 8.5 250 BY-20: Kenneth' Reeverts Dairy Farm 2.1 37 !
-Richard Oltmann Dairy Farmc 2.2 .180 BY-25. i BY. (C) , Hazzard Dairy Farm 13.5 355 :j BY-27 Kenneth Druien Dairy Farmd. -
- 5. 3 ' ~ 236 l 4
a Control (reference) locations' are denoted by a "C" af ter site code. - All 3
'other locations are-indicators.-
b Whitten Dairy was replaced by.Hazzard Dairy Farm on July 2,1990.
- c Bill Leupkes farm .was burned out 'on December 25, 1989 and was replaced by Richard:Oltmann f ann on March 19. 1990~.
d Additional < dairy was not; required by 0DCM but was included to ensure that the program has at least- four dairies.
51
TABLE 5.0-2 (continued)
BYRON STATION ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM, SAMPLING LOCATIONS
- 4. VEGETABLES Distance Di aection Site Code Location (miles) (*)
BY-19-1 River Road Across from AP-1 3.5 25 BY-19-2 Just South of AP-5 3.6 180
- 5. GROUND /WELL WATER Distance Di rection Site Code Location (miles) (*)
BY-14 Ceco Off-site Well 0.3 101 BY McCoy Farmstead 1.0 235 :
l (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 Distance Direction Site Code Location (miles) (*)
BY-12 Oregon Pool of Rock River 4.5 213
-BY-13 Rock River Upstream 2.6 302 52
TABLE 5.0-2 (continued)
BYRON STATION ENVIRONMENTAL RADIOLOGICAL HONITORING PROGRAN, S/MtE COLLECTION AND ANALYSES toc ation Collection Type of Frequency Site Frequency Analys t s of Analysts Remarks Sample ikola Codea Byron Conti nuous Gross beta Weekly On all samples.
- 1. Airborne BY-1 Quarterly On qudrterly composites frau each l oc at ion.
Particulates BY-2 (C) 5ttliman valley operation Gamma Isot BY-3 hearsite East for a week Gamma Isot Weekly if gross beta activity in air particulate BY -4 Paynes Point sawples >10 times the yearly mean of (ontrol sampIes.
B f-5 hearsite South B Y -6 Oregon Filter Weekly BY-T (C) kt. Morris Enchange BT-6 (C) Leaf River BY-21 keer Site North BY-22 Near $tte East-Southeast B Y-23 Near Site South BY-24 Near 5tte Southwest om GJ Weekly On all samples.
- 2. Airtvorne Same as 1. Continuous 1-131 ,
lodine operat t on l for a week Test and Weekl y On all semples.
- 3. Air Semplir.9 Saee as 1. -- 1 Train Maintenance j
- 4. TLD Same as 1. Quarterly Camma Quarterly Two sets at all AP locations. One set read quarterly. Second set read af 8 Y-101-1,2 inner Ring required by Corruww.calth Ecoson. At otner locations, all sets read quarterly.
10 2-1 ,2 103-1,2 Mtatsum of two ILDs per set.
104-1,2 i 105-1.2 l
106-1,2 l 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 ( reference) locations are denoted by a *C" In this Coluen. All other locations are indicators.
.. 4 TABLE 5.0-2 (continued) 8YRON STAilGN E*ttlR0fatENT AL RADiot0GICAL tt0NITOHlfiG PROGRAtt sat:PLE C0ttECTION Af0 AtJtYSES tocation (011ection Type of Frequen(y frequency Analysis of Analysis Amark s senple tied 14 Code 8 Site 4 11 0 s BY-201-1,2 Outer Rtng (continued) 202-1,2 203-1,2 204-1,2 205-1,2 206-1,2 2U1-1,2 206 1.2 209-1,2 210-1,2 211-1,2 212-1.2 213-1,2 214-1,2 215-1,2 m 216-1,2 h
- u. Donakas Dairy seraironthly 1-131 senisionthly on all sarapies.
- 5. tnik BY-lb Play-0(tober bY-IT (C) Whitten Noistein Dasryt . tiay-October Garna Isot.
87-20 K. Reeverts R. Oltman DairyC tu thly t:onthly BY-25 forecher- Apr il H32241d Dairy P4ove.Ler-April BY-26 (C)
BY-27 K. Druten Cairy d by-19 1 An w ily at Games Isot. Annually Four vartettes frua east. Iccation as
- 6. Vryct teles harvest evati.Lle at t rvest. R ev-a isotos:( w*
8f-19-2 edible portion only.)
Smluent hly Cross beta Hunt hl y On r.onthly custosite for eeth l w(at e s .
- 1. Ground /Lt11 PV-14 0 00 Offstte bril Un conthly couposite for eeth locattua.
Larria Isot. tionthlj Later Tritium Qua rt er ly On quarterly (or.posite f or enh to(ation.
87-18 ticCoy f armstead On semicenthly conoosite when duse telcu-1-131 $w monthly lated f or water u.astanption is greater then one r;reu per year.
ueekly Tritium Quacterly on quarterly ca.posite frrsi each loc.tson.
- 8. Serface water B Y-09 woodland Creek On nr.onthly cor4estte f rori each loc ation.
Oregon Pool of Gaea Isot. o t'nthly 6f-12 Rock River BY-13 (C) Rock River, Upst ream a Control (referer.cer ) locations are denoted by a "C" in this (clum. All other locations are indicaters.
b kbitten Detry was replaced by tsarzard Catry on July 2, 1990.and was replaced by dichard 01taann f aru on 7: arch 19,1990.
C Bill leupkes farm was burned out on De(ev:ber 25, 1969 4 Additional dairy was not required by (OCtt t,ut was included to ensure that the grogram has at least tour def ries.
TABLE 5.0-2 (continued)
BYR0it STATION EhVIRONft[hiAL RADIOLOGICAL f;ONITORING PROGRAft, 5Ar1PLE COLLECT 10ft AND AftALYSES t ocation Collection Type of Frequency Frequency Analysis of Analysts Reaart s Sample tiedia Code
- Site -
Three tises Garc.a Isot ihree tiraes F rom Cregon pool of Roc k R iver , on Fish BY-12 Oregon Pool of edible portions only. At least two 9.
Rock River a year. a year, spring, species.
BY-13 Rock River, upstream sumer ,
and fall Semiannual On all sanples
- 10. Shoreline BY-12 Oregon Pool of semiannual w e.a Isot Sed iments Rock River BY-13 Upstream of Oregon Dam Site boundary to 2 miles -- a. Enumeration Annual ly During graaing seastm.
- 11. Dairy Census a.
by a door-to-door or e wiva.
lent counting
$ techatque,
- b. Enumeration Annually During grazing season.
- b. 2 miles to 5 miles -
by usiny referenced information frors county agricultural agents or other reliable sources.
- c. Inquire as Annually Durin9 srazing season.
- c. At dairies listed in Item 5. --
to feeding pr actices :
- 1. Pasture only.
l 2. reed and cnop only.
- 3. Pasture and feed; if t>oth, ask farver to estir, ate fraction of food f rom pasture: 4251 25 501, 50 751. or
>75%.
in all 16 sectors up to 5 miles Annually During gro.ing season.
- 12. hearest Residence Census 8 Control (reference) IcCations are denoted by a *C" in this Column. All other locations are indicators.
. TABLE 5 5-3 RADIOLOGICAL ENVIRO *tMENTA1. MONITORING PROGRAM QUARTERLY
SUMMARY
.. Mame of f acility _ Byron Nuclear Power Station' Docket No. 50-454, 50-455 Location of facility _ Ogle, lilinois Reporting Period 1st Quarter 1990 (County. State)
Indicator Location with Highest Control Sample Type and Locations ' Quarterly Mean locations 8hrter of Type Number of a Mean . Mean Neana Non-routine (Units) Analyses LLO Range Location Range Range Results Air Particulates Gross Beta 156 0.01 0.022 (117/117) By-22. Onsite 0.024 (13/13) 0.021 (39/39) 0 (pC1/m3) (0.006-0.033) 0.3 mi 9 109* (0.013-0.031) (0.007-0.031)
Garna Spec. 12 0.01 <tLD - -
<ttD 0 Airborne lodine I-131 '156 0.07 <t LD - -
<tLO O (pCi/m3)
Garria Background Gamma Dose 12 3.0 14.2 (9/9) ' By-22. Onsite 16.8 (1/1) 13.3 (3/3) 0 (itDs) (mR/Otr.) (11.3-16.8) 0.3 mi 9 10l* -
(12.2-14.0)
Milk I-131 10 0.5 <tL D - -
<tLD 0 (PCIII)
Gamma Spec. 10 Cs.134 5.0 <tL D - -
<tL D 0 Cs-137 5.0 <tLD - -
<tLD 0 Other Careas 10.0 <tLD - -
<tLD 0 Surface Water Gamma Spec. 8 (PCi/3)
Cs-134 10 <tLD - -
<LL O O Cs.137 10 <tLD - -
<LLD 0 Other Gammas 15 <tLD - -
<LLD 0 Tritium 3 200 404 (1/2) By-12 Downstream of 404 (1/2) <tLD 0
Intake 4.4 mi 9 213*
Well Water Gross Beta- 6 2.0 2.7 (2/6) By-18, McCoy Farm-(DCi/1) 2.8 (1/1) None 0 Gamma Spec. 6 Cs-134 10 <LLD - -
None 0 Cs-137 10 <tt 9 - -
None 0 Other Camas 15 <LLP - -
.None 0 Trit t uri 2 200 <tt D - -
None 0 a Mean and range based on detectable measurements only. Fraction indicated in parenthesis.
~ ~ - , . - .- -- . _ _ , . _ = , _ - = _ . _ _ _ , _ _ . - . - . _
~ .s .
t :
3 TABLE 15.0-4.
- y. -
4 i .y
. RADIOLOGICAL ENVIRONMENTAL . MONITORING PROGRAM QUARTERLY SUP91ARY-a Name'of Facility Byron Nuclear Power Station . Docket No. 50-454, 50-455'-
Location of facility Ogle. Illinofs Reporting Period 2nd Quarter'1990 (County. State) .
-Sample
- Indicator _ Location with Highest Control- I
' Type andi ' locations' Quarterly Mean r
, . Type ' Muster of Meana Locations-- Number of.
. pean . n,ana non. root tne (Units)
_ Analyses , LLD ' Range location &enge
+
I Range Results. ;;
Air Particulates LGross Bets 1155 '. 0.01 0.017 (116/116) By-22, nearsite [5E.. 1
!/ (pct /m3 ) 0.019 (13/13) 0.015 (39/39) (O I. I (0.007-0.035) .. 0.35 at 9 10l* (0.010-0.035) (0.007 0.025)' ti Camma spec. 12 0.01' <tLD ' -
4
-: ALD 0 3 Airborne Iodine I-131 156 0.07 ' <tLD -
i (PC1/m3)
'-: 410 0 Gamma Background. Gansaa Dose 3.0 i 12 14.3 (9/9) . , By-05. Nearsite South 16.6 (1/l). 13.8 (3/3) -0
' -(TL0s) (mR/Qtr.) (11.0-16.6) ' 3.6 et 9180*
~ .
(12.4-15.2)
- By-22, hearsite ESE 16.6 (1/1) 0.35 at 9101* [
$ Milk. ' . I-131 ' 20 0.5 <tLD (PC f / L) '
ALD 0L
' Gamma Spec. ' 20 Cs-134' 5.0 ' 4LD - !
<Lt.0 0 !
Cs-137- 5.0 . 4LD - -
4LD '0 'i Other Gansmas ~ 10.0 4LD -
<tLO O ;
Surface Water Gamma Spec.. 9 t 4
- (pC1/L)
Cs-134 10 . 4LD - -
ALD 0
- Cs-137 10 <tLD - -
4LD 0
- ;Other Gansnas 15 <tLD -
'i
<t LD 0 i Tritium 3' 200 40 - -
4LD 0 1
Well Water ' Gross Beta 6 ' 2. 4 ' 4 LD -
(pC1/L)
None 0 1.
' Gamma spec.!
6
- Cs-134 10 <tLD ' - -
None o Li i
j Cs-137. c10 ALD -
.f.
hone 0 Other Gaasnas 15 <LLD - --- I
' None 0 ,
l Tritfun. .2 200 - 4LO .. .- ~ None o i
I
'f
, - . _ _ _s ~ - , _ _, _.m.__ , , _ , , . __ -- , ,. .. .. - _m ,.-,_m._.
E l
TABLE 5.0-4 (continued)
I
' RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM QUARTERLY
SUMMARY
Name of facility Byron Nuclear Power Station Docket No. 50-454. 50-455 l
Location of facility Ogle tilinois Reporting Period 2nd Quarter 1990 l
'(County, State)
Indicator Location twith Highest Control Sample Type and Locations Quarterly Mean tocations sa u ce>cr of l
Number of Meana Mean Meana Non-routfee Type Results i
Range tocation Range Range (Units) Analyses LLD Fish Gamma Spec. 5 (pCi/gteet) <tLD 0 Cs 134 0.1 <tLD - -
0.1 4LD - - <tt o 0 Cs-137 0.13 <t LD - - <tLD 0 Other Gammas Bottom Sediments Gamma Spec. 7 g (pCl/g dry) <tLD 0 co Cs-134 0.1 <tLD - -
0.1 4 LD - - <t L D 0 Cs-137 0.2 <t L D - - <LLD 0 Other Gammas 8 Pean and range based on detectable measurements only. Fractions indicated in parentheses.
TABLE 5.0-5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRArt QUARitRLY SLpl#Y hame of f acility Byron Nuclear Power Station Docket No. 50-454. 50-455 Location of Facility Ogle. Illinois' Reporting Period 3rd Quarter 1990 (County. State)
Indicator Location i.ith Highest Control j Locations Quarterly Mean Locations Aster of f Sample Type and Meane savn-routine {
Neona Nean Type Ant >er of l Range Results I Analyses LLD Range location j Range (Units) i By-23. hearsite South 0.025 (13/13) 0.018 (39/39) 0 Air Particulates Gross Beta 156 0.01 0.022 (111/117)
(pCi/oJ) (0.006-0.047) 0.6 m 9 182* (0.013-0.047) (0.010-0.030) . ,
- <LLD 0 Garur.a Spec. 12 0.01 <tLD l I
<tLD 0 l Airborne lodine 1-131 156 0.07 <tLD (PCi/m3) {
f by-22. hearsite LSE 11.0 (1/1) 13.4 (3/3) 0 Gansna Background Ganna Dose 12 3.0 14.2 (9/9)
(10.9-17.0) 0.3 et # 101* -
(12.4-14.9)
$ (ILDs) (eR/Qtr.)
- <tto O !
Milk 1-131 30 0.5 <tLD -
l (pCi/L) j Garna Spec. 30 l i
- <tLD 0 j (s-134 5.0 <tL D -
l
<tLD 0 f
Cs-137 5.0 <t LD -
<LLO O f
Other Gaessas 10.0 <tLD -
' l I t
j Canas spec. 9 l surface Water ,'
(pCi/L ) f' <tLD 0 e 1
i
! Cs-134 10 <tLD l
<tLO - - <ttD 0 Cs-137 10
- <tLD 0 Other Gansnes 20 <tLD -
i by-12. Downstream of {339(1/1) 4to 0 Tritium 3 200 339 (1/2)
- Oregon Dam. 4.6 mi , -
9 213' l
- Mean and range based on detectable IBeasurements onis. rraction indicated in parentnesis.
TABLE 5.0-5 (contir.aed) }'
1 l
RADIOLOGICAL EhYIR0teENTAL MONITORING PROGRAM QUARTERLY SOf1 MARY Byron Nuclear Power Station Docket ho. 50 454, 50-455 Neme of facility _
Location of Facility gLLouity
- t. r j linois Reporting Period _3rd Guarter 190
, St?'.tp indicator tocation with Ifighest Control .
Quarterly Mean tocations seusnber of i ,
Sac >ple type and locations the ena 9 sun-rou" one !
Mean8 Heat Type %mber of Ra!.y* Hany kesu' .s [
Analyses LLC Range Location (Units) -
BY-18. McLoy Farm- 2.6 (1/6) hone 0 Well Water Gross Beta C ?.4 2.4 (t/6)
(pCi/L) I stead. 1.0 mi @ 235*
Gaama spec. 6
- None O Cs-134 10 <t t D -
- - Mone 0 Cs-237 10 <tts
- hane 0 Other Genesas 15 <tLD -
hore 6 1ritium 2 200 <ttD - -
ch o
fish Ger.sr.4 Spec. 3 9 ** <tLD
- <Lt0 0 Cs-134 0.10 -
- <ttD 0 Cs.137 0.10 <tLD -
i 0.13 <ttD - - <ttD 0 Other Gansnas I t
Vegetables Gaesw Spec. 8 !
- hone O Cs-134 0.06 <tt0 - ;
Pene 9 Cs-137 0.08 <tLD - -
f
- hone O other Gammas 0.15 <tLD -
o I
- None I-131 0.06 <tLD -
l i i i
- Mean and range based on detectable measurements only. fractions indicated in parentheses.
lIfl
! it lr e
f n oiS tt rul eou 0 0 0 0 0 0 0 O 0 0 0 0 crs a - e NnR o M
))
h9 34 )
s /0 )6 l
oong n*e 8 3 . D D D D 30 D D /6 D D D O L t L L rian ( - t L 31 I L L L t L t t tt ea 2 t t ( - t t t t < < < <
naMR 41 < < 5 < < < <
oc 20 Co 6. 4 t 0.
0(
0 51 1(
0 <
9 ))
9 29 1 14 5 / 0 ) )
5 r ng e 2 1 2 4 e 1 0 / /
- t an ( - - - 1 - - - - -
0 5
r a t ea PR 71 7 ( - - -
1
( -
u s 20 7 0
Q e 4
5 h h
ign 00 0(
8 1
2 1
8 4 t a Y - 4 H e R 0 H ; s ,1 l, A 5 h h
'r t
t y t t d i. l u t
5 i o .re r S o
r nt e m.
Y L
e or n
v i*
e en*
R .P i a t u o R5 t*
i0 ra3 tD1 E 0 g aC i 1 s8 s 2 T 5 n c t f3 - - r1 - - - - - - -
R i o a a a eno A t t e r L c o e@ e9 og@
J Q
M dp o o e L
L 8
.im N
5
.im .
Det 2
.O re -
D R 6 A
R 00 06,
- 1f G Y7 V4 - c4 y
0 H
B B" C 6 P
}
- n )
0 E 1 i o 7 ~
1) 5 R t rs 1 6 0
T t a
)
en /4 ;
is e t oa e 50 )1 )
1 S ai n g D o 9 E :
1 o t ct en 1
10 t t /8 D O D D D D D 2 L 0 r n a iaea ( - L. L L L t L /
B 1
7 e i t dcPR t 4
L t
31
( - <t L
L L U< < <
t t 1
(
w l S no 40 A L o l IL 20 0.1 r. 0 T A T
P I y
- 0. 0 61 8 N r 0( 1(
2 a e,t e l nu E 1 s
t l g o 0 c O L 1 1 7 Pl e ( O 0 0 0 0 5 0 0 0 L
v L 0 0 0 3 0 5 5 0 0 n n 1 0 5 0 0
E o 1 1 1 2
r L y
A B C 5 2 6 2 0 0 I y 5 1 5 1 2 2 9 3 G t 1 1 O i L l O yi f I t c dos s s D s a n e a a A 1 f ars . . c . n R t ey a c e v cf e>l e c m c e a o pr a t t e s e a e a yun p o p G p G f B S D S 4 7 S 4 7 m n T hA 3 3 r 3 3 r u f o s a 1 a 1 a 1 1 e e 1 1 e i oi s 3 m 3 - n - h e a t c r
m a
1 m a
1 m s. 5 t m s- s t i t
- - o C C O a C C O m
a o c G G J G 1 G G T r
N L
)
s dr e e nt t n uQ a o/ r
) l u
id rR gm e le et s c) l) o k(
t a
p pi myn i3 t m em 3 c a)
)
L W) aTU r/ a r/ B s L S ( / e/
ai ri D t c1 Pt oC aL C aC p bp n k p f p ir{ r( n (T a
l( r(
A i
A G u Mi S i
l l\ lll l i
TABLE 5.0-6 (continued)'
RADIOLOGICAL Ehv!R0fttEhTAL H0hlTORlhG PkOGRAN QU/-RTERLV $L9 MARY hane of Facility Byron Nclear rower Station Docket feo. 50-454. 50 455 Location of facility 09 e. Illinois 1 Reporting Period 4th Ouarter 1990 (County. State)
Indicator Location with highest Contrul Type and Locations Quarterly Pean Locations Aseer of Sample Peana hon-routine Heano Peen Type Nuf@er of Range Results Analyses LLD Range location kange (Units)
None 0 Well Water Gross Beta 2 2.6 <tLD - -
(pCi/L)
Cama Spec. 2
<tLD - - None 0 (s-134 10 ,
(LLD - Mne O ts-131 10
<tLD - - hone O Other Ganrtas 15
<tLD - - none 0 l m Tritium 2 200 ru fish Gama Spec. 4 (PC1/9 wet) <tt0 None 0 Cs-134 0.10 - -
hone 0 Cs-137 0.10 <LLD - -
<tLD - None 0 Other canetas 0.13 -
bottom Sedtesents Gew.a Spec. 2 (pCf/9 dry ) <t LO O 05-134 0,1 (LLD - -
BY-12. Downstream of 0.45 (1/1) 0.26 (1/1) 0 Cs-131 0.' O.45 (1/1)
Oregon Dam. 4.6 et 9 213*
<LL D 0 Other Gamries 0.2 <t L D - -
- Penn and range based on detectable a+asurements only. Fractions indicated in parentheses.
, - r- -
r APPEN0ix 11 METEOROLOGICAL DATA I
1 63
BYRON NUCLEAR POWER STAT!ON PERIOD OF RECORD - JANUARY-MARCH 1990 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 O O O O NE O O O O O O O ENE O O O O 1 0 1 E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S O O -0 0 0 0 0 j SSW O O O O O O O l SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 1 0 1 ours of calm in this stability class: 0
- ours of missing wind measurements in this stability class: 0 ours of m_issing stability measurements in all stability classes: 2 64 i'
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990
- 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 O O O O O NNE O 0 0 0 0 0 0 NE O O O O O O O ENE O O O O 4 0 4 E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S O O O 1 0 0 1 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 2 1 3 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 1 6 1 8 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 classes: 2 65
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 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 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 1 0 1 E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 1 2 0 0 3 WSW 0 0 0 0 1 1 2 W 0 0 0 0 0 0 0 WNW 0 0 1 0 0 0 1 NW C 0 2 4 0 0 6 NNW 0 0 0 3 0 0 3 VARIABLE O O O O O O O TOTAL 0 0 4 9 2 1 16 iours of calm in this stability class: 0 iours of missing wind measurements in this stability class: 0 dours of missing stability measurements in all stability classes: 2 66
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - NEUTRAL (DIFF TEMP 250-30 FT) i WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 '3-18 19-24 GT 24 TOTAL N 2 9 12 18 5 7 53 NNE O 4 8 25 23 8 68 NE 1 6 8 8 28 7 58 ENE O 3 21 31 50 4 109 E O 8 8 4 16 0 36 ESE O 3 5 2 1 0 11 SE 2 6 6 7 4 0 25 SSE 1 6 4 23 22 9 65 S 1 6 16 34 14 15 86 SSW 1 7 16 37 25 22 108 SW 0 5 23 22 14 8 72 WSW 0 6 13 29 20 23 91 W 0 5 19 17 8 26 75 WNW 1 4 9 34 24 20 92 NW 1 3 14 46 30 30 124 NNW 2 7 15 20 7 7 58 VARIABLE O O O O O 9 0 TOTAL 12 88 197 357 291 186 1131 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: 2 67
, BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT)
WINDS HEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .d-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 1 5 12 0 0 19 NNE O 1 1 5 2 0 9 NE O 4 5 1 1 0 11 ENE O 1 3 2 O O 5 E 1 4 4 7 8 0 24 ESE O O O 5 9 3 17 SE O 2 7 12 3 11 35 SSE 1 2 9 7 20 34 73 S O 2 3 36 58 62 161 SSW 0 1 13 43 41 16 114 SW 0 0 18 28 19 9 74 WSW 0 3 12 32 8 1 56 W O 3 21 25 5 4 58 WNW 1 0 19 24 7 1 52 NW 0 1 13 18 4 0 36 NNW 0 3 13 19 5 0 40 VARIABLE O O O O O O O TOTAL 4 28 146 276 190 141 785 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 2 i
l i
68
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANU4RY-MARCH 1990 STABILITY CLASS - MODERATEL) STABLE (DIFF TEMP 250-30 FT)
WINDS MEASLRED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 0 2 0 0 0 3 NNE O 1 1 0 1 0 3 NE O 2 0 1 0 0 3 ENE 1 1 1 0 0 0 3 E O O 1 2 0 0 3 ESE O 1 2 1 2 0 6 SE O 2 2 8 4 0 16 SSE O 2 1 6 6 2 17 S 0 0 2 12 23 3 40 SSW 0 0 1 11 5 0 17 SW 0 0 3 13 0 0 16 WSW 0 0 3 6 1 0 10 W 0 2 8 0 0 0 10 WNW 0 4 2 2 0 0 8 NW 1 0 1 4 0 0 6 NNW 1 1 1 3 0 0 6 VARIABLE O O O O O O O TOTAL 4 16 31 69 42 5 167 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: 2 69
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1990 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 1 0 1 0 0 0 2 NE O O O O O O O ENE O 1 0 0 0 0 1 E O 1 0 0 0 0 1 ESE O O O O O O O SE 1 1 1 2 1 0 6 SSE O O O 4 4 0 8 S 0 2 1 7 7 0 17 SSW 0 1 3 2 0 0 6 SW 0 2 1 3 0 0 6 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 1 1 0 0 0 2 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 2 9 8 18 12 0 49 iours of calm in this stability class: 1
-iours of missing wind measurements in this stability class: 0 4ours of missing stability measurements in all stability classes: 2 70
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 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 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 ESS O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 2 0 0 2 WNW 0 0 0 0 0 0 0 NW 0 0 0 1 5 0 6 NNW 0 0 0 0 1 0 1 VARIABLE O O O O O O O TOTAL 0 0 0 3 6 0 9 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: 10 71
BYRON NUCLEAR POWER STATION l PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 250-30 FT)
WINOS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
OIRECTION .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 3 0 0 3 NE O O 1 0 0 0 1 ENE O O O O O O O E O O O O C 0 0 ESE O O 1 0 0 0 1 SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 1 1 SW 0 0 0 1 0 0 1 WSW 0 0 1 0 0 0 1 W 0 0 3 7 0 0 to WNW 0 0 0 1 4 0 5 NW O O O 3 6 0 9 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 8 15 10 1 34 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: 10 72
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 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 3 0 0 5 NNE O 1 2 3 0 0 6 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 1 2 0 0 0 3 SE O O O 1 1 0 2 SSE O O 3 1 3 0 7 S 0 0 2 1 1 0 4 SSW 0 0 3 3 2 0 8 SW 0 0 2 2 1 0 5 WSW 0 0 1 1 0 0 2 W 0 1 5 5 0 0 11 WNW 0 1 4 4 3 0 12 NW 0 0 2 5 7 1 15 NNW 0 2 1 0 0 1 4 VARIABLE O O O O O O O TOTAL 0 6 29 29 18 2 84 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: 10 73
BYRON NUCLEAR POWER STATf0N PERIOD OF RECORD - APRIL-JUNE 1990 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 3 17 26 18 1 65 NNE 1 2 15 12 7 5 42 NE O 3 10 15 8 3 39 ENE O 1 10 15 4 8 38 E O O 12 20 9 0 41 ESE O 12 14 5 8 0 39 SE O 3 14 16 1 1 35
.SSE 1 5 8 14 10 6 44 S 1 3 29 35 31 25 124 SSW 0 5 27 31 21 24 108 SW O 8 25 12 11 9 65 WSW O 6 15 14 10 8 53 W 1 8 19 21 3 18 70 WNW 1 5 25 32 24 33 120 NW 2 7 9 27 36 7 90 l NNW i 1 6 26 11 5 50
~
VARIABLE 0 0 0 0 0 0 0 TOTAL 8 72 255 321 214 153 1023 sours of calm in this stability class: 0 sours of-missin9. wind measurements in this stability class: 0 dours of missing' stability measurements in all stability classes: 10 74
8YRON NUCLEAR POWL e7AT80N PER20D OF RECORD - APRIL-JUNE 1990 I STA8ILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 TEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 5 3 11 2 0 21 NNE 1 3 6 8 6 0 24 NE 1 6 9 8 4 0 28 ENE O 5 13 7 1 1 27 E O 2 5 13 10 3 33 ESE 2 3 3 10 12 3 33 SE O 1 6 15 14 3 39 SSE O 1 5 21 39 3 69 S 1 2 13 24 63 8 111 SSW 0 0 14 25 43 11 93 SW 1 5 25 16 6 1 54 WSW 0 5 17 19 4 6 51 W 4 5 11 25 8 0 53 WNW- 1 3 15 15 7 0 41 NW 0 1 6 24 to 1 42 1
NNW 0 8 5 7 1 0 21 l VARIABLE 0- 0 0' O O O O TOTAL 11 55 156 248 230 40 740 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: O Hours of missin9 stability measurements in all stability classes: 10 75
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 250-30 FT)
WINDS HEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 1 5 5 0 0 11 NNE O O 1 7 0 0 8 NE O O 2 6 1 0 9 ENE O O 2 3 0 0 5 E O O 1 1 5 0 7 ESE O O 1 6 5 0 12 SE O O 3 10 7 0 20 SSE O O 1 4 11 9 25 S 0 1 2 10 18 1 32 SSW 0 0 5 2 2 0 9 SW 0 0 7 12 5 0 24 WSW 0 1 5 2 0 0 8 W 1 1 6 14 0 0 22 WNW 0 2 9 8 0 0 19 NW 0 1 3 11 0 0 15 NNW 0 2 7 5 0 0 14 VARIABLE O O O O O O O TOTAL 1 9 60 106 54 10 240 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: 10 76
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1990 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 1 0 2 2 0 0 5 NNE O O O 5 0 0 5 NE O O O O O O O ENE O O 1 0 0 0 1 E O 2 1 1 0 0 4 ESE O O 1 1 1 0 3 SE O O O O 1 0 1 SSE O O O 2 1 0 3 S O 1 0 2 1 0 4 SSW 0 1 0 1 2 0 4 SW O O O 6 0 0 6 WSW 0 0 1 0 0 0 1 W 0 0 1 0 0 0 1 WNW 1 0 0 0 0 0 1 NW 0 0 1 0 0 0 1 NNW 1 1 2 0 0 0 4 VARIABLE O O O O O O O TOTAL 3 5 10 20 6 0 44 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: 10 77
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 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 2 2 7 1 0 12 NNE O O 3 0 0 0 3 NE O O 1 2 3 0 6 ENE O O 3 0 0 0 3 E O O 1 0 0 0 1 ESE O 1 2 1 0 0 4 SE O O O 1 0 0 1 SSE O 1 3 7 0 0 11 S 0 0 1 1 1 0 3 SSW 0 1 3 5 3 0 12 SW 0 2 3 8 0 0 13 WSW 0 0 1 9 4 0 14 W 0 0 2 3 0 0 6 WNW 0 0 0 3 4 2 9 NW 0 0 1 6 1 0 8 NNW 0 1 0 1 2 0 4 VARIABLE O O O O O O O TOTAL 0 8 26 54 19 2 109
- .ours of calm in this stabi1ity elass
- 0 ours of missing wind measurements in this stability class: 0 ours of missing stability measurements in all stability classes: 0 78
BYRON NUCLEAR POWER STATZON PERIOD OF RECORD - JULY-SEPTEMBER 1990 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 12 2 3 0 17 NNE O O 2 3 0 0 5 NE O O 2 3 1 0 6 ENE O O 5 5 0 0 to E O 2 0 0 0 0 2 ESE O 3 3 0 0 0 6 SE O 4 2 0 0 0 6 SSE O 1 2 4 0 0 7 S 0 2 8 5 2 0 17 SSW 0 1 11 3 2 0 17 SW 0 2 3 8 6 0 19 WSW 0 0 1 3 1 0 5
.W 0 0 2 1 0 0 3 WNW 0 1 2 0 1 0 4 NW 0 1 4 2 1 0 8 NNW 0 1 6 0 1 0 8 VARIABLE O O O O O O O TOTAL 0 18 65 39 18 0 140
-Hours of calm in this stability class: 0 Hours:of missing wind measurements in this stability class: 5 Hours of missin9 stability measurements in all stability classes: 0 79
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 STAl\ILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
, iNECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 2 6 4 0 0 12 NNE O O 6 7 0 0 13 NE O 1 2 1 1 0 5 ENE O 1 3 1 0 0 5 E O 3 1 1 0 0 5 ESE 3 2 0 0 0 0 5 SE O 3 7 0 0 0 10 SSE O 4 4 6 2 0 16 S O 1 4 3 1 0 9 SSW 0 6 8 11 2 0 27 SW 0 2 3 8 1 0 14 WSW 1 1 3 3 1 0 9 W 0 0 1 3 0 0 4 WNW 0 2 8 0 0 0 10 NW 0 1 5 2 4 2 14 NNW 0 3 5 2 0 0 10 VARIABLE O O O O O O O TOTAL 4 32 66 52 12 2 168 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: 6 Hours of missing stability measurements in all stability classes: 0 80
BYRON NUCLEAR PODER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 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 1 11 13 11 2 0 38-NNE 1 10 26 40 1 0 78 NE O 8 13 22 15 0 58 ENE 1 8 13 19 1 0 42 E 3 7 15 8 0 0 33 ESE 2 11 14 2 0 0 29 SE O 1 10 6 2 0 19 SSE 1 4 17 22 9 0 53 S 3 1 29 22 3 0 58
'SSW O 8 23 25 13 0 69 SW 0 8 15 23 5 1 52 WSW 2 8 10 8 1 1 30 W 1 5 2 3 0 0 11 WNW 5 10 8 5 0 0 28 NW 1 5 18- 5 14 2 45
'NNW 3 8 14 1* 4 1 44 VARIABLE O O O O O O O TOTAL 24 113 240 235 70 5 687 Hours of calm in this stability class: 1 Hours of misning wind measurements in this stability- class: 18 Hours of missing stability measurements in all stability classes: 0 81
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1990 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 1 7 14 12 1 1 36 NNE 1 4 15 30 5 1 56 NE 1 0 13 19 2 0 41 ENE 2 5 15 12 1 0 35 E O 9 9 13 2 0 33 ESE O 4 5 13 5 0 27 SE O 8 7 11 17 0 43 SSE 2 5 10 21 27 1 66 S 0 4 12 27 27 0 70 SSW 0 3 13 49 30 1 96 SW 1 2 8 27 28 2 68 WSW 0 0 6 8 1 0 15 W 2 3 4 4 0 0 13 WNW 1 4 4 7 0 0 16 NW 0 0 12 9 0 0 21 NNW 2 1 8 26 1 0 38 VARIABLE O O O O O O O TOTAL 13 65 155 268 147 6 674 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: 7 Hours of missing stability measurements in all stability classes: 0 82
BYRON NUCLEAR POdER STAT 80N PERIOD OF RECORD - JULY-SEPTEMBER 1990 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 5 1 1 0 9 NNE O 1 3 7 0 0 11 NE O O 4 12 2 0 18 ENE- 0 2 0 0 0 0 2 E O 3 2 1 2 0 8 ESE O 4 7 3 4 0 18 SE O 2 9 4 3 0 18 SSE O 3 6 13 14 1 37 S 0 4 5 20 15 0 44 SSW 0 2 12 23 1 0 38 i
SW 0 4 9 11 1 0 25 l WSW 0 3 8 3 0 0 14 W 1 1 4 6 0 0 12 WNW 1 2 1 7 0 0 11 NW 1 1 6 1 0 0 9 l
NNW 0 0 3 6 0 0 9 VARIABLE O O O O O O O TOTAL 3 34 84 118 43 1 283 Hours of calm in this stability class: 0 Hours of missins wind measurements in this stability class:
~
4 Hours of missing stability measurements in all stability classes: 0 83
-*--'we" f eu- --w9 yry--T u'- e. gy ..enw+ r-r
- r r ir-e---ep 9-*w---T-T w H -.e
- - - e
BYRON NUCLEAR POdER STAT 20N PERIOD OF RECORD - JULY-SEPTEMBER 1990 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 1 2 0 0 0 3 NNE O O 2 0 0 0 2 NE O 1 0 2 0 0 3 ENE O O O O O O O E 1 0 0 1 1 0 3 ESE O O O O 2 0 2 SE O 4 0 4 2 0 10 SSE O O 1 5 7 1 14 S O O 3 19 0 0 22 SSW 0 0 6 8 0 0 14 SW 0 0 4 4 2 0 10 WSW 0 0 5 0 0 0 5 W 0 0 8 1 0 0 9 WNW 0 1 0 2 0 0 3 NW 0 0 0 5 0 0 5 NNW 0 0 0 1 0 0 1 VARIABLE O O O O O O O i - TOT A L- 1 7 31 52 14 1 106 l
l ours of calm in this stability class: 0 ours of missing wind measurements in this stability class: 0 Nours of . missing stability measurements in all stability classes: 0 84
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 250-30 FT)
WINDS HEASURED AT 250 FEET WINO WIND SPEED (IN HPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 1 0 0 0 1 NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O 1 0 0 0 1 SE O O 1 0 0 0 1 SSE O O O 5 3 1 9 S O O 2 9 2 4 17 SSW 0 0 2 1 0 0 3 i
SW 0 0 1 1 3 1 6 WSW 0 0 6 0 0 1 7 W 0 0 1 0 0 0 1 WNW 0 0 0 1 1 0 2 1 NW O O O 2 0 0 2 NNW 0 0 0 0 1 0 1 VARIABLE O O O O O O O TOTAL 0 0 15 19 10 7 51 Houro 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 l
l 85
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 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 i
N O O 1 0 0 0 1 NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O J 0 0 0 ESE O O 2 0 0 0 2 SE O O O O 1 0 1 SSE O O 1 2 1 0 4 S 0 1 2 3 4 7 17 SSW 0 2 1 2 1 1 7 SW 0 1 2 4 1 5 13 WSW 0 0 1 0 0 0 1 W 0 0 1 3 0 1 5 WNW 0 0 3 2 0 1 6 NW 0 0 2 3 2 3 10 NNW O O 2 3 2 0 7 VARIABLE O O O O O O O TOTAL 0 4 18 22 12 18 74 Wours of calm in this stability class: 0 Moura-of-missing wind measurements in this stability class: 1 Mours of missing stability measurements in all stability classes: 1 86
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP'250-30 FT)
WINDS MEASURED A~ 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 1 0 0 0 1 NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O 1 0 0 0 1 ESE O O O 3 0 0 3 SE O O 1 1 1 0 3 SSE O O O 1 1 0 2 S O 1 1 3 1 2 8 SSW 0 4 2 3 2 1 12 SW 0 1 3 3 1 4 12 WSW 0 3 0 2 1 0 6 W 0 1 0 0 2 0 3 WNW 0 0 0 3 1 4 8 NW 0 1 4 6 0 1 12 NNW 0 0 1 2 1 0 4 VARIABLE O O O O O O O TOTAL 0 11 14 27 11 12 75 Hours of calm in this stability class: 0 Hours of missing wina measurements in tnis stability class: 6 Hours of missing stability measurements in all stability classes: 1 87
BYRON NUCLEAR POdER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - NEUTRAL (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN HPH)
_ DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 0 8 12 21 4 46 NNE- 0 2 3 28 46 8 87 NE O 3 2 3 3 0 11 ENE- 3 1 0 4 2 12 19 E O 2 1 2 3 3 11 ESE O 2 4 8 3 1 18 CE 1 1 8 29 28 4 71 SSE 1 0 22 36 18 19 96 S O 4 9 26 18 23 80 SSW 0 6 22 15 15 22 PO SW 1 6 14 28 19 9 77 WSW 4 8 8 22 11 14 67 W 3 3 19 22 18 12 77 WNW 2 7 19 42 28 10 108 NW 1 4 29 52 22 15 123 NNW- 1 5 17 28 9 6 66 VARIABLE O O O O O O O TOTAL 15 54 185 357 264 162 1037 eurs of calm in this stability clasc: 0
- @urs of missing wind measurements in this stability class
- 6
- @urs of missing stability measurements in all stability classes: 1 88 -
BYRON NUCLEAR POWER $7AT80N PERIOD OF RECORD - OCTOBER-DECEMBER 1990 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 2 2 8 1 0 13 NNE O 1 0 7 0 0 8 NE O 2 2 5 0 0 9 ENE O O 4 11 4 0 19 E O 1 2 5 6 6 20 i
ESE O 1 0 1 3 0 $
SE O 1 0 4 9 2 16 SSE 1 2 1 9 25 13 51 S 0 1 7 11 35 24 78 SSW 2 1 10 26 43 54 136
-SW 0 3 11 23 17 12 66 WSW 0 5 6 14 15 1 41 W 1 0 9 27 11 4 52 WNW 1 2 7 15 3 0 28 NW 0 1 10 22 6 0 39 NNW 1 0 7 21 8 0 37 VARIABLE O O O O O O O TOTAL 6 23 78 209 186 116 618 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
l BYRON NUCLEAR POWER STATION l PERIOD OF RECORD - OCTOBER-DECEMBER 1990 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 1 2 3 9 1 0 16 NNE O 1 2 3 0 0 6 NE O 1 2 2 1 0 6 ENE 1 2 2 0 0 0 5 E O O 1 1 1 0 3 ESE O 1 0 2 2 1 6 SE O O 2 4 11 0 17 SSE 1 1 1 7 13 4 27 S i 0 3 10 11 2 27 SSW 0 2 6 10 12 4 34 SW 0 0 1 17 1 0 19 WSW 0 0 2 9 0 0 11 W 0 1 6 4 0 0 11 WNW 0 0 3 5 0 0 8 NW O 2 8 10 1 0 21 NNW 0 2 8 12 2 0 24 VARIABLE O O O O O O O TOTAL 4 15 50 105 56 11 241 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missirgj stability measurements in all stability classes: 1 90
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1990 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND 3 PEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 2 4 5 1 0 12 NNE O 'O O O 1 0 1 NE O 1 0 1 1 0 3 ENE O O O O O O O E O O O O O O O ESE 1 0 0 1 1 0 3 SE O 1 0 4 2 0 7 SSE O O 3 2 1 0 6 S 0 1 2 14 9 1 27 SSW 0 1 5 8 4 0 18 SW O 2 2 4 2 0 10 WSW 1 1 0 2 0 0 4 W 0 0 4 0 0 0 4 WNW 0 1 0 0 0 0 1 NW 0 0 0 1 0 0 1 NNW 0 0 1 0 0 0 1 VARIABLE- 0 0 0 0 0 0 0 TOTAL 2 10 21 42 22 1 98 LH ours of calm-in this stability class: 0
'Houro of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 1 91
,,A - _
a * - -
i l
APPENDIX} 1990 REMP SAMPLE RESULTS 92
( BYRON ! TABLE Of CONTENTS , Section Page List of Tables . . . . , ' ' ** *........... 94 t
- -- .i.0 INTRODUCTION . . . ' ' '- . . . . . . . . . . . . , . . . . 95 2.0 LISTING Of t!!SSED SAfiPLES ....'***........** 96 l
( b ( l
?
93
. -. -- .z. .. . - -. . .. .- . - . . .- - . ..-. _ - - .-. -. - .
BYRON LIST OF TABLES No. Title Pale 1 Airborne Particulates and lodine 131, loc at i on s By-01, 02, 03, 04 . . . . . . . . . . . . . . . 97 2 Airborne Particulates and lodine-131, loc a t i o n s By -05 , 06 , 07 , 08 . . . . . . . . . . . . . . . 98 3 Airborne Particulates and lodine-131, Loc ati ons 8y 21, 22, 23, 24 . . . . . . . . . . . . . . . 101 4 Airborne Particulates, Quarterly Com;osites of Weekly Collections ................... 103 5 Gamma Radiation, as Measured by TLDs . . . . . . . . . . . . . 105 6 Milk............................. 109 7 Fish, Edible Portions .................... 112 i 8 . Vegetables . . . . . . . . . . . . . . . . . . . . . . . . . . 113 9 Surface Water ........................ 114 10- Wel l Wa t e r . . . . . . . . . . . . . . . . . . . . . . . . . . 116 i 11 Bo t t om S ed i m en t s . . . . . . . . . . . . . . . . . . . . . . . 118 Milch Animal, Nearest Re-idence and Nearest Cattle Census. .- . 119 L 94
BYRON
1.0 INTRODUCTION
J l The following constitutes the annual sumation of sample results 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 prograia and to be expected in the environmental media sampled. 1
- For all gamma isotopic analyses, spectrum is computer scanned from 80 to 2048 kev. Specifically included are Mn 54, Co-58 Fe-59, C0-60, 2n-65, Zr-95, Nb-95, Ru-103, Ru-106,1-131, Ba-La-140, Cs-134, Cs-137, Ce 141, and Ce-144.
Naturally occurring gamma-emitters, such as K-40 and Ra daughters, are fre-t 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 otherwi se, the less than value ("<") reported under "Other Gammas" is for C0-60 and may be higher or lower for other radionuclides. All concentratiou, except gross beta, are decay corrected to the time of
. collection.
. Deviations from Scheduled Sampling and Corrective Actions Taken l All . samples were collected within +.he scheduled period unless noted otherwise in the Listing of. Missed Samples.
Unusual Environmental Measurements Sample Date-Type Location Collected Comments i 1 95 i
BYRON ! i 2.0 LISTING OF MISSED SAMPLES Expected Collection Sample Type Location Date Reason Mil k BY-25 01-02-90 Dairy destroyed in fire. Surface Water BY-09 January River frozen. l Mil k BY-25 02-05-90 Dairy destroyed in fire. ,
- l. Air Particulate 'BY-24 05-07-90 Sample lost in the field.
Air Particulate BY-8 10-29-90 Sample lost in the field. t 96 L .. . . . . - , . . .. .- -.- - - . . . . - .-- - , , ..-- - -
BYRON Table 1. Airborne Particulates and lodine-131a Weekly Collection:2 Units: 10- pC1/m3 Byron Stillman Valley Near Site E Paynes Point BY-01 BY 02 (C) BY 03 BY-04 Week Volyme Gross ~Volyme Gross Volume Gross Volyme Gross Ending (ms) Beta (m3) Beta (m3) Beta (mJ) Beta 01-08-90 242 2.810.4 231 2.110.4 238 2.620.4 237 3.010.4 01 15-90 288 3.0t0.4 286 3.0t0.4 288 2.910.4 288 2.920.4 01-22-90 285 2.420.3 284 2.610.3 283 2.110.3 283 2.720.4 01-29-90 239 2.310.4 285 2.220.3 285 0.720.2 285 1.820.3 02-05-90 286 2.0t0.3 292 1.610.3 287 1.910.3 286 2.210.3 02-12-90 287 2.110.3 280 2.420.3 286 2.410.3 286 2.520.3 02 19 90 282 2.210.3 283 2.4t0.3 283 2.220.3 283 2.210.3 1 02-26-90 288 2.520.4 288 2.410.4 287 2.610.4 287 2.120.3 l 03-05-90 284 2.420.3 290 2.420.3 285 2.810.4 285 2.420.3 03 12-90 286 1.810.3 279 1.610.3 286 2.010.3 286 1.520.3 03-19-90 285 1.320.3 291 1.6*0.3 285 1.610.3 285 1.720.3 03-26 90 286 2.110.2 280 2.110.2 285 2.010.2 285 2.210.2 04-02-90 287 1.310.3 297 0.7t0.2 290 1.210.3 290 1.210.3 1st Qtr reanis.d. 2.220.5 2.110.6 2.110.6 2.210.5 04-09-90 285 1.720.3 274 1.120.3 283 1.910.3 283 1.710.3 04-16 90 284 2.310.3 285 2.220.3 2 84 2.010.3 284 2.210.3 04-23-90 284 1.7t0.3 284 2.310.3 285 1.9t0.3 285 2.410.3 04-30-90 288 1.510.2 287 1.6t0.2 287 1.620.2 287 1.7*0.2 05-07-90 285 1.120.3 294 1.920.3 287 2.0t0.3 286 1.620.3 05-14 90 284 1.220.3 279 1.5*0.3 282 1.710.3 283 1.820.3 05-21-90 284 0.710.2 290 1.110.2 284 1.220.2 284 1.420.2 05-28-90 288 1.410.4 281 1.820.4 288 2.410.4 288 2.420.4 06-04-90 284 0.810.3 293 1.410.3 286 1.420.3 286 1.110.3 06-11-90 282 1.410.3 272 1.210.3 279 1.210.3 279 1.210.3 06-18-90 289 1.6t0.4 285 1.410.4 279 1.620.4. 286 1.510.4 06-25-90 287 1.120.3 292 1.220.3 300 1.020.3 290 1.110.3 07-02-90 285 1.210.3 298 1.6t0.3 287 1.510._3_ 289 0.810.3
-2nd Qtr meants.d. 1.410.4 1.620.4 1.610.4 1.610.5 a lodine-131 concentrations are <0.07 pC1/m3 unless noted otherwise.
97
BYRON l l Table 1. Airborne Particulates and lodine-131a (continued) Byron Stillman Valley Hear Site E Paynes Point BY-01 BY-02 (C) BY-03 BY-04 Week Volume Gross Volyme Gross Volyme Gross Volyme Gross Ending (m3) Beta (m3) Beta (m4) Beta (m3) Beta 07-09-90 2B4 2.310.3 270 2.410.4 284 1.610.3 284 2.410.3 07-16-90 284 1.310.3 292 1.910.3 278 2.110.4 278 2.010.3 07-23-90 285 2.310.3 285 2.310.3 286 2.410.4 286 2.210.3 07-30-90 288 3.010.4 283 3.010.4 290 2.820.4 290 3.310.4 08-06-90 282 1.610.4 289 2.310.4 282 1.820.4 282 2.110.4 08-13-90 288 1.710.3 281 1.510.3 288 1.310.3 288 0.610.2 08-20-90 282 1.510.3 288 1.320.3 281 1.310.3 281 1.410.3 08-27-90 289 1.820.3 283 1.410.3 289 1.310.3 289 1.810.3 09-04-90 325 2.210.3 332 2.210.3 325 2.410.3 325 1.210.3 09-10-90 245 2.910.4 238 2.210.4 244 2.610.4 244 2.910.4 09-17-90 284 2.810.4 290 1.710.4 284 2.820.4 284 2.610.4 09-24-90 286 1.210.3 281 1.110.3 286 1.610.3 286 1.210.3 10-01-90 288 1.510.3 298 1.810.3 292 1.910.3 290b 1.910.3 3rd Qtr meants.d. 2.010.6 1.9 0.5 2.010.6 2.010.7 10-08-90 284 2.610.4 273 2.310.4 280 1.510.4 281 2.110.4 10-15 91 285 2.010.3 292 1.910.3 286 1.610.3 286 2.110.3 10-22-90 286 2.010.3 285 1.710.3 286 1.910.3 278 2.010.3 10-29-90 287 2.210.3 283 2.010.3 288 1.610.3 288 1.710.3 11-05-90 286 2.120.3 294 2.310.5 286 2.510.4 286 2.710.4 11-12-90 286 2.010.3 278 1.810.3 285 1.810.3 285 2.210.4 11-19-90 284 2.510.4 285 2.410.4 283 2.610.4 284 2.610.4 11-26-90 288 2.910.4 285 2.610.4 289 2.710.4 289 2.610.3 12-03-90 287 2.210.3 295 1.210.3 286 1.910.3 286 1.910.3 12-10-90 2B4 2.120.4 273 2.220.4 274 2.710.4 285 2.210.4 12-17-90 286 2.410.3 289 2.020.3 295 2.420.3 231 2.810.4 12-24-90 283 4.310.4 284 3.910.4 283 4.510.4 283 4.110.4 12-31-90 292 2.710.4 329c 3.210.4 323c 3.710.4 323c 2.720.4 4th Qtr meants.d. 2.510.6 2.310.7 2.410.9 2.410.6 a lodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. Volume is estimated; timer reading seems in error. c Collected 01-01-91. 98
BYRON Table 2. Airborne Particulates and lodine-131a Collection.2 Weekly Units: 10- pC1/mJ Near Site S Oregon Mt. Morris Leaf River BY-05 BY-06 BY-07 (C) BY-08 (C) Week Volume Gross VoTume Gross Vol me Gross o Tolume Gross Ending (m3) Beta (m3) Beta (m ) Beta (m3) Beta 01-08-90 238 2.820.4 245 3.010.4 246 2.6i0.4 244 2.810.4 01-15-90 288 3.1t0.4 286 2.810.4 286 2.810.4 286 3.110.4 01-22-90 283 2.310.3 285 2.6t0.3 285 1.610.3 284 1.810.3 01-29-90 288 1.910.3 285 2.120.3 285 1.810.3 285 1.820.3 02-05-90 286 1.9i0.3 285 2.220.3 285 2.210.3 285 1.8t0.3 02-12-90 287 2.510.3 287 2.510.3 287 2.220.3 289 1.910.3 02-19-90 283 2.210.3 282 2.310.3 282 2.210.3 283 2.110.3 02-26-90 287 2.7t0.4 288 2.610.4 288 2.710.4 2 88 2.910.4 03-05-90 285 2.6i0.4 283 2.420.3 283 2.210.3 283 2.510.4 03-12-90 286 1.410.3 286 1.810.3 286 1.520.3 286 1.910.3 03-19-90 285 1.310.3 285 1.410.3 285 1.210.3 285 1.420.3 03-26-90 285 2.310.2 285 2.120.2 286 1.710.2 286 1.910.2 04-02-90 289 1.010.3 286 1.320.3 284 1.310.3 286 1.8i0.3 1st Qtr meants.d. 2.220.6 2.220.5 2.0i0.5 2.110.5 04-09-90 283 1.610.3 286 1.910.3 286 1.710.3 286 2.0 0.3 04-16-90 284 2.210.3 285 2.210.3 285 1.810.3 285 1.910.3 04-23-90 284 1.810.3 284 2.210.3 284 1.520.3 284 2.210.3 04-30-90 288 1.7t0.2 287 1.720.2 287 1.510.2 287 1.410.2 05-07-90 286 1.620.3 285 1.910.3 284 1.410.3 285 1.5t0.3 05-14-90 283 2.020.3 285 2.320.3 285 1.7t0.3 285 1.620.3 05-21-90 285 1.210.2 285 1.320.2 285 1.010.2 285 1.110.2 05-28-90 288 2.510.4 287 2.3 0.4 287 1.910.4 287 2.510.4 06-04-90 286 0.920.3 285 1.320.3 285 0.910.3 285 1.110.3 06-11-90 281 1.120.3 28? 1.610.3 282 0.710.3 282 1.020.3 06-18-90 281 1.710.4 289 1.120.4 289 1.210.4 289 1.510.4 06-25-90 293 1.420.3 287 1.3 0.3 287 1.010.3 287 1.410.3 07-02-90 290 1.2 0.3 282 1.6i0.3 284 0.9!0.3 284 1.710.3 2nd Qtr meants.d. 1.620.5 1.710.4 1.310.4 1.610.4 a lodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. 99
BYRON ~ r Table 2. Airborne Particulates and lodine-131a (continued) Near Site S Oregon Mt. Morris Leaf River BY-05 BY-06 __ _ BY-07 (C) _ BY-08 (C) Week Gross Gross Volgme Gross Vol me Gross Volgme Volgme
- . . . Ending (m) Beta (m) Beta (m ) Beta (m) Beta 67-09 285 2.410.3 284 2.420.3 284 1.310.3 284 2.0*0.3 07-16-90 278 2.110.4 278 1.410.3 278 1.010.3 278 1.420.3 07-23-90 .285 2.310.3 286 2.3t0.3 287 2.110.3 287 2.310.3 07-30-90 291 .3.310.4 289 3.510.5 289 2.610.4 289 3.010.4 08-06-90 281 2.410.4 282 1.910.4 282 1.910.4 281 1.410.3 08-13-90 288 1.710.3 288 1.810.3 286 1.010.3 289 1.810.3 08-20-90 281 1.610.3 282 1.620.3 282 1.310.3 282 1.1t0.3 08-27-90 289 1.4i0.3 288 -1.710.3 289 1.510.3 289 1.410.3 !
09-04-90 -326 2.720.3 325 2.810.3 324 1.910.3 323 2.110.3- i
'09 10-90 244 3.010.4 245 2.4*0.4 246 2.220.4 24 3 2.620.4- !
09-17-90 -284 3.420.5 284 3.210.41 284 2.520.4 '284 2.510.4 { 09-24-90 286 - 1.310.3_ 287 1.310.3 287 1.310.3 287 1.4t0.3 1
~10-01-90 291 1.920.3 287 2.0t0.3 286 1.520.3 285 1.7*0.3 ]
3rd - Qtr meant s.d. 2.310.7 2.210.7 1.710.5 1.910.6 ; , J 10-08-90 281 2.920.4 285 2.910.4- 286 2.410.4 287 2.210.4 10-15-90 ~286 0.810.3 - 285 2.320.3 283- 2.120.3 - 284 .2.0t0.3
.-10-22 286 1.810.3 286 2.210.3 287 2.010.3 - 287 2.010.3 J 10-29 - 288 2.110.3 .287 2.010.3 287 2.110.3 NSb-. .- 1 11-05-90 - 285' 2.5t0.4 285 3.420.4 '285 3.310.4 284 3.2t0.4 1 11-12-90= 286 2.220.3 286- 2.3t0.4 287 2.310.4 288 2.510.4 311-19 90 284 3.110.4 285 3.520.4 285 2.720.4 285 2.520.4 11-26-90' 289. 3.210.4 286 3.420.4 -286 2.010.3- 286 -3.220.4 12-03 287 . 1.910.3 288 0.4 20. 2c .- 288 1.7t0.3- 288 l'.7 t0.3 ,
1.210.3 2.010.4 12-10 284 - 2.420.4 284 283L 282_ 2.410.4 12-17-90 ~ 265 - 2.520.4 285 2.410.3 287 1.220.3~ 288 '2.4i0.3: , 12-24-90 283' -
' 4.5t0.4 --
283 3.810.4 283' . 2.910.4 283 4.920.4 - 12-31-90 -322d 2.510.4' . 291 3.520.4 291- 2.210.4 289' 3.2t0.4 4th.Qtr meants.d.- 2.520.9_ 2.611.0 2.210.5- 2.710.9 i
? lodine-131 concentrations are '<0.07 pC1/m3 unless noted otherwise.
b NS = No sample;. filter holder broken; sample lost tin field. Filter very light; pump was frozen and replaced with spare. < ~ [ Coll ected ' 01-01-91. l2 5 h 100 . m > !Li ,;-..*.....,z-- ...m.,,,...m..,.. ___---.,...,,,,m..-,_,,._._ .._...m,~..,m_,,-c ___. ,,,,.._s;
i BYRON Table 3. Airborne Particulates and lodine-131a i l Collection:2 Weekly Units: 10- pC1/m3 BY-21 BY-22 BY-23 BY-24 , Week Volume Gross Volyme Gross Volyme Gross Volyme Gross Ending (m3) Beta (m3) Beta (m3) 8 eta (m3) Beta 01-08-90 244 2.910.4 240 3.110.4 240 3.320.4 240 2.920.4 l 01-15-90 288 3.120.4 288 3.020.4 288 2.510.3 288 3.120.4 l 01-22-90 283 2.210.3 283 2.420.3 283 3.020.4 283 2.520.3 ' 01-29-90 285 2.110.3 285b 2.110.3 285 2.220.3 285 2.220.3 02-05-90 286 2.410.3 286 2.3t0.3 286 2.210.3 286 2.420.3 02-12-90 287 2.420.3 287 2.710.3 287 2.220.3 287 0.620.2 ' 02-19-90 282 2.310.3 282 2.720.4 282 2.310.3 283 0.620.2 02-26-90 288 2.720.4 288 2.920.4 287 2.520.4 287 2.710.4 03-05-90 284 2.820.4 2 84 3.020.4 284 2.620.4 285 2.720.4 ; 03-12-90 286 1.810.3 286 1.710.3 286 1.920.3 286 1.710.3 ! 03-19-90 285 1.620.3 285 1.310.3 285 1.510,3 285 1.610.3 03-26-90 285 2.110.2 286 2.420.2 285 2.310.2 285 2.110.2 'l 04-02-90 287 1.210.3 287 1.620.3 288 1.6t0.3 288 1.610.3 1st Qtr meants.d. 2.310.5 2.410.6 2.320.5 2.010.8 04-09-90 285 2.110.3 285 2.010.3 285 2.010.3 284 2.110.3 ) 04-16-90 284 2.220.3 284 1.810.3 284 2.620.3 284 2.310.3 04-23-90 284 2.110.3 284 2.220.3 284 2.010.3 284 2.110.3 04-30-90 287 1.720.2 288 1.620.2 287 2.010.2 288 1.820.2 05-07-90 285 1.710.3 285 2.310.4 286 1.920.3 NDC 05-14-90 284 1.810.3 283 3.5 0.4 283 1.910.3 283 1.910.3 ; 05-21-90 284 1.010.2 285 1.010.2 285 1.010.2 285 1.120.2 i 05-28-90 288 2.120.4 287 2.510.4 287- 2.410.4 288 2.210.4 ; 06-04-90 285 1.310.3 285 1.310.3 285 1.420.3 285 1.410.3 06-11-90 282 1.220.3 281 1.510.3 281 1.1t0.3 281 1.410.3 06-18-90 281 1.610.4 281 1.420.4 281 1.910.4 281 1.810.4 l 06-25-90 294 1.310.3 294 1.620.3 293 1.610.3 293 1.520.3 07-02-90 286 1.420.3 286 2.010.3 287 L710.3 287 1.920.3 2nd Qtr meants.d. 1.610.4 1.910.6 1.810.5 1.810.4 a Iodine-131 concentrations are <0.07 pCi/m3 unless noted otherwise. b Timer out of order; volume is assumed. c ND = No data; Sample lost in the field. l 4 101
BYRON Table 3. Airborne Particulates and lodine 131a (continued) BY-21 BY-22 __ BY-23 BY-24 Week Volyme Gross Volyme Gross Vol' me Gross Volyme Gross Ending (mJ) Beta (m3) Beta (m) Beta (m3) Deta 07-09-90 284 2.820.4 284 2.310.3 287 3.620.4 287 2.510.3 07-16-90 283 1.610.3 283 1.310.3 279 2.010.3 279 1.510.3 07-23-90 285 2.810.4 285 2.310.4 285 3.010.4 285 2.910.4 07-30-90 289 3.620.5 289 3.510.4 290 4.720.5 290 2.910.4 08-06-90 282 2.210.4 282 2.220.4 282 3.310.4 282 2.820.4 08-13-90 288 2.020.3 288 1.510.3 288 1.410.3 288 1.410.3 08-20 282 1.410.3 282 1.410.3 282 1.310.3 2 82b 1.Si0.3 08-27-90 289 1.810.3 289 1.610.3 289 1.710.3 289b 1.710.3 09-04-90 325b 1.210.3 325 2.610.3 325 2.320.3 325 2.310.3 09-10-90 24 5 2.910.4 24 5 2.610.4 24 5 2.520.4 244 2.610.4 09-17-90 284 2.510.4 284 3.li0.4 284 3.010.4 284 3.220.4 09-24-90 286 1.310.3 285 1.610.3 286 1.910.3 286 1.610.3 10-01-90. 288 1.810.3 290 1.610.3 290 1.810.3 290 1.9*0.3 3rd Qtr meants.d. 2.110.7 2.120.7 2.511.0 2.210.6 10-08-90 283 2.410.4 282 2.320.4 282 2.010.4 282 2.310.4 i 10-15-90 285 2.0t0.3 285 1.920.3 285 1.810.3 285 1.820.3 10-22-90 286 1.410.3 286 1.910.3 286 2.010.3 2 86 2.710.4 10-29-90 287 1.620.3 287 2.110.3 287 1.910.3 288 2.120.3 11-05-90 286 2.710.4 286 3.310.4 286 3.410.4 286 2.410.4 11-12-90 286 1.710.3 286 2.510.4 286- 2.0t0.3 286 2.310.4 , 11-19-90 284 3.3t0.4 284 2.910.4 284 2.610.4 2 84 2.4i0.4 l 11-26-90 '288 3.210.4 288 2.610.4 288 1.310.3 288b 3.020.4 12-03-90 287- 2.1*0.3 275 1.920.3 287 2.010.3 287 1.610.3 12-10-90 284 2.210.4 110c <1.1 284 2.310.4 2 84 2.610.4 i 12-17-90 286- 2.420.3 286 2.310.3 286 2.310.3 285 2.5*0.4 l 12-24-90 283 2.6t0.4 283C <0.4 283 0.6i0.3 283b 4.610.4 : 12-31-90 292 3.620.4 319d 1.810.3 319d 3.220.4 320d 4.0t0.4 4th Qtr meants.d. 2.410.7 2.310.5 2.120.7 2.620.8 l Timer replaced; volume was estimated. Iodine-131 concentrations are <0 , c Pump f ailure; replaced with spare. Collected 01-01-91. 102
BYRON Table 4. Airborne Particulates l Collection: - Units: pCi/mparterlycompositesofweeklycollections i Volyme Other Location. Lab Code (m3) Cs-134 Cs-137 Gammasa 1st Quarter 1990 BY-01 BYAP-1899 3625 e0.01 <0.01 <0.01 l BY-02 1900 3666 <0.01 <0.01 <0.01 BY-03 1901 3668 <0.01 <0.01 <0.01 BY-04 1902 3666- <0.01 <0.01 <0.01 BY-05 1903 3670 <0.01 <0.01 <0.01 BY 1904 3668 <0.01 <0.01 <0.01 BY 1905 3668 <0.01 <0.01 (0.01 BY-08 1906 3670 <0.01 <0.01 <0.01 BY-21 1907 3670 <0.01 <0.01 <0.01 BY 22- 1908 3667 <0.01 <0.01 <0.01 BY-23 1909 3666 (0.01 <0.01 <0.01 BY-24 1910 3668 <0.01 <0.01 <0.01 V , 2nd Quarter 1990 BY-01 BYAP-2114 3709 <0.01 <0.01 <0.01 BY-02 2115 3714 <0.01 (0.01 <0.01 BY-03 2116 3711- <0.01 <0.01 <0.01 _ BY 04 2117 3710 - < 0. 01 - <0.01 (0.01 BY-05 2118 3712 <0.01 (0.01 (0.01 BY-06 2119 3709 <0.01 (0.01 <0.01 BY-07 2120 3710- <0.01 <0.01 <0.01 JBY-08 2121 3711 (0.01 <0.01 <0.01 BY 2122 3709 <0.01 <0.01 <0.01' BY-22 2123 3708 <0.01 (0.01 <0.01 BY-23 2124 3708 <0.01 _ 0.01
< <0.01 BY-24 2125- -3423 -<0.01 < 0.01 <0.01 a See Introduction.
r i 303 m._ ._. . - - . - _ m- _ _ . _ _ _ _ _ - . _ _ . _ _ _ _ _ -
. - - ~ . _ . . _ _ . _ _
.- - . . - - . . . - _ - . - - - - . . __ . - - . - - _ - . ~ _ . . .-_ - -
BYR0!i Table 4. Airborne Particulates Collection: Qyarterly composites of weekly collections Units: pCi/m3 Volyme Other Location Lab Code (mJ) Cs-134 Cs-137 Gammasa 3rd Quarter 1990 BY-01 BYAP-2224 3710 <0.01 <0.01 <0.01 BY-02 2225 3710 <0.01 <0.01 <0.01 BY-03 2226 3709 <0.01 <0.01 <0.01 BY-04 2227 3707 <0.01 <0.01 <0.01 BY-05_ 2228 3709 <0.01 <0.01 <0.01 BY-06 2229 3705 <0.01 <0.01 <0.01 , BY-07 2230 3704 <0.01 <0.01 <0.01 BY-08 2231 3701 <0.01 <0.01 <0.01 BY-21 2232 3710 <0.01 <0.01 <0.01 i BY-22 '2233 3712 <0.01 <0.01 <0.01 BY-23 2234 3712 <0.01 <0.01 <0.01 BY-24 2235 3711 <0.01 <0.01 <0.01 l _4th Quart er 1990 BY-01 BYAP-2468 -3718 (0.01 <0.01 <0.01 ' BY-02 2469 3745 <0.01 <0.01 <0.01 BY-03 2470 3744 <0.01 <0.01 <0.01 BY-04 2471 3685 <0.01- <0.01 -<0.01 BY-05 2472 3746 <0.01 (0.01 <0.01 BY-06 2473 3716 (0.01 <0.01 <0.01 BY-07 2474 3718 <0.01 <0.01 <0.01 BY-08 2475 3431 <0.01 <0.01- <0.01 i- BY-21 2476' 3717 <0.01 <0.01 <0.01 ,' BY-22 2477 3557 <0.01 <0.01 <0.01 BY-23 2478- 3743 <0.01 <0.01 <0.01 BY-24 -2479 37'4 <0.01 <0.01 _0.01 e_ a See' Introduction. 1; l-104
BYRON Table 5. Germa Radiation, as Measured by Thermoluminescent Dosimeters (TLDs) STANDARD RADIOLOGICAL MONITORING PROGRAM 1st__ Quarter 2nd Ouarter 3rd Quarter 4th Quarter Date Placed: 01-02-90 04-02-90 07-02-90 10-01-90 Date Removed: 04-02-90 07-02-90 10-01-90 01-01-91 Days in the field: 90 91 91 92 Location Average mR/Qtr. Offsite Indicator Locations BY-01 Byron 11.321.1 11.710.8 11.021.0 14.310.9 BY hearsite East 14.821.0 13.910.7 14.811.2 16.120.8 BY Paynes Point 13.621.2 15.820.9 14.421.1 17.021.0 BY Hearsite South 16.321.0 16.611.6 16.121.0 18.720.9 BY Oregon 13.321.2 _13.221.0 _13.521.0 14.520.8 Hean i s.d. 13.921.8 14.212.0 14.011.9 16.121.8 Onsite Indicator Locations BY Onsite North 11.421.0 11.0 1.2 .10.920.9 11.821.2 BY Onsite ESE 16.821.0 16.620.8 17.011.4 18.510.8 BY Onsite South 15.511.4 15.510.9 15.811.3 16.910.9 BY Met. Tower 14.4il.4, 14.811.0 14.221.0 16.511.2 Mean s.d. 14.522.3 14.522.4 14.512.6 15.912.9 Background Locations l BY-02 Stillman Valley 12.211.0 12.420.7 12.420.9 15.721.0 BY ht. Morris 14.021.2 15.211.0 14.011.0 16.521.3 BY Leaf River 13.720.7 13.7*0.8 13.920.9 14.521.3 Mean 2 s.d. 13.3t1.0 13.821.4 13.410.9 15.611.0 105 W ^ ' " - 4
BYRON Table 5. Gamma Radiation, as Measured by TL0s (continued) SPECIAL PROGRAM Inner Ring, Near Site Boundary, Indicator Locations 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 01-02-90 04-02-90 07-02-90 10-01-90 Date Removed: 04-02-90 07-02-90 10-01-90 01-01-91 Days in the Field: 90 91 91 92 Location Average mR/Qtr. BY-101-1 15.611.5 15.911.2 15.411.3 16.620.9 BY-101-2 14 .911.5 16.3 1.5 14.521.2 18.211.3 BY-102-1 15.4 0.7 17.521.1 15.411.1 18.511.2 BY-102-2 13.710.7 17.011.1 15.211.5 16.911.3 BY-103-1 14.211.1 15.211.1 14.711.2 15.021.4 BY-103-2 14.510.9 16.510.9 14.511.1 17.610.8 BY-104-1 15.221.4 17.011.0 15.311.3 16,821.3 BY-104-2 15.511.4 17.211.1 15.121.4 17.711.1 BY-105-1 15.911.1 17.411.3 16.021.2 17.711.6 BY-105-2 15.421.1 17.210.9 15.211.1 18.0tl.0 BY-106-1 15.921.1 16.411.0 16.211.4 17.311.2 BY-106-2 13.621.1 15.111.2 13.611.3 15.811.1 BY-107-1 15.811.5 17.721.9 16.621.2 20.211.5 BY-107-2 15.921.3 17.520.8 15.911.0 17.4 0.8 BY-108-1 16.821.1 17.110.8 17.111.5 18.211.2 BY-108-2 13.911.2 13.721.0 13.511.1 13.911.1 BY-109-1 14.720.8 14.621.3 14.711.0 16.411.2 BY-109-2 16.011.3 13.711.3 14.011.3 14.111.7 BY-110-1 14.210.9 15.210.8 13.820.8 16.411.0 BY-110-2 14.310.9 14.711.6 14.610.8 14.911.3 BY-111-1 15.710.9 16.4 1.0 15.510.8 17.310.9 BY-111-2 15.410.8 13.011.4 16.4 0.9 16.8 1.5 BY-112-1 15.811.0 15.921.0 14.911.0 16.621.0 BY-112-2 14.110.8 14.211.3 14.410.8 15,621.2 BY-113-1 15.111.1 15.711.1 14.521.0 16.211.3 BY-113-2 13.510.9 12.811.0 13.211.0 15.411.1 BY-114-1 12.610.9 13.210.9 12.021.0 14.321.0 BY-114-2 15.111.0 14.511.1 14.820.8 16.211.0 BY-115-1 14.321.4 13.911.2 14.211.3 15.5 1.3 BY-115-2 14.111.0 14.7 0.7 14.010.8 16.7 0.9 BY-116-1 12.620.7 12.621.1 12.110.9 13.521.0 BY-116-2 14.910.9 15.120.8 14.610.8 17.510.8 Mean i s.d. 14.921.0 15.411.6 14.711.2 16.511.5 106
BYRON Table 5. Gamma Radiation, as Measured by TLDs (continued) . s SPECIAL PROGRAM Outer Ring. Near 5 Mile Radius. Indicator Locations ) 1st Quarter -2nd Quarter 3rd Quarter 4th Quarter
~Date Placed: 01-02-90 04-02-90 07-02-90 10-01-90 Date Removed: . 04-02 07-02-90 10-01-90 01-01-91 Days:in_the Field: 90 91 91 92 Location Average mR/Qtr.
^
BY-201-1 15.410.7 15.011.2 12.620.7 16.111.0
- BY-201-2 17.211.2 16,910.9 16.211.0 17.510.8 BY-202 13.211.3 13.811.2 12.811.3 15.121.2 BY-202-2 15.611.0 17.020.8 14.610.8 18.211.3
. BY-203-1 13.611.1 10.510.9 10.710.9 11.720.9 .
BY-203 11.811.2 14.811.3 13,710.9 16.310.8
= BY-204-1= 12.021.1 11.911.1 11.821.1 13.211.0
- BY-204-2 14.810.9 17.210.9 15.320.9 18.921.1
- BY-205-1 15.020.9 16.011.2 15.711.2 17.011.2 BY-205 14.711.1 15.510.7 14 .221.1 16.210.9 BY-206-1 16.111.0 16.811.1 16.411.2 17.010.8 BY-206-2 17.ltl.la 15.110.9 15.311.1 16.811.1 BY-207-1L 16.610.9 17.111.0 16,920.8 17.921.2 BY-207-2. 14.820.9 15.010.8 14 .711.1 16.711.0 BY-208-1= 18.511.1 .17.310.8 18.410.9 19.9 1.0 BY-208-2' 16.011.1 16.111.2 15.911.2 16,911.2 BY-209-1 16.910.8 16.611.0 15.110.9. 18.511.2 .
BY-209-2 13.910.8 13.611.0 15.521.0 14.910.9
-BY-210-1 15.521.0 15.810.7 16.011.1 17.710.8 L BY-210-2 15.820.9 15.610.9 15.610.9 17.310.9 '
BY-211-l' 15.811.2 13.911.2 15.210.8- 16.211.2 l~ h BY-211-2 16.921.1 16.811.1 17.011.0 17.410.9 BY-212-1 16.711.0 15.510.9 -16,821.0 17.210.9, BY-212-2 16.411.3' 18.310.7 16.411.2 18.821.6' - BY-213-1. 15.6 1.0 14.011.2 15.721.0 15.821.5 BY-213;2 17.511.3- 17.710.9 17 .311.0 19.111.0 BY'214-1
- -14.920.9 14.510.9 14.711.0 15.510.8 BY-214 16.311.2 16.110.7 15.511.0 -17.510.8-
' BY-215-1 15.211.0 15.310.8 15.011.2 16,711.1- ,
Bi-215-2 .16.0il .0 17.011.0 16'.010.9 18.511.1 BY-216 17.011.2 14.911.3 16.521.2 16.011.7
- BY-216 16.121.1 -17.0i0.7 15.611.2 18.011.1 lMean i s.d.- 15.6 1.5 15.611.7 15.311.6 16.911.7 a Spare No.1 used at location 206-2.
107 t
'I .A,', .-i-#..,,--.,.....~.i,,..-..._..-, , , .L.,._-.--,-.~..i.._.-.L,_-----._._a..--.,_.... .
BYR0f4 Table 5. Ganuna Radiation, as Measured by TLDs (continued) RESTRICTED AREA *t0NITORING PROGRAM 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 01-02-90 04-02-90 07-02-90 10-01-90 Date Removed: 04-02-90 07-02-90 10-01-90 01-01-91 Days in the Field: 90 91 91 92 Locationa Average mR/Qtr. BY-302-1 , 16.111.1 12.310.8 14.410.9 12.111.1 a Description of location. BY-302-1 Security Gatehouse (parking lot). 108
BYRON Table 6. Mil k Collection: Monthly; semimonthly during grazing season (May-October) Units : pCi/L Collection Other Date Lab Code 1-131 Cs-134 Cs-137 0amasa Warren Danakas Dairy Farm BY-15 01-02-90 BYMI-4358 <0.5 <5 <5 <10 02-05-90 4449,50 <0.5 <5 <5 <10 03-05-90 4514.5 <0.5 <5 <5 <10 04-02-90 4572 <0.5 <5 <5 <10 05-07-90 4684 <0.5 <5 <5 <10 05-21-90 4759,60 <0.5 <S <5 <10 06-04-90 4812 <0.5 <5 <5 <10 06-11-90 4849 <0.5 <5 <5 <10 07-02-90 4966 <0.5- <5 <5 <10 {- 07-16-90 5043 <0.5 <5 <5 <10 08-06-90 5146 <0.5 <5 <5 <10 08-20-90 5227 <0.5 <5 <5 <10 09-04-90 5298 <0.5 <5 <5 <10 09-17-90 5372 <0.5 <5 <5 <10 10-01-90 5454,5 <0.5 <5 <5 <10 m - 10-15-90 5525 <0.5 <5 <5 <10
- 11-05-90 5619 <0.5 <5 <5 <10 F
{ 12-03-90 5678,9 <0.5 <5 <5 <10 Richard Oltmann Dairy Farmb BY-25 01-02-90 NSc .. .. .. .. 02-05-90 NSc .. .. .. .. 03-19-90 BYMI-4556 <0.5 <5 <5 <10 04-02-90 4576 <0.5 <5 <5 <10 05-07-90 4687 <0.5 <5 <5 <10 05-21-90 4763 <0.5 <5 5 <10 04-90 4816 <0.5 <5 s5 <10 06-18-90 4900 <0.5 <5 <5 <10 07-02-90 4968 <0.5 <5 <5 <10 07-16-90 5047 <0.5 <5 <5 <10 08-06-90 5143,9 <0.5 <5 <5 <10 08-20-90 523) <0.5 <5 <5 <10
;_ 09-04-90 53r,0 <0.5 <5 <5 <10 09-17-90 53/4 <0.5 <5 <5 <10 10-01-90 5457 <0.5 <5 <5 <10 10-15-90 5527 <0.5 <5 <5 <10 11-05-90 5621 <0.5 <5 <5 <10 12-03-90 5681 <0.5 <5 <5 <10 a
b See Introduction. c Replacement dairy for Bill Leupkes Farm, which was destroyed in a fire. NS = No sample available; dairy destroyed in fire. 109
BYRON Table 6. Milk (continued) Collection Other Date Lab Code 1-131 Cs-134 Cs-137 Gammasa Whitten Holsteins BY-17 01-02-90 BYM1-4359 <0.5 <5 <5 <10 - 02-05-90 4451 <0.5 <5 <5 <10 03-05-90 4516 <0.5 <5 <5 <10 04-02-90 4573 <0.5 <5 <5 <10 05-07-90 4685 <0.5 <5 <5 <10 65-21-90 4761 <0.5 <5 <5 <10 06-04-90 4813,4 <0.5 <5 <5 <10 06-18-90 4898 <0.5 <5 <5 <10 Hazzard Dairy Farm BY-26b 07-16-90 BYMI-5044,5 <0.5 <5 <5 <10 07-23-90 5083 <0.5 <5 <5 <10 08-06-90 5150 <0.5 <5 <5 <10 08-20-90 5231 <0.5 <5 <5 <10 09-04-90 5301,2 <0.5 <5 <S <10 09-17-90 5375 <0.5 <5 <5 <10 10-01-90 -5458- <0.5 <5 <5 <10 10-15-90 5528 <0.5 <5 <5 <10 11-05-90 5622,3 <0.5 <5 <5 <10 12-03-90 5682 <0.5 <5 <5 <10 Kenneth Reeverts Farm BY-20 1 01-02-90 BYMI-4360- <0.5 <5 15 <10 02-05-90 4452 (0.5 <5 <5 <10 03-05-90 .4517 <0.5 <5 <5 <10 02-90 4574,5 <0.5 <5 <5- <10 05-07-90 4686 <0.5 <5 <5 <10 05-21-90 4762 <0.5 <5 <5 <10 06-04-90 4815 <0.5 <5 <5 <10 06-18-90 4899 <0.5 <5 < 5- <10 02-90 4967 <0.5 <5 <5 <10. 07-16-90 5046 <0.5 <5 <5 <10 08-06-90 5147 <0.5 <5 -<5 <10 08-20-90 5228,9 <0,5 <5 <5 <10 09-04-90' 5299 <0.5 <5 <5 <10 09-17-90 5373 .<0.5 <5 <5 <10 10-01-90 5456 <0.5 <5 <5 <10 110-15-90 5526 <0.5 <5 <5 <10 05-90 5620 <0.5 <5 <5 <10 12-03-90 5680 <0.5 <5 <5 <10 a b See Introduction. Whitten-Holsteins was replaced by Hazzard Dairy Farm on July 16, 1990. 110
BYRON Table 6. Milk (continued) Collection Other Date~ Lab Code 1-131 Cs-134 Cs-137 Gammasa Druien Dairy Farm BY-27b 10-01-90 BYMI-5459 <0.5 <5 <5 <10 10-15-90 5529 <0.5 <5 <5 <10 11-05-90 5624 <0.5 <5 <5 <10 12-03-90 5683 <0.5 <5 <5 <10 a See Introduction. New location; Kenneth Druien Dairy Farm, 2490 Route 64 West, Mt. Morris, Illinois; 5.3 miles at 236*. 111
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 05-07-90 BYF-1030 Bass <0.10 <0.10 <0.13 07-09-90 1142 Carp <0.10 <0.10 <0.13 07-09-90 1143 Sheepshead <0.10 <0.10 <0.13 10-15-90 1246 Walleye <0.10 <0.10 <0.13 11-19-90 1342,3 Wall eye <0.10 <0.10 (0.13 Upstream BY-13 05-07-90 BYF-1031 Bass <0.10 <0.10 <0.13 05-14-90 1038 Carpsucker <0.10 <0.10 <0.13 05-14-90 1039 Catfish <0.10 <0.10 <0.13 05-14-90 1040 Sheepshead <0.10 <0.10 <0.13 08-13-90 1191 Carp <0.10 <0.10 <0.13 11-19-90 1344 Bass <0.10 <0.10. <0.13 11-19-90 1345 Walleye <0.10 <0.10 <0.13 a See introduction. 112
____._.._.._:~_ _..-.___._.._..,__m._ . l l l BYRON j Table: 8._ Ve9etables ;
- Collection: Annually -
- Units: -pCi/9 wet weight
.. Coll ect i o'n Other
- 0 ate Lab Code Type 1-131a Cs-134 Cs-137 Gammasb
, , BY-19-1c . River Road ' Across from AP-1 , 27-90 BYVE-961 Rhubarb <0.06- <0.06 <0.08 <0.15 !
^
'08-27 962 ~ Zucchini -- <0.06 <0.08 <0.15 08-27 963 Cucumbers --
<0.06 <0.08 ' <0.15 i
'BY-'19-2c :Just' South of AP-5 108-27 BYVE-964 -Tomatoes ' :-- <0.06 <0.08 . <0.15- t 08-27-90 965 iYellow Squash. --
<0.06 (0.08 <0.15- .
- 08-27-90' 966,71 Cucumbers- --
<0.06' <0.08_ .<0.15
,08-27-90. 968E Rhubarb- <0.06' <0.06 - <0.08 <0.15-08-27-90' 969: Zucchini -- <0.06- <0.08 <0 .' 15 a
La Analysis for l-131' required for green leafy _ vegetation only.
- c Not-See required Introduction.Lby Technical -Specifications; _ water not: being used for-
_ irrigation.1 I
; -j l-L li 113-J
n ,. .. - . - .- , _ . - = - . - . - . - . ~ _ - . -
. BYRON 2
Table'9.. Surface Water-Units : pCi/L MONTHLY COMPOSITES OF WEEKLY COLLECTIONS Composite 1 Other Period' ; Lab- Code Cs-134 Cs-137 Gamasa Woodland Creek BY-09 :
. January, 90 NSb February. 90 .
BYSW-5142. <10 <10 <15-March, 90 5888- <10 <10 <15 April', 90: 6171 <10 <10- <15 May ,1.90 . 6618 <10 <10 <15 June. 90- 7036 <10 <10 <15 July, 90 7374 <10 <10 <15 : 4 August, 90- 7697. <10 <10 -<15 1
' September,.90 _ 8206 <10 <10 ~ <15 l
-October, 90~ 8561 <10: <10 <15 November,.90 '8831 <10 <10 <15 iDecember,:90 9308 <10 <10- <15 Downstream BY-12 January,L90- BYSW-5128 <10 <10- <15
-_ February.- 90 5378 <10 <10 <15
. March, 90 '
5889 <10 <10. <15 iApr11,90 6172,3 <10- <10 <15 May,L901 '6619,20 <10- <10 <15 June, 90: 7037L <10 <10 <15 July, 90 _ 7376 <10 <10 <15
' August, 90 7698 <10 <10 <15 September, .90 : 8207' . <10' <10 <15
' October =,- 90.- 8562 <10 <10 <15 Nov' ember, 90 8832 <10 <10 - <15-December., 90 9303L <10 <10 H
<15 Upstream- BY-13 -
-J anua ry ,190-- BYSW-4883- <10 <10 <15 February, 90L- 5379 <10 <10 <15-1 March,.90; 5890,1~. - <10- <10 <15 i
-: Apri1,: 90 -6174 <10 <10- <15 1 cMay, 90- 6621' <10 <10 <15
/ June,190- 17038- <10- <10-
<15 '
; July,90- 7375 <10 < 10 -- <15-
. August ,~'90 - 7699 <10 <10 <15 iSeptember,90~ 8208,9
<10 <10 <15
- .0ctober, 90' _8563- <10 <10 <15 November, 90 8833
- <10 <10 <15 December, 90- 9310 <10 <10- <15
' a'SeeJintroduction. .
-b1NSi= No sample available; river frozen.
114 e em *- ss-r r s . . - + - . _. ___-.u__s , _ _ _ _ _ _ ________________-__m_____-h - _ _ _ _ _ _ _
l BYRON Table 9. Surface Water (continued) QUARTERLY COMPOSITES OF WEEKLY COLLECTIONS Concentration (pCi/L) Composite Period Lab Code Tritium Woodland Creek BY-09 1st Quarter,1990 BYSW-5812 <200 2nd Quarter, 1990 6923 <200 3rd Quarter, 1990 8071 <200 4th Quarter, 1990 9077 <200 Downstream BY-12 1st Quarter, 1990 BYSW-5810,1 404277 I 2nd Quarter,1990 6924 <200 3rd Quarter, 1990 8072 3391101 4th Quarter, 1990 9075 12812132a Upstream BY-13(C) 1st Quarter, 1990 BYSW-5813 <200 2nd Quarter, 1990 6925 <200 3rd Quarter, 1990 8073,4 <200 4th Quarter, 1990 9076 <200 a Monthly composites were analyzed for tritium: October 5052122 pCi/L November 337 116 pCi/L December 2590 170 pCi/L 115
BYR0fl Table 10. Well Water Units: pCi/L. Collection : Composite of semimonthly collections. f10NTHLY COMPOSITE OF SEMIMONTHLY COLLECTIONS BY-14 BY-18 Other Gross Other ! Collection Gross Gammasa Lab Code Beta Cs-134 Cs-137 Gammasa Date Lab Code Beta Cs-134 Cs-137 BYWW-5130,1 <1.9 <10 <10 <15 January, 90 BYWW-5129 <2.0 <10 <10 <15
<15 5382 2.8 1.4 <10 <10 <15 February, 90 5380,1 2.6 1.0 <10 <10
<15 5893 <1.9 <10 <10 <15 March, 90 5892 <1.6 <10 <10 April, 90 6175 <2.4 <10 <10 <15 6176 2.0 1.2 <10 <15 <15
<15 6623 1.3 0.7 <10 <10 <15 May, 90 6622 <1.3 <10 <10
<15 7035 1.321.0 <10 <10 <15 June, 90 7034 <1.9 <10 <10
<15 7378 <2.0 <10 <10 <15 July, 90 7377 <1.9 <10 <10 August , 90 7701 <1.4 <10 <10 <15 7700 2.6 0.8 <10 <10 <15
<15 8211 <1.5 <10 <10 <15 September, 90 8210 <1.5 <10 <10
<10 <15 8565 <1.9 <10 <10 <15 October, 90 8564 <2.4 <10
<10 <15 8830 <1.3 <10 <10 <15 November, 90 8829 <1.4 <10 December, 90 9311,2 <1.1 <10 <10 <15 9313 1.4 0.8 <10 <10 <15 a See Introduction.
BYRON-Table 10. Well Water Units: pCi/L QUARTERLY GRAB SAMPLES Collection Date Lab Code Tritium Off-Site Well BY-14 1st Quarter, 90 BYWW-5814 <200 2nd Quarter, 90 6926 <200 3rd Quarter, 90 8173- <200 4th Quarter, 90 9182 <200 McCoy Farmstead Well BY-18 1st Quarter, 90 BYWW-5815 <200 2nd Quarter, 90 6927 <200 3rd Quarter, 90 8174 <200 4th Quarter, 90 9183 <200 117
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 05-07-90 BYBS-750 <0.1 <0.1 <0.2 10-01-90 819 <0.1 0.4510.07 <0.2
. Upstream BY-13 05-07-90 BYBS-751 <0.1 <0.1 <0.2 10-01-90 820 <0.1 0.2620.04 <0.2 a See Introduction.
118
BYRON l MILCH ANIMALS, NEAREST RESIDENCE, AND NEAREST CATTLE CENSUSES i 119
BYRON BYRON DAIRY CENSUS 1990 A. Site Boundary to 2 mi. None B. 2 mi. to 5 mi.
- 1. Reeverts Dairy Farm (BY-20) 5674 N. German Church Road Route 1 Byron, Illinois 2.1 miles 0 037' Milks 33 cows
- 2. Warren Danakas Dairy Farm (BY-15) 5845 East Holcomb Road Route 1 Oregon, Illinois 3.3 miles 0 110' Milks '10 cows
- 3. Oltmann Dairy Farm; Richard Oltmann, owner (BY-25) 1858 N. German Church Roaj Route 1 Oregon, Illinois 2.2 miles 0 180' Milks 15 cows O
120
i.
-BYRON.DAIRYCENSUS~1990(continued)_
s
- 4. . Ashel ford: Dairy Farm
'4210 IL-Route 2 Route 3:
-Oregon,. Illinois '
2.6 m11es;9 275' Milks 12: cows 5.- - CAM-DEE: Dairy Farms, Gerald DeVries, owner' ! 5213 N. Town Hall Road Route 3-
- -Oregon, Illinois-4 3.3 miles 0. 290' l
.. Milks.35 cows:
76;- iDuane Camling Dairy Farm . i i 50 East-lCamling. Road 4
-Route 3 -1 Oregon, Illinois' ,
3.2Lmiles 9:305' l
- Milks 35 cows' f
' C.; Sampling Locations--
-BY-15) ~ Warren Danakas Farm .
I
- 3.3 miles- @ 110'
--Milks 30 ' cows -
l Diet :i - c May -: October: . Pasture-:5 acres. Pasture, hay, corn, ,
- oats ,~ protein / mineral' supplement ' ~
- NovemberJ- April: FeedlotL3 acres.? Hay , corn ,--oats' and : l e- protein / supplement; 3
N i 1 . a II h 121
?
,. . < , -> .a- . , , ~ - . .
l BYRON DAIRY CENSUS 1990 (continued) BY-25 Richard Oltmann Dairy Farm 2.2 miles 0180* Milks 11 cows Diet: May - October: Pasture feedlot 3 acres. Haylage, corn, hay, and protein / mineral supplement. November - April: Feedlot less than 2 acres. Hay, corn silage, oats, and protein / mineral supplement . BY-17 Whitten Farma 8.5 miles 0 250' 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 Reeverts Dairy Farm 2.1 miles 0 037' Milks 33 cows Diet: May -' October: Pasture-7 acres. Pasture, Haylage, hay, oats, corn, protein / mineral supplement. November - April: Feedlot less than 2 acres. Hay, silage, oats, corn, protein / mineral supplement. BY-26' Hazzard Dairy Farm 23115 Hoisington Rd., Pecatonica, il 13.5 miles 0 355' Milks 38 cows l Diet: May - October: Feedlot 5 acres. Haylage , corn , oats, hay, silage. November - April Feedlot 5 acres. Haylage, corn, oats, hay, silage.
' Census conducted by L. Coleman on July 9,1990, a Whitten farm was replaced by Hazzard Farm on July 2, 1990.
122 9
f BYRON NEAREST RESIDENCE CENSUS, 1990 Nearest resicent 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 l i 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 WNW 0.8 miles-FN 1.2 miles NNW 1.3 miles I L Census conducted by L. Coleman on July 9, 1990. l 123
BYRON NEAREST CATTLE CENSUS,1990 Nearest cattle of the Byron Station within a five (5) mile radius. Direction Distance N 3.75 miles NNE 2.1 miles NE 1.5 miles ENE 1.5 miles E 2.5 miles ESE 1.33 miles SE 2.75 miles SSE 2.38 miles S 2.4 miles SSW 0.75 miles SW 1.0 miles WSW 1.75 miles W 1.75 miles TitN 1.38 miles NW 1.25 miles I NNW 2.4 miles i
-Census conducted by L. Coleman on July 9, 1990.
124
h I i I
.l I
a w < y APPENDIX 1y INTERLABORATORY COMPARIS0N PROGRAM RESULTS H j .- l 125 I.
Appendix IV 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 l but not to parti _cipant -laboratories. The purpose of such a program is to provide an independent check on the laboratory's analytical procedures and to alert it to any possible problems.
. Participant laboratories measure the concentrations of specified radionuclides l
and report them to -the issuing agency. Several months later, the agency i reports the known values to the participant laboratories and specifies control limits. Results consistently higher _ or lower than the known valtes or outside the ' control limits indicate a need to check the instruments or procedures used. The results in Table A-1 were 'obtained through participation in the environ-mental sample crosscheck program for milk, water, air filters, and food samples
.during the period January '1986 through December,1990. This program has been conducted by .the U.S. Envi ronmental Protection Agency Intercomparison and Calibration _ . Section, Quality Assurance Branch, Environmental Monitoring and -Support Laboratory, Las Vegas, Nevada. -The:results in . Table A-2 were obtained for thermoluminescent-dosimeters (TLDs) during the period 1976,1977,1979,1980,1984, and 1985-1986 through partici-pation in the= Second, Third, Fourth, fif th, Seventh, and Eighth International -Intercomparison of Environmental Dosimeters under the sponsorships listed in Table' A-2. Also Teledyne testing results- are listed. -Table' A-3 lists results of the analyses on in-house spiked samples. = Table 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. 126
Table A-1. U.S. Environmental Protection Agency's crosscheck program, ccmparison of EPA and Teledyne isotopes Hidwest Laboratory results for milk, water, air filters, and food samples,1986 through 1990.a Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 12 cC 15, N=1 Limits STF-447 Food Jan 1986 Sr-89 24.312.5 25.015.0 16.3-33.7 Sr-90 17.320.6 10.021.5 7.4-12.6 1-131 22.722.3 20.020.6 9.6-30.4 Cs-137 16.320.6 15.015.0 6.3-23.7 K 927146 9502144 701-1199 STW-448 Water Feb 1986 C r-51 45.013.6 38.015.0 29.3-46.7 Co-60 19.721.5 18.025.0 9.3-26.7 Zn-65 44.0 3.5 40.025.0 31.3-48.7 Ru-106 <9.0 0.015.0 0.0-8.7 Cs-134 28.312.3 30.015.0 21.3-38.7 Cs-137 23.710.6 22.015.0 13.3-30.7 STW-449 Water Feb 1986 H-3 5176248 52271525 4317-6137 STW-450 Water Feb 1986 V total 8.020.0 9.026.0 0.0-19.4 STM-451 Mil k Feb 1986 1-131 7.010.0 9.016.0 0.0-19.4 STW-452 Water Mar 1986 Ra-226 3.80.1 4.120.6 3.0-5.2 Ra-228 11.010.5 12.411.8 9.2-15.5 STW-453 Water Mar 1986 Gr. alpha 6.7 0.6 15.025.0 6.3-23.7 Gr. beta 7.320.6 8.025.0 0.0-16.7 STW-454' Water Apr 1986 1-131 7.020.0 9.026.0 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 2.0 0.3 1.5-2.5 Uranium 4.720.6 5.0 6.0 0.0-15.4 Sample B Gr. beta 28.7 1.2 35.025.0 26.3-43.7 Sr-89 5.720.6 7.0 5.0 0.0-15.7 Sr-90 7.020.0 7.021.5 4.4-9.6 Co-60 10.711.5 10.025.0 1.3-18.7 Cs-134 4.011.7 5.0 5.0 0.0-13.7 Cs-137 5.310.6 5.025.0 0.0-13.7 127
Table A-1. ( continued )- Concentration in pCi/Lb EPA Resultd
- Lab Sample Date TIML Result Control Code. Type Collected Analysis 12cc Is, N=1 Limits 4 STAF-457 Air Apr 1986 Gr. alpha 13.710.6 15.015.0 6.3-23.7 i Filter Gr. beta 46.310.6 47.015.0 38.3-55.7 Sr-90 14.710.6 18.011.5 15.4-20.6 Cs-137 10.710.6 10.015.0 1.3-18.7 STU-458- Urine .Apr 1986 Tritium 4313270 44231189 4096-4750
.STW-459 Water May.1986 Sr-89 4.310.6 5.015.0 0.0-13.7 Sr-90 5.020.0 5.011.5 2.4-7.6 STW-460 Water May,1986 Gr. alpha 5.310.6 8.015.0 0.0-16.7 Gr. beta 11.321.2 15.025.0 6.3-23.7 STW-461 Water Jun 1986 Cr-51 <9.0 0.015.0 0.0-8.7 Co-60 66.011.0 66.015.0 57.3-74.7 2n-65 87.311.5 86.025.0 77.3-94.7 Ru-106 39.712.5 50.0 5.0 41.3-58.7 Cs-134 49.312.5 49.015.0 40.3-57.7 '
Cs-137 10.321.5 10.025.0 1.3-18.7 STW-462. Water Jun 1986 Tritium 3427225 3125 361 2499-3751 STM-464 Milk Jun-1986 Sr-89 <1.0 0.025.0 0.0-8.7 Sr-90 15.3 0.6 16.0il.5 13.4-18.6 1-131 '48.322.3 41.026.0 30.6-51.4 Cs-137 43.721.5 31.015.0' 22.3-39.7 K 1567t114 1600180 1461-1739 STW 465 Water. Jul 1986 .Gr. al pha- 4.710.6 6.015.0 0.0-14.7 Gr. beta 18,711.2 18.015.0 9.3-26.7 STW-467 Water. Aug 1986 I-131 30.310.6 45.026.0 34.4-55.4 STW-468 ; Water Aug 1986 Pu-239. 11.320.6 '10.111.0 8.3-11.9-STW-469 Water- Aug 1986 -Uranium- 4.010.0 4.0 6.0 0.0-14.4 STAF-470. Air Sep 1986 Gr.- alpha 19.321.5 22.0 5.0 13.3-30.7
'471: Filter -Gr. beta 64 .0 2 .6 66.015.0 57.3-74.7 472 Sr-90 22.0 1.0 22.025.0 19.4-24.6 4
'Cs-137 25.7 1.5 22.025.0. 13.3-30.7 STW-473- Water Sep 1986 Ra-226 6.020.1 6.1 0.9 4.5-7.7 i Ra-228 8.7 1.1 9.121.4 6. 7- 11. 5 ~
128 4
Table A-1. (continued)- Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Cont rol . Code _ Type Collected Analysis 12cc Is, N=1- Limits STW-474 Water Sep 1986 Gr. alpha 16.323.2 15.025.0 6.3-23.7 Gr. beta 9.021.0 8.015.0 0.0-16.7 STW-475 W'ater Oct 1986 Cr-51 63.315.5 59.015.0 50.3-67.7 Co-60 _ 31.012.0 31.015.0 22.3-39.7-- 2n-657 87.315.9 85.015.0 76.3-93.7 Ru-106 74.727.4 74.025.0 65.3-82.7 Cs-134 25.720.6 28.015.0 19.3-36.7 Cs-137 46.311.5 44.015.0 35.3-52.7 STW-476 ' Water Oct 1986 _'H-3 5918160 59731597 4938-7008 SPW-477 Water Oct 1986
-(Blind)
Sample A Gr. alpha 34.016.0 40.025.0 31.3-48.7 Ra-226 5.810.2 6.010.9 4.4-7.6-Ra-228- 2.711.0 . 5.020.8 3.7-6.3 Vranium 11.020.0 10.016.0 0.0-20.4 Sample. B Gr. beta '38.721.2 51.025.0 42.3-59.7 ' Sr-89 5.010.0 10.025.0 1.3-18.7 S r-90 3.010.0 4.021.5 1.4-6.6 Co-60 24.721.2 24 .0 5.0 15.3-32.7 Cs-134 11.022.0 12.0 5.0 3.3-20.7 .. Cs-137 9.311.2 8.015.0 0.0-20.4 1 STM-479 -Mil k Novi1986- Sr-89 7.711.2 9.015.0- 0.3-17.7 i Sr-90 1.020.0 0.021.5: 0.0-2.6 I-131 52.323.I' 49.016.0 38.6-59.4 Cs-137 -45.713.1 39.025.0 30.3-47.7 ' X 14892104 1565t78 1430-1700
>STU-480 Urine- Nov-1986 H-3 5540226 52571912 4349-6169 STW-481 Water Nov 1986 Gr. alpha 12.024.0 20.015.0 11.3-28.7 Gr. beta. 20.023.5 20.025.0 11.3-28.7 Water- Dec 1986 6.710.2 6.811.0 5.0-8.6 STW-482 .Ra-226 l Ra-228 5.2 0.2' 11.121.7 8.2-14.0 STW-483- Water Jan 1987 Sr-89 19.7i5.0 25.025.0 16.3-33.7 L Sr-90 21.022.0 25.011.5 22.4-27.6 L
129
~
i 1ablelA-1r (continued)- Concentration in pC1/Lb EPA Resultd ; LLab- Sample Date TIML Result Control - I Code . Type Collected Analysis 22cC 15, N=1 Limit 5-- <
-STW-484 Water Jan 1987 Pu-239 17.012.3 16.711.7 13.8-19.6 STF-486- Food Jan 1987 Sr-90 36.024.0 49.0210.0- 31.7-66.3 i 1-131 78.023.4 78.028.0 64.1- 91 .9 Cs-137 89.713.0 84.015.0 75.3-92.7 K 942256 980149 895-1065
-STF-487 Food Jan 1987 Sr-90 2.010.0 ---
3 (Blank) 1-131 <3 --- l Cs-137 <2 --- K 9932102 --- STW-488- Water Feb 1987- Co-60 49.020.0 50.025.0 41.3-58.7 Zn-65 96.027.2 91.015.0 82.3-99.7 Ru-106 92.0120.2 100.025.0 91.3-108.7 Cs-134 53.023.4 59.015.0 50.3-67.7 Cs-137 89.314.6 87.015.0 78.3-95.7_ .; L. .STW-489 Water Feb 1987 H-3 41302140 42092420 3479-4939 STW-490 Water Feb 1987 Uranium 8.3 1.2 8.016.0 0.0-18.4 ' STM.491: - Mil k Feb 1987- I-131 10.0 0.0 9.010.9 7.4-10.6
. STW-492 _W ater Mar 1987 Gr. alpha 3.721.2 3.0 5.0 0.0-11.7 E
Gr. beta 11-.311.2 13.015.0 4.3-21.7 "
. STW-493- Water Mar-1987 Ra-226 7.020.1- 7.311.1 5.4-9.2-Ra-228' 7.112.3 7.511.1- 5.5-9.5-
'STM-494 . Water LApr 1987 l'-131 8.020.0 7.010.7 5.8-8.2.
- STAF-495 -Air. Apr.1987' Gr.. alpha 15.010.0 14.0 5.0 '5.3-22.7-Filter'- Gr. beta 41.022.0 43.025.0 34.3-51.7 Sr-90 16.321.2 17.011.5 14.4-19.6 Cs-137 7.020.0 8.015.0 0.0-16.7 STW-496 Water - Apr 1987- l 497 (Blind)-
Sample A Gr. alpha 30.721.2 30.028.0 16.1-43.9-
-Ra-226 =3.9t0.2 3.9 0.6 2.9-4.9 Ra-228 4.910.9 4.0i0.6 3.0-5.0 Uranium 5.010.0 5.0 6.0 0.0-15.4 13 0 1
,,+n--
Table A-1. ;(continued)- Concentration'in pCi/lb EPA Resultd Lab Sample Otte TIML Result . = Control Code Type- Collected Analysis 12cC 1s, N=1 Limits-STW-496 Water- Apr.1987 497 (Blind)' Sample B Gr beta 69.319.4 66.015.0 57.3-74.7 Sr-89 16.313.0 19.015.0 10.3-27.7- - I Sr-90 10.010.0- -10.011.5 7.4-12.6-Co-60 8.313.0 8.015.0 0.0-16.7 Cs-134 19.012.0 20.015.0 11.3-28.7 Cs-137 14.711.2- 15.015.0 6.3-23.7
- STU-498 - Urine Apr 1987 H-3 60171494 56201795 4647-6593 1
STW-499 Water May-1987' . S r-89 38.016.0 41.015.0 32.3-49.7 Sr 21.022.0 - 20.011.5 17.4-22.6 STW-500 -Water May 1987 Gr. alpha - 9.013.4 11.015.0 2.3-19.7 Gr. beta 10.311.2 '7.015.0. 0.0-15.7-STW-501; . Water: Jun 1987 .Cr-51 4 0.018.0 41,015.0 32.3-49.7 j Co-60 60.313.0 64.015.0 55.3-72.7 ;
- 2n-65-' 11.315.0 10.015.0- -1.3-18.7 Ru-106 78.316.4 75.015.0 66.3-83.7 Cs-134- 36.713.0 40.015.0 31.3-48.7 '
Cs-137 80.314.2: 80.015.0 71.3-88.7-t
- STW-502 Water.- .Jun 1987 H-3 2906186 28951357 2277-3513
.STW-503- Water Jun-1987 Ra-226 6.910.1- 7.311.1 5.4-9.2 Ra-228 13.321;0- 15.212.3 11.2-19.2
'STM-504 - ' Mil k - Jun.1987 'Sr-89 57.014.3 69.015.0 60.3-77.7 Sr-90 32.021'.0 35'.015.0 32.4-37.6
'l-131 64.0 2.0 59.026.0 -48.6-69.4 Cs-137 77.720.6 74.015.0- '
65.3-82.7L , K 1383117 1525176- 1393-1657
'STW-505 . Water Jul-1987- Gr._ alpha 2.310.7 5.015.0 0.0-13.7 4
Gr. beta 4.011.0. 5.015.0 0.0-13'7 .
- STF-506 Food Jul 1987 I-131 '82.714.6- -80.018.0 66.1-93.9; Cs-137 53.723.0 50.015.0 41.3-58.7-K 1548157 1680184 1534-1826' ST W-507 - -
- llater AUg1987 I-131 45.714.2 48.016.0 37.6-58.4
-131
. . . _ . _ . _ . __ _. . . . _ . -- ., . ~ _ _ _
Table A-li f(continued)' Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result . Control L Code Type . Collected Analysis 12cC ls, N=1 Limits -
- STW 508 Water Aug 1987_ Pu-239 5.810.2 5.320.5 4.4-6.2 .
STW-509 Water Aug 1987 Uranium 13.310.3 13.016.0 2.6-23.4
'STAF-510- Air Aug 1987 Gr. alpha 9.710.4 10.015.0 1.3-18.7 Filter Gr. beta 28.310.6 30.015.0 21.3-38.7 Sr 90 .10.010.9 10.011.5 7.4-12.6 Cs-137 10.011.0 10.015.0 1.3-18.7 STW-511 Water -Sep 1987 Ra-226 9.910.1 9.711.5 7.2-12.2 Ra-228 8.111.4 6.311.0 4.6-8.0 STW-512 Water Sep 1987 Gr. alpha 2.010.6 4.015.0 0.0-12.7-Gr. beta .11.311.3 12.015.0 3.3-20.7-
-STW-513 Water Sep-1987 H-3 44731100 44921449 3714-5270 STW-514 . Water' Oct 1987
- (Blind)
Sample - A'- Gr. alpha 29.312.6 28.0 7.0 15.9-40.1 Ra-226 4.910.1 4.810.7 3.6-6.1 > Ra-228 4.211.0- 3.610.5 2.7-4'5 . Uranium 3.0 0.1 3.016.0 0.0-13.4 Sample B Sr-89 ~14.3 1.3 16.015.0 -7.3-24.7 Sr-90 ~9.710.4 .10.011.5 7.4-12.6 Co-60 16.723.0 16.015.0 7.3-24.7
-Cs-134 16,712.3 16.015.0 7. 3-2 4 . 7- -
Cs-137 24.313.3 24.025.0 15.3-32.7 STW-516 Water Oct 1987 Cr-bl- 80.3117.5 70.015.0. 61.3-78.7 Co-60 16.012.3 15.0 5.0 6.3-23.7
- Sampl e ' A ' Zn-65 . 46.315.6 46.015.0- -37.3-54.7 4 Ru-106- 57.3215.4 61.0 5.0 52.3-69.7- J Cs-134 23.712.5- 25.015.0 16.3-33.7.
Cs-137 51.723.2 51.025.0 42.3-59.7 STU-517 Usine Nov 1987 H-3 72672100 74321743 6145-8719;
. STW-518 3 Water Nov 1987 Gr. alpha 3.012.0 7.025.0 0.0-15.7-
-Gr. beta- 15.712.3 19.015.0 10.3-27.7-STW-519 ~ Water Dec 1987 I-131 26.013.0 25.026.0 15.6-36.4 L-l 132
! . _ . . - , . _ . _ _ . _ - _ ~
.- ~ . _ . . . , , - . .
, Table A-1.- (continued)
Concentration in pCi/L b EPA Resultd lab ; Sample Date TIML Result Control Code Type- Collected Analysis 120C 15, N=1 Limits STW-520 Water Dec 1987 Ra-226 5.110.8 4.810.7 3.6-6.0 Ra-228 3.420.1 5.320.8 3.9-6.7 STW-521 Water Jan 1988 Sr-89 27.325.0 30.015.0 21.3-38.7 Sr-90 15.321.2- 15.021.5 12.4-17.6 STW-523 - Water .Jan 1988 Gr. alpha 2.311.2 4.025.0 0.0-12.7-Gr. beta 7.711.2 8.025.0 0.0-16.7 STF-524- Food Jan 1988 Sr-89 44.024.0 46.025.0 37.3-54.7 Sr-90 53.012.0 55.012.8 50.2-59.8 I-131 102.314.2 -102.0110.2 84.3-119.7 L Cs-137 95.726.4 91.015.0 82.3-99.7-L X 10111158 1230162 1124-1336 STW-5253 -Water JFeb 1988 Co-60 69.312.3 69.015.0 60.3-77.7 2n-65 99.0 3.4 94.029.4 77.7-110.3 Ru-106 92.7114.4 105.0210.5 86.8-123.2 1 Cs-134 61.718.0 64.025.0 55.3-72 .7 l Cs-137: 99.723.0 94.015.0 85.3-102.7 l
- STW- 526'- Water- Feb 1988 H-3 34532103 3327 362 2700-3954 7
.STW-527 Water Feb 1988 Uranium- 3.010.0 3.026.0. 0.0-13.4
-STM-528- Mil k-- Feb 1988 1-131 4.711.21 4.010.4 3.3-4.7
~STW-529 Water- Mar 1988 Ra-226 7 110.6
. 7.6 1.1 "5.6-9.6 Ra-228 nae 7.711.2 5.7-9.7 STW-530 Water Mar 1988 Gr. . al pha 4.321.2 6,015.0 0.0-14.7 1Gr. beta 13.311.3 13.015.0 4.3-21.7 i .STAF-531 JAir. Mar 1988 Gr. alpha 21.022.0 20.025.0- -11.3-28.7 L ~ Filter- Gr. beta 48.0 0.0- 50.015.0 41.3-58.7 l' Sr-90 16.7tl.2. 17.011.5 14.4-19.6 p
Cs-137 18.711.3 16.0 5.0 7.3-24.7-L lSTW-532- Water- Apr 1988 1-131 9.012.0 7.510.8 6.2-8.8. 133
=
---,- ~ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ __
Table A-1. (continued) Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 22cc Is, N=1 Limits STW-533 Water Apr 1988 534 (Blind) Sample A Gr. alpha NDf 46.0211.0 27.0-65.0 Ra-226 ND 6.411.0 4.7-8.1 Ra-228 ND 5.620.8 4.2-7.0 Uranium 6.0 0.0 6.016.0 0.0-16.4 Sample B Gr. beta ND 57.015.0 48.3-65.7 Sr-89 3.321.2 5.015.0 0.0-13.7 Sr-90 5.321.2 5.011.5 2.4-7.6 Co-60 63.311.3 50.015.0 41.3-58.7 Cs-134 7.721.2 7.015.0 0.0-15.7 Cs-137 8.3 1.2 7.025.0 0.0-15.7 STU-535 Urine Apr 1988 H-3 64832155 62021620 5128-7276 STW-536 Water Apr 1988 Sr-89 14 .721.3 20.025.0 11.3-28.7 Sr-90 20.022.0 20.011.5 17.4-22.6 STW-538 Water Jun 1988 Cr-51 331.7113.0 302.0130.0 250.0-354.0 Co-60 16.022.0 15.015.0 6.3-23.7 Zn-65 107.7 11.4 101.0110.0 83.7-118.3 Ru-106 191.3111.0 195.0 20.0 160.4-229.6 Cs-134 18.3 4.6 20.015.0 11.3-28.7 Cs 137 26.321.2 25.0 5.0 16.3-33.7 STW-539 Water Jun 1988 H-3 5586192 55651557 4600-6530 STM-541 Mil k Jun 1988 Sr-89 33.7111.4 40.015.0 31.3-48.7 Sr-90 55.315.8 60.013.0 54.8-65.2 , 1-131 103.713.1 94.029.0 78.4-109.6 Cs-137 52.7 3.1 51.015.0 42.3-59.7 X 1587 23 1600180 1461-1739 STW-542 Water Jul 1988 Gr. alpha 8.724.2 15.025.0 6.3-23.7 Gr. beta 5.3 1.2 4.025.0 0.0-12.7 STF-543 Food Jul 1988 Sr-89 NDf 33.025.0 24.3-41.7 Sr-90 ND 34.012.0 30.5-37'.5 1-131 115.015.3 107.0111.0 88.0-126.0 Cs-137 52.716.4 49.015.0 40.3-57.7 K 1190166 1240 62 1133-1347 l l l l 134 r' ~
l Table A-1. (continaed) Concentration in pC1/Lb EPA Resultd Lab Sample Oate TIML Result Control Code Tyoe Collected Analysis 22cc Is, N=1 Limits STW-544 Water Aug 1988 1-131 80.020.0 76.018.0 62.1-89.9 STW-545 Water Aug 1988 Pu-239 11.020.2 10.211.0 8.5-11.9 STW-546 Water Aug 1988 Uranium 6.010.0 6.016.0 0.0-16.4 STAF-547 Air Aug 1988 Gr. alpha 8.020.0 8.025.0 0.0-16.7 Fil ter Gr. beta 26.321.2 29.025.0 20.3-37.7 Sr-90 8.0 2.0 8.011.5 5.4-10.6 C s-137 13.022.0 12.025.0 3.3-20.7 STW~548 Water. Sep 1988 Ra-226 9.310.5 8.422.6 6.2-10.6 Ra-228 5.820.4 5.411.6 4.0-6.8 STW-549 Water Sep 1988 Gr. alpha 7.012.0 8.0 5.0 0.0-16.7 Gr. beta 11.321.2 10.0 5.0 1.3-18.7 STW-550 Water Oct 1988 Cr-51 252.0214.0 251.0225.0 207.7-294.3 Co-60 26.012.0 25.025.0 16.3-33.7 Zn-65 158.3 10.2 151.0215.0 125.0-177.0 Ru-106 153.029.2 152.0115.0 126.0-178.0 Cs-134 28.715.0 25.015.0 16.3-33.7 Cs-137 16.311.2 15.025.0 6.3-23.7 STW-551 Water Oct 1988 H-3 23331127 2316 350 1710-2927 STW-552 Water Oct 1988 5B3 (Blind) Sample A Gr. alpha 38.3 8.0 41.0110.0 23.7-58.3 Ra-226 4.5 0.5 5.0 0.8 3.6-6.4 Rh-228 4.4t0.6 5.220.8 3.6-6.4 Uranium 4.7 1.2 5.0 6.0 .0.0-15.4 Sample B Gr. beta 51 .3 3 . 0 54.015.0 45.3-62.7 Sr-89 3.711.2 11.0 5.0 2.3-19.7 Sr-90 10.721.2 10.0 1.5 7.4-12.6 Cs-134 15.3 2.3 15.025.0 6.3-23.7 Cs-137 16.7 1.2 15.0 5.0 6.3-23.7 l 135
l Table A-1. (continued) Concentration in pCi/lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 22cC 15 N=1 Limits STM-554 Mil k Oct 1988 Sr-89 40.327.0 40.025.0 31.3-48.7 Sr-90 51.022.0 60.023.0 54 .8-65.2 1-131 94.023.4 91.029.0 75.4-106.6 Cs-137 45.024.0 50.015.0 41.3-58.7 K 1500245 1600280 1461-1739 STU-555 Urine Nov 1988 H-3 3030 209 30252359 2403-3647 STW-556 Water Nov 1988 Gr. alpha 9.013.5 9.025.0 0.3 17.7 Gr. beta 9.721.2 9.025.0 0.3-17.7 STW-557 Water Dec 1988 1-131 108.723.0 115.0212.0 94.2-135.8 STW-559 Water Jan 1989 Sr-89 40.028.7 40.015.0 31.3-48.7 Sr-90 24.323.1 25.021.5 24.4-27.6 STW-560 Water Jan 1989 Pu-249 5.821.1 4.210.4 3.5-4.9 STW-561 Watcr Jan 1989 Gr. al pha 7.321.2 8.0 5.0 0.0-16.7 Gr. beta 5.321.2 4.0 5.0 0.0-12.7 STW-562 Water Feb 1989 C r-51 245146 235224 193.4-276.6 Co-60 10.012.0 10.015.0 1.3-18.7 Zn-65 170210 159216 139.2-186.7 Ru-106 18127.6 178i18 146.8-209.2 Cs-134 9.723.0 10.015.0 1.3-18.7 Cs-137 11.7 1.2 10.025.0 1,3-18.7 STW-563 Water Feb 1989 I-131 109.024.0 106.0211.0 86.9-125.1 STW-564 Water Feb 1989 H-3 2820220 2754 356 2137-3371 STW-565 Water Mar 1989 Ra-226 4.2 0.3 4.920.7 3.7-6.1 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 Air Mar 1989 Gr. al pha 21.721.2 21.025.0 12.3-29.7 Filter Gr. beta 68.324.2 62.015.0 53.3-70.7 Sr-90 20.0 2.0 20.021.5 17.4-22.6 Cs-137 21.3 1.2 20.025.0 11.3-28.7 I 136 l
Table Aolo (continued) ( Concentration in pC1/Lb EPA Resultd L ab Sample Date TIML Result Control Code Type Collected Arilysis 12 6 15, N=1 Limits STW-568 Water Apr 1989 569 (Blind) Sample A Gr. alpha 22.712.3 29.017.0 16.9 41.2 Ra-226 3.610.6 3.520.5 2.6-4.4 Ra-228 2.6 1.0 3.6t0.5 2.7-4.5 V 3.010.0 3.016.0 0.0-13.4 Sample B Gr. beta 52.326.1 57.015.0 43.3-65.7 Sr-89 9.315.4 8.025.0 0.0 16.7 Sr-90 7.020.0 8.011.5 5.4-10.6 Cs-134 21.015.2 20.015.0 11.3-28.7 Cs-137 23.012.0 20.015.0 11.3-28.7 STW-570 Mil k Apr 1989 Sr-89 26.0110.0 39.015.0 30.3 47.7 S r-90 45.714.2 55.023.0 49.8-60.2 Cs-137 54.016.9 50.015.0 41.3-58.7 K-40 15212208 1600180 1461-1739 STW-5719 Water May 1989 Sr-89 <0.7 6.015.0 0.0-14.7 Sr-90 5.011.0 6.011.5 3.4-8.6 STW-572 Water Mey 1989 Gr. al pha 24.012.0 30.018.0 16.1-43.9 Gr. beta 49.3115.6 50.015.0 41.3-58.7 STW-573 Water Jun 1989 Ba-133 50.721.2 49.015.0. 40.3-57.7 Co-60 31 .312 .3 31.015.0 22.3-39.7 Zn-65 167110 165117 135.6-194.4 Ru-106 12319.2 128113 105.S-150.5 Cs-134 40.311.2 3915 30.3-47.7 Cs-137 22.321.2 2015 11.3-28.7 STW-574 Water Jun 1989 H-3 45131136 45031450 3724-5282 STW-575 Water Jul 1989 Ra-226 16.813.1 17.712.7 13.0-22.4 Ra-228 13.813.7 18.312.7 13.6-23.0 STW-576 Water Jul 1989 U 40.311.2 41.026.0 30.6-51.4 STW-577 Water Aug 1989 l-131 84.715.8 83.018.0 69.1-96.9 STAF-579 Air Au9 1989 Gr. alpha 6.020.0 6.015.0 0.0-14.7 Filter Cs-137 10.312.3 10.015.0 1.3-18.7 137
Table A-1. (continued) Concentration in DC1/L b EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 22cC 15, N=1 Limits STW-580 Water Sep 1989 Sr-89 14.721.2 14.025.0 5.3 22.7 Sr-90 9.711 .2 10.021.5 7.4-12.6 STW-581 Water Sep 1989 Gr. alpha 5.020.0 4.015.0 0.0 12.7 Gr. Beta 8.722.3 6.015.0 0.0 14.7 STW-583 Water Oct 1989 Ba-133 60.3110.0 59.016.0 48.6-69.4 Co-60 29.024.0 30.025.0 21.1-38.7 Zn-65 132.326.0 129.0113.0 106.5-151.5 Ru-106 155.326.1 161.0116.0 133.3-186.7 Cs-134 - 30.726.1 29.015.0 20.3-37.7 Cs-137 66.324.6 59.015.0 50.3-67.7 STW-584 Water Oct 1989 H-3 34071150 3496t364 2866-4126 STW-585 Water Oct 1989 586 (Blind) Sample A Gr. Alpha 41.729.4 49.0212.0 28.2 69.8 Ra-226 7.920.4 8.421.3 6.2-10.6 Ra-228 4.420.8 4.110.6 3.1 - 5.1 0 12.020.0 12.016.0 1.6-22.4 Sample B Gr. Beta 31.7tf 3 32.015.0 23.3-40.7 Sr-89 13.314.2 15.025.0 6.3-23.7 Sr-90 7.022.0 7.013.0 4.4-9.6 Cs-134 5.010.0 5.015.0 0.0-13.7 Cs-137 7.020.0 5.025.0 0.0-13.7 S TW-587 Water Nov 1989 Ra-226 7.920.4 8.711.3 6.4-11.0 Ra-228 8.911.2 9.321.2 6.9-11.7 579-588 Water Nov 1989 U 15.010.09 15.016.0 4.6-25.4 STW-589 Water Jan 1990 Sr-89 22.725.0 25.015.0 16.3-33.7 S r-90 17.321.2 20.011.5 17.4-22.6 STW-591 Water Jan 1990 Gr. Alpha 10.323.0 12.015.0 3.3-20.7 Gr. Beta 12.311.2 12.025.0 3.3-20.7 138 1
l Table A 1. (continued) l --- Concentration in PC1/Lb EPA Restl,td Lab Sample Date TIML Result Control Code Type Collected Analysis 22cc 15, N=1 Limits STW-592 Water Jan 1990 Co-60 14.722.3 1525.0 6.3423.7 Zn-65 135.016.9 139.0214.0 114.8 163.2 Ru-106 133.3113.4 139.0214.0 114.8 163.2 Cs-134 17.311.2 18.025.0 9.3-26.7 Cs 137 19.321.2 18.015.0 9.3-26.7 0a-133 78.020.0 74.017.0 61.9-86.1 S TW-593 Water Feb 1990 H-3 4827283 49161498 4113-5839 STW-594 Water Mar 1990 Ra-226 5.020.2 4.910.7 4.1 5.7 Ra-228 13.510.7 12.711.9 9.4-16.0 STW-595 Water Mar 1990 V 4.020.0 4.0t6.0 0.0-14.4 STW-596 Air har 1990 Gr. Alpha 7.311.2 5.0x5.0 0.0 13.7 Filter Gr. Beta 34.010.0 31.015.0 22.3-39.7 Sr-90 10.020.0 10.011.5 7.4-12.6 Cs-137 9.311.2 10.015.0 1.3-18.7 STW-597 Water Apr 1990 598 (Blind) Sample A Gr. Alpha 81.0t3.5 90.0223.0 50.1-129.9 Ra-226 4.810.4 5.0t0.8 3.6-6.4 Ra-228 10.620.3 10.211.5 7.6-12.8 U 16.7t3.0 20.026.0 9.6-30.4 Sample B Gr. Beta 51.0210.1 52.015.0 43.3-60.7 Sr-89 9.311.2 10.015.0 1.3-18.7 Sr-90 10.323.1 10.011.5 8.3-11.7 Cs-134 16.020.0 15.025.0 6.3-23.7 Cs-137 19.012.0 15.025.0 6.3-23.7 STM-599 Milk Apr 1990 Sr-89 21.713.1 23.015.0 14.3-31.7 Sr-90 21.017.0 23.025.0 14.3-31.7 l-131 98.711.2 99.0110.0 81.7-116.3 Cs-137 26.016.0 24.015.0 15.3-32.7 K 1300.0269.2 1550.0178.0 1414.7-1685.3 STW-600 Water May 1990 Sr-89 6.022.0 7.015.0 0.0-15.7 Sr-90 6.721.2 7.015.0 0.0-15.7 STW-601 Water P.3y 1990 Gr. Alpha 11.012.0 22.016.0 11.6-32.4 Gr. Beta 12.311.2 15.0i5.0 6.3-23.7 l 139
l Table A-1. (continued) Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 12 cC 1s, N=1 Limits STW-602 Water Jun 1990 Co-60 25.322.3 24.015.0 15.3-32.7 Zn-65 155.0110.6 148.0115.0 130.6-165.4 Ru-106 202.7217.2 210.0121.0 173.6-246.4 Cs-134 23.711.2 24.025.0 18.2-29.8 Cs-137 27.713.1 25.025.0 16.3-33.7 Ba-133 100.718.1 99.0110.0 81.7-116.3 STV-603 Water Jun 1990 H-3 29271306 29331358 2312-3554 STW-604 Water Jul 1990 Ra-226 11.820.9 12.111.8 9.0-15.2 Ra-228 4.111.4 5.111.3 2.8-7.4 STW-605 Water Jul 1990 V 20.321.7 20.813.0 15.6-26.0 STW-606 Water Au9 1990 1-131 43.021.2 39.016.0 28.6-49.4 STW-607 Water Aug 1990 Pu-239 10.011.7 9.110.9 7.5-10.7 STW-608 Air Aug 1990 Gr. alpha 14.020.0 10.015.0 1.3-18.7 Fil ter Gr. beta 65.321.2 62.015.0 53.3-70.7 Sr-90 19.016.9 20.015.0 11.3-28.7 Cs-137 19.022.0 20.015.0 11.3-28.7 STW-609 Water Sep 1990 Sr-89 9.012.0 10.015.0 1,3-18.7 Sr-90 9.022.0 9.025.0 0.3-17.7 STM-610 Water Sep 1990 Gr. alpha 8.321.2 10.015.0 1.3-18.7 Gr. beta 10.321.2 10.015.0 1.3-18.7 STM-611 Mil k Sep 1990 Sr-89 11.723.1 16.015.0 7.3-24.7 Sr-90 15.010.0 20.015.0 11.3-28.7 I-131 63.016.0 58.026.0 47.6-68.4 Cs-137 20.022.0 20.015.0 11.3-28.7 K 1673.3270.2 1700.0285.0 1552.5-1847.5 STW-612 Water Oct 1990 Co-60 20.323.1 20.015.0 11.3-28.7 Zn-65 115.3112.2 115.0 12.0 94.2-135.8 Ru-106 152.028.0 151.0115.0 125.0-177.0 Cs-134 11.010.0 12.015.0 3.3-20.7 Cs-137 14.012.0 12.015.0 3.3-20.7 Ba-133 116.719.9 110.0111.0 90.9-129.1 STW-613 Water Oct 1990 H-3 71672330 72031720 5954-8452 l 140
Table A-1. (continued) Concentration in pCi/Lb EPA Resultd Lab Sample Date TIML Result Control Code Type Collected Analysis 22cc Is, N=1 Limits STW-614 Water Oct 1990 615 Sample A Gr. alpha 68.727.2 62.0116.0 34.2-89.8 Ra-226 12.910.3 13.612.0 10.1-17.1 Ra-228 4.210.6 5.011.3 2.7-7.3 V 10.420.6 10.213.0 5.0-15.4 Sample B Gr. beta 55.028.7 53.015.0 44.3-61.7 Sr-89 15.722.9 20.015.0 11.3-28.7 Sr-90 12.012.0 15.015.0 6.3-23.7 Cs-134 9.021.7 7.015.0 0.0-15.7 Cs-137 7.711.2 5.015.0 0.0-13.7 STW-616 Water Nov 1990 Ra-226 6.821.0 7.411.1 5.5-9.3 Ra-228 5.321.7 7.711.9 4.4-11.0 STW-6179 Water Nov 1990 V 35.010.4 35.523.6 29.3-41.7 a Results obtained by Teledyne isotopes Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Intercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Laboratory, U.S. Environmental Protection Agency (EPA), Las Vegas, Nevada. b All results are in the pCi/1, except for elemental potassium (K) data in milk, which are in mg/1; air filter samples, which are in pC1/ filter; and food, which is in mg/kg. c Unless otherwise indicated, the TIML results are given as the mean i 2 standard deviations for threr determinations. d USEPA results are presented s. the known values and expected laboratory precision (1s,1 deter ination) and control limits as defined by EPA. e RA = 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 (all data on file). l l 141
Table A-2. Crosscheck program results, thermoluminescent dosimeters (TLDs), mR Teledyne Average 22cd Lab Result Known (All Code TLD Type Measurement !?ca ValueC Participants) 2nd International Intercomparisonb 115-2 CaF2 :Mn Field 17.011.9 17.1 16.417.7 Bulb Lab 20.824.1 21.3 18.817.6 _3rd International Intercomparisone 115-3 CaF2 :Mn Field 30.723.2 34.924.8 31.513.0 Bulb Lab 89.626.4 91.7214.6 86.2124.0 _4th International Intercomparisonf 115-4 CaF2 :Mn Field 14.121.1 14.121.4 16.019.0 Bulb Lab (Low) 9.311.3 12.222.4 12.017.4 Lab (High) 40.411.4 45.829.2 43.9213.2 _Sth International Intercomparison9 115-5A CaF2 :Mn Field 31.421.8 30.026.0 30.2214.6 Bulb Lab at beginning 77.415.8 75.217.6 75.8240.4 Lab at the end 96.615.8 88.428.8 90.7131.2 115-5B Lif-100 Field 30.324.8 30.026.0 30.2214.6 Chips Lab at beginning 81.127.4 75.217.6 75.8240.4 Lab at the end 85.4111.7 88.428.8 90.7231.2 _7th International Intercomparisonh 115-7A Lif-100 Field 75.422.6 75.826.0 75.1229.8 Chips Lab (Co-60) 80.013.5 79.914.0 77.9227.6 Lab (Cs-137) 66.622.5 75.023.8 73.0122.2 142
Table A-2. (continued) mR Teledyne Average 12cd Lab Result Code TLD Type Known (All Measurement 22ca Yaluec Participants) 115-7B CaF2 :Mn Field 71.522.6 75.826.0 75.1229.8 Bulbs Lab (Co-60) 84 *2 6.4 79.924.0 77.9127.6 Lab (Cs-137) 78.811.6 75.023.8 73.0122.2 115-7C CaSO4:Dy Field 76.822.7 75.826.0 75.1229.8 Cards Lab (Co-60) 82.513.7 79.924.0 77.9227.6 Lab (Cs-137) 79.023.2 75.023.8 73.0222.2 8th International Intercomparisoni 115-8A Lif-100 Field Site 1 29.521.4 29.721.5 28.9112.4 Chips Field Site 2 11.320.8 10.420.5 10.129.06 Lab (Cs-137) 13.720.9 17.220.9 16.226.8 115-88 CaF2 :Hn Field Site 1 32.321.2 29.721.5 28.9212.4 Bulbs Field Site 2 9.021.0 10.420.5 10.119.0 Lab (Cs-137) 15.820.9 17.2 0.9 16.226.8 115-8C CaSO4 :Dy Field Site 1 32.320.7 29.711.5 28.9212.4 Cards Field Site 2 10.620.6 10.420.5 10.129.0 Lab (Cs-137) 18.120.8 17.210.9 16.226.8 Teledyne Testing) 89-l' Lif-100 Lab 21.020.4 22.4 -- Chips 89-2 Teledyne Lab 20.921.0 20.3 -- CaSO4:Dy Cards l l 143
l Table A-2. (continued) mR Teledyne Average 22od Lab Result Known (All Code TLD Type Measurement 22ca Yaluec Participants) _Teledyne Testingj 90-1k Teledyne Lab 20.621.4 19.6 -- CaSO4 :Dy Cards 90-1 1 Teledyne Lab 100.824.3 100.0 -- CaSO4:Dy Cards 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 York, New York, and the School cf Public Health of the University of Texas. Houston, Texas. c Value determined by sponsor of the irdercomparison using continuously operated pressurized ion chamber. d Mean 12 standard deviations of results obtained by all laboratories parti-cipating in the program. e Third International Intercomparison of Environmental Dosimeters conducted in sunner 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 sunner of 1979 by the School of Public Health of the University of Texas, Houston, Texas. 9 Fifth International Intercomparison of Environmental Desimeter conductcJ in fall of 1980 at Idaho Falls, Idaho and sponsored by the School of Public Health of the University of Texas Houston, Texas and Environmental Measure-ments Laboratory, New York, New York, U.S. Department of Energy. h Seventh International Intercomparison of Environmental Dosimeters conducted in the spring and sunner 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. i Eighth International Intercomparison of Environmental Dosimeters conducted in the fall and winter of 1985-1986 at New York, New York, and sponsored by the U.S. Department of Energy. J Chips were submitted in September 1989 and cards were submitted in November 1989 to Teledyne Isotopes, Inc., Westwood, NJ for irradiation. k Cards were irradiated by Teledyne Isotopes, Inc., Westwood, NJ on June 19, 1990. I Cards were irradiated by Dosimetry Associates, Inc., Northville, M1 on October 30, 1990 l 144 l
l Table A 3. In-house spiked samples. Concentration (pCi/L) Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-MI-6 Mil k Feb 1986 Sr-89 6.011.9 6.413.0 8.7 Sr 90 14.211.7 12.912.0 5.2 1-131 34.223.8 35.213.5 10.4 Cs-134 32.011.8 27.315.0 8.7 Cs-137 35.812.1 35.015.0 8.7 QC-W-14 Water Mar 1986 $r-89 1.610.4 1.611.0 7.1 Sr-90 2.410.2 2.412.0 4.2 QC-W-15 Water Apr 1986 1-131 44.922.4 41.517.0 10.6 Co-60 10.611.7 12.115.0 7.lb Cs-134 30.212.4 25.818.0 7.lb Cs 137 21.911.9 19.915.0 7.lb QC-MI-7 Mil k Apr 1986 1 131 39.713.3 41.517.0 10.4 Cs-134 28.712.8 25.818.0 8.7 Cs-137 21.212.8 19.915.0 8.7 SPW-1 Water May 1986 Gr. alpha 15.811.8 18.015.0 Sc QC-W-16 Water Jun 1986 Gr. alpha 16.210.7 16.912.5 8.7 Gr. beta 38.413.5 30.215.0 8.7 QC-MI-9 Mil k Jun 1986 Sr-89 <1.0 0.0 7.lb Sr-90 12.611.8 13.313.0 4.2b l-131 38.917.0 34.817.0 10.4 Cs-134 33.013.4 36.115.0 8.7 Cs-137 38.512.8 39.015.0 8.7 SPW-2 Water Jun 1986 Gr. alpha 16.821.8 18.015.0 SC SPW-3 Water Jun 1986 Gr. alpha 17.710.8 18.015.0 Sc QC- W-18 Water Sep 1986 Cs-134 34.715.6 31.315.0 8.7 Cs-137 51.117.0 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 6.222.0 4.2b 14 5
Table A-3. In-house spiked samples (continued) ~ Concentration (pci/L) Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=38 QC-W-21 Water Oct 1986 Co-60 19.222.2 18.513.0 8.7 Cs-134 31.715.2 25.618.0 8.7 Cs-137 23.821.0 21.625.0 8.7 QC-MI-11 Mil k Oct 1986 Sr-89 12.311.8 14.313.0 8.7 QC-W-20 Water Nov 1986 H-3 38551180 39601350 520b QC-W-22 Water Dec 1986 Gr. alpha 9.821.4 11.224.0 8.7 Gr. beta 21.722.0 23.825.0 8.7 QC-W-23 Water Jan 1987 1-131 29.822.5 27.923.0 10.4 QC MI-12 Milk Jan 1987 1-131 36.521.3 32.625.0 10.4 Cs-137 32.624.2 27.418.0 8.7 QC-MI-13 Mil k Jan 1987 Sr-89 10.412.1 12.224.0 8.7 Sr-90 14.621.6 12.623.0 5.2 1-131 49.521.2 54.918.0 10.4 Cs-134 <1.6 0.0 8.7 Cs-137 33.310.6 27.418.0 8.7 QC-W-24 Water Mar 1987 Sr-89 24.723.6 25.925.0 8.7 Sr-90 23.913.8 22.818.0 5.2 QC-W-25 Water Apr 1987 1-131 28.021.9 29.325.0 10.6 QC-HI-14 Milk Apr 1987 1-131 25.012.2 23.915.0 10.4 Cs-134 <2.1 0.0 8.7 Cs-137 34.222.0 27.217.0 8.7 QC-W-26 Water Jun 1987 H-3 3422:100 33621300 520 Co-60 24.821.4 26.527.0 8.7 Cs-134 <2.0 0.0 8.7 Cs-137 21.220.5 21.627.0 8.7 QC-W-27 Water Jun 1907 Gr. alpha 8.521.9 10.1 4.0 8.7 Gr. beta 22.621.9 21.225.0 8.7 QC-W-28 Water Jun 1987 Gr. alpha 8.721.3 10.114.0 8.7 Gr. beta 12.215.2 9.413.0 8.7 ~ l 14 6
Iable A 3. In-house spiked samples (continued) Concentration (pC1/L) Lab Sample Date TIML Expected Code Type Col ected Analysis Result Known Precision n=3 Activity 15, n=3a QC-W-29 Water Jun 1987 Gr. alpha 16.411.3 18.925.0 8.7 Gr. beta 15.924.0 11.824.0 8.7 QC-M1-15 Mil k Jul 1987 Sr-90 19.411.6 18.813.5 5.2 1-131 43.520.7 45.317.0 10.4 Cs-134 17.922.2 16.015.3 8.7 Cs-137 25.421.8 22.715.0 8.7 QC-W-30 Water Sep 1987 Sr-89 17.513.0 14.325.0 8.7 Sr-90 18.412.2 17.Si2.2 5.2 QC-W-31 Water Oct 1987 H-3 20531939 20592306 520 QC-W-32 Water Dec 1987 Gr. alpha 8.6tl.0 10.115.0 8.7 Gr. beta 15.210.1 13.113.0 8.7 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 QC-W-34 Water Dec 1987 Gr. alpha 4.010.9 5.113.0 8.7 Gr. beta 9.410.9 7.923.0 8.7 QC-M1-16 Milk Feb 1988 Sr-89 31.824.7 31.716.0 8.7 Sr-90 25.522.7 27.813.5 5.2 1-131 26.410.5 23.225.0 10.4 Cs-134 23.812.3 24.226.0 8.7 Cs-137 26.520.8 25.116.0 8.7 QC-MI-17 Mil k Feb 1988 1-131 10.611.2 14.311.6 10.4 QC-W-35 Water Feb 1986 1-131 9.711.1 11.621.1 10.4 QC-W-36 Water Feb 1988 1-131 10.521.3 11.621.0 10.4 QC-W-37 Water Har 1988 Sr-89 17.122.0 19.818.0 8.7 Sr-90 18.7t0.9 17.3 5.0 5.2 QC-M1-18 Mil k Mar 1988 1-131 33.212.3 26.725.0 10.4 Cs-134 31.312.1 30.225.0 8.7 Cs-137 29.911.4 26.225.0 8.7 l l 147
lable A-3. In-house spiked samples (continued) Concentration (pCi/L) Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=3a QC-W-38 Water Apr 1988 1 131 17.111.1 14.225.0 10.4 QC-W-39 Water Apr 1988 H-3 4439:31 41761500 724 QC-W-40 Water Apr 1988 Co-60 23.710.5 26.114.0 8.7 Cs-134 25.412.6 29.224.5 8.7 Cs-137 26.622.3 26.214.0 8.7 QC-W-41 Water Jun 1988 Gr. sipha 12.310.4 13.115.0 8.7 Gr. beta 22.611.0 20.115.0 8.7 QC-M1-19 Mil k Jul 1988 Sr-89 15.121.6 16.415.0 8.7 Sr-90 18.020.6 18.315.0 5.2 1-131 88.424,9 86.618.0 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 10.911.0 11.4t3.5 5.2 QC-W-43 Water Oct 1988 Co-60 20.923.2 21.413.5 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 Milk Oct 1988 1-131 59.810.9 60.619.0 10.4 Cs-134 49.621.8 48.617.5 8.7 Cs-137 25.824.6 24.714.0 8.7 QC-W-46 Water Dec 1988 Gr. alpha 11.512.3 15.215.0 8.7 Gr. beta 26.512.0 25.725.0 8.7 QC-MI-21 Mil k Jan 1989 Sr-89 25.5110.3 34.0110.0 8.7 Sr-90 28.323.2 27.123.0 5.2 1-131 540113 550220 10.4 Cs-134 24.522.6 22.6 5.5 8.7 Cs-137 24.020.6 20.515.0 8.7 l 148
Table A-3. In-house spiked samples (continued) Concentration (pC1/L) Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Activity 1s, n=38 QC-W-47 Water Mar 1989 Sr-89 15.223.8 16.125.0 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 20.8*2.8 20.728.0 8.7 Cs-137 22.222.4 20.428.0 8.7 QC-W-48 Water Apr 1989 Co-60 23.522.0 25.128.0 8.7 Cs-134 24.2il.1 25.928.0 8.7 Cs-137 23.621.2 23.018.0 8.7 QC-W-49 Water Apr 1989 l-131 37.213.7 37.215.0 10.4 QC-W-50 Water Apr 1989 H-3 ^11159 30891500 724 QC-W-51 Water Jun 1989 Gr. alpha 13.011.8 15.025.0 8,7 Gr. beta 26.021.2 25.518.0 8.7 QC-MI-23 Mil k Jul 1989 Sr-89 19.426.5 22.0:10.0 8.7 Sr-90 27.613.5 28.613.0 5.2 1-131 46.813.2 43.425.0 10.4 Cs-134 27.421.8 28.326.0 8.7 Cs-137 24.121.8 20.826.0 8.7 QC MI-24 Mil k Aug 1989 Sr-89 25.422.7 27.2110.0 8.7 Sr-90 46.011.1 47.819.6 8.3 QC-W-52 Water Sep 1989 l-131 9.610.3 9.721.9 10.4 QC-W-53 Water Sep 1989 I-131 19.010.2 20.924.2 10.4 QC-W-54 Water Sep 1989 Sr-89 25.814.6 24.724.0 8.7 Sr-90 26.515.3 29.715.0 5.2 QC-MI-25 Mil k Oct 1989 l-131 70.013.3 73.5120.0 10.4 Cs-134 22.112.6 22.618.0 8.7 Cs-137 29.411.5 27.518.0 8.7 QC-W-55 Water Oct 1989 l-131 33.3 1.3 35.3110.0 10.4 149
Table A-3. In-house spiked samples (continued) Concentration (pC1/L) Lab Sample Date TIML Expected Code Type Collected Analys is Result Known Precision n=3 Activity 15, n=3a QC-W-56 Water Oct 1989 Co-60 15.210.9 17.415.0 8.7 Cs-134 22.114.4 18.918.0 8.7 Cs-137 27.211.2 22.928.0 8.7 QC-W-57 Water Oct 1989 H-3 3334122 33792500 724 QC-W-58 Water Nov 1989 Sr-89 10.911.4d 11.lil.0d 8.7 Sr-90 10.411.0d 10.3tl.0d 5.2 QC-W 59 Water Nov 1989 Sr-89 101.026.0d 104.1210.5d 17.5 Sr-90 98.0 3.0d 95.0210.0d 17,o QC-W-60 Water Oec 1989 Gr. alpha 10.811.1 10.614.0 8.7 Gr. beta 11.610.5 11.414.0 8.7 QC-MI-26 Milk Jan 1990 Cs-134 19.311.0 20.818.0 8.7 Cs-137 25.211.2 22.818.0 8.7 . QC-MI-27 Mil k Feb 1990 Sr-90 18.011.6 18.815.0 5.2 QC-MI-28 Mil k Har 1990 1-131 63.822.2 62.616.0 6.3 QC-M1-61 Water Apr 1990 Sr-89 17.915.5 23.128.7 8.7 Sr-90 19.412.5 23.525.2 5.2 QC-MI-29 Mil k Apr 1990 1-131 90.729.2 82.5 8.5 10.4 Cs-134 18.311.0 19.715.0 8.7 Cs-137 20.321.0 18.215.0 8.7 QC-W-62 Water Apr 1990 Co-60 8.720.4 9.4 5.0 8.7 Cs-134 20.0 0.2 19.715.0 8.7 C s-137 28.711.4 22.725.0 8.7 QC-W-63 Wat er Apr 1990 1-131 63.528.0 66.016.7 6.6 QC-W-64 Water Apr 1990 H-3 19412130 1826.02350.0 724 QC-W-65 Water Jun 1990 Ra-226 6.4 0.2 6.91.0 1.0 QC-W-66 Water Jun 1990 V 6.220.2 6.016.0 6.0 l 150
Table A-3. In-house spiked samples (continued) Concentration (pC1/L) Lab Sample Date TIML Expected Code Type Collected Analysis Result Known Precision n=3 Acti vi ty is, n=3a QC-M1-30 Mil k Jul 1990 Sr-89 12.820.4 18.4110.0 8.7 Sr-90 18.211.4 18.716.0 5.2 Cs-134 46.021.3 49.015.0 8.7 Cs-137 27.611.3 25.315.0 8.7 QC-W-68 Water Jun 1990 Gr. alpha 9.820.3 10.616.0 8.7 Gr. beta 11.420.6 11.327.0 8.7 QC-MI-31 Mil k Aug 1990 1-131 68.821.6 61.4212.3 10.4 QC-W-69 Water Sep 1990 Sr 89 17.721.6 19.2210.0 8.7 Sr-90 13.911.6 17.4110.0 5.2 QC-MI-32 Milk Oct 1990 1-131 34.810.2 32.416.5 8.7 Cs-134 25.811.2 27.3210.0 8.7 Cs-137 25.312.0 22.4110.0 8.7 QC-W-70 Water Oct 1990 H-3 2355159 22761455 605 QC-W-71 Water Oct 1990 1-131 55.920.9 51.8110.4 10.4 QC-W-73 Water Oct 1990 Co-60 18.322.7 16.825.0 8.7 Cs-134 28.312.3 27.015.0 8.7 Cs-137 22.721.3 22.415.0 8.7 QC-W-74 Water Dec 1990 Gr. alpha 21.421.0 26.116.5 11.3 Gr. beta 25.911.0 22.315.6 9.7 a n = 3 unless noted otherwise, b n = 2 unless noted otherwise. c n = 1 unless noted otherwise. d Concentration in pCi/ml. 151
l l Table A-4 In-house " blank" samples. Concentration (pCi/L) Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66 c) (4.66 o) BL 1 D.I. Water Nov 1985 Gross alpha <0.1 <1 Gross beta <0.4 <4 BL-2 0.1. Water Nov 1985 Cs-137 (gamma) <1.9 <10 BL-3 D.I. Water Nov 1985 Sr-89 <0.5 <5 Sr-90 <0.6 <1 BL 5 0.1. Water Nov 1985 Ra-226 <0.4 <1 Ra-228 <0.4 <1 SPW-2265 0.1. heter 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 (gamma) <7.4 <10 BL-6 D.I. Water Apr 1986 Gross alpha <0.4 <1 BL-7 0.I, Water Apr 1986 Gross alpha <0.4 <1 BL-8 D.I. Water Jun 1986 Gross alpha <0.4 <1 BL-9 D.I. Water Jun 1986 Gross alpha <0.3 <1 SPW-3185 D.I. Water Jan 1987 Ra-226 <0.1 <1 Ra-228 (0.9 <1 SPS-3292 Milk Jan 1987 1-131 <0.1 <1 C5-134 <6.2 <10 C s-137 <6.4 <10 SPW-3554 0.1. 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 (10 152
Table A 4 In-house " blank" samples (continued) Concentration (pC1/L) Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66 o) (4.66o) SPS-3732 D.1, Water Mar 1987 Sr 89 <0.9 <5 Sr-90 <0.8 <1 1-131 <0.3 <1 Co-60 <2.3 <10 C5-134 <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 0-238 <0.03 <0.1 SPS-4023 Mil k May 1987 1-131 <0.1 <1 SPS-4203 D.I. Water May 1987 Gross alpha <0.7 <1 Gross beta <1.7 <4 SPS-4204 Mil k May 1987 Sr-89 <0.5 <5 Sr-90 2.420.6a <1 SPS-4390 Mil k Jun 1987 Cs-134 <4.7 <10 Cs-137 <5.2 <10 SPS-4391 D.J. Water Jun 1987 Sr-89 <0.4 <5 Sr-90 <0.4 <1 1-121 <0.1 <1 Co-60 <3.8 <10 Cs-137 <5.7 <10 Ra 226 <0.1 <1 Ra-228 <0.9 <1 SPW-4627 D.I. Water Aug 1987 Gross alpha <0.6 <1 Gross beta <1.4 <4 Tritium <150 <300 SPS-4628 Mil k Aug 1987 Sr-89 <0.6 <5 Sr-90 2.420.6a <} 153
Table A-4 In-house " blank" samples (continued) Concentration (pCi/L) Acceptance Lab Sample Date Code Results Criteria Type Collected Analysis (4.66o) (4.66 o) SPS-4847 Mil k Sep 1987 Cs 134 <4.4 <10 Cs-137 <5.3 <10 SPS-4848 0.1. Water Sep 1987 l 131 (0.2 <1 SPW-4849 D.I. Water Sep 1987 Co-60 <4.1 (10 Cs-134 (4.8 (10 Cs-137 <4.0 <10 Sr-89 <0.7 <5 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 Mil k Dec 1987 Cs-134 <2 . 3 <10 Cs-137 (2.5 <10 SPW-5384 D.1. Water Dec 1987 Co-60 <2.8 <10 Cs-134 <2.6 <10 Cs-137 <2.8 <10 1-131 <0.2 <1 Ra-226 <0.1 <1 Ra-228 <1.2 <2 Sr-89 <0.5 <1 Sr-90 <0.4 <1 SPW-5385 0.1. Water Nov 1987 Gross alpha <0.4 <1 Gross beta (2.2 <4 Fe-55 (0.3 <1 SPS-5386 Mil k Jan 1988 1-131 <0.1 <1-SPW-5448 " Dead" Water Jan 1988 H-3 (177 <300 i 154 l
. . . _ _ . . --~ - - - -- . . . . _ _ . . - _ _ . .
Table A-4 In house " blank" samples (continued) Concentration (pC1/L) Acceptance Lab Sampl e Date Results Criteria Code Type Collected Analysis (4.66 o) (4.66 o) SPS-5615 Mi' k Mar 1988 Cs-134 <2.4 <10 Cs-137 <2.5 <10 1-131 <0.3 <1
$r-89 <0.4 <5 Sr 90 2.420.5a <1 SPS-5650 0.1. Water Har 1988 Th-228 <0.3 <1 Th-230 (0.04 <1 i Th-232 <0.05 <1 U-234 <0.03 <1 U-235 <0.03 <1 U-238 <0.03 <1 Am-241 <0.06 <1 Cm-242 <0.01 <1 Pu-238 <0.08 <1 Pu-240 <0.02 <1 SPS-6090 Mil k Jul 1988 Sr-89 <0.5 <1 S r-90 1.820.5 <1 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 l-131 <0.2 <1 Cs-134 <6.1 <10 Cs-137 <5.9 <10 SPW-6478 Water Oct 1988 1-131 <0.2 <1 SPW-6479 Water Oct 1988 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 Wat er Dec 1988 Gross alpha <0.7 <1 Gross beta <1.9 <4 155
i i
; Table A 4 In house " blank" samples (continued) :
1 l { Concentration (DCi/L) l Acceptance Lab Sample - Date Code Type Results Criteria Collected Analysis (4.66 o) (4.66 o) SPS-6723 Milk Jan 1989 Sr-89 (0.6 <5 " Sr 90 1.920.Sa <1 l-131 <0.2. <1 Cs 134 <4.3 <10 Cs-137 <4.4 <10 i
- SPW-6877 Water Mar 1989 Sr-89
" <0.4 <5 Sr 90 <0.6 <1
.SPS-6963 Milk Apr 1989 l-131 <0.3 <1 Cs-104- <5.9 <10
- Cs 137 (6.2 <10
~
. SPW 7561 Water Apr 1989 H-3 <150 <300 .
- SPW-7207- Water Jun 1989 Ra-226 <0.2 <1 1
Ra-228 <0.6 <1 SPS-7208 Mil k Jun 1989 . S r-89 <0.6 (5 Sr-90 2.120.Sa <1= l-131- <0.3 .<1 Cs-134' <6.4 <10-Cs-137 <7.2 <10 SPW-7558- Water Jun 1989 Gross alpha <0.2 <1 Gross beta. <1.0 <4
. SPS-7322- Mil k Aug 1989 Sr-89 <1.4 <S Sr-90 4.821.0a <1 1-131 <0.2 <1 Cs-134 (6.9 <10 Cs-137 <8.2 <10
- SPW-7559? Waterz Sep 1989- -Sr-89 <2.0 <5
, .Sr-90 <0.7 <1-SPW-7560 iWater Oct 1989 l-131 <0.1 <1 SPWk 7562 Water Oct 1989. H-3 <140 <300-
-156
. -- :. . . . _ . . . . . . . _ - . _ . . .-...-.a-..,... - - - . . - . . - - . . . ., i
+
E Table A-4 In-house " blank" samples (continued) Concentration (DC1/L) Acceptance Lab Sample Date Type-Results Criteria Code Collected 4 Analysis , (4.66 o) (4.66 o) SPS-7605 Mil k Nov 1989 l 131 <0.2 <1 Cs-134 <8.6 <10 Cs-137 (10 <10 i E SPW-7971 Water Dec 1989 Gross alpha <0.4 _ <1 Gross beta <0.8 <4
.SPW-8039 Water Jan 1990 Ra-226 <0.2 <1 !
1 SPS-8040 -Mil k Jan 1990 Sr-89 <0.8 <5 Sr-90 <1.0 <1 1 SPS-8208 Mil k Jan 1990 Sr-89 <0.8 <5 ' Sr 90 1.610.Sa <1 Cs-134 <3.6 <10- , Cs-137 <4 . 7 (10 i SPS-8312 Mil k Feb 1990- Sr <0.3 <5 Sr-90 1.210.3a <1 SPW-8312A- Weiei- Feb 1990 -Sr-89 <0.6 <5 Sr-90 <0.7- <1 SPS-8314 Mil k Mar 1990 1-131 <0.3 <1
~SPS-8510 Mil k - May 1990 1-131L <0.2 <1 C s-134 <4.6 <10--
Cs-137- <4.8 <10 SPW-8511A Water. May 1990 H-3 <200 -<300-SPS -8600 Mil k - 'Jul 1990 Sr-89' <0.8 <5-Sr-90 1.710.6a <1 1 131- <0.3 <1 Cs-134 <5.0 '<10 Cs-137 <7.0 <10 SPM-8877 - Milk Aug 1990 1-131 <0.2 (1 ; p SPW-8925 Water- 'Aug 1990 H-3 <200 <300 l
-157 i
u
Table A-4 In-house " blank" samples (continued) Concentration (pC1/L) Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66o) (4.66o) SPW-8926 Water Aug 1990 Gross alpha <0.3 <1 Gross beta <0.7 <4
$PW-8927 Water Aug 1990 U-234 <0.01 <1 U-235 <0.02 <1 0-238 <0.01 <1 SPW-8928 Water Aug 1990 Mn-54 <4.0 <5 0o-58 <4.1 <5 Co-60 <2 . 4 <5 Cs-134 <3.3 <5 Cs-137 <3.7 <5 SPW-8929 Water Aug 1990 Sr 89 <1.4 <5 Sr-89 <0.6 <1 SPW 69 Water Sep 1990 Sr-89 <1.8 <5 Sr-90 <0.8 <1 SPW-106 Water Oct 1990 H-3 <180 <300 SPM-107 Mil k Oct 1990 1-131 <0.4 <1 :
Cs-134 <3.3 <5 Cs-137 <4.3 <5 SPW-370 Water Oct 1990 Hn-54 <1.7 <5 Co-58 <2.6 <5 Co-60 <1.6 <5 Cs-134 <1.7 <5 C s-137 <1.8 <5 ' SPW-372 Water Dec 1990 Gross alpha <0.3 <1 Gross beta <0.8 <4 a low level of Sr-90 concentration in milk (1 - 5 pCi/L) is not unusual. 158
~
Jf flHL. BLIND 01 Revision 0, 12 29 86 ATTACHMENT B ACCEPTANCE CRITERI A FOR "$PlKE0" SAMPLES LABORATORY PRECISION: ORE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSES 8 One Standard Deviation Analysis Level for Single Determination Gama Emittert 5 to 100 pCi/ liter or kg 5 pC1/ liter
>100 pCi/ liter or k- 5% of known value Strontium 89b 5 to 50 pC1/ liter or kg 5 pC1/ liter
>50 pCi/ liter or kg 10% of known value Strontium 90b 2 to 30 pCi/ liter or kg 3.0 pCi/ liter
>30 pC1/ liter of kg 10% of known value Potassium >0.1 g/ liter or kg 5% of known value Gross Alpha <20 pCi/ liter 5 pCi/ liter
>20 pC1/ liter 25% of known value Gross Beta <100 pCi/ liter 5 pC1/ liter
>100 pCi/ liter 5% of known value Tritium (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 Radium-228 Plutonium 0.1 pCi/ liter, gram, 10% of known value or sample lodine-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 Nickel-63b , >35 pCi/ liter 15% of known value Technetium-99b Iron-55b 50 to 100 pCi/ liter 10 pCi/ liter
>100 pCi/ liter 10% of known value a
From EPA publication, " Environmental Radioactivity Laboratory Intercompari-b son Studies Program, Fiscal Year 1981-1982 EPA-600/4-81-004 TIML limit. l l 159
ADDENDUM TO APPENDlX IV The following is an explanation of the reasons why certain samples were outside J the control limit specified by the Environmental Protection Agency for the Interlaboratory Comparison Program starting January 1987. EPA TIML Control Result Limit Lab Code Analysis (pCi/L)a (pCi/L)a Explanation STM 504 Sr-89 57.014.3 60.3-77.7 Milk had high fat content which Sr-90 32.011.0 32.4-37.6 made analyses difficult. Ad-dition of errors to TIML result would put values within EPA j control limits. EPA also had the same probicm in analyzing its own sample. STW-511 Ra-228 6.111.4 4.6-8.0 TIML results are usually within EPA control limits. Analysis of the next sample was within EPA control limits. No further action is planned. STW-516 Cr-51 80.3217.5 61 .3-78.7 Results in the past have been within EPA control limits and TIML will monitor the situation in the future. STF-524 K 1010.71158.5b 1123.5-1336.5b Error in transference of data. Correct data was 1105133 mg/kg. Results in the past have been within the limits and TIML will monitor the situation in the future. STW-532 1-131 9.012.0 6.2-8.8 Sample recounted af ter 12 days. The average result was 8.811.7 pC1/L (within EPA control limits). The sample was recounted-in order to check the decay. Results in the past i have been within the limits and TIML will continue to monitor the situation in the future. 8 Reported in pCi/L unless otherwise noted. b Concentrations are reported in og/kg. 160
ADDENDUM TO APPENDlx IV (continued)
._._.n.. f EPA j TIML Control Result Limit Lab Code Analysis (pC1/L)a (pCi/L)a Explanation
.n.-,..
STW-534 Co-60 63.321.3 41.3-58.7 High level of Co-b0 vat 4w to .' contaminatko of t'<aker. Besker L was disi.mded upu discovery of J-contamination and sample was l. recounted,, Recount results t 53.N.5 LN 50.912.4 pCi/L. ( STM-554 Sr-90 51.022.0 54.8-65.2 T1e cause of lew result was due to very high fat content in the mitt, it should be roted that H% of all participanti f ailed tnis te:;t . Al to , '.ne average for oll carticipar,ts was 54.0 pCi/l befove the Grubb and 55.8 pCi/L af; w the Grubb. STW-560 Pu-239 5.821.1 3.5-4.9 The cause of h!gh results is not known it is 5 iMacted that the standard as 30*. properly calibrated by supt/ tier and is under investigation. New Pu-236 star. dant was obtained and will be usni for the next test. STW-568 Ra-228 2.611.0 2.7-4.5 The cause of low results is not k n o wn . Next EPA crosscheck results were within the control lirits . No further action is pl armed , STM-570 Sr-89 26.0210.0 30.3-47.7 The cause of low results was Sr-90 45.724.2 49.8 60.2 falsely high recovery due to suspected t re:omplete calcium removal. Since EPA sample was used up, internal spike was prepared and anclyzed. The results were wi tr<in control limits (See table A-3, sampl e QC-MI-24 ) . No further action is planned. a Reported in pCi/L unless otherwise noted. 161
l-i ADDEt40Vt1 TO APPENDIX IV (continued) EPA TIML Control Resul.t Limit Lab Code Analysis (pCi/L)a (pCi/L)a Expl anati on STW-589 Sr-90 17.321.2 17.4-22.6 Sample was reanalyzed in tri-plicate; results of reanalyses 18.811.5 pCi/L . No further action is planned. STM-599 K 1300.0 69.2c 1414.7-1685.3c Sample was reanalyzed in trip-licate. Results of reanalyses, 1421.7295.3 mg/L. The cause of low results is unknown. STW-601 Gross 11.022.0 11.6-32.4 Sample was reanalyzed in trip-Alpha licate. Results of reanalyses, 13.411.0 pCi /L . a Reported in pCi/L unless otherwise noted. c Concentratiens are reported in n9/L. 162
. APPENDIX V ADDENDA 5 163
BYRON NUCLEAR POWER STATION EFPLUENT AND WASTE DISPOSAL SEMI- ANNUAL REPORT l JANUARY TO' JUNE 1990 l l ADDENDUM i A. The following data is the estimated composition of Byron's solid waste streams t , 1
- 1. Dry Active Waste (DAW) 2. Primary Resin 3. Radwaste Resin i
C-14 4.3% -Mu-54 19.26% Mn-54 3.26% Mn-54 1.53% Co-58 4.25% Co-58 41.80% Pe-55 60.6% Co-60 14.06% Co-60 7.51% Co-58 13.3% Cs-134 3.12% Cs-134 16.70% Co-60 15.5% Cs-137 5.04% Cs-137 15.20% Cs-134 1.3% H 0.40% H-3 0.037% Cs-137 :1.4% C-14 3.83% C-14 0.312% Ni-63 2.06% Pe-55 47.00% re-55 7.19% Ni-63 3.03% Tc-99 0.007% Tc-99 0.005% St-90 0.0016% I-129 0.0074 I-129 0.0001% Tc-99 0.0026% Pu-239 0.003% 1-129 0.0004% Pu-238 0.008% ; Pu-239 0.0001% Am-241 0.024% Pu-238 0.0001% Cm-244 0.026% Am-241 0.0001% Ni-63 1.44%
-CM-244 0.0001 SB-125 2.46%
Pu-241 0.004% I-131 3.80% SR-90 0.024% PU-241 0.092% B. There were no major changes or modifi ations to the PCP or to any 11guld, gaseous or solid radwaste treatment systems for this period. There was a Radwaste Vendor charge from Hittman Services to Nu Pac Services. Nu Pac
'Syrvices is responsible for recin and fiator shipments.
C. . Per Technical Specification (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 Technical-Specifications:
- 1. ORE-PR002-Gas Decay Tank Effluent was inoperable for greater-than 14 days. The extended period of inoperability was due to difficulties in troubleshooting the problem.
- 2. : 0RE-PR041-Condensate polisher sump discharge was inoperable.for greater than 30 days. The estended period of.inoperability was due to noise spikes which made it difficult to identify the problem.
(2308s/45) 164 2
. .m. - , _ _. . _ _ ._ -_ . _ __ --- - _ , _ ~ , . . , _
D. Error Analysis The following is an estiaate 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% y nt Stack floy ntes error = 1.5% Tota'. error = 11 - 12%
- 2. Liquid Effluents Sampling error = 1%
Calibration error = 10% Sample volume error = 1% Ditch uged volume error = 1% Total error = 10%
- 3. Waste Resin Sampling error = 5%
Counting Statistics error = 7% Unight error = 1% V3tl.umit_M r o r = 5) Total error = 10%
- 4. DAW Counting Statistics error = 7%
Calibration error = 10% Neight error = 2% Total error = 12.4% E. Meteorological and environmental impact information is reported in the Station Annual Radiological Environmental Operating Report as required by Technical Specification 6.9.1.6. F. No limits were exceeded in liquid hold up tanks as stated in Technical Specifications 3.11.1.4 or in waste gas decay tanks as sta'ed t la Technical Specifications 3.11.2.6. G. There were no irradiated fuel shipments during this period. H. There are no elevated releases. All releases are considered ground level releases. (2308s/45) 16 5
__ _ -. . . . . . . _ - . .. _ _._ _ _ _ _.-. _ _ -.-.._ _ m._. _ _. _ . BYRON NUCLEAR POWER STATION . EFTLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT JULY TO DECEMBER:1990
-)
ADDENDUM
'A.- The following data is the estimated composition of Byron's solid waste streams: .
t L1. Dry Active Waste (DAW) 2.- Primary Resin 3. Radwaste Resin l L C-14 1.44% Mn-54 19.26% Mn-54 1.72% : Mn-54 0.3% Co-58 4.25% Co-58 4.2% ! Fe-55 70.6% Co 14.06% Co-60 19.4% Co-58 .1.10% Cs-134 3.12% Cs-134 7.4% Co-60 3.10% -Cs-137 5.04% Cs-137 .17.2% Cs-134- 0.20% H-3 040 % H-3 0'.01%
"Cs-137' O.80% C-14 3.83% C-14 10.56%
'Ni-63L-22.40%L Fe-55 47.00% Fe-55 12.5%
.Tc-99 .023% Ni-63 3.03% Tc-99 005%
~1-129 .023% -Sr-90 -0.0016% I-129 .n24% -
Tc-99 0.0026% Ni-63 2/.0% "
-I-129- 0.0004%
Po-239 0.0001% lu 238 0.0001%' -
~*
-Am-241 0.0001%
Cm*244 0.Mtl% P!-241 C.004% ? B. ;-Thornere iso major changes r modiT ;ations -to the Pti or to any liquid, , igaheous or' solid radwaste treatme ly6tems fo: Ot ti period. Syron Station '
'.oati;tues/ te utili=e the service- f Nu. Pac :ior deverering and coliotitcation p ,
servicesi -i i < C. :Per-Technical Specification (3.3.3.9 an1 3.5.3i1N , the to11 cuts 's 4 inauca ry . o f., e f flue ht ; rien t t o r ir,3 inntrumentu' ton-inoperable for a #.3;,od c,f
- _ time greater than J rcifief in Technical-Specificationer a {p^
- 1. . . ORE-PR041-Cond_ensate polikher sump disch&rge ga inoperab'.4
- for greater than 30 days. The- extended period of .aoperabiy ,
n, was due to *oise spikes. j ni Error Analysis. I
-The'following'i. an estimat of the errors associated with effluent monitcrir.3 andianalysis. : The cettmate it' calculated using tin quare ,
Moot:of the cum of.the squares methodology, 2
- 1. Caseous Effluents Sc. ipi ttd :e rror = 1 to 3.5%- .
- p. Calioration#rror = 10% -'
f -Counting : Statistics error = 5% 71ent Stack flowrates error = 1.5% Total error == 11 - 12*f 166 2
- -. . - a. - . - . - . - _ - - - - . - . .. - -. . . ,
- 2. Liquid Effluents Sampling error = 1%
Calibration error = 10% Sample volume error = 1% , Discharged volume error = 2% Total error = 10%
- 3. Weste Resin Sampling error a 5%
Counting Statistica error = 7% Weight error = 1% Volume error = 5% Total error = 10%
- 4. DAW Counting Statistics error = 7%
Calibration error = 10% W61ght e rg = 2% Total error = 12.4%
?.'
E. .Heteorological and -nvirot .) ental it ?act information is reported in t the .ctatica Annual R diological Environmental Opera *ing Report as required by Technical Specification 6.9.1.6, ^ F. No limits vert exceeded in liquid hold up tanke ao stated in Terbnical Specifications 3.11.1.4 or in waste gas decay tanks as stated in Technical Specificati ns 3.11.2.6. C. There were no irradi.ced fuel ehtpmerce during this period. H. There are-no elevats;. relesmes. All re'.aeres are c.onsidered ground level teleases. 167 m s-s & w _ - o? Mn u' 3
., .: -}}