ML20153C749
| ML20153C749 | |
| Person / Time | |
|---|---|
| Site: | Byron  |
| Issue date: | 12/31/1987 |
| From: | Queiro R COMMONWEALTH EDISON CO., TELEDYNE ISOTOPES MIDWEST LABORATORY |
| To: | Davis A NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III) |
| References | |
| BYRON-88-0120, BYRON-88-120, NUDOCS 8805060304 | |
| Download: ML20153C749 (138) | |
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-. BYRON STATION. .
i RADI0 ACTIVE WASTE AND ENVIRONMENTAL MONITORING I
ANNUAL REPORT 1987 t
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l TELEDYNE IS0 TOPES MIDWEST LABORATORY 1
NORTHBROOK, ILLIN01S ,h 4
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APRIL 1988 -
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W RADI0 ACTIVE WASTE AND ENVIRONMENTAL MONITORING ANNUAL REPORT 1987 i
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l APRIL 1988 .
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t TABLE OF CONTENTS Page INTRODUCTION ,.......................... 1
SUMMARY
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 1.0 EFFLUENTS 1.1 Gaseous ........................... 3 1.2 Liquid . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 2.0 SOLID RADI0 ACTIVE WASTE . . . . . . . . . . . . . . . . . . . . . . 3 3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways .................. 3 3.2 Liquid Effluent Pathways . . . . . . . . . . . . . . . . . . . 5 4.0 SITE METEOROLOGY- ......................... 5 5.0 ENVIRONMENTAL MONITORING ..................... 5 5.1 Gamma Radiation ....................... 6 5.2 Airborne I-131 and Particulate Radioactivity . . . . . . . . . 6 5.3 Terrestrial Radioactivity .................. 6 5.4 Aquatic Radioactivity .................... 7 5.5 Milk . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8 5.6 S amp l e Co l l ec t i o n s . . . . . . . . . . . . . . . . . . . . . . 8 6.0 ANALYTICAL PROCEDURES . . . . . . . . . . . . . . . . . . . . . . . 8 7.0 MILCH ANIMAL CENSUS . . . . . . . . . . . . . . . . . . . . . . . . 8 8.0 NEAREST RESIDENT CENSUS . . . . . . . . . . . . . . . . . . . . . . 11 9.50 INTERLABORATORY COMPARIS0N PROGRAM RESULTS ............ 12 AF'PENDIX I - DATA TABLES AND FIGURES . . . . . . . . . . . . . . . . . . 34 Station Releases Table 1.1-1 Gaseous Effluents .................. 35 Table 1.2-1 Liquid Effluents . . . . . . . . . . . . . . . . . . . 43 iii
O TABLE OF CONTENTS-(continued)
Page APPENDIX I - DATA TABLES AND FIGURES
. Station Releases (continued)
< Table 2.0-1 Solid Waste Shipments ................ 47 Figure 3.1 Figure 3.1-4 Isodose and Concentration Contours . . . . . . . . . . 59 Table 3.1-1 Maximum Doses Resulting from Airborne Releases . . . . 63 Table 3.2-1 Maximum Doses Resulting from Liquid Discharges . . . . 65
. Environmental Monitoring Figure 5.0 Figure 5.0-4 Locations of Environmental Radiological Stations . . . 67 Table 5.0-1 Environmental Radiological Monitoring Sampling Sites . . . . . . . . . . . . . . . . . . . 71 Table 5.0-2 Environmental Radiological Monitoring Program .... 72 Table 5.0 Table 5.0-6 Environmental Summary Tables . . . . . . . . . . . . . 80 Table 5.1-1 Gamma Radiation Measurements (TLD) . . . . . . . . . . 96 APPENDIX II - METEOROLOGICAL DATA ................... 99 APPENDIX III - LIST OF MISSING SAMPLES . . . . . . . . . . . . . . . . . 128 ADDENDUM . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 130 iv
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r INTRODUCTION Byron Station, a two-unit DWR 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. 1 loaded fuel in November 1984 and went on line:
February 2,1985. Unit No. 2 went on line January 9,1987. The plant has been designed to keep releases to the environment at levels below those specified in the regulations.
Liquid effluents from Byron Station are released into the Rock River in controlled batches af ter radioassay of each batch. Gaseous effluents are released to the atmosphere after delay to permit decay of short half-life.
gases. Releases to the atmosphere are calculated on the basis of analyses' of daily grab samples of noble gases and continuously collected composite samples of iodine and particulate matter. The results of effluent analyses -
are summarized on a monthly basis and reported to the Nuclear Regulatoryt Commission as required per Technical Specifications. Airborne concentrations of noble gases, I-131 and particulate radioactivity in off-site areas are' calculated using effluent and meteorological data on isotopic composition of-effluents.
Environmental monitoring is conducted by sampling at indicator and reference (background) locations in the vicinity of the Byron Station to measure changes in radiation or radioactivity levels that may be attributable to plant opera-tions. If significant changes attributable to Byron Station are measured, these changes are correlated with effluent releases. External gama radiation exposure from noble gases and I-131 in milk are the most critical pathways at this site; however, an environmental monitoring program is conducted which includes other pathways of less importance.
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SUMMARY
Gaseous and liquid effluents for the period remained at a fraction of the Technical Specification limits. Calculations of environmental concentrations based on effluent, Rock River flow, and meteorological data for the period indicate that consumption by the public of radionuclides attributable to the plant are unlikely to exceed the regulatory limits. Gamma radiation exposure from noble gases released to the atmosphere represented the critical pathway for the period with a maximum individual dose estimated to be 1.01E-03 mrem for the year, when a shielding and occupancy factor of 0.7 is assumed. The assessment of radiation doses are performed in accordance with the Offsite Dose Calculation Manual (0DCM). The results of analysis confirm that the station is operating in compliance with 10CFR50 and 40CFR190.
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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 1.30E+03 curies of fission and activation gases was released with a maximum release rate of 4.98E+04 pCi/sec.
A total of 1.23E-02 curies of I-131 and I-133 was released during the year.
A total of 1.32E-04 curies of beta-ganrna emitters and an undetect-able amount of alpha emitters were released as airborne particulate matter.
A total of 0.98 curies of tritium was released.
1.2 Liquids Released to the Rock River A total of 3.68E+07 liters of radioactive liquid waste (prior to dilution) containing 2.48 curies (excluding tritium, gases, and alpha) were discharged after dilution with a total of 3.65E+10 liters of water. These wastes were released at a nunthly average concentration of 7.00E-08 pCi/ml, discharged on an unidentified nuclide basis. An undetectable amount of alpha radioactivity and 410.1 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 Richland, Washington; and Barnwell Nuclear Center, South Carolina. The record of waste shipments is summarized in Table 2.0-1.
3.0 00SE TO MAN 3.1 _G_aseous Effluent Pathways Gamma Dose Rates Gamma air and whole body dose rates off-site were calculated based on measured release rates, isotopic composition of the noble gases, "
and 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 dose to an individual would_ be 1.01E-03 mrem for the year, with an occupancy or shielding factor of 0.7 included. The maximum gama air dose was 4.05E-03 mrad.
Beta Air and Skin Rater The range of beta particles in air is relatively small (en the order of a few meters or less); consequently, plumes of gaseous effluents may be considered "infinite" for purpose of calculating the dose from beta radiation incident on the skin. However, the actual dose to sensitive skin tissues is difficult to calculate because this depends on the beta particle energies, thickness of inert skin, and clothing covering sensitive tissues. For purposps of this report the skin is take1 to have a thickness of 7 mg/cmd and an occupancy factor of 1.0 is used. The skin dose from beta and gama radiation for the year was 8.22E-03 mrem.
The air concentrations of radioactive noble gases at the off-site receptor locations are given in Figure 3.1-2. The maximum off-site beta air dose for the year was 1.66E-02 mrad.
Radioactive Iodine The human thyroid exhibits a significant capacity to concentrate ingested or inhaled iodine, and the radioiodine, I-131, released during routine operation of the plant, may be made available to man thus resulting in a dose to the thyroid. The principal pathway of interest for this radionuclide is ingestion of radioiodine in milk by an infant. Calculation made in previous years indicate that contributions to doses from inhalation of I-131 and I-133, and I-133 in milk, ara negligible.
Iodine-131 Concentrations in Air The calculated concent ation contours for I-131 in air are shown in Figure 3.1-3. Included in these calculations is an iodine cloud depletion factor which accounts for the phenomenon of elemental iodine deposition on the ground. The maximum o concentration is estimated to be 1.38E-03 pCi/m{f-site average for the year.
Dose 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 6.25E-02 mrem during the year (Table 3.1-1).
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Cnncentrations of Particulates in Air Concentration contours of radioactive airborne particulates are shown in Figure 3.1-4. The maximum of f-site average level is estimated to be 1.75E-05 pCi/m3 Summary of Doses Table 3.1-1 summarizes the doses resulting from releases of airborne radioactivity vir the different exposure pathways. ,
3.2 Liquid Effluent Pathways The three principal pathways through the aquatic environment for potential doses to man from liquid waste are ingestion of potable water, eating aquatic foods, and exposure while walking on the 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
- GI tract, thyroid, bone and skin; specific parameters for use in the equations are given in the Commonwealth Edison Off-site Dose Calcu-lation Manual. The maximum whole body dose for the year was 7.66E-02 mrem and no organ dose exceeded 1.62E-01 mrem.
4.0 SITE METEOROLOGY A summary of the site meteorological measurements taken during each quarter of the year is given in Appendix II. The data are presented as cumulative joint frequency distributions of 250' level wind direction and wind speed class by atmospheric stability class determined from the temperature difference between the 250' and 30' level s . Data recovery for these measurements was about 98.8%.
5.0 ENVIRONMENTAL MONITORING Tables 5.0-1 and 5.0-2 provide an outline of the radiological environ-mental monitoring program as required in the Technical Specifications.
Except for tables of special interest, tables listing all data are no longer included in the annual report. All data tables are available for inspection at the Station or in the Corporate offices.
Specific findings for various environmental media are discussed below.
- Nuclear Regulatory Commission, Regulatory Guide 1.109 (Rev. 1).
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5.1 Gamma Radiation External radiation dose from on-site sources and noble gases re-leased to the atmosphere was measured at nine indicator and three reference (background) locations using CaSO 4:Dy thermoluminescent dosimeters (TLD). A comparison of the TLD results for reference stations with on-site and off-site indicator stations is included in Table 5.1-1. Additional TLDs, a total of 64 were installed on September 28, 1981, such that each sector was covered at both five miles and the site boundary.
5.2 Airborne I-131 and Particulate Radioactivity Concentrations of airborne I-131 and particulate radioactivity at moni toring locations are sumarized in Tables 5.0-3 through 5.0-6.
Locations of the samplers are shown in Figure 5.0-1. Airborne I-131 remained below the LLO of 0.07 pCi/m3 throughout the year.
Gross beta concentrations ranged from 0.005 to 0.050 pCi/m3, and averaged 0.027 pCi/mJ, similar to the average concentration in 1986 (0.026 pCi/m3). The average of 0.G26 pCi/m3 for 1986 does not include the results from May 12 to June 9, 1986, which were influenced by the accident at Chernobyl. '
All gamma-emitting isotopes and Sr-89 and -90 activities were below their respective LLD levels. No radioactivity attributable to plant operation was detected in any other sample.
5.3 Terrestrial Radioactivity Precipitation samples were collected monthly from four milk sampling locations and analyzed for gross beta, tritium, strontium-89 and
-90, and gamma-emitting isotopes. Except for gross beta and tritium, all radioactivity was belnw the limits of detection indicating that there was no measurable amount of radioactivity attributable to the station releases.
Annual mean gross beta concentrations measured 31.0 pCi/1, which is the level expected in precipitation samples.
Tritium was detected in one sample and measured 223 pCi/1, barely above the LLD level of 200 pCi/1.
Vegetables were collected in August and analyzed for gross beta, strontium-89 and -90, and gama-emitting isoto pes . In addition, green leafy vegetables were analyzed for iodine-131. Gross beta concentration ranged from 1.5 to 5.0 pCi/g wet weight and averaged 2.9 pCi/g wet weight. The range and mean values were those expected in the vegetation samples. All other isotopes were below the limits of detection indicating that there was no measurable amount of radioactivity attributable to the station releases.
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Cattle feed and grass samples were collected quarterly from milk sampling locations and analyzed for gross beta, strontium-89 and -90 and gama-emitting isotopes. Except for gross beta, the level of radioactivity was be: low the detection limits. Gross beta concen-trations were at the level usually encountered in these samples.
Well water was collected quarterly from two off-site wells and-analyzed for gross beta, tritium, strontium-89 and -90, and gama-emittinng isotopes. The annual mean gross beta concentration was 7.5 pCi/1. All other results were below the lower limits of detec-tion.
5.4 Aquatic Radioactivity Surf ac ? water samples were collected weekly from five locations and analyzed for gross beta content. Weekly samples from the Rock River near the intake and discharge pipes were composited monthly and analyzed for gama-emitters, tritium, and strontium-89 and -90.
In all samples, except from discharge pipe, gross beta concentra -
tions averaged 3.0 pCi/1. Cesium-134 and -137 concentrations were below the LLD level of 10 pCi/1. Strontium-89 was below the LLD of 10 pCi/1, and t.trontium-90 concentrations were below the LLO of 2 pCi/l in all samples. Tritium concentration was below the LLD of.
200 pCi/l in all samples but two (279 and 267 pCi/1). These levels were similar to those obtained during the preoperational program,-
indicating that there was no measurable amount of radioactivity due to station operation.
At discharge pipe, gross beta averaged 10.1 pCi/1, and tritium averaged 56,350 pCi/1, ranging from 200 to 499,640 pCi/1. Strontium
-89 and strontium-90 were below their respective LLD levels of 10 and 2 pCi/l in all samples. Cs-134 and Cs-137 were below the LLO level of 10 pCi/1. All other gamma-emitters were below their re-l spective LLDs. Elevated levels of gross beta and tritium at dis-charge pipe are attributable to the station operation.
! Sediment samples were collected three times, from cne control and i one indicator location, and analyzed for gross beta and gamma-emitters. Mean gross beta activity in indicator samples measured l
11.4 pCi/g and 10.9 pCi/g at control location. Cesium-137 was i
detected in ane indicator sample (1.30 pC1/g) and in one control sample (0.20 pCi/g) Presence of Cs-137 in indicator sample is attributable to the station operation.
l Collection sites, frequency, and analysis of aquatic vegetation were identical to those of sediments. As expected, the gross beta i concentration was lower for aquatic vegetation than for sediments.
All gama-emitters were below the detection levels.
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Levels of gamma radioactivity in fish were measured and found in all cases to be below the lower limits of detection for the program.
Gross beta concentration averaged 2.5 pCi/g wet weight and was at the level expected in fish.
5.5 Milk Milk samples were collected monthly from November through April and bi-weekly from May through October and analyzed for strontium-89 and -90, iodine-131 and gamma-emitting isotopes. Sr-90 concentra-tions were variable within the usual range for milk and Sr-89 was below the limit of detection.
Cs-134 and Cs-137 were below the LLD level of 5 pCi/1. All other gamma-emitting isotopes, except naturally-occurring X-40, were below their respective LLDs. There was no indication of the effect on the environment due to station operation.
5.6 Sample Collections All samples were collected as scheduled except those listed in Listing of Missed Samples, Appendix III.
6.0 ANALYTICAL PROCEDURES A summary of the procedures used for analyzing radioactivity in environ-mental samples is given in Appendix Ill of the report for the period January-December 1985. Procedures used during the period covered by this report remained essentially unchanged.
7.0 MILCH ANIMAL CENSUS A census of milch animals was conducted within five miles of the Station.
The survey was conducted by "door-to-door" canvas and by information from Illinois Agricultural Agents. The census was conducted by P. Coulter on August 10, 1987. Dairies that were surveyed are listed below.
A. Site Boundary to 2 mi.
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B. 2 mi to 5 mi.
- 1. Reevert's Dairy Farm 5674 N. German Church Road Route 1 Byron, Illinois 2.1 miles 0 037' Milks 20 cows 8
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- 2. Ed Seabold Dairy Farm (BY-20) 6021 N. German Church Road i
Route 1 Byron, Illinois 2.8 miles 0 40*
Milks 107 cows
- 3. J. A. Reeverts Pine Hill Dairy (BY-15) 5728 E. Holcomb Road Route 1 Oregon, Illinois 3.2 miles 0108*
Milks 17 cow;
- 5. Kenneth Druien (Bf-16) 1725 N. Marril Road Route 1 Oregon, Illinois 3.3 miles 0134' Milks 37 cows
- 6. Oltmann Dairy Farm; Richard 01tmann, owner 1858 N. German Church Road Route 1 Oregon, Illinois 2.2 miles 0180*
Milks 18 cows
Milks 52 cows 9
- 8. Ashelford Dairy Farm 4210 IL Route 2 Route 3
- Oregon, Illinois 2.6 miles 9 275' Milks 27 cows
- 9. CAM-DEE Farms, Gerald DeVries, owner 5213 N. Town Hall Road Route 3 Oregon, Illinois 3.3 miles 0 290' '
- 10. Allen Camling, Jr.
285 West Camling Road Route 3 Oregon, Illinois 3.4 miles 0 299*
Milks 50 cows
- 11. Duane Camling 50 East Camling Road Route 3 Oregon, Illinois 3.2 miles 0 305' Milks 26 cows C. Sampling Locations BY-15 J. A. Reevert's Pine Hill Dairy Milks 17 cows Diet:
May - October: Pasture 5 acres. Hay, corn, protein /
mineral supplement November - April: Feedlot 1 acre. Hay, corn, protein /
supplement 10
BY-16 Kenneth Drufen Farm Milks 37 cows Diet:
May - October: Pasture 10 acres. Hay corn, oats and >
protein / mineral supplement November - April: Feedlot less than 2 acres. Hay, corn, silage, oats, and protein / mineral supplement BY-17 Bosecker/Lingel Farm Milks 35 cows Diet:
May - October: Pasture feedlot 2 acres. Green chop, corn, hay, oats, protein / mineral supplement November - April: Feedlot 2 acres. Silage, haylage, corn, oats, protein / mineral supplement BY-20 Ed Seabold Farm Milks 107 cows Diet:
May - October: Feedlot less than 2 acres. Haylage, hay, corn, protein / mineral supplement November - April: Feedlot less than 2 acres. Haylage, hay, corn, protein / mineral supplement 8.0 NEAREST RESIDENT CENSUS The census was conducted by P. Coulter on August 10, 1987.
Nearest residence of the Byron Station within a five (5) mile radius.
N 1.4 miles NNE 1.8 miles NE 1.4 miles ENE 1.3 miles E 1.2 miles ESE 1.6 miles SE 1.3 miles SSE 0.8 miles S 0.7 miles SSW 0.6 miles SW 0.8 miles WSW 1.7 miles W 1.9 miles WNW 2.1 miles NW 0.8 miles NNW 1.2 miles 11
9.0 INTERLABORATORY COMPARIS0N 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 concen-trations of radionuclides known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent check on the laboratory's analytical procedures and to alert it to any possible problems.
Participant laboratories measure the concentrations of specified radio-nuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used.
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The results in Table A-1 were obtained through participation in the environmental sample crosscheck program for milk, water, air filters, I
and food samples during the period May 1984 through December 1987. This program has been conducted by the U. S. Environmental 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 l (TLDs) during the period 1976, 1977, 1979, 1980, 1984, and 1985-1986 l through participation in the Second, Third, Fourth, Fifth, Seventh, !'
and Eighth International Intercomparison of Environmental Dosimeters under the sponsorships listed in Table A-2. l Table A-3 lists results of the anaises on in-house spiked samples.
Tabel A-4 lists results of the analyses on in-house "blank" samples.
Attachment B lists acceptance criteria for "spiked" samples.
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I Table A-1. U.S. Environmental Protection Agency's crosscheck program, com-parison of EPA and Teledyne Isotopes Midwest Laboratory results for milk, water, air filters, and food samples,1984 through 1987.a Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis 12ac Is, N=1 Control Limits STW-358 Water May 1984 Gr. alpha 3.010.6 315.0 0.0-11.7 Gr. beta 6.7 1.2 615.0 0.0-14.7 STM-366 Milk June 1984 Sr-89 21i3.1 25 5.0 16.3-33.7 Sr-90 1312.0 17tl.5 14.4-19.6 I-131 46i5.3 4316.0 32.6-53.4 Cs-137 3814.0 3515.0 26.3-43.7 K 15771172 1496175 1336-1626 STW-368 Water July 1984 Gr. alpha 5.111.1 615.0 0.0-14.7 Gr. beta 11.9 2.4 1315.0 4.3-21.7 STW-369 Water August 1984 I-131 34.3i5.0 34. 016.0 23.6-44.4 STW-370 Water August 1984 H-3 30031253 2817f356 2200-3434 STF-371 Food July 1984 Sr-89 22.015.3 25.015.0 14.3-33.7 Sr-90 14.713.1 20.011.5 17.4-22.6 I-131 <172 39.016.0 28.6-49.4 Cs-137 24.015.3 25.015.0 14.3-33.7 K 25031132 2605i130 2379-2831 STAF-372 Air August 1984 Gr. alpha 15.311.2 17f5.0 8.3-25.7 Gr. beta 56.0f0.0 42.3-59.7 Filter 5115.0 Sr-90 14.3tl.2 18tl.5 15.6-20.4 Cs-137 21.012.0 1515.0 6.3-23.7 STW-375 Water Sept 1984 Ra-226 5.110.4 4. 91 0. 7 3.6-6.2 Ra-228 2.2i0.1 2.310.4 1.7-2.9 STW-377 Water Sept 1984 Gr. alpha 3.3tl.2 5.015.0 0.0-13.7 Gr. beta 12.712.3 16.0i5.0 7.3-24.7 STW-379 Water Oct 1984 H-3 28601312 28101205 2454-3166 STW-380 Water Oct 1984 Cr-51 <36 40f5.0 31.3-48.7 Co-60 20.3fl.2 20i5.0 11.3-28.7 Zn-65 150i8.1 14715.0 138.3-155.7 Ru-106 <30 4715.0 36.3-55.7 Cs-134 31.317.0 3115.0 22.3-39.7 Cs-137 26.711.2 2415.0 15.3-32.7 13
Table A-1. (continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis
- 2cc Is, N=1 Control Limits STM-382 Milk Oct 1984 Sr-89 15.714.2 2215.0 13.3-30.7 Sr-90 12.7tl.2 1611.5 13.4-18.6 I-131 41.7t3.1 4216.0 31.6-42.4 Cs-137 31.316.1 3215.0 23.3-40.7 K 1447166 15.7i76 1386-1648 STW-384 Water Oct 1984 Gr. alpha 9.7 1.2 1415.0 5.3-22.7 (Blind) Sample A Ra-226 3.310.2 3.010.5 2.2-3.8 Ra-228 3.4*l.6 2.110.3 1.6-2.6 Uranium NA8 0.0-15.4 Sample B Gr. beta 48.315.0 6415.0 55.3-72.7 Sr-89 10.714.6 1115.0 2.3-19.7 Sr-90 7.3fl.2 1211.5 9.4-14.6 Co-60 16.3fl.2 1415.0 5.3-22.7 Cs-134 <2 215.0 0.0-10.7 Cs-137 16.711.2 1415.0 5.3-22.7 STAF-387 Air Nov 1984 Gr. alpha 18.711.2 1515.0 6.3-23.7 Filter Gr. beta 59.015.3 5215.0 43.3-60.7 Sr-90 18.3fl.2 21i1.5 18.4-23.6 Cs-137 10.311.2 1015.0 1.3-18.7 STW-388 Water Dec 1984 I-131 28.0i2.0 3616.0 25.6-36.4 STW-389 Water Dec 1984 H-3 35831110 3182f360 2558-3806 STW-391 Water Dec 1984 Ra-226 8.411.7 8.6tl.3 6.4-10.8 Ra-228 3.lio.2 4.110.6 3.0-5.2 STW-392 Water Jan 1985 Sr-89 <3.0 3.015.0 0.0-11.7 Sr-90 27.315.2 30.011.5 27.4-32.6 STW-393 Water Jan 1985 Gr. alpha 3.3tl.2 Sf5.0 0.0-13.7 Gr. beta 17.3t3.0 1515.0 6.3-23.7 STF-395 Food Jan 1985 Gr. alpha 4.712.3 6.015.0 0.0-14.7 Gr. beta 11.3fl.2 15.0t5.0 6.3-23.7 Sr-89 25.316.4 34.015.0 25.3-42.8 Sr-90 27.018.8 26.011.5 23.4-28.6 I-131 38.012.0 35.016.0 24.6-45.4 Cs-137 32.712.4 29.015.0 20.3-37.7 K 14101212 13821120 1174-1590 14
Table A-1. (continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis 120c Is, N=1 Control Limits
.STW-397 Water Feb 1985 Cr-51 <29 4815.0 39.3-56.7 Co-60 21.313.0 2015.0 11.3-28.7 Zn-65 53.7t5.0 55t5.0 46.3-63.7 Ru-106 <23 2515.0 16.3-33.7 Cs-134 32.311.2 3515.0 26.3-43.7 Cs-137 25.313.0 2515.0 16.3-33.7 STW-398 Water Feb 1985 H-3 38691319 37961634 3162-4430 STM-400 Milk March 1985 1-131 7.3f2.4 9. Dt0. 9 7.4-10.6 STW-402 Water March 1985 Ra-226 4.610.6 5.010.8 3.7-6.3 Ra-228 <0.8 9.011.4 6.7-11.3 Reanalysis Ra-228 9.0f0.4 STW-404 Water March 1985 Gr. alpha 4.7t2.3 615.0 0.0-14.'7 Gr. beta 11.311.2 1515.0 6.3-23.7 STAF-405 Air March 1985 Gr. alpha 9.311.0 10.015.0 1.3-18.7 Filter Gr. beta 42.011.1 36.015.0 27.3-44.7 Sr-90 13.311.0 15. 0il . 5 12.4-17.6 Cs-137 6.3fl.0 6.015.0 0.0-14.7 STW-407 Water April 1985 I-131 8.010.0 7.510.8 6.2-8.8 STW-408 Water April 1985 H-3 33991150 35591630 2929-4189 STW-409 Water April 1985 (Blind) Gr. alpha 29.711.8 32.015.0 23.3-40.7 Sample A Ra-226 4.410.2 4.110.6 3.1-5.1 Ra-228 nae 6.210.9 4.6-7.8 .
Uranium NA8 7.0 6.0 0.0-17.4 Sample B Gr. beta 74.3111.8 72.015.0 63.3-80.7 Sr-89 12.317.6 10.015.0 1.3-18.7 Sr-90 14.7t2.4 15.011.5 12.4-17.6 Co-60 14.7i2.4 15.015.0 6.3-23.7 Cs-134 12.012.0 15.0i5.0 6.3-23.7 Cs-137 14.012.0 12.015.0 ' 3-20.7 15
Table A-1. (continued)
~'
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis doc Is, N=1 Control Limits STW-413 Water May 1985 Sr-89 36.0112.4 39.015.0 30.3-47.7 Sr-90 14.3t4.2 15.0*1.5 12.4-17.6 STW-414 Water May 1985 Gr. alpha 8.314.1 12.015.0 3.3-20.7 Gr. beta 8.711.2 11.0 5.0 2.3-19.7 STW-416 Water June 1985 Cr-51 44.716.0 44.015.0 45.3-52.7 Co-60 14.3 1.2 14.015.0 5.3-22.7 Zn-65 50.317.0 47.015.0 38.3-55.7 Ru-106 55.315.8 62.015.0 53.3-70.7 Cs-134 32.7tl.2 35.015.0 26.3-43.7 Cs-137 22.7i2.4 20.0i5.0 11.3-28.7 STW-418 Water June 1985 H-3 2446t132 24161351 1807-3025 STM-421 Milk June 1985 Sr-89 10.314.6 11.015.0 2.3-19.7 Sr-90 9.0i2.0 11.011.5 8.4-13.6 I-131 11.7tl.2 11.0i6.0 0.6-21.4 Cs-137 12.7tl.2 11.015.0 2.3-19.7 K 1512i62 1525i132 1393-1657 STW-423 Water July 1985 Gr. alpha 5.010.0 11.015.0 2.3-19.7 Gr. beta 5.0i2.0 8.015.0 0.0-16.7 STW-425 Water August 1985 I-131 25.713.0 33.016.0 22.6-43.4 STW-426 Water August 1985 H-3 4363183 44801447 3704-5256 STAF-427 Air August 1985 Gr. alpha 11.310.6 13.015.0 4.3-21.7 Fil ter Gr. beta 46.011.0 44.0t5.0 35.3-52.7 Sr-90 17.710.6 18.011.5 15.4-20.6 Cs-137 10.310.6 8.0i5.0 0.0-16.7 STW-429 Water Sept 1985 Sr-89 15.7i0.6 20.Di5.0 11.3-28.7 Sr-90 7.0i0.0 7.0il.5 4.4-9.6 STW-430 Water Sept 1985 Ra-226 8.210.3 8.9tl.3 6.6-11.1 Ra-228 4.110.3 4.6t0.7 3.4-5.8 STW-431 Water Sept 1985 Gr. alpha 4.710.6 8.015.0 0.0-16.7 Gr. beta 4.711.2 8.0i5.0 0.0-16.7 16
O Table A-1. (continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Coll ected Analysis 120c 15, N=1 Control Limits STW-433 Water Oct 1985 Cr-51 <13 21.015.0 12.3-29.7 Co-60 19.310.6 20.015.0 11.3-28.7 Zn-65 19.710.6 19.015.0 10.3-27.7 Ru-106 <19 20.015.0 11.3-28.7 Cs-134 17.011.0 20.0f5.0 11.3-28.7 Cs-137 19.311.2 20.0 5.0 11.3-28.7 STW-435 Water Oct 1985 H-3 1957150 19741345 1376-2572 STW-436 Water Oct 1985 437 (Blind) -
Sample A Gr. alpha 53.011.0 52.0i13 29.4-74.6 Ra-226 5.910.1 6.3tl.0 4.1-7.9 Ra-228 S.210.1 10.111.5 7.5-12.7 Uranium nae 8.Di10.4 0.0-18.4 Sample B Gr. beta 85.7t2.5 75.015.0 76.3-83.7 Sr-89 21.311.5 27.0i5.0 18.3-35.7 Sr-90 10.310.6 9.0il.5 6.4-11.6 Co-60 18.311.2 18.015.0 9.3-26.7 Cs-134 16.311.2 18.015.0 9.3-26.7 Cs-137 19.011.0 18.0i5.0 9.3-26.7 STM-439 Milk Oct 1985 Sr-89 50.310.6 48.015.0 39.3-56.7 Sr-90 23.310.6 26.011.5 23.4-28.6 I-131 45.713.2 42.0i6.0 31.6-52.4 Cs-137 60.710.6 56.0t5.0 47.3-64.7 K 1547129 1540i77 1406-1674 STW-441 Water Nov 1985 Gr. alpha 5.3i0.6 10.0i5.0 1.3-18.7 Gr. beta 11.7tl.2 13.0i5.0 4.3-21.7 STW-443 Water Dec 1985 1-131 46.712.1 45.016.0 34.6-55.4 STW-444 Water Dec 1985 Ra-226 6.510.1 7.lil.1 5.2-9.0 Ra-228 6.li0.1 7.311.1 5.4-9.2 STW-445 Water Jan 1986 Sr-89 29.7f2.5 31.015.0 22.3-39.7 Sr-90 13.710.6 15.0fl.5 12.4-17.6 STW-446 Water Jan 1986 Gr. alpha 3.010.0 3.015.0 0.0-11.7 Gr. beta 5.310.6 7.015.0 0.0-15.7 17
Table A-1. (continued)
Concentration in pCi/lb Lab Sample Date- TIML Result EPA Resultd Code Type Collec ted Analysis f2cc Is, N=1 Control Limits STF-447 Food Jan 1986 Sr-89 24.312.5 25.015.0 16.3-33.7 Sr-90 17.310.6 10.0fl.5 7.4-12.6 I-131 22. 712.~ 3 20.016.0 9.6-30.4 Cs-137 16.3 0.6 15.0f5.0 6.3-23.7 K 927146 950i144 701-1199 STW-448 Water Feb 1986 Cr-51 45.013.6 38.0i5.0 29.3-46.7 Co-60 19.7tl.5 18.0i5.0 9.3-26.7 Zn-65 44.0i3.5 40.015.0 31.3-48.7 Ru-106 <9.0 0.015.0 0.0-8.7 Cs-134 28.3i2.3 30.0f5.0 21.3-38.7 Cs-137 23.7*0.6 22.015.0 13.3-30.7 STW-449 Water Feb 1986 H-3 5176t48 52271525 4317-6137 STW-450 Water Feb 1986 V total 8.010.0 9.016.0 0.0-19.4 STM-451 Milk Feb 1986 I-131 7.010.0 9.016.0 0.0-19.4 STW-452 Water March 1986 Ra-226 3.810.1 4.110.6 3.0-5.2 Ra-228 11.0f0.5 12.411.8 9.2-15.5 STW-453 Water March 1986 Gr. alpha 6.710.6 15.015.0 6.3-23.7 Gr. beta 7.310.6 8.015.0 0.0-16.7 STW-454 Water April 1986 I-131 7.0t0.0 9.0i6.0 0.0-19.4
, STW-455 Water April 1986 456 (Blind)
Sample A Gr. alpha 15.0il.0 17.0f5.0 8.3-25.7 Ra-226 3.110.1 2.910.4 2.1-3.7 Ra-228 1.5i0.2 2.0i0.3 1.5-2.5 Uranium 4.7 0.6 5.016.0 0.0-15.4 Sample B Gr. beta 28.711.2 35.0i5.0 26.3-43.7 ,
Sr-89 5.710.6 7.015.0 0.0-15.7 Sr-90 7.010.0 7.0fl.5 4.4-9.6 Co-60 10.7tl.5 10.015.0 1.3-18.7 Cs-134 4.011.7 5.0i5.0 0.0-13.7 Cs-137 5.310.6 5.0i5.0 0.0-13.7 l
18
l Table A-1. (continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Coll ec ted Analysis 120c is, N=1 Control Limits STAF-457 Air April 1986 Gr. alpha 13.710.6 15.015.0 6.3-23.7 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 10.7i0.6 10.015.0 1.3-18.7 STU-458 Urine April 1986 Tritium 4313170 4423i189 4096-4750 STW-459 Water May 1986 Sr-89 4.310.6 5.015.0 0.0-13.7 Sr-90 5.0f0.0 5.011.5 2.4-7.6 STW-460 Water May 1986 Gr. alpha 5.310.6 8.015.0 0.0-16.7 Gr. beta 11.311.2 15.015.0 6.3-23.7 STW-461 Water June 1986 Cr-51 <9.0 0.015.0 0.0-8.7 Co-60 66.0tl.0 66.0i5.0 57.3-74.7 Zn-65 87.311.5 86.015.0 77.3-94.7 Ru-106 39.712.5 50.015.0 41.3-58.7 Cs-134 49.3f2.5 49.015.0 40.3-57.7 Cs-137 10.3tl.5 10.015.0 1.3-18.7 STW-462 Water June 1986 Tritium 3427125 3125i361 2499-3751 STM-464 Milk June 1986 Sr-89 <1.0 0.0i5.0 0.0-8.7 Sr-90 15.310.6 16.011.5 13.4-18.6 I-131 48.312.3 41.0i6.0 30.6-51.4 Cs-137 43.7tl.5 31.015.0 22.3-39.7 K 1567*114 1600180 1461-1739 STW-465 Water July 1986 Gr. alpha 4.710.6 6.Di5.0 0.0-14.7 Gr. beta 18.7tl.2 18.015.0 9.3-26.7 STW-467 Water August 1986 I-131 30.310.6 45.016.0 34.4-55.4 STW-468 Water August 1986 Pu-239 11.3t0.6 10.111.0 8.3-11.9 STW-469 Water August 1986 Uranium 4.010.0 4.0i6.0 0.0-14.4 STAF-470 Air Sept 1986 Gr. alpha 19.3*1.5 22.015.0 13.3-30.7 471 Filter Gr. beta 64.012.6 66.0i5.0 57.3-74.7 472 Sr-90 22.011.0 22.015.0 19.4-24.6 Cs-137 25.7tl.5 22.0i5.0 13.3-30.7 STW-473 Water Sept 1986 Ra-226 6.010.1 6.110.9 4.5-7.7 Ra-228 8.711.1 9.111.4 6.7-11.5 19
l i
Table A-1. (continued),
we Concentration in pCi/lb Lab Sample Date TIMi. Result EPA Resultd Code Type Collected Analysis 12ac Is, N=1 Control Limits J
STW-474 Water Sept 1986- Gr. alpha 16.3t3.2 15.0i5.0 6.3-23.7 Gr. beta 9.0tl.0 8.0i5.0 0.0-16.7 STW-475 Water Oct 1986 Cr-51 63.315.5 59.015.0 50.3-67.7 Co-60 31.0t2.0 31.0t5.0 22.3-39.7 Zn-65 87.3t5.9 85.015.0 76.3-93.7 i Ru-106 74.7t7.4 74. 0* 5. 0 65.3-82.7 Cs-134 25.710.6 28.0i5.0 19.3-36.7 i Cs-137 46.3*1.5 44.015.0 35.3-52.7 l STW-476 Water Oct 1986 H-3 5918i60 59731597 4938-7008 s
SPW-477 Water Oct 1986 478 (Blind)
J Sample A- Gr. alpha 34.016.0 40.0i5.0 31.3-48.7 i j, Ra-226 5.8i0.2 6.0t0.9 4.4-7.6
. Ra-228 2.7tl.0 5.0t0.8 3.7-6.3 Uranium 11.0i0.0 10.0t6.0 0.0-20.4 Sample 8 Gr. beta 38.711.2 51.0t5.0 42.3-59.7 '
- Sr-89 5.0t0.0 10.0i5.0 1.3-18.7 3.0*0.0 4.0t1.5 1.4-6.6 Sr-90 4
Co-60 24.7tl.2 24.015.0 15.3-32.7 ,
! Cs-134 11.0*2.0 12.0i5.0 3.3-20.7 Cs-137 9.311.2 8.0i5.0 0.0-16.7 r STM-479 Milk Nov 1986 Sr-89 7.7tl.2 9.015.0 0.3-17.7 Sr-90 1.0i0.0 0.0tl.5 0.0-2.6 I-131 52.3f3.1 49.0t6.0 38.6-59.4
, Cs-137 45.7*3.1 39.0t5.0 30.3-47.7 i K 1489*104 1565*78 1430-1700 ,
3 STU-480 Urine Nov 1986 H-3 5540*26 5257t912 4345-6169 ;
i STW-481 Water Nov 1986 Gr. alpha 12.0t4.0 20.015.0 11.3-28.7 i Gr. beta 20.0t3.5 20.0t5.0 11.3-28.7
, STW-482 Water Dec 1986 Ra-226 6.710.2 6.811.0 5.0-8.6 i
Ra-228 5.210.2 11.lil.7 8.2-14.0 STW-483 Water Jan 1987 Sr-89 19.7t5.0 25.0f5.0 16.3-33.7 Sr-90 21.0t2.0 25.0t1.5 22.4-27.6 i
20 i i i
c
. Table A-1. (continued).
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis t2oc Is, N=1 Control Limits STW-484 Water Jan 1987 Pu-239 17.012.3 1.5.711.7 13.8-19.6 STF-486 Food Jan 1987 Sr-90 36. 0t4.0 49.0110.0 31.7-66.3 I-131 78.0i3.4 78.018.0 64.1-91.9 Cs-137 89.7*3.0 84. 015.0 75.3-92.7 K 942iS6 980*49 895-1065 STF-487 Food Jan 1987 SR-90 2.010.0 ---
(Blank) 1-131 <3 ---
Cs-137 <2 ---
K 993i102 ---
STW-488 Water Feb 1987 Co-60 49.0f0.0 50.Di5.0 41.3 58.7 Zn-65 96.0i7.2 91.015.0 82.3-99.7 Ru-106 92.0i20.2 100.Di5.0 91.3-108.7 Cs-134 53.0i3.4 59.0i5.0 50.3-67.7 Cs-137 89.3i4.6 87.015.0 78.3-95.7 STW-489 Water Feb 1987 H-3 4130i140 4209*420 3479-4939 STW-490 Water Feb 1987 Uranium 8.311.2 8.016.0 0.0-18.4 STM-491 Milk Feb 1987 1-131 10.010.0 9.0f0.9 7.4-10.6 STW-492 Water Kar 1987 Gr. alpha 3.7*1.2 3.0*5.0 0.0-11.7 Gr. beta 11.311.2 13.015.0 4.3-21.7 STW-493 Water Mar 1987 Ra-226 7.0f0.1 7.311.1 5.4-9.2 Ra-228 7.112.3 7.5fl.1 5.5-9.5 STW-494 Water Apr 1987 I-131 8.0f0.0 7.010.7 5.8-8.2 STAF-495 Air Apr 1987 Gr. alpha 15.010.0 14.015.0 5.3-22.7 Filter Gr. bets 41.012.0 43.0t5.0 34.3-51.7 Sr-90 16.3fl.2 17.011.5 14.4-19.6 Cs-137 7.010.0 8.015.0 0.0-16.7 STW-496 Water Apr 1987 497 (Blind)
Sample A Gr. alpha 30.711.2 30.0i8.0 16.1-43.9 Ra-226 3.910.2 3.910.6 2.9-4.9 Ra-228 4.910.9 4.010.6 3.0-5.0 Uranium 5.010.0 5.016.0 0.0-15.4 21 1
. l 1
Table A-1. (continued)
Concentration in pCi/lb Lab Sampie Date TIML Result __
EPA Resultd Code Type Collected Analysis t20c 15, N=1 Control Limits ,
STW-496 Water Apr 1987 497 (Blind)
Sample B Gr. Beta 69.319.4 66.0t5.0 57.3-74.7 Sr-89 16.3i3.0 19.0t5.0 10.3-27.7 Sr-90 10.0i0.0 10 Dil.5 7.4-12.6 Co-60 8.3 3.0 8.015.0 0.0-16.7 Cs-134 19.0i2.0 20.0i5.0 11.3-28.7 Cs-137 14.7tl.2 15.015.0 6.3-23.7 STU-498 Urine Apr 1987 H-3 6017t494 5620i795 4647-6593 STW-499 Water May 1987 Sr-89 38.016.0 41.015.0 32.3-49.7 Sr-90 21.0i2.0 20.011.5 17.4-22.6 STW-500 Water May 1987 Gr. alpha 9.0i3.4 11.015.0 2.3-19.7 Gr. beta 10.3tl.2 7.015.0 0.0-15.7 STW-501 Water June 1987 Cr-51 40.0f8.0 41.015.0 32.3-49.7 Co-60 60.3t3.0 64. 0i 5. 0 55.3-72.7 Zn-65 11.315.0 10.0t5.0 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 80.0f5.0 71.3-88.7 STW-502 Water June 1987 H-3 2906t86 28951357 2277-3513 STW-503 Water June 1987 Ra-226 6.910.1 7.3tl.1 5.4-9.2 Ra-228 13.3tl.0 15.2i2.3 11.2-19.2 STM-504 Milk June 1987 Sr-89 57.0t4.3 69.0t5.0 60.3-77.7 Sr-90 32.011.0 35.Dil . 5 32.4-37.6 I-131 64.0t2.0 59.0i6.0 48.6-69.4 Cs-137 77.7t0.6 74.015.0 65.3-82.7 K 1333i17 1525176 1393-1657 i STW-505 Water July 1987 Gr. alpha 2.310.7 5.0t5.0 0.0-13.7 Gr. beta 4.0il.0 5.015.0 0.0-13.7 STF-506 Food July 1937 1-131 82.714.6 80.0i8.0 66.1-93.9 Cs-137 53.713.0 50.015.0 41.3-58.7 K 1548157 1680184 1534-1826 STW-507 Water Aug 1987 !-131 45.7f4.2 48.0t6.0 37.6-58.4 STW-508 Water Aug 1987 Pu-239 5.810.2 5.3t0.5 4.4-6.2 22 l
Table A-1. (continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis 12ac 15, N=1 Control Limits STW-509 Water Aug 1987 Uranium 13.310.3 13.016.0 2.6-23.4 STAF-ben Air Aug 1987 Gr. alpha 9.710.4 10.025.0 1.3-18.7 Filter Gr. beta 28.310.6 30.0t5.0 21.3-38.7 Sr-90 10.Dio.9 10.0il.5 7.4-12.6 Cs-137 10.0tl.0 10.015.0 1.3-18.7 STW-511 Water Sept 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 Sept 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 Oct 1987 H-3 44731100 4492i449 3714-5270 STW-514 Water A Oct 1987 Gr. alpha 29.312.6 28.017.0 15.9-40.1 Ra-226 4.910.1 4.810.7 3.6-6.1 Ra-228 4.2il.0 3.6i0.5 2.7-4.5 Uranium 3.010.1 3.016.0 0.0-13.4 STW-515 Water B Oct 1987 Gr. beta 72.312.7 72.015.0 63.3-80.7 Sr-89 14.3tl.3 16.015.0 7.3-24.7 Sr-90 9.7i0.4 10.0fl.5 7.4-12.6 Co-60 16,713.0 16.015.0 7.3-24.7 Cs-134 16.7f2.3 16.015.0 7.3-24.7 Cs-137 24.313.3 24.015.0 15.3-32.7 STW-516 Water Oct 1987 Cr-51 80.3117.5 70.0i5.0 61.3-78.7 Co-60 16.012.3 15.015.0 6.3-23.7 Zn-65 46.315.6 46.015.0 37.3-54.7 Ru-106 57.3i15.4 61.0 5.0 52.3-69.7 Cs-134 23.7f2.5 25.015.0 16.3-33.7 Cs-137 51.7f3.2 51.0f5.0 42.3-59.7 STU-517 Urine Nov 1987 H-3 7267f100 74321743 6145-8719 STW-519 Water Dec 1987 I-131 ?6.0i3.0 26.016.0 15.6-36.4 a Results obtained by Teleayne Isotopes Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Iritercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Laboratory, U. S. Environmental Protection Agency (EPA) Las Vegan, Nevada, b All results are in the pCi/1, except for elemental potassium (K) data, which are in mg/1; air filter samples, which are in pCi/ filter; and food, which is in pCi/kg.
c Unless otherwise indicated, the TIML results are given as the mean 12 standard deviations for three determinations.
23
y Table A-2. Crosscheck program results, thermoluminescent dosimeters (TLDs).
1 mR Teledyne Average 12 o d Lab TLD Result Known (all Code Type Measurement 12aa Valuec participants) 2nd International Intercomparisonb 115-2 CaF2:Mn Field 17.011.9 17.1 16.417.7 Bulb Lab 20.814.1 21.3 18.817.6 3rd International Intercomparisone 115-3 CaF2:Mn Field 30.7i3.2 34.914.8 31.513.0 m Bulb
- Lab 89.616.4 91.7114.6 86.2124.0 4th International Intercomparisonf 115-4 CaF2:Mn Field 14.111.1 14.111.4 16.019.0 Bulb Lab (Low) 9.311.3 12.212.4 12.017.6 Lab (High) 40.411.4 45.819.2 43.9113.2 Sth International Intercomparison9 115-5A CaF2:Mn Field '
31.411.8 30.016.0 30.2114.6 Bulb Lab at 77.415.8 75.217.6 75.8140.4 beginning Lab at 96.615.8 88.418.8 90.7131.2 end
O Table A-2. (Continued) mR Teledyne Average 120 d Lab TLD Result Known (all-Code Type Measurement 12oa valuec participants) 115-58 LiF-100 Field 30.314.8 30.016.0 30.2114.6 Chips Lab at 81.117.4 75.217.6 75.8140.4 beginning Lab at 85.4111.7 88.418.8 90.7131.2 the end 7th International Intercomparison h 5 115-7A LiF-100 Tield 75.412.6 75.816.0 75.1129.8 Chips Lab (Co-60) 80.013.5 79.914.0 77.9127.6 Lab (Cs-137) 66.612.5 75.013.8 73.0122.2 115-78 CaF2:Mn Field 71.512.6 75.816.0 75.1129.8 Bulbs Lab (Co-60) 84.816.4 79.914.0 77.9127.6 Lab (Cs-137) 71 811.6 75.013.8 73.0122.2 115-7C CaSO4 :Dy Field 76.812.7 75.816.0 75.1129.8 Cards Lab (Co-60) 82.513.7 79.914.0 77.9127.6 Lab (Cs-137 79.013.2 75.013.8 73.0122.2
4 Table A-2. (Continued) mR Teledyne Average 12e d Lab TLD Result Known (all Code Type Measurement 12da Valuec participants) 8th International Intercomparison i ll5-8A LiF-100 Field Site 1 29.511.4 29.711.5 28.9112.4 Chips 11.310.8 10.410.5 10.119.06 Field Site 2 Lab (Cs-137) 13.710.9 17.210.9 16.216.8 115-8B CaF2:Mn Field Site 1 32.311.2 29.711.5 28.9112.4 Bulbs Field Site 2 9.011.0 10.410.5 10.119.0 Lab (Cs-137) 15.810.9 17.210.9 16.216.8 115-8C CaSO4 :Dy Field Site 1 32.310.7 29.711.5 28.9112.4 Cards Field Site 2 10.610.6 10.410.5 10.119.0 l m Lab (Cs-137 18.110.8 17.210.9 16.216.8 i
l a Lab result given is the mean 12 standard deviations of three determinations.
b Second International Intercomparison of Environmental 00simeters conducted in April of 1976 by the Health and Safety Laboratory (GASL), New York, New York, and the School of Public Health of the University of Texas, Houston, Texas.
1 c Value determined by sponsor of the intercomparison using continuously operated pressurized ion chamber.
d Mean 12 standard deviations of results obtained by all laboratorits participating 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 sumner of 1979 by the School of Public Health of the University of Texas, Houston, Texas.
9 Fif th International Intercomparison of Environmental Dosimeter conducted in fall of 1980 at Idaho Falls, Idaho and sponsored by the School of Public Health of the University of Texas, Houston, Texas and Environmental Measurements Laboratory, New York, New York, U.S. Department of Energy.
I h
Seventh International Intercomparison of Environmental Dosimeters conducted in the spring and sunner of l 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 1 1985-1986 at New York, New York, and sponsored by the U.S. Department of Energy. -
Table A-3. In-house spiked samples.
Concentration in pCi/1 ;
Lab Sample Date TIML Result Known Expec ted Code Type Collected Analysis n=3 Activ ity Precision !
15, n=3a QC-MI-6 Milk Feb. 1986 Sr-89 6.0tl.9 6.4t3.0 8.7 Sr-90 14.2tl.7 12.9t2.0 5.2 .
1-131 34.2*3.8 35.213.5 10.4 Cs-134 32.0t1.8 27.315.0 8.7 Cs-137 35.8t2.1 35.0i5.0 8.7 QC-W-14 Water Mar. 1986 Sr-89 1.610.4 1.6tl.0 7.1 Sr-90 2.4t0.2 2.4*2.0 4.2 QC-W-15 Water Apr. 1986 1-131 44.9t2.4 41.5t7.0 10.6 Co-60 10.6tl.7 12.115.0 7.lb Cs-134 30.212.4 25.818.0 7.lb Cs-137 21.911.9 19.9i5.0 7.lb QC-MI-7 Milk Apr. 1986 I-131 39.713.3 41.5t7.0 10.4 Cs-134 28.7f2.8 25.8t8.0 8.7 Cs-137 21.212.8 19.9t5.0 8.7 SPW-1 Water May 1986 Gross alpha 15.8tl.8 18.015.0 Sc QC-W-16 Water June 1986 Gross alpha 16.2t0.7 16.912.5 8.7 Gross beta 38.4f3.5 30.2i5.0 8.7 QC-MI-9 Milk June 1986 Sr-89 <1.0 0.0 7.lb Sr-90 12.611.8 13.313.0 4.2b I-131 38.917.0 34.817.0 10.4 Cs-134 33.0t3.4 36.li5.0 8.7 Cs-137 38.5t2.8 39.0t5.0 8.7 SPW-2 Water June 1986 Gross alpha 16.8tl.8 18.015.0 Sc SPW-3 Water June 1986 Gross 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 51.1t7.0 43.318.0 8.7 QC-W-19 Water Sep. 1986 Sr-89 13.614.1 15.613.5 7.lb Sr-90 6.4tl.6 6.2*2.0 4.2b l
27
Table A-3. In-house spiked samples (continued)
Concentration in pC1/1 Lab Sample Date TIML Result Known Expec ted Code Type Collec ted Analysis n=3 Activity Precision 1s, n=3a QC-W-21 Water Oc t. 1986 Co-60 19.212.2 18.St3.0 8.7 Cs-134 31.715.2 25.6t8.0 8.7 Cs-137 23.811.0 21.6t5.0 8.7 QC-MI-11 Milk Oct 1986 3r-89 12.311.8 14.3t3.0 8.7 QC-W-20 Water Nov . 1986 H-3 38551180 3960i350 520b QC-W-22 Water Dec.1986 Gross alpha 9.811.4 11.214.0 8.7 Gross beta 21.7t2.0 23.815.0 8.7 QC-W-23 Water Jan. 1987 I-131 29.8i2.5 27.9*3.0 10.4 QC-MI-12 Milk Jan. 1987 I-131 36.511.3 32.615.0 10.4 Cs-137 32.614.2 27.418.0 8.7 SPM-13 Milk Jan 1987 Sr-89 10.412.1 12.214.0 8.7 Sr-90 14.611.6 12.613.0 5.2 :
I-131 49.511.2 54. 9t8.0 10.4 Cs-134 <1.6 0.0 8.7 Cs-137 33.310.6 27.418.0 8.7 SPW-24 Water Mar 1987 Sr-89 24.713.6 25.915.0 8.7 Sr-90 23.9t3.8 22.8t8.0 5.2 SPW-25 Water Apr 1987 I-131 28.0*1.9 29.315.0 10.5 SPM-14 Milk Apr 1987 I-131 25.0*2.2 23.915.0 10.4 Cs-134 <2.1 0.0 8.7 Cs-137 34.212.0 27.217.0 8.7 i SPW-26 Water Jun 1987 H-3 34221100 3362*300 520 Co-60 24.811.4 26.517.0 8.7 Cs-134 <2.0 0.0 8.7 Cs-137 21.2i0.5 21.617.0 8.7 SPW-27 Water Jun 1987 Gr. alpha 8.Sil .9 10.114.0 8.7 Gr. beta 22.6t'. 9 21.215.0 8.7 ;
SPW-28 Water Jun 1987 Gr. alpha 8.7*1.3 10.114.0 8.7 Gr. beta 12.215.2 9.4t3.0 8.7 28
O Table A-3. In-house spiked samples (continued)
Concentration in pCi/l Lab Sample Date TIML Result Known Ex pected Code Type Collec ted Analysis n=3 Ac tiv ity Precision 1s, n=3a SPW-29 Water Jun 1987 Gr. alpha 16.4tl.3 18.9i5.0 8.7 Gr. beta 15.9i4.0 11.824.0 8.7 SPM-15 Milk Jul 1987 Sr-89 19.411.6 18.813.5 5.2 1-131 43.5t0.7 45.3t7.0 10.4 Cs-134 17.9t2.2 16.0i5.3 8.7 Cs-137 25.4tl.8 22.715.0 8.7 SPW-30 Water Sep 1987 Sr-89 17.St3.0 14.315.0 8.7 Sr-90 18.4t2.2 17.5i2.2 5.2 SPW-31 Water Oct 1987 H-3 2053t93 2059*306 520 a n=
b n=3 2. unless noted otherwise, c n=1.
29
Table A-4. In-house "blank" samples.
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66 o ) (4.660)
BL-1 0.I. Water Nov. 1985 Gross alpha <0.1 <1 Gross beta <0.4 <4 BL-2 0.I. Water Nov. 1985 Cs-137 (gama) <1.9 <10 BL-3 D.I. Water Nov. 1985 Sr-89 <0.5 <5 Sr-90 <0.6 <1 BL-5 D.I. Water Nov .1985 Ra-226 <0.4 <1 Ra-228 <0.4 <1 SPW-2265 0.I. Water Apr. 1985 Gross alpha <0.6 <1 Gross beta <2.2 <4 Sr-89 <0.2 <5 Sr-90 <0.4 <1 1-131 <0.2 <1 Cs-137 (gama) <7.4 <10 BL-6 0 I. Water Apr. 1986 Gross alpha <0.4 <1 BL-7 D.I. Water Apr. 1986 Gross alpha <0.4 <1 BL-8 0.I. Water June 1986 Gross alpha <0.4 <1 SL-9 0.1. Water June 1986 Gross alpha <0.3 <1 SPW-3185 D.I. Water Jan 1987 Ra-226 <0.1 <1 Ra-228 <0.9 <1 SPS-3292 Milk Jan 1987 I-131 <0.1 <1 Cs-134 <6.2 <10 Cs-137 <6.4 <10 SPW-3554 0.I. Water Feb 1987 H-3 <180 <300 Gross beta <2.6 <4 SPS-3555 Milk Feb 1987 Sr-89 <0.6 <5 Sr-90 1.910.4a <1 SPS-3731 Milk Mar 1987 Cs-134 <2.2 <10 Cs-137 <2.5 <10 a low level (1 - 4 pCi/1) of Sr-90 concentration in milk is not unusual.
30
3w 0 Table A-4. In-house "blank" samples (continued).
Concentration in pCi/1 ,
Acceptance :
Lab Sample Date Results Criteria l Code Type Collec ted Aaalysis (4.66o) (4.66o)
SPS-3732 0.I, Water Mar 1987 Sr-89 <0.9 <5 Sr-90 <0.8 <1 1-131 <0.3 <1 Co-60 <2.3 <10 Cs-134 (gama) <2.2 <10 Cs-137 (gama) <2.4 <10 i Ra-226 <0.1 <1 Ra-228 <1.0 <1 No-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 U-238 <0.03 <0.1 SPS-4023 Milk May 1987 I-131 <0.1 <1 SPS-4203 0.I. Water May 1987 Gross alpha <0.7 <1 Gross beta <1.7 <4 SPS 4204 Milk May 1987 Sr-89 <0,5 <5 Sr-90 2.410.6a <1 SPS-4390 Milk Jun 1987 Cs-134 <4.7 <10 Cs-137 <5.2 <10 SPS-4391 D.I. Water Jun 1987 Sr-89 <0.4 <5 Sr-90 <0.4 <1 i 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 0.I. Water Aug 1987 Gross alpha <0.6 <1 Gross beta <1.4 <4 Tritium <150 SPS-4628 Milk Aug 1987 Sr-89 <0.6 <5 Sr-90 2.410.6 <1 SPS-4847 Milk Sep 1987 Cs-134 <4.4 <10 Cs-137 <5.3 <10' a low level (1 - 4 pCi/1) of Sr-90 concentrai. ion in milk is not unusual, -
t 31 l
Table A-4. In-house "blank" samples (continued).
Concentration in pCi/l Acc eptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66o) (4.66o)
SPS-4848 0.I. Water Sep 1987 I-131 <0.2 <1 SPW-4849 0.1. Water Sep 1987 Co-60 <4.1 <10 Cs-134 <4.8 <10 Cs-137 <4.0 <10 Sr-89 <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 Milk Dec 1987 Cs-134 <2.3 <10 Cs-137 <2.5 <10 SPW-5384 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 Water Nov 1987 Gr. alpha <0.4 <1 Gr. beta <2.2 <4 Fe-55 <0.3 <1
32
, . - - - - - - , . - , , . . _ , . _ ,_v__ _,-g-- ___.,. _._ _ . _ , _ - - _
TIML-BLINO-01 Revision 0, 12-29-86 ATTACHMENT B ACCEPTANCE CRITERIA FOR "SPIKE 0" SAMPLES LABORATORY PRECISION: ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa One Standard Deviation Analysis Level for Single Determination Gamma Emitters 5 to 100 pCi/ liter or kg 5 pCi/ liter
>100 pCi/ liter or kg 5% of known value Strontium-896 5 to 50 pCi/ liter or 'kg 5 pCi/ liter '
>50 pCi/ liter or kg 10% of known value Strontium-90b 2 to 30 pCi/ liter or kg 3.0 pCi/ liter
>30 pCi/ 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 pCi/ liter 25% of known value Gross Beta <100 pCi/ liter 5 pCi/ liter
>100 pCi/ liter 5% of known value Tritium <4,000 pCi/ liter is = (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
<55 pCi/ liter 6 pC1/ liter Iodine-131, b >55 pCi/ liter 10% of known value Iodine-129 Uranium-238, <35 pCi/ liter 6 pCi/ liter Nickel-630, >35 pCi/ liter 15% of known value Technetium-99b Iron-55b 50 to 100 pCi/ liter 10 pCi/ liter 10% of known value a
From EPA publication, "Environmental Radioactivity Laboratory Intercompari-son Studies Program, Fiscal Year 1981-1982. EPA-600/4-81-004.
b TIML limit.
33
l e
APPENDIX I DATA TABLES AND FIGURES l
l 34
TABLE 1.1-1 titen IRC1LAA fede Stattel EfftnOff ass taL5tt tilretu teammeau utent feeJensarv-Jone,1987 643tWS (fftnertl e $seelleu er ut uttAtti t natif1 i JAN I FSS I MARCN i l e tamana rrai APR I L g MT twv== p he manain C. $66aien and &ctleetIsa See teleteet men. ate I te g4.11t+13 S.44B+42.4250 31.35E+3 3 7.2230 g4.45B+2 g 1.125*2 15.64 t+ 2
- i. innai n.i
- s. w w n.i- n t. I su. 11.2 t a+11 1 nan +1i .ss=*211. sin +1 I a.39a+1 I4.90s+4 1 6.49s+2 k.9es*4
- s. n s we inan . '
so.34
- a. -i- n.a. rann --w i e a in.61 to.ei no.co to.cl e o.00 10.34 a0.00
- m. nat. sinna w ,i I n In ni in.nl la.no Io.ei I o.oo 10.3e 1 0.00 10 . 3 0
- a. , .# iersana s i.ain
- a. --- m.,t-i . e n -w i n 0.00 0.01 0.00 0.01 0.00 0.02 0.01 10 . 0 3
- m. a.u h.,u,i. e na -wi n 0.00 0.02 0.00 0.02 0.00 0.06 0.01 b.o?
- n. - -i s ia -wi n 0.00 0.00 0.00 0.00 0.00 0.01 0.00 b.on n 0.00 0.01 0.00 ,0,01 0.00 0.03 0.00 b.oi
- m. a.u - -i un wi
- s. lediae teleetes fi 19.4Du* d t .02R- al l . 6& R-d 2.81R-1 01.16E.4 11.11E-1 in.471 4 l$.013 1
- t. taa.i t.ili a 1.i11 hit.lin i
- n. n s wwwa ai.iu
- e 5 et 14Cf t29 lle4tt is based en the mestems celease tote fee the perted seasideese,
- ledles, partleslete. and telttan 16etts are empressed as a tetel 1Wl. See Step 4.
35
TABLE 1.1-1 (continued) trean tuttgaa 99dtt lfAflW fffLWut Ase tek$ft O!580$AL 5tniassaint tapest fea Jag . etttiert. test GA$t0WS (ffLWtW18. Spotsf!ON OF ALL 4(LtAlti i tatt f t i uv 1 ma f ust 1 tan maatral act I maat I att I atm maatra A. Flesten and 4ctivatlee 6as teleases L tatal aminaam as t i.i t. I et t 2.aar.1 i f att.1 I i ter.1 i f . ?ar.1 t t t v .s I t fir 32 1 t est.7 I t ter.2
- 2. ma.t animaan aata 1 c t fine i t.eir.2 1 2. tit.2 I a.11r.2 I a_ fir.2 l t aar.a l 1 asr.t I t nr.2 l P. au .1 i_ t at latra2a ttaitae
- a. nasala made flaa mesm/anart t t i a na 1 e as f a.ma I e na t a at i a at t a.as i~ a_M
- a. tata rinna w ,i i t I a.ma f a. ma I a as I a ne I a at I a_na I a.as I a na
- a. t at tareana t taita a_ " - kartart e l a mean t 1 a _ na a _ na a.as e.as a at a . a2 a.ma e at t a . as a aa a.at a at a at a_a1 a _ az a_na
- h. nata hartari. ria meant
,. *-- - -i ria meadi 1 a . as a . as e ma a _ na a.as a_ai a.aa a . a2
- m. nata a-- -1 f2e menat t a as a_as a aa 6.na e as e.a2 a.ai a ai S. ledine teleases f atii t.in maa 1.lM atti.1t o ft i 1.12f.1 i a 9&r.d t a mar.a i 9 1Lr.1 1 1. l ar .1 l 1. mer .d i 1.aar.a 1 1.e lf .1
- 1. i
- s. n at terrasanattana t eat ta**
- 5 et 14CrtM lletts is based es the osalma release rate for the perted seasleered.
- Ieelee. partissiste, and tellius lletts are espressed as a total llett. See Step t.
36
TABLE 1.1-1 (continued)
Diese IREttAA fest 114fles EfftlENT AIS Inlft Dllf96&L $tNasanal Otptt! Pgg Jeauery* June,1542 6AtteWE (PFLIEMS e tseafles GF ALL atttAMS I nant r1 1 J AN I PRE I IIARCE I l a t annassai ape t t, l etat I JVirs 3 2nd amatra C. Porticolate (6 9 dog half lifel teltetoe t_ a,.** aa n. tt. t ti e < tJa 11.30s-es 1.cos-e s.10s-4 af.16s S i3.173-$ st.00s-5 #1.14e-4
- s. a . mi m a.mi.ia. I ca i cum I < Lta I <ttm I <t.2m I<LLO I < tim I < tim I <tta
- 1. E af taff ataliatrana it.a ta**
- 9. lettism teleeses
- 1. t a.t h.i - annt.it. I ti i <ttE 13.013-201.01E-E 1. M a-1 14.30E-2 e4.013-2 12.123-2 11.123-3
- 2. E at tetrasattatrana a t.ata**
- 8. Sam of ladlee. Porticolete (6 e es, belf-life), and trillen Beteeses e_ t.s a a,s i.i e. t en 39. 403-4 s 5. 3 45-2 1.05 E- 4 1. 375-1 g4.335-3 g5 335*3 g3.4 W 3 ga.4 w &
- n. n as natraan a n.an
- a. a a s taan w.mant I n 10.00 t0.00 a0.00 t0.00 a0.00 s0.00 s0.00 g 0.W
- 1. a m# tarsana timan
- a. hans.,t. a a af.m - i e a to 00 t0.00 t0.00 a 0.00 a0.00 a0.49 0.05 i 0.34 ~
- m. - t a a s ta.a . -.i l n 10.00 10,00 1 0.00 1 0.00 10.00 10.24 Io.03 1 0.37
- ledtes, particolete, and tettles llette are eieressed es e total llett. SesI Sta, t.
(Lib =tso detectable activity above lower Limit of Detectice for conating room imetrummatatloa.
37
-TABl.E 1.1-1 (continued) greau eattLaa peat lfatten tfflutut ass taltt tipulAt Matasenat mpent fee Jut? . WCtsett,1987 4AMOUS (FFtWWil . Speufitu ef att MLLAMS
- I tatif t 1 imy I aut I upt i sen ihanfral art t new I are i ein snaatta C. portteelste (> 0 eer half.Ilfel teleases
- i. s,.an aconite i ei i et t a i atta I atta i es ta i et ta t a.aar.a t etta i n. ear.a
- f. E,.an ath ma t t it. l ft I etta l et ta l tila l etta I et ta l ella I alta { e t ta L E .# intrafa/tarrana t tatta**
- 9. frittua teleases a,ti.it. I ti i n.tir.a t t ?#d.2 1 T_aar.2 I i _ aw.t i 1 mar.t I t_str.t i f . ter . t I a _ ner.t W.t2i n.1 ..
- f. t .# tErilif tatrana t tat tn**
- t. lesi of ladine, particalete (p 8 esp belf.1tfe), ead fritium teleetet
- t. v.a.i a,ti.it. t et t t _ avr.1 I t aar.2 I t.aar.2 I t _ au . i e t _ ner.1 t f.itt.t t f . t er .1 1 a _ tar.
2- t .f 1atrata ttait ,
a.. a, nana w .,i e n e a as e a as I a _ as e a na e a_an I a.as a a na e a as
- 1. E .f tetrana i taia I a.ia i a_na i a sa 1 a.fm t a ma i a2 l a _ na e a na
._ wt.,1. A.. a, r t.t ) I t a, I E I n an I a_ai I a.at I a in I a_na I a_na i n.aa I a _ na
- n. -
-t a. r tt _ a w
- todene, parties 1ste, and tentle lletts are espressed as a total llett. See Step t.
38 i
TABLE 1.1-1 (continued)
Dutus IREttaa P988 Stellel EffLIENT age tabitt Ditftlet maasessat Efeet fg Jannery-Jane,1W Gotten ttfusstl . IEW" llats EttAMS t-- a mes sinem I nant ta i JAR I PBS I IthDCs ist ananatta t APSIL t MAT I JUWS t 2hesa
- f. fItalen ame Astteetles GM teleasee ,
an. t u. ce n.2?m-1 a.oia-1 1.293 1 1.0630 6.983-2 4.71 5 4.063-2 4,$2W an. t um t.aan.1 1.2en.1 a t.nm 1.173-1 4.272-2 4.172 1.15 W l 36 5 m tsam < 13m s t32 e 11A a 1.12 < 132 < t.Im a t.12 < L1h an. t n a_nlaal a.ssa41 1.nsen 1 tamas a.saan a.12a42 1. Dea +2 1.47362 an.t na s_s,a.1 t_tta.1 1. tan.) 1.aan-1 1_ nan.1 1.eten 1.aten 2. ate an. ann < tem i_1tm.t s tim 1.11m.1 1 ata.1 2 ata-a 1.lan.1 1. ian.1_
,sann '
ms E s 11m.1 1 RAmn 1 nimi s.1am 1 s_htan 1.taa.1 1. Tam ___
ag.a1 etth et2A e t.sh et3h s tih 41th et1h 01_t h as E sinA steA st3A ettM 1_1&m.1 9_%1a.9 a t_t B 2 ada-2 a,a t s uma a ama t s sam s s 9,s., 1 sam.s 1 aan.s _t_lan.9 a. alm 1 Othoes llectifgl e
t I
I
- 0. IWite bleMet
- a. int ta '5.238-4 4.940-4 1.663-4 1.355-3 1.145-4 4.705-3 4.HB-4 4.755 4
- a. ant < tJA S.968-5 < LIA S.989-5 < 1JA (LIA < Lth (Lim t.in 4.175-4 2.000-4 ~< Lib 6.258-4 .0 't-4 9. :>00-4 2.173-4 1.353-1 a.11a < tJA (Lla < tJA < ble - .t . l'IB-l 3.1199-4 (Lie 4.15B*4
- a. tia 1.153-4 3.648-4 9.508-1 S.708-4 < tJA 3.'PSB-4 1, MS-4 S.258-4 Stters llee<4ff l .
(L1&*to detec' table Mt191ty tbtTe lanser Limit of Detectice for eeust!Dg tema inettismestaties.
39
l l
t l
TABLE 1.1-1 (continued) 1 I
evnen ieKttaa peas Statten Efftutwf ass taktti DilMi&L Stataamaan etpget pga mg . gtClett.1981 4Alteul EffLututt . $seellas er att stitAltl nearmaf t ari rma 1 intf f t I hv I u I uff I saa ataatral art i new I are i sta etaarra F. fistles and Activettes &ss htuses hth et t. sara a tarJ 1. eM .1 1.afra t. w .1 , 1sf . i 1_ su.1 f . tfra hi1h I . tal.1 e . aft. i a tv.i a t t f.1 e war.1 1. t Ma i una 1.afta hth atta elLA 1 eM.1 1. tat.1 (LLS (LLA < LLS (LLA h ill 1.a& fat f . kW, g3 1 aaf a1 f .1er a l 1. tar d f . t er d t _ ewd t tpr.)
htM ?. mar J 1. Tes .1 f. tat.1 t _ atf.1 e mer.1 p.m.1 t . 3ar. ) 1. gtta Erh at ta E.1er.1 t _ Mt.1 1. t at .1 t . int.2 a _ f yr.2 1 par.g 1 air.)
Er E ?. t&f J A . tal.2 1.1 u.1 f. Dr.1 1.1er.1 et ta t yer.1 ) mar.1 Er.A7 < ttB <tta etLA etta etLA eLLB e t ta gr E t . atf.1 & tir.1 a _ tdr.1 fstLB RM.1_ , _ 1 mar.1 et ta 1.112 .1 f _ tat.1 1 aMJ f.? ti d f Lat.1 1. T M .) a sar J A taf J f mat.2 1 W .1 A,.at Mhers (Spettfp)
{
l
- s. Imeia. a i.nes ft a t.ar.J a fMJ 1 9M.J 1 mar.1 9 sar.J a . Mf a t mat.a t_1af.1 t.111 (LLA tL LS etta atta a t LE alta al ta at ta 1.112 1 11r J t _ mar.J R &af.1 4 . a&f .A d larJ 1. t M .J et LA 4 71tJ 1.t11
- 1. tM .R ttta alta T _ tM.R alta 2.?af .J ettB 2.7af J
- t. tid d .1 t f .J 1. f M.J & inf.R 1. E?r.d 1. tat.1 f _ fft .d atta 1 PM.1 1.tig Mhers (Specift )
l 40
e TABLE 1.1-1 (continued) een utan me. sr iin EffL4Est alt taitt Ditselet usamment alpet fu Jammery-June, IM7 M LifLWWtl e VENI SIME NLEAMI I- ^ ^-t afi naana t entti Bas was t ""
- N llat ammataat amm11 3 my l ,ygga i 1 '"su
- n. Portitetete in 8 de, helf.Ilfet teleetse h tA et E LIA (1.12 (IJA (Lla ( RJA (LIA (LIA (L1b r na itJa (IJA ( Lib (Lla (LIA (Lim (L33 (Lab A ta rtEm ( f.la (13 2 (IJJ (IJA (LEA (lJJ (Lib a na rilm < tla 7.aon-4 1.aoa-4 1.laa.1 1.683-S 3.90R-4 5.*13-5 u r tam < f 32 s tam s tam 1.afa-1 1.493-3 1. 30 E-4 1.543-1 g, m . . . og3,13 1 . . . og3,jg.g be . . . ett la.A . . . eti.ja.a 12 IfJa (IJA (12h (1JA (RJA (LIA (Lt& (L33 bla3 1 t3m f1Jm (12 2 (tJJ (IJA (RJA (LIA ( L1b w l Ren n tim e tim t tim tilh (11 2 (1Jb (Llp _(Lib _ _
g ggiu rum t_ sam-a num t. sam.a < t2m < tim s.lon-e n.lon-a ti. t m rum <um num num num cum num num t tu rum <um ,um ,um 1.tsa.a num num 1.11a-a .
as}LL. tn n tlm i tlm t 112 4 t_tm t Elm ' d Elm t tim t t_tJb t.a. ten r t_tm t t1m e 133 e 1_tm e tim e tim ttim 4 tim
$thers 11pecifp) l (LL>ee detectable activity above lauer Limit of Detection for count &og room toetrumentatten.
- =&aetrete performed by offette vendor. Telee listed Q,the IJA for the smanyste.
i I
i i
41
TABLE 1.1-1 (continued)
Dveau sagttas past ifatte (ffLauf Me ustt tilaelet Mutasonsht Mpest tes Jyty . M(tiete, iget 6AlteWS (ffLIAWil
- hf8EllW Of ALL MttAl($
teatheti haitiash I tafft i 117 I asa i upf I m mantrat het t unw I htf I arm mahtra N. Portis,1ste (t $ esy helf.Ilfe) Meeses t LLA eLLA eLLh t L Lh eLLh (LLB (LLA atth bM ft kM eLLA e LLh tLLR eLLA e LLA tLLh tLLR tL LB kM (LLS LLLh t L LB tLLS tLLh tLLS tLLS t t th AM (LLB (LLA tllh (L LB eLLh etLR tLLh eLQ t LLA tLLA tLLh (L LA (LLB h _ htf J ti LB h ahr 1 fAJh b.nh LL LR eL LE e L LA tLLA AL Lh t L LR ELLS E L LB ELLh tLLB ELLR tLLB tLLA EL LR ELLA ELLA MA tL LB t LLh e L Lh (LLA t L LA tLLB tLLh L L LA Tm EL LA tLLA eLLB ELLh tL LB e L LB tith eL th h lh1 t L LB (LLh eLLE ELLA tLLA tLLB eLLh eL L h ha.11Am nt th LLLA tLLR ELLA t L Lh tLLE t L LS t L LB t_n. t M tLLn ELLA a t LB tLLA tL LA ELLR nLLA tL LA E n.1 M e L LA ti th tLLB (LLS mLLB ti LB ELLh tL LS f_n. t U ELLB tLLS EL LA tLLh LLLS tLLS ELLh tLLB Rs}LA.16 atta atta Ltth tith atth atth etth Ltta c iaa 9%hert (Spe(if f)
+
%9 5
l I
l 1
42
e l
TABLE 1.2-1 Duess tarttAd pense llatim gifttset as3 talet Mtpetal tintassasht alpest ten Jemmerv* June,1967 LISMS ttFtqEWil = Susenfle Of ALL alttatti t munit LI AS IFES IIqASCE I l et a.marral &P9IL i stA Y I JVIr3 1 2-' re_a
- 1. fisslea and ktleetles Predssts
- 3. va at u s a-a a. a a -- " i et G .MR.2 tl .103.lil .lano t i.11an 16.013 1 1 2.113 1 1 7.07R-2 i R . to n.1_
- s. a , e - -.. i a.i- " I siw h ama 91a. Tam. alt.sta.111.ata.? It san., I a.sen.a 1 2. san.a I 1 tan 1 -
- 1. t as mes sie aa-aan a ti_ie nu su s ss n ta n ss a_1a a_en
- i. a
- min m i. aman e n t .- n
- h. h ,tml. Ana - R& _a - - " a h na A ss 1 na 1 is n as a sa ~ n na i 1a n k na a s, i sa s ai a sa a ,, n ,a a an
- n. - -i in t. m e s_a -i 0;ce c;Se
- a. -- -i an. - nia.a w a D.03 0.11 0.53 0.67 0.41 0.13 J. lettism i_ eain m a t.it. a u-- " in 9.47s.) 1,0$0-3 2.339-2 3.938 2 4.313 2 3.128 2 2.328 2 1. 04 e.1_
a_ e --. ..a t a t - " saw R.925 9 3.345 9 7.243 9 4.273 9 1.693 8 1.453-0 7.013 9 1.293 0 s_
a b.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
- m. m as a n.a a s ur.n s aw n B. 34seelved amble lastet sa in w at ta m.u- -
et m iin.1 e .eam.a n .21a.1 1.ien.1 1 tin.1 a.aan 1 1.sna.1 a . nen.1_
n_
s- aa a.e- " saw h.eam.a 1 ita.1;l 1 ala. h 1 nam.a a.ata.e 3.aan-a 1. nan.1 1.01a.a n.
n b as n_an n_an n_ni n_an n at a ne n_n1 s_ m as ti an maa siwi
- 4. Groeg Alphe a- e.a.1 hat-ta_. a.e-
' i en ktn e t t_tm l a t_tm i < tn i e tn i sin i < t.tm i sun 3_ u r--a .a t ami- '
I saw kin le tn I c tn [ rru I s tu I stu I stu I st_tm a_ in t - at ta a..a.-a. ta as -
I titana ta .11a sa it aan.n l a . m s m aal 1_ sna.1 is_asmaa i e ma nia 1 3 stmaa i e_nimia e
m_ m.i- na ma i a t.m - I titara E.81A*9t].14t*911.21E+9tt.203+9 12.11399 e 2.573+9 l 2.97B+9 1 8.093+9 _
(1.1b450 detectable activity gbeve lawer Limit of Detectica for comatleg race imetrumentaties.
43
r 1
l - I 1
TABLE 1.2-1 (continued) tvaen saActtAA 94hSt ifAtlW '
EffLWuf Ase id4Y3 elleenat Maf- street fet Jint . MCtlett,1987 LtWO (ff twuf t . Inseafleu Of Att MitAtti i tattit i laT t M i Mpf f ieA Anahaffal Af f i amW t Mf I afu manatra
- 1. Fissten and Astleetten Prodwts
- 1. tatat A,t t.i t. Sai-- " t fl i f said i 1 laf J t 1 *ef J t 1 Uf.1 i t EM J l 1. EM .1 i i 17f J l l fM.t f A.a, man r am, mm e .at t aa a.1 --- " l d oni I a fer.t I a ast.t I f.tarJ l t . faf .a I t Saf.a i a tif.e I f ttta i t.aAf a
- 1. E af 1AfftAA Llat ta
- a. bartart s tahata hans ft.1 meman 1 t_fa A la A la AM t.11 A_Af A.M t 1a h_ kartarl e aan teena 11. A meaal 1 A . la iM t 22 A .1A A_IA R.Af G .M A_ta
- r. -1 mia Aman in A meman i G .12 A.A7 tH G.M A.M A_At A_la R.11 m_ ^ - -1 Aan temma f 1A. A m-1 1 AH A.11 A.11 t_It A AA A Al A A1 e _ t?
J. Tet tles
- 1. f atal Ar t t u t t a ha t - - " ft ? PAf e t i_faraf R.Mtat f tafa? a _ eM a t 1 taf a 1 1 hat a t 1 Of af
- f. Amarama Pu-mat rat lan Ral- - " dt/m1 f _ &M.t 1_ tM.i t . f M.R f taf.1 1 Mf.1 1. fu .1 1.1Af.t 1_11f .1 1_ 1 af itat a f M.141/ ail 1 R . Af 1M A_it A 11 A_mi A A2 1 R1 A.t?
- 1. Sl*$41eed table 064644
- 1. Taami An t i e t t e hai---" ft l _ t i ta t EM.1 1 Lit.t f . t MA 1_ tti.1 A _ f tf .a 4 .1M .1 1.aM A
- 1. Amaraan Funmae sat taa Rei- " di /mi 1.1 M J f.tal.1 a.itf J f . RM.? A . fts .A f Alf.ta f hat.? 1 AM.1 1.19 G_11 G ,42 R _ la A Af A.M R 1A A AA
- 1. 1 af t Lat t f M.a 4 t /mi t i L. Orell Alphe
" e ft t rita i at ta i atta t at ta i at ta i et ta i atta i e t ta ,
t_ taaat aatt.tte nat-
- f. A.arama Pa.ne mme sat t na hal - - " l d t /mi ! (113 ! et ta I ri tB I (Lta I alla I ek ta l etta I alta
- n. mi.ma a# timia inatta ta Auruen. I i n tar. 1 i taf aa t i sM aa i i .tMaa i 1.uf ma i f 1Maa 1 i LM aa e f.naf aa i t aM as
- m. mi m af til at t aa **** *= 1 11 tars i 1. t tf at i 1 ?M at i 1.1Al at t t _tMala i 1 AMat i f _ taf at i f _ f ?f a t i A . th a t f
I 4
I I
i 44
O TABl.E 1.2-1 (continued)
DTEDI RELLA8 Dett Stattel (ff1WWf ase Whlft 98980541 lintessesht etspf f 5 Jo#*erY*Jumes 1981 IlWiG If fIIEstI n- - tasiranat I mit t LTMI I Fas tethpC3 t iet amavant hreIL e anAT IJVWS 3 2" taa
- 4. Llgste If flesatt 1,.as et . . - Dra.on-t - - - *(4.0s-1 n,.aa . . - pra en-a - . - * (A .at -4 _
emaa 3.21a-1 a.223-1 1.2am*1 6.113-1 t.793-1 ?.303-2 1.923 2 3.?13-1 97.12a-3 1.013-2 1.023 1 1.20a-1 L . &2a- 1 1.933-1 1.373-2 2.603-1 ,
cm T tin-a 1.ata-1 1.113-1 2.11a-2 t.lan-1 1.103-1 9.903-4 1.eaa-3 ca.tna g i. i n n rm 1. nam-a t ten.d m.ain-a 1.aan-a s tam 2.643-4 g -
1.429-3 5.445-3 2.235-J 2.925-2 5.375-3 3.195 3 3.305 3 v. -
ti til 1.gsu 3 totia 1.243-3 6.935-3 1.440 1 9.615-3 0.095-5 1.335 3 5.073-3 2.250-$ 3.678-5 < I4A > 920-5 < LLA 2.023-3 6.733-3 5.74F 3 n.asi 3.218 9 ?.399-4 2.530-d . 0 2 9. .I < taa 1.143-5 2.013-4 2.123-4 annu nas
- 1. ,10-1 S.448-5 S.228-1 ,.469- i 2.2 3-2 6.648-2 ll.065-1 3.958 3 a 111
- 1. l55-4 9.135-4 < LIA D.2SO-4 3. 2llB-5 (LIA '
i.44 9-3 9.919-3 a iu 3.WJW-3 T.135-3 7W3 3 3.gIW-3
- 1. h 3 3 * ' l 5.535-3 4.333 3 4.515 3 9t W e lipe<lty) Cr*ll 6.600 3 2.340-3 sen- 54 b.123 4 2.575-3 4.108 2 4.450-2 2.973-2 3.tle 2 Pe-59 b.6(se-l 1.399-2 1.279-1 1.410-1 4.609 2 1.378-2 4.373-3 6.418-2 co-t? < Lim S.638-5 1.168 3 .220-3 S.548-4 5.535-5 < tab 6.098-4 iib-95 1.693-4 1.103-4 1.949-1 !.038-2 1.178 2 4.299 3 0.698-4 1.688 2 sr-96 1.998-4 2.813-4 9.750-1 .028-2 1.218-2 2.700-3 S.628-4 1.548 2 s>12 2 < Lla 7.729-4 < LIA P.720-4 < Lla 2.128-l < LIA 2.128-5 su lle < Lib 4.068-3 3. l'? g- l 1.439 3 1.978-3 1.989-3 4.759-4 4.433-3 str125 < Lib 4 218-2' 2.448- 3.469-2 7.548-3 2.125-2 4.42h-3 3.323-2 to-4 5 < Lib < Lib 1.333 1.333 2 4.tes 3 4.149-4 1.30s l S.433 3 <
Ba- ill 5.878-5 (IJA 3.140-1 9.038-6 1.428-4 < Lla (Lla 1.625-4
~
ae- ,31a 1.353-3 < LIA < Lab 1.350-3 < LIA <144 2.250-3 2.2$9-3 se% 3 3e 2.973-4 < taa < LIA 2.97B-4 < L1h < LIA 1.578-3 1.578-3
< Lib 2.650-5 < Lth 2.658-l < Lla < LIA (LLA < LIA Er-te mo-99 < Lla 1.243-4 1.273-4 2.619-4 < Lla (Lie 1.595-5 7.590-5 an-24 < Lib 3.698-6 1.470-1 1.50J-3 1.198-4 3.003-4 (LIA 4.198-4 (LLD 1.353-4 1.375-3 1.415-3 s.175-e 4.355-3 u.am s.sau-a to-103
< Lib 1.075-4 .L1h 1.073-4 Lib < LIA < Lla ( LIA 9e-132
< Lib < Lla C215-3 1.315-3 1.058-3 7.553-4 < Lla 3.513-3 51-45 Ag-110m < Lim < Lla , ~ < Lib < Lib 6.338-5 3.418-5 <LIA 9.000-5
< Lim < L13 <LLD (Lib < Lib < LIA 5.905-6 5.7D5-4 46MMffl tr-99m
- enaalyste perforimod by effette readet. Palee listed to the Lia for the smanysis.
a i
d 45
r TABt.E 1.2-1 (continued)
Oveen engttaa pen 43 llatten Ef fLWat ase taalf t 335pplu Statannam Mpent f an Aity . w(guage, topp LISitt (ffLWuf t . Sapetallen Of ML Ntta$tt t :.:=1 mai nitsa I tatit t t it? I am i upt I saa maatral aft i amt i Mr I atu haatra
- 0. Ligold Ef flosets e e fi - _
A .as
- w ea - - - e y _ us.1 a _ aM.1 7.eaa.1 t uf.2 a _ tu.1 ?_aar.1 m int.1 t.ufa funa
- c. aa G w.1 t . tar a e 911.1 1 mera 1 mer a e . mar .1 9 aina v . nu .s fa.11a i ett.a 1. 5m.a f. AM.a 1_ LM .1 2_ Bar J t . ttf a a _ tM.a i 3}r.3'~
e ant.1 at ta a . mar .1 1 taf J et ta attB cita et ta f a. t M a . i M .1 a _ i M .1 2 ist.1 t _aM s a 1ar a _ a . tar .a t ut.1 1.a n .1 f_a.nr i nar.1 a var.1 a mar.1 t _ aM.m a . sar.a a tar.a 1 tM.a , ans.1 n.ni
- 1. w .a 1 ans.a n tas.a 1 ass.a e air.m ettA i nas.a 1 a1f.t ,
n.in 1 aM a 1 ant.a i IM.a e tu.t a aan.1 a ait.1 m m . tan tier.a __ a nar.a e _ enf.i e. aan . i t 11f.1 s anaa i tar.1 a rM.a a tM.s t maf.t aman f Air.a an.11a a taf.a 1. tar.1 a 9ar.a a AM.1 7 aaf.a < t LB a ett.Q a sar.a e aM.1 t aM.s a . tar.a 1 Gas.a 1 naf.1 a.atf.1
~ gg % gg,,ggg,g f,.at i fff.a a aM.4 I aM.) a ser.1 m aa e att.a 1.19f .1 1 mar.1 e aar.1 1. t u.1 e 1M.a 1 tat.a 1 1er.1 1 AM.1 1. t M J 1. aM .E f air.1 1. taf .1 rate a aMJ at tA 9 ter.a 1 Bar.R a. ptf .a ettB attB a inf t P&at 1%erJ e. har J 1. Gas.1 1 I 17. 1 1.1 H.1 1_ a2r J e aar.a 1.f tr ol M
t _ aM J 1 taf J f_ Tar.1 1.168 .1 1 anf.2 1 LM.t a AM.a 1 maf.1 1s.m et ta a t LA ( L tB ttr a alta b111 at L A iLLB a t LA _
a t LA a Aar,1 a amt.t i 1M .a h tia 1 amf.R atia t taf J t _ ealJ E t31 a tard t .W .a f . sal .a 1.1M .1 1 at*J 1_ ?M.1 1 TM .1 ? saf.(
atta e LM 1 e . tM.R a ald J ttLa (t LA 4. ant J sw alta 1 aald ella ttta dita alla ha. t n at LA 1 and.a et tA f aMJ t _1M.R ttO < t tA t taf.1 hm et tA attA f_aaf a
- 1. tM .1 t .laf.t alta itLO a t ta f miJa (tta at ta _e t tA ga. tism e aar.1 a _ aM el 9 1M 1 9 aM.I I f af.1 fttB I nM J P _ GM .1 )
f.?MJ 1.11 f.2 f . 7M J tita a sar.1 a uf.a na.111m 1 mf.1 R.aL1 1 eat.1 a t LA et t B f . ast .a ? _ aM .a anda etta t_eaf.t atta at ta
- at ta f _ aM .1 etta t aM .1 et LA altB a lat
,t ta t aM.a ,tta 1 aM.a . i tB <tta .i t a ttB a.in ettB tita at ta 1 tar J 1 Laf J ttta at ta site rutM la. n 1 .i t A .tta n nr.s n.nr. tier a 1 mar.1 ng f . tif .a _
1 i
f I
i 46
TABLE 2.0-1 Dveel saltttaa pese stattei littutet ass talet Mlfetai 3Duestma GEfeet i MLIG Pe840eCf M tlktli sosta Jea u 1981 Deepeellten et emerset hif sh a lma k . flua . 1.ma . emitaar t.m - maan at t-- --a watmat- ht- w au - - - ita It w w w 'ema-1-12 spent meetne, Class A, 2 Linere, Coment Baelsein Dee, seravell, 354 0.341 open B.C.
1-23 Dewetered seein, Class A Liner sa Ceek, mese Baelseite Dee eerswell, !?? 2.74 s.C.
1 37 Dewetered poeta, Class A, Liner in Cask, some tueleetM Dee teravell, !?? 0.319 s.C.
t' l
MI **LII 1 100 3.42 i
47
~
TABLE 2.0-1 (continued)
Dragu attgas pese ttattes ifFttRest age tNM Mtfekt tim 84mem Mpest MtIS RISteagtput t seen Nb vus I ei iii .e sm-.i I u af te- nua tma tm un t- , =* a - - aft n 2,e lm MA t --
g_ .hu tma tm _ rim .ta . I tat f in ' .
o.ote 34 o... . .a ...t. ca... a, St , sa c..=, . i.ei..in o.. s r - it, att S.C. .
n.. ..t = o u r m it, att e ??
a.:o . .. 4 .. . ca... a, St . t. c .i. .
B.C.
t k
I i
M' MII : 354 0. 44 s
48
TABLE 2.0-1 (continued) eveen InfttEAA POWE0 lieflee (fftasNI set tie $tt 9($p9&M 3Dilseas4 GEftti SOLID teetteCf tyt taltt somme s tarch , gas 1987 9ttpoeltles of notorial mafr ra. .analan- riana . t -me . ent tat s ima - man at t, _ ama n t maa taa mi- en, m e -- - ret t I t.,taa on,' w -.
3-3 Dewstered Rosine, Class A, Liner la Cesk, nosh Bacluelve Use Bernwell, 177 2.1 S.C.
3-10 Filters, Cloce 3, Liner la Cesk, none Esclosive One Bernwell, 135 113' 8.C.
3*2 Dewatered Resia, Class A, t.iner in Cesk, none sneleelve Use gnwe'.1, 177 14.7 3-19 Dewatered Desie, Class A Li in Cesk, none saclesive Use gyll, 177 1.42 3-24 Dewetered Besia, Class C, ner la Ceek, none saclusive Coe serswell, 73.5 302 '-
..e.
3-25 Dewetered Peela, Class A, f. inst in cook, nome pseluelve Use Bernwell, 177 0.269 S.C.
(
Dewe t.r.d ...ia, C1..e A, u , s a ca.=, ..no a .lasive o.e ser.well, in 0.134
! 3-n
..e.
l saunar m Ml: 9 go,o l 434 i
i l
l 49
TABLE 2.0-1 (continued) evees entstas pow 1 staties Ifft'Auf AIS taklft 989806 4 Spaaammeu atpast SOLle testeaClivt teL5ft NgNfu &aril TEAd 1987 Diepeettles af Meteriet
- marr rm..,.tantaa. ti ma n f _ s.1 tat t ta - made af f,--t ama t an ian u.s e.,emi-- - get In w in o., mi _.
4-2 Dewstered posin, Class A Liner in Cask, none Exclusive One tornwell, 135 30.3 S.C.
4-10 DAN, close A, 2 tones /59 Drums, W/A Baclusive Use sichtend, 634.5 0.494 von wA 4-13 Spent seetne, Class 3, Liner in Cesk, coment Excluelve Use Be rnwell, 172.5 40.0 S.C.
4-24 Spent Resias, Close A Lingr in Cesk, cement tacluelve Dee Bernwell, 172.5 18.5 S.C.
4-29 Spent Resine, C1ses e, Linst in Cesk, cement Escluelve Dee Sstnwell, 172.5 21.0 S.C.
le maf 19T45* 5 1290 110 50
1 TABLE 2.0-1 (continued) l l
l swees arttaa peae Staties tffLW3ft AIS Witt NS8964 SDelasseau Mpest 90Ltt MifW mitt sertu NeY vtaa 1987 94apesItles of sentedel aaer s a.u n t a tam _ rh a .ta . tat tat f etas - aman .# 1,-- -4 mma n t-s t an mt -. e., mi -- - a t t 3i c.,i e.,' m i --
5-8 spent aesine, Class A, Liner in Cask, coment asclusive Use Barnwell, 172.5 0.37 S.C.
5-15 spent gesias, Class A, Liner in Cask, eenent saclusive Dee Barnwell, 172.5 0.411 S.C.
5-22 Dewatered seelne, Class A. Liner in Cask, nonassclusive Use Bernwell, 163 5.92 S.C.
l I
Mamarsoful* 3 508 6.70 51
1 TABLE 2.0-1 (continued)
SYtel IRKLt.AA 70148 Stalles (FFHENT AIS ilhltt Mts9tal Mielassesnt atPWI mie awwim mitt ISBfM Juna .__ ftAA 1987 4;
.. iu .e m.ci.i or, . . ci . . . i.i ui . -
-.,,--4 .n . mi- s., m - - ...,. c
,., m i _ .
6-15 Dewatered Rosin, Class A, Liner in Cask, none Exclusive Use sarnwell, 177 3.39 s.C.
6-19 Dewatered Resia, Class A, Liner in Cask, none Esclusive Use sarnwell, 177 0.47 8.C.
6-26 Deva;ared Rosin, Class A. Liner in Cask, none Raelusive Use Barnwell, 177 0.343 S.C.
l*'MY MalSl g ggg 4,gg 52
TABLE 2.0-1 (continued)
STROM IRJCLEAR p0WER STAf t9f ,
EffLutNT Ase instT! SIl80%L lin1 Assent stegat SOLIO RA010ACfivt tan $tt DONTM JULY TEAR 1987 Otsposittee of material haff f barriat taa_ fim . fees Salidif wiam Ammat enda a f f r == = et haettnattaa Valm Par int-e fft'l fortaa par tht amaat 7-23 De.etered testa. Class A. Llaer la Cask, neae tatlestre Use tarewell. 177.3 0.941 S.C.
7-24 OAW. Class A.12 overpaths/59 dres, h/A tativstee Use Richard, ida $80.3 0.620 7-27 De.etered testa. Class C. timer la Cash, mene Est1=sive use ter== ell. 73.4 290 S.C.
pCNTAT 10 tall 1 Eli M
53
l
.- 1 l
TABLE 2.0-1 (continued)
BYeDI EELEAR Nt $fATIDI EffLIKh1 Ase m$Tt Dt5895AL Stn1Assant street SOLIO RA010ACifvt W5ft leuTM AUGL$f YEAR 1987 Dispeellten of Haterial haff t haar et at t aa. flaan . fees h1 f d i f et aa Aaaat them af framanast heat t aat t aa Valm lar hiammal fit I furt aa par hiammat S-7 Deustered tesla. Class A. Liner ta Cask, sene tsclosive Use Berew11, 177,3 g,$$$
5,C.
5-14 temetered tesla, Class A, Liner la Cash, sene Esclosive Use 84rnme11, 135.8 3,42 S.C.
De-stered testa. Class A. Liner la Cask, none tatlesive Use Bernmell, 177.3 3,33 b24 S.C.
4 ete a 6 d' leuT*V 10fAtt i 54
1 l
l TABLE 2.0-1 (continued) tytes laKLIAA Pedt If ait0N EFFLUENT ase iak5ft DISPOSAL MM!assaakt etPoef SOLID RA010 ACTIVE IdA$tt pertM MPitJett YTAA 1987 eis siti .f n.teriet I fortaa par ini-me matt r am a r ri at t am - finna f =aa tail di f et na immat mada af f raataart naut i nat t aa vat par tht anent ef t t w . Ci.s. A, u es-,.i drwi, ae t ci.iive Use tico d, i2er.s i.22 tak SAW, Class A. $4 SS-gs) drws. neae Esclestre Use Alchland, 621.0 9.437 9 11 ten Sometered tesia. Class A. Liner in Cash, mens Catlosive Use larmeell . 177.3 1.47 9-18 S.C.
DAW, Class A. 29 85-gel drums /36 SS-esi dres, neae tsc1.sive Use techland. 643.5 0.272 9-22 ten De.atere) tesis, Class A. Liner in Cash none Cactosive Use Sarosell 177.3 0.518 9-28 5.C.
pouTuf 10fAtt _, _ t traA.a 1.42 55
- 1 TABLE 2.0-1 (continued) 07 eel saKLtAA pewt liATISM (ffLWNT Ase ten $ft DISPOSAL SEMIAasaAL etpoet SOLIO RActthCT!vt taalit 89tfM OCfWit TEAR 1907 Dispositten of festerial Raff t haar e lat t aa - fina a . imaa - ialldif elam Ammat Itada af Trumaart hee t t aati na Walm per thiansat fft 1 forlat Per ihlansat IM De=atered testa. Class A. Liner la Catt none (sclusive use Bernme11 177.3 0.631 S.C.
94-19 Coatered tests. Class A. Liner la Cast none tsclosive use te rnme11, 177.3 0.133 S.C.
IM3 So etered testa. Class A. Liner la Cash, mene tat)estee Use Barosell, 163.3 2.29 5.C.
penTMLV TOTALS 1 m.e 1 as 56
1 1
a TABLE 2.0-1 (continued)
Dveau enitLEAA PIMI STAf tee (FFLutWT Aae elft D15P05AL SEMIAsstat etposi SOLIO tAcleaCTIVE 25ft MDufM tevDett TEAR 1987 Disposillen of Material u at tr . ,t a.attaatana va1 par ut - e ret n I cort aa p., ui-.e marr rh..retneta _ ri a . t tai t ai t. tan amare Estlestre Use Be rawell . 177.3 0.235 11-4 Deuetered Reste. Class A. Liner la Cast, neae 5,C.
tscivsive Use Bernwell . 177.3 0.53%
11 16 temetered Besta. Class A. Liner la Cask. eene 5.C.
fatleslee Use Bernwell . 177.3 8.434 11-20 temetered Resta. Class A. Liner la Cask esas 5.C.
t 111.e a ama ICuTmv T0fALS 57
l TABLE 2.0-1 (continued)
BYeon IeKLIAA POKA STAf!OM (ffLIANT Ase m$tt stSpe$AL $(MIAas4JAL MPett SOLIO RA010aC11vt tellit
,enin uCt ca vtAs iwi eis,. site .e =i.ri.i mast r a.ar el at t an . flaa n f as talidif eine am e made af f rama art neit ima ti an I
valm ter thimment af t t carina per titaneet in-a ti.ii.d w iii, ai - i er nas i. ..a..,ter t.ci.si.e we o.i sie,.. m .: e.in
,r .ssin,es.ri.i i m icni.a..
=
it ti.it., o niti, Sni-i .< eaw t. ..ad.r e.r e.si.si.e Use m ,.. 4w.. ..i pr. cessing /bertal TK/ticnimad, ist 12-9 Oswetered besia. Class A. Liner le Cast, a.ae tas1 si.e Use Sara ell. 177.3 0.345 l.C.
in-14 te tered Besis. Class A. Liner in Cast o.ae Enclosi.e Use Saravell. 177.3 0.165 S.C.
sewf*T TOTAtl 4 tiaa.s e .as t 58
l FfGURE 3.1-1 Estimated Cumulative Gama Dose (in mrem) from the Byron Station for the period January-December 1987 ;
100 Isopleth Labels Small figure - multiply by 10-5 - 100 Large figure - multiply by 10-5 300 :
l N
( o V 400 j
\ ' 100 % 150 /
YT e i ,-
- Pecatonice ROCKFOR
~
/,
/ ..
g e /
3,,,,,..... ,, w,,.,3 il vs A -
\
q
- m. ,0 j - . .
l ;.. . n.
oinen u s 59 0 ,
,s 10 9 2p mi
i ^1 1
- i FIGURE 3.1-2 l
l 7 i Estimated Total Concentrations (in pCi/m3) V of Noble Gases from the Byron Station for the period January-December 1987 l f
l Isopleth Labels Sinall figure - multiply by 10+0 "j *"
25 Large figure - multiply by 10-1 YRW u e
'5 W.
7s N5 50 d
)
. w * ',
W- 2*
- Pecotonice ROCKFORD,
- b,
/ .
T 1- _,,
/ 't) 25 250 qq' 8$RN
\, ;, .5 6
- 09el.
. ..... ~ ..
- i,... .n.
3 /
Dison N
60
' L 1
FIGURE 3.1-3 l Estimated Total Concentrations (in pCi/m3) 50 of lodines from the Byron Station for the period January-December 1987 ~
Isopleth Labels 100 Small figure - multiply by 10-5 Large figure - multiply by 10-6 , ;
25
^* N )!/ ,
\
', 2*
?
- Pecolonica ROCKFORD 25
-to-
- l 100 ft 250 as
- RN pg
- l, A o,....*[ ~ '
- L
- ,.i.
g, 25 *
- ,... .n.
oison ' ' *d '
- 61 0 $ 10 1 2,0 mi
-_ . - . ._--.._..--_\ - - f" . :27 .i .. .._ - _ -__9_ . - . . _ _ _ _
^
1 FIGURE 3.1-4 Estimated Total Concentrations (in pCi/m3) of Particulate Matter from the Byron Station /
25 for the period January-December 1987 25 Isopleth Labels L
" l Small figure - multiply by 10-7 .
Large figure - multiply by 10-8 joo .
! erb { l
~
- , I j
%, 1Q 25 I
V 9 50 V[
! 2
- Pecolonice ROCK D, 50 e' / 25
(
), F .tr e . gy I rs 250 ik .
b....
4 L
.......%,;,A ..
25 3
- j.i.n.
3 /
l N
62 0 a lo is to mi l ,
1 l
l i
TABLE 3.1-1 BYRON UNIT ONE I
1987 ANNUAL REFORT MAXIMUM DOSES RESULTING FROM AIR $CRNE RELEAIE3 PERIOD OF RELEASE - 01/01/87 TO 12/31/67 CALCULATED 01/13/38 !
IST OND 3RD 4TH T fPE QUARTER Q U A F.T E R QUARTER O U M. T E F. Apu;t L JAN-MAR AFR-JUN JUL-SEF CCT*0EC GAMMA AIR 3 87E-04 6 9fE-04 4.37E-0! 8 01E-05 1 23E-21 (MRAD) (SE ) (SE ) .it ) (3C : (!E >
BETA AIR 1.6:E-03 2.90E-03 0 570-04 3. 8E-04 !.11E-33 (MRAD) (SE ) (SE ) (iE ) (SE > (SE >
TOT. BODY 9.52E-05 1 72E-04 1 6:E-05 2.1:E-05 3.0 E-04 (MREM) (SE ) (SE 3 (SE ) (SE ) ($E SKIN 7.99E-04 1.43E-03 1 28E-C4 1 67E-C4 2.572-03 (MREM) (SE ) (SE 3 (SE > (SE i (SE .
ORGAN 2 87E-04 2 01E-02 7.74E-C3 3. ?E-03 3.12E *:
(MREM) (SE ) (NE ) (NE ) (NE i (nE i THYROID THYROID THYROIP T H f F.0 ! D 18 77 JI;'
THIS IS A REPORT FOR THE CALENDAR YEAR 1987 COMPLIANCE STATUS - to CFR 50 AFF. ! ,
.............. : OF AFF I. .............
OTRLY IST OTR 2ND OTR 3RD OTR 4Y9 GTR ri. *. OF OBJ JAN-MAR APR-JUN J U L -! E F- 00T-N3V CE. AFF.!
SAMMA AIR (MRAD) 5.0 0.01 0.01 0.0 :.C0 13.) 0.31 BETA AIR (MRAD) 10.0 0.02 0.03 0.C0 C.03 .'..' O.03 707. BODY (MREM) 25 0.00 0.01 0.
- .;? ., 0 01 SKIN (MREM) 7.5 0 01 3.02 0.C! C.C3 !!.. 0.0:
ORGAN (MREM) 7.5 0.00 0.27 ^ . !! :.(4 ;! ,.21 THYROID THYRDID THYRCID THYRDID THYROID F.EIULT E l a ti! UF O:i OL03 FL. "Ca ;;
UvD4Ti :s.ti 6 { } F. '.% ~ *i;3 63
G TABLE 3.1-1 (continued)
SYRON UNIT TWO 1987 ANNUAL REPORT MAXIMUM DOSES RESULT!ND FROM AIRBORNE RELEASES PERIOD OF RELEASE - 01/01/87 TO 10/31/87 CALCULATED 01/13/88 IST ND 3RD 4TH TYPE QUARTER QUARTER QUAFTER CUARTER ANNUAL JAN-MAR APR-JUN JUL 3EP CCT-DEC
, GAMMA AIR 1.99E-06 1 07E-03 1.79E-04 1.57E-03 :.8 E-03 (MRAD) (SE ) (SE ) (SE ) (SE ) (SE )
DETA AIR 1.00E-05 4.34E-03 7 13E-04 6.41E-03 1.15E-02 (MRAD) (SE ) (SE > (SE ) (SE ) (SE )
TOT. 90DY 5.14E-07 2.49E-04 4.6 E-05 3.87E-04 7.03C-04 (MREM) (SE ) (SE ) (SE ) (it ) <!E )
SKIN 5.3 E-06 :.18E-03 3 61E-04 3 14E-03 5.4?E-03 (MREM) (SE I (SE ) (SE > (SE ) (SE >
ORGAN 2.41E-05 2 01E-02 7.7eE-03 3.2'E-03 3.10E-00 (MREM) (NE ) (NE ) (NE ) (NE ) (NE i THYR 0!D THYR 0!D THYRDID THYR 0!D THYFOID THIS IS A REPORT FOR THE CALENDAR YEAR 1987 COMPLIANCE STATUS - 10 CFR 50 APP. 3
.............. g or arp g, .............
OTRLY 1ST OTR ND OTE 3RD OTE ATH QTR Y F.L Y L CF OBJ JAN-MAR APR-JUN JUL-SEP CCT-NOV 0$J AtP.!
8AMMA AIR (MRAD) 5.0 0.00 0.12 0.00 0.03 1^.0 0.00 BETA AIR (MRAD) 10 0 0.00 0.C4 0.01 0.Ce 20 0 0 06 TOT. 30DY (MREM) 25 0.00 0.01 0.00 S.0: 5.0 " . 01 SKIN (MREM) 7.5 0.00 0.C3 0.C0 C.C4 15 0 ".*4 ORGAN (MREM) ,7 5 0.C0 0.27 0 1C 1.C4 10.0 21 THYROID THYRO D THYROID THYK0lt. THYFO*D RESULT 3 DASED U W ODCa REVISION !?
UPD4ft CS114 FEIEUARY 19E.
64
.o.
TABLE 3.2-1 DYRON UNIT ONE 1987 ANNUAL REPORT MAXIMUM DOSES (MREM) RESULTING FROM LIQU:D EFFLUENTS PERIOD OF RELEASE - 01/01/87 TO 12/31/8? CALOULATED 01/13/3E
.157 OND 3ED 479 DOSE TYPE. QUARTER GUARTER Q U A S:TE; 30ARTER AO : ;i '.
JAN-MAR APR-JUN JUL-SEP CCT-DEC t
TOTAL 2.91E-02 7 09E-03 4. eE-03 2.6:E-03 4.32E-00 SODY' INTERNAL 4.00E-02 2.90E-02 9. LE-03 4 08E-03 S.:tt-0:
ORGAN LIVER OI-LLI DI-LLI O!-LLI O! .L:
THIS 18 A REPOPT FOR THE CALENDAR YEAR 1987 COMF LI ANCE ST ATUS - 10 CFF. 50 AF F . :
% OF AFP !. -------------
QTRLY IST OTR OND OTR 3RD GTR 4TH QTR 7 F. '. ' % OF OBJ JAN-MAR APR-JUh JUL-l*P CCT-NCY 01.- AFF.*
TOTAL $0DY (MREM) 15. 1.94 0.49 0.;t 0.t7 :. 1 44 CRIT. CRGANIMREMI 5.0 0.30 0.58 0.tv 0 1: 1 .: 0 3-LIVER 01 LL1 OI-LLI OI-LLI 01 *.L I RESULi! fA!!D JF0r ODCM RE's: 10N 11 UPDATF3113 F E S R'J A ' 1736 65
Q TABLE 3.2-1 (continued)
&YRON UNIT TWO 1987 ANNUAL REFORT MAXIMUM DOSES (MREM) RESULTING FROM LIQUID EFFLUENTS PERIOD OF RELEASE - 01/01/87 TO 12/31/87 CALCULATED 01'13/33 157 OND 3RD 4TH DDSE TYPE QUARTER QUARTIF. QUARTEE QU RYER ANNUA.
JAN-MAR AFR-JUN JUL-SEP CCT-LEC TOTAL 1 91E-0 7.29E-03 4.*4E-03 :.4:E-03 3.33E-0 90DY IN1ERNAL 3.48E-02 .90E-3: 9. :E-03 4 38E-03 7.'1E-4:
ORGAN GI-LL1 01-LLI 01-LLI 01-LLI 03-LLI THIS IS A REFORT FOR THE CALENDAR YEAR 1987 COMPLIANCE STATUS - 10 CFR $0 AFF. !
.............. : or AFF 3, .............
OTRLY iST OTR IND OTR *RD OTR ATH QTP TFL/ : OF OBJ JAN-MAR AFR-JUN JUL-SEP QCT-NOV 0FJ AFF.:
i TOTAL 90DY (MREM) 15 1 28 C.49 0.*f 0.17 .." i.11 CRIT. ORGANtMREM) 50 0.70 0.58 0.11 0.1: 1;.: 0.**
01-LLI $1-LLI O!aLLI 01-LLI 31-LLI RE U'.T 3 t ' E D L'? O h' 0D5? FE*!!!!CN 11 USI4T4 ~3111 Filiut's t7ff 66
. i
- SYRON STATION Figure 5.0-1 0FFSITE AIR SAMPLING Afl0 TLD LOCATIONS
[(
. ., f .m g
g Y g,t , 4-zm .
~
Addl tinaal llData l faus; I
N s
BYROW e3 ML liTATION L -
7 Wmis FA e<
' /, ${'
- m. e x SCALE t-! i r , , sus Air Sanplers 1 - Byron 5 - Nearsite Station - S 2 - Stillman Valley 6 - Oregon 3 - Nearsite Station - E 7 - Mt. Morris 8 - Leaf River 2
4 - Paynes Point TLD Same as air sanplers plus a sufficient nunter of additional dosimeters placed near the site and near 5 miles to assure that one dosimeter is located at each range in each of the 16 meteorological sectors.
67
D BYRON STATION Figure 5 g_2 TE AIR SAMPLING AND TLD LOCATIONS Byzi
"' "'I m
6 A,rq
. I c
BYRON STArroy
- , m Bygg O
I
.:I=
,Br 24 id
=
% a, Y 6
Br DEERpsin go _ . as
/) 7 y
68
BYRON STATION Figure 5.0-3 ENVIRONMENTAL RADIOLOGICAL MONITORING LOCATIONS
. t 1 - Byron Air Sag ler 2 - Stillman Valley Air Sag ler 3 - tiearsite Station - East Air Sagler er 7
i :ffEN 4 - Paynes Point Air Sagler 8 x ^ g- .
5 - rearsite Station - South Air Station 8 -
j 6 - Oregon Air Sampler r IE 8 r
e .ae
'g 7 - Mt. Morris Air Sag ler
$ 8 - Leaf River Air Sanpler n, E se h\
9 - Woodland Creek Surface Water Sam le , j !
I v.n., J 10 - Intake Surf ace Water Sagle 7 11 - Discharge Surface Water Sag le a i
_" em0# *" fr ,a 12 - Conposite Downstream Surf ace Water Segle 13 - thstream Surf ace Water Sagle #
ML . .
Sl*" f w
"*'"' - 18 14 - Of f site Well Water r 8, m e. 7 15 - J. A. Reeverts Pine Hill Dairy **
3 16 - Kenneth Durien Farm I g y s ,16 rei 17 - Bosecker/Lingel Dairy Farm 18 - Of f site Well Water Sagle >iz
- 4 "*'
19 - Vegetable Farm
' s'L!E L- 4M 20 - Ed Seabold Farm s or e ? _ !o 21 - Onsite 22 - Onsite ,, , ' p 23 - Onsite **<* i 24 - Onsite _
L=? ? ? ? .__ J ""
BVRON STATION Figure 5.0-4 SPECIAL TLD LOCATIONS J. h. ,. _-
m.!._.,.d.h<-<.
_e. _ . ,
- ,I ~P 1 ' <
EEssr-a
? _e_ ' m>w - L;pn _
q l M
~
l ~v2 @ %. j . ' "-
_ "m 11 . .-fg -
y #p usV, .m e.
3 ..,
L ,.... .r...r see, m_ &Q Ir'7_9
. e g, 4w s: g+ ,n ,g.n.t
.- ~ . . .
4 .-. ' n --
) e M.' \ x 2 M .y5,9
,A t[.
-.+
s h ..sm _f.i.le .
% >gs 'A i jf % ers a
1: s
.c
- /," -, j l", i iP
- g r*
, f#! ! f., i',~, y i ,, ,e fd g
.s.nNL- __ s..
s-c . m .a ~ n- .-
- p.cygm iu3.s j'u+6C3 rs '-
- " ,=,c. T' u
e x - wy,g ~" nn 7,A, 7 4 a
gf-v.,
- - le 1- m. w s.
w .~ t i D:lt V . i_ .)
. m x
- m n ,-
1.
res.
.e o_ ,u =
p;gt-i t -. u ti q . , , . _~ "'t c- ,g 3 4. 2.. -
=_ fu 'c
.g m -- s, c-k,e-m
,-> i
.e w M-v: s
=
~
?_- %_ ,
- .=
< 1.-.
! g___y
-i . ..1, m:.w, -
a g '" & N .are
@l
- n. -
p ,,,1 g) -%
putv n, i jr&.. +. &s. 8 %1 r, e.
- c n- ..
y u
w a s -
- -E n y r.L....
i ,,,, d, + P Tl Em AW i e.f./e g;m M.6,(? 4 N y'1 ~ {,I j' 9- 3 4 yKi, ; *'ff kh , y. ,
- "' )splib -7
( .. A :fe . ! .;. g ah .
r -
n
._p. 4- .
p 4.r
'c t
U!
t T eb .~.79,
/[i 14 -- !. N3V~ L,' _
.%. I 011 d' "Ifi II i 70
Table 5.0-1
$YWUN STAlluN (NVIRO* ENTAL RAUlVLUGICAL NUNiitMING SAMPLING blit$
MLDIA
- D e 4 s 8 t 3
- 3 j
t I & E U' :*: o 4' 3, 3s 3 . . t *
. . E i 3 i i Location Location o k b h b 5 3 5 $ i $ $ C Code Typea Location E d Y O $ 5 C 5 E 2 & 3 J it s .
SY-01 C Syron Air Sa gler I I BY-02 C Stillman Valley Air Sagler I X BY-03 Nearsite - East Air Sagler I X BY-04 Paines Point Air Sampler X X 8Y 05 Nearsite - South Air Sampler I X BY-01 C Mt. Morris Air Sagler X X 87-08 C Leaf River Air Sampler I X 8Y 09 Woodland Creek Surf ace Water Sampler I BY-10 Intake Surf ace Water Sampler 1 8f-11 Olscharge Surf ace Water Sampler X 87-12 Composite Downstream Surf ace Water I I I I Sampler Bf 13 C lbstream Surf ace Water Sampler I X X X 87-14 Wfsite Well Water X BY-15 Reeverts Pine. Hill Dairy I I I I X 87 16 Kenneth Durten Fara I I I I X SY 11 C Bosecker/Lingel Dairy Fara I I I I I SY 18 Of f-site Well Water X 87-19 Vegetable Farm I 8Y 20 Seabold Fara I I I I X 8f-21 Byron Nearsite N I X SY-22 Byron Nearsite ESE X X g Bf 23 Byron Nearsite 5 X X SY 24 Syron hearsite SW X X g
- Control (background) locations are indicated by a 'C' in this colunri. All other locations are indicators.
71
Table 5.0-2 BYRON STATION ENVIROM4 ENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS
- 1. AIR SAMPLERS Distance Direction l Site Codea Location (miles) (*)
BY-01 a. Byron 3. 5 25 BY-02(C) b. Stillman Valley 6.2 56 BY-03 c. Nearsite - East 3. 8 85 BY-04 d. Paynes Point 4. 5 140 Bi-05 e. Nearsite - South 3. 6 180 "
BY-06 f. Oregon 4. 6 213 BY-07(C) g. Mt. Morris 7. 8 240 BY-08 (C) h. Leaf River 7. 0 315 BY-21 1. Onsite 0.26 9 BY-22 j. Onsite 0. 3 101 BY-23 k. Onsite 0. 6 182 BY-24 1. Onsite 0.65 229
- 2. TLDs
- a. Same as No. 1.
- b. Special TLD Sanplers Distance Direction ,
Site Codea (miles) (*) !
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 1,7 0.9 235 BY-112 1,2 0.8 247 a Control (reference) locations are denoted by a "C" af ter site code. All '
other locations are indicators.
! 72
Table 5.0-2 (continued)
BYRON STATION ENVIROM4 ENTAL RADIOLOGIAL MONITORING PROGRM, SMPLING LOCATIONS
- 2. TLDs
- b. Special TLD Sanplers (continued)
Distance Direction Site Codea (miles) (*)
BY-113 1,2 0.7 270 BY-114 1,2 1. 8 298 BY-115 1,2 1.0 314 8Y-116 1,2 1. 4 329 BY-201 1,2 4.8 36 0 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 8Y-206 1,2 4.2 112 BY-207 1,2 4.2 140 BY-208 1,2 4.1 159 BY-209 1,2 3. 8 189 BY-210 1,2 3. 6 218 BY-211 1,2 5. 2 .
238 BY-212 1,2 4.9 257 BY-213 1,2 5. 0 280 BY-214 1.2 4.8 298
. BY-215 1,2 5. 2 32 2 BY-216 1,2 4.8 337
- 3. MILK Distance Direction Site Codea Location (miles) (')
BY-15 a. J. A. Reeverts Pine Hill 3. 2 108 Dairy BY-16 b. Kenneth Druien Farm 3. 3 134 BY-17 (C) c. Bosecker/Lingel Farm 7. 0 53 BY-20 d. Ed Seabold Farm 2. 5 41 -
a Control (reference) locations are denoted by a "C" af ter site code. All other locations are indicators.
73
Table 5.0-2 (continued)
BYRON STATION ENVIR0ffiENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS 4 PRECIPITATION Same as No. 3.
- 5. VEGETABLES l
Distance Direction Site Code Location (miles) (*)
BY-19-1 Oregon Stand -
BY-19-2 Oregon Stand
- 6. CATTLE FEED AND GRASS Same as No. 3.
- 7. WELL WATER Distance Direction Site Code Location (miles) (*)
BY-14 a. Off-site Well 0. 3 101 BY-18 o. McCoy Farmstead 1. 0 235 (CECO-owned well)
- 8. SURFACE WATER Distance Direction Site Code Location (miles) (*)
BY-09 a. Woodland Creek 2.1 32 0 BY-12 b. Downstream at Oregon Dam 4. 5 213 BY-13(C) c. Upstream of Intake 2.6 302 l
- 9. COOLING WATER
^
. Distance Direction Sitetode ' Loation (miles) (*)
BY-10 a. Byron Intake Pipe / River 2. 4 283 BY'-11 b. Byron Discharge Pipe / 2. 3 283 River 74
Table 5.0-2 (continued)
BYRON STATION ENVIRONMENTAL RADIOLOGI AL MONITORING PROGRAM, SAMPLING LOCATIONS
- 10. FISH Distance Direction Site Code Location (miles) (*)
BY-12 a. Downstream at Oregon Dam 4. 5 213 BY-13 (C) b. Upstream of Intake 2.6 302
- 11. AQUATIC PLANTS Same as No.10.
- 12. BOTTOM SEDIMENTS Distance Direction Site Code ' Location (miles) (*)
BY-12 a. Downstream at Dregon Dam 4. 5 21 3 BY-13(C) b. Upstream of Intake 2. 6 302 75 i
e,,-,- , , - - - -.-,--,,,----,.------,---,n,-. -,-w,--, ---,,,..-,--,,-,-m x ,
l l
Tabla 5.0-2 (continued) 8Ywum 5fAfl0N ENv!RufefmTA h310 LOGIC,4 i90NITORING PROGRM. 5MPLE COLLECTidh ANU A.WDfS Location Collection Type of Frequency Sag le Media Code
- dite Frequency Analys t s of Analysts Nemaras l
- 1. 46rborne 8Y-1 Syron Continuous Gross beta weekly On all sagles.
Particulates 8Y-2 (C) 5ttllman Valley operation Sr-89.-90 @arterly On quarterly cogosttes f rom each location.
8Y-3 Nearsite-E for one Gemisa Isot Sarterly On quarterly cogosttes f rom eacn location.
8Y-4 Paynes Fotnt week SY-5 Nearsite-5 non-routtne Neporting Levelsh 8Y-6 Oregon l SY-7 (C) Mt. Morris Cs-134 10. Cs-137 20 pct /m3 l
BY-8 (C) Leaf River 8Y-21 @ site 8Y-22 thstte SY-73 Gisito 8Y-24 Unstte
- 2. Airborne Same as 1. Coatinuous I-131 wekly On all sagles.
todine operation N for one Non-routine deporttag tevel
- meek C.9 pct /m3 l
l
- 3. Mr Sagling Same as 1. -- Test and Weekly On all 56aelers.
Tra6a Maintenance 4 ftD Same as 1. 4arterly r-ima @arterly Two sets at all AP locations. Une set read guarterly. Second set read if required j 8Y-101-1.2 inner ding by r % alta Edison. at otner loca-through tions, all sets read quarterly. Miniswa l
116-1.2 of two TLDs per set.
l 8Y-201-1.2 thter wing l througn.
l 216-1.2 l
!
- Coatrol (ref erence) locations are denoted by a -c- in this column. All otner locations are indicators.
l Average concentration Over Calendar quarter.
l
._m-. -.,,_--m .. _ _ - . , .__,_. _ - - . . - . _ - . . .%. , -. ,,__ e , --. m -w_ m . _ , . . - - . _ __ _ _
Table 5.0-2 (continued)
BYRON STATION ENVIRONMENTAL RADIOLOGICAL MONITURIG PROGRAM. SAMPLE CULLECTION ANO ANALYSL5 (continued)
Location Collection Type of Frequency Site Frequency analysis of Analysis menarks Saanle Media Code * ,
- 5. N61k 87-15 J. A. Reeverts Pf ne Bl=eekly: 1-131 81=cekly un all samples. Llo: 0.$ pCl/I.
Hill Dairy May through Gamma Isot. May -
Bf-16 Kenneth Druten Fare October Sr-89.-90 October non-routine Neporting tevels8 Bf-17(C) Bosecker/Lingel Dalry Fara Monthly: Monthly 1-131 3; Cs-134 60; ts-137 70; BY-20 Ed Seabold Farn hovee er hoveeer - Sa-La-leu J00 pCI/I through Apri1 April 6 Precipitation Sanc as 5. Monthly Gross beta Monthly On all samples.
Gamma Isot Quarterly. On quarterly composites from each location.
Tritium Quartre/ly On quarterly composites from each location.
y Sr-99.90 W arterly on quarterly composites from esca location.
- 7. Veget ables 87-19-1 Oregon Stand Annually at Gross beta Annually Four varietf es (at least one green leafy BY-19-2 harvest Ganssa Isot Annually vegetable) from each location as avalleele Sr-u9.-90 Annually at harvest. (I-131 on green leafy vege-I-131 Annually tables.)
P. Cattle Feed Same as 5. Quarterly Gross beta Quarterly Grass: :wsumer (May - octeeer) and Grass Gamma Isot Quarterly Feed: hinter (noved er - April)
Sr-59.-90 Quarterly.
- 9. Well Water. BY-14 Off-site Well Quarterly Gross l' eta Quarterly on all ',asples.
Offsite Gassna Isot Quarterly on all samples.
87-18 McCoy Farmstead Tritium Quarterly on all samples.
Sr-89, 90 uuarterly on all samples. .
- Eontrol (reference) locations are denoted by a "C" in this column. AIL other locations are indicators.
Average concentration over calendar quarter.
Table 5.0-2 (continued)
BYRON STATIUN
[NVIRONMENTAL HAD10 LOGICAL MONITOR!hG PROGtM. SePLE COLLECTIUN AND ANALY5E5 (Continued) location Collection Type of Frequency Saaple Media Lode
- 56te Frequency analysts of malysts menarks
- 10. Surf ace Water 87-09 Woodland Creek Weekly (if Gross beta Weetly Ori all samples.
8Y-12 Downstream at Oregon Woodland Trittum @arterly te quarterly composttes from escn location.
8Y-13 (C) Dem Creek is Gaassa Isot reonthly (> monthly compost tes f ro.a eacn locat soa, tpstream of Intake flowing) Sr-89.-90 Warterly m quarterly composttes from eacn location.
hon-routine ueporting Levels 0 (See f ootnote *c.")
- 11. Cooling Waterd 8Y-10 Intake pipe Weekly Gross beta Weekly On all samples.
8Y-11 Discharge pipe Gassna Isot Montnly tb montnly composites f rom escn location.
Tritium Monthly (D 9enthly rotVostles from eaCn loCatt0n.
$r-89.-90 Monthly m contnly composttes from caca location.
- 12. Fish BY-12 Downstream at Oregon Three times Gross beta Three times From uregon pool of doct utver, on estele BY-13 Dam a year. Gaassa Isot a year. portions only. At least two species.
testream of Intake Sr-89.-90 mon-routane seporting teweIs#
Mn-54 kl048 : Fe-591:10 4; Co-58 3:10 8-
! Co-601:10 In-65 2x104 ; Cs-134 1:10 5; I
Cs-131 2s103 plt /kg met metgnt.
- 13. Aquatic Same as 12. Three times Gross beta Three times If available.
Plants a year. (,asuna Isot a year 14 Bottom 8Y-12 Pawnstream at Oregon Three times Gross beta Three times tm all samples. -
5ediments 8Y-13 Dam a year Genena Isot a year (> all sosples.
tpstream of Intake
- Lontrol (ref erence) locations are denoted oy a "C" in this colueri. all other locations are endicators.
mver a ge oncentration over calendar quarter.
' N-3 2:10 . An-54 1x103 . Fe-59 4x102 . Co-581x103 . Co-60 3x10 2 . In-65 Ja10 2 . Zr-Mb-95 4ml0 2 .1-1312. Cs-134 30. (s-137 do, sa-La-140 2s lu2 pc fl.
. , Provided by station personnel.
4
T Table 5.0-2 (continued)
SYN 0ct STATION ENVIRONMENTAL NAD10 LOGICAL MONITORING Pn0GR49. SMPLE COLLECTION AND ANALYSES (continued) location Collection Type of Frequ.ency Sagle Media F. ode htte Frequency Malysts of Analysis demarks
- 15. Detry Census a. 5tte boundary to 2 slies -- a. Enumeretton by a coor- Anavally turing yarsag season.
to-door or equivalent counting technique,
- b. 2 miles to 5 miles -- D. Enumeration by using envally taaring grareng season.
referenced information free county agricultural agents or other reliable sources,
- c. At datries listed in Item 5. -- c. Inquire as to feeding annually [maring grazing season.
practices:
w (1) Pasture only.
e (2) Feed and chop only.
(3) Pasture and feed; if both, ask farmer to estimate fraction of food from pasture:
<255,25-50E 50-755 or >151.
- 16. Nearest In all 16 sectors Annually Residence Census
TABLE 5.0-3 ,
ENVIR00sENTAL RADIOLOGICAL MONITORING PROGUM QUARTERLY 5tsecutY Name of Factifty Byron uwclear Power Statten Docket No. 50-454. 50-455 Location of Factifty Ogle I11tnois Reporting Period 1st Quarter 1987 (County. 5tatel Indicater Locatten with Highest Centrol Sample Type and Locations Quarterly Mean Locations Numer of Type Number of Meena Rean Meena gon.reuttne (Units) Analyses LLD Range Location Range Range Aesults Af r particulates Gross Beta 156 0.01 0.028 (117/117) By-02, 5tt11 men Valley 0.029 (13/13) 0.028 (39/39) 0 (pCf/mJ ) (0.005-0.049) 6.2 at # 56' (0.014-0.050) (0.007-0.050)
Gamme Spec. 12 0.01 <LLD <LLD 0 Sr-89 12 0.01 <LLD - -
<LLD 0 Sr-90 12 0.01 4LD - - <LLD 0 Afrborne ledine 1-131 156 0.07 <LLD - -
<LLD 0 (pC1/m3 )
co O
Gemme Background Gemme Dose 12 3.0 14.5 (9/9) By-22, Onsite 17.6 (1/1) 13.2 (3/3) 0 (TLDs) (udt/Otr.) (11.9-17.6) 0.3 mi e 101* -
(13.2-14.0) <
Milk 1-131 12 0.5 <tLD - -
<LLD 0 fpCf/1)
Games Spec. 12 Cs-134 5.0 <tLD - -
<LLS O Cs-137 5.0 <LLD - -
<LLD 0 Other Gammes 10.0 <LLD - - <LLD 0
$r-89 12 10 <LLD - - <LLD 0 Sr-90 12 2 2.6 (9/9) By-16. Drufen Defry 3.2 (3/3) 2.7 (3/3) 0 (1.6-3.8) Farm, 3.3 of 9 134* (2.5-3.8) (2.0-3.7)
Precfpftation Gross Beta 10 12.26 4LD - -
<tLD 0 Gamme spec. 4 20 <LLD - -
<LLD 0 Trftfue 4 200 <LLD - -
<LLD 0 Sr-89 4 10 <LLD - -
<LLD 0 3r-90 4 2 4LD -
<LLD 0
TABLE 5.0-3 (continued)
ENVIR0est[uTAL RADIOLOGICAL PIONITORING PROGRMI QUARTERLY 5tsetARf me.e of rectitty syron m ci.ar r ec Statt n Docaet me. s0-4s4. so-4ss Location of rect 11ty Ogle, I111 mots Reporting Perted 1st Quarter 1987 Wounty. statel I Indicator Location with Highest Centrol 5 ample Type and Locations Quarterly steen Locations w of Type Number of Meena Rean pleana aten-routine (Units) Analyses LLD Range Location Range Range Rosmits cooltag Water Gross Beta 26 1.0 10.0 (13/13) By-11. Discharp 10.0 (13/13) 2.5 (12/13) 0 (pCf/1) (1.6-37.2) 2.3 at 9 283 (1.6-37.2) (1.7-3.9)
Gamma spec. 6 Cs-134 10 4LD - - ALD 0 Cs-137 10 4LD - - <LLD 0 Other Gammes 20 ALD - - <tLD 0 m
s-.
Tritfum 6 200 2130 (3/3) Dy-11. Discharp 2130 (3/3) <LLD 0 (1250-2910) 2.3 et # 283 (1250-2910)
Sr-89 6 10 ALD - - 4LD 0 Sr-90 6 2 4LD - - <tLD 0 Surface Water Gross Beta 39 1.5 2.4 (17/26) By-13. Upstream of 2.8 (8/13) 2.8 (8/13) 0 (pCf/1) (1.4-3.9) Intake (1.9-4.0) (1.9-4.0) 2.6 of 9 302*
I Gamma spec. 9 Cs-134 10 4LD - - <tLD 0 Cs-137 10 (LD - - <tLD 0 Other Gammes 20 <LLD - - (LLD 0 Trittum 3 200 ALD - - <tLD 0 Sr-89 3 10 <LLD - - <LLD 0 Sr-90 3 2 (LD - -
<LLD 0 e
i TABLE 5.0-3 (continued)
ENVIRONMENTAL RADIOLOGICAL MONITORING PR0QUM QUARTERLY SutetARY Name of Facility Byron Nuclear Power Station Docket No. 50-454, 50-455 Location of Facility ogle, 111fnois Reporting Period 1st Quarter 1987 (county , statel Indicator Locatien vith Hfghest Centrol Sample Type and Locattens Quarterly Mean Locations Number of Type Number of Meena Nean Meena Non-routine (Units) Analyses LLD Ran9e Location Range Range Results Well Water Gross Beta 2 2.1 7.2 (1/2) Sy-18. McCoy Farmstead 7.2 (1/2) None 0 (pCf/1) - 1.0 of 9 235' -
Gassia Spec. 2 Cs-134 10 <tLD - - None O Cs-137 10 <LLD - -
None 0 Other Gesumas 20 <LLD - -
None 0 Trftfum 2 200 <LLD - -
None 0 Sr-89 2 10 (LLD - -
None O Cattlefeed & Grass Gross Beta 10 1.0 10.9 (7/7) By-20. Reeverts Dalry 16.9 (2/2) 7.4 (3/3) 0 (pCf/g wet) (3.0-29.9) 3.2 of 9 106* (3.9-29.9) (2.6-16.0)
Gesuma Spec. 10 Cs-134 0.1 <LLD - -
<tLD 0 Cs-137 0.1 <LLD - -
<LLD 0 Ot>er Gammas 0.2 <tLD - -
<LLD 0 Sr-89 10 1.0 <LLD - -
<tLD 0 Sr-90 10 1.0 <tLD - -
<LLD 0
- Mean and range based on detectable measurements only. Fraction indicated in parenthesis.
LLD value dependent on volume of sample available for analysis.
+
TABLE 5.0-4 ENVIROISIENTAL RADIOLOGICAL MONITORING PROGUM QUARTERLY 58A91ARY Mame of Factif ty Syron Nuclear Power Station Docket No. 50-454, 50-455 Location of Factitty Ogle, Illinois Reporting Period 2nd Quarter 1987 (Lounty. 5 tate) 1 Indicator Location with Hfghest Control Sample Type and Locattens Quarterly Mean Locations Iluminer of Type Number of Meena Reen Meena Ilan-routine i
(Units) Analyses LLD 2ange Location Range Range Results Gross Beta 156 0.01 0.024 (117/117) Sy-22. Onstte 0.026 (13/13) 0.023 (39/39) 0 Afr Particulates (0.010-0.038) (0.006-0.047)
(pCf/M) (0.006-0.049) 0.3 et 9 101*
Gmune Spec 12 0.01 (LD - - <tLD 0 Sr-89 12 0.01 4LD - - <tLD 0 CD Sr-90 12 0.01 4LD - - <tLD 0 w
Afrborne Iodine 1-131 156 0.07 4LD - - <tLD 0 (pCf/m3 )
Gamma Eack9round Gamma Dose 3.0 15.2 (9/9) By-22. hstte. 0.3 13.1 (1/1) 14.3 (3/3) 0 (TLDs) (mR/Qtr.) (11.3-18.1) of 9 101* - (12.5-15.7)
NUk I-131 ZU U.5 RLD - - <LLD G l
(PCf/1)
Gamma spec. 20 Cs-134 5.0 (LD - - <tLD 0 Cs-137 5.0 (LD - - ALD 0 Other Gennes 10.0 (LD - - <LLD 0 i
Sr-89 10 4LD - - 4LD 0 Sr-90 2 2.7 (15/15) By-16 Druf en Def ry 2.8 (5/5) 2.7 (5/5) 0 (1.6-3.9) Farm, 3.3 et 9 134' (2.4-3.2) (2.0-3.9)
A k
TABLE 5.0-4 (continued)
ENVIROWENTAL RADIOLOGICAL MONITORING PROGRAM QUARTERLY Stp0MRY Nome of Facility Syron Nuclear power Statten Docket No. 50-454. 50-455
) Reporting Perfed 2nd ()earter 1987 Location of Factitty Ogle.111tnet s (Ecunty, statel 4
Indicator Location with Highest Centrol Type and Locations Quarterly Mean Locattens hunter of Semple -
pean Meena Non-routine Type Number of Meena Analyses LLD Range Location Range Range Aesults (Units) 1.4 3.2 (25/26) Sy-12. Oregen Peel 3.3 (13/13) 3.2 (13/13) 0 Surface Water Gross Sets 39 (pCf/1) (1.5-4.8) of Rock River (2.5-4.1) (2.2-4.3) 4.5 at 9 213*
Genne spec. 9 4LD - - 4LD 0 Cs-134 10 (LD - - 4LD 0 g Cs-137 10 15 (LD - - 4LD 0 Other Gennes 3 200 ALD - - 4LD 0 Tr1 tium Sr-89 3 10 (LD - - ALD 0 Sr-90 3 2 (LD - - 4LD 0 Well Water Gross Beta 2 2.1 6.4 (1/2) By-18. McCoy 6.4 (1/1) None 'O (pCf/11 - Fernstead Well 1.0 et 0 235*
Gamma Spec. 2
' Cs-134 10 4LD - - mene 0 1
Cs-137 10 ALD - - None 0 Other Gaunes 20 4LD - - None 0 Tritium 2 200 (LD - - None 0
$r-89 2 10 4LD - - mene 0 Sr-90 2 2 (LD - - mene 0 e
. O o
TABLE 5.0-4 (continued)
ENVIR01stENTAL RADIOLOGICAL MONITORING PROGUM QUARTERLY sipeenRY Name of Factitty Byron mucteer Power Statten Docket me. 50-454, 50-455 Location of Fact 11ty Ogle.1111nois Reporting perfed 2nd Quarter 1987 Lcounty, state)
Indicator Locatten with Nighest Centrol Type and Locations Quarterly IIeen Locattees number of Sanple pg,,,a gg,, ,,,gg,,
pteena n,,,
Type Iluster ef Analyses Range Locatten Range Range Results (Units) LLD By-17. Whitten 38.0 (2/3) 38.0 (2/3) 0 Procf pitation Gross Beta 12 12.8C 27.3 (7/9)
(7.1-58.8) Molstefas (12.8-63.2) (12.8-63.2) 7 et 9 53' Gemme Spec. 4 20 ALD - - <LLD 0 4LD 0 Tritfue 4 200 (LD - -
- Sr-89 4 10 ALD - - 4LD 0 ui Sr-90 4 2 (LD - - 4LD 0 1.0 12.6 (13/13) 12.6 (13/13) 3.2 (13/13) 0 Cooling Weter Gross Beta 26 Sy-11. Discherp (pCf/11 (4.5-59.7) 2.3 el 8 283 (4.6-59.7) (2.1-4.31 Gamme Spec. 6 Cs-134 10 ALD - - 4LD 0 Cs-137 10 4LD - - 4LD 0 Other Genees 20 4LD - - 4LD 0 Tritten 6 200 11.240 (3/3) Sy-11. Dischery 11.240 (3/3) (LD 1 (562-23.130) 2.3 et 8 283 (562-23.130) sr-89 6 10 <LLD - - 4LD 0 Sr-90 6 2 4LD - - 4LD 0
. TABLE 5.0-4 (continued)
ENVIR0eseEllTAL RA010 LOGICAL 840 NIT 0RtuG Pn0 Gun QUARTERLY SipetARY Name of Factitty Syren leucteer Peuer Stetten Decket Ilo. 50-454, 50-455 Locetton of Fact 11ty Ogle,111tnet s Reporting Perted 2nd Quarter 1987 (county, 5tetel Indicator Lecetten with Highest. Centrol Type and Lecettens Quarterly 8 teen Lacettens leseber of Sample gg,,ne Hunter of 80eena yg,,, leon-routine Type Results Range Lacetten Range Range (Units) Analyses LLD 5 1.0 3.1 (2/2) By-12, Oregon Peel of 3.1 (2/2) 3.0 (3/3) 0 Fish Cross Sete (pct /g met) (3.0-3.2) Rect River (3.0-3.21 (2.9-3.2) 1 1
4.5 mi 9 213*
Gessee Spec. 5 0.1 4LD - - ALD 0 Cs-134 0.1 4LD - - 4LD 0 Cs-137 co 4LD 0
- Other Gemmes 0.13 (LD - -
1.0 (LD - ALD 0 Sr-89 5 -
t 1.0 (LD - 4LD 0
$r-90 5 -
I Cattlefeed & Grass Gross Sete 4 1.0 6.1 (3/3) By-20 E. Seebeld 7.0 (1/1) 4.0 (1/1) 0 (pCf/g uset) (5.4-7.0) Defry Farm - -
2.5 et 0 41' Gemme Spec. 4 Cs-134 0.1 4LD - - 4LD 0 Cs-137 0.1 4LD - - 4LD 0 Other Gastses 0.2 4LD - - <LLD 0 Sr-89 4 1.0 4LD - - <tLD 0 Sr-90 4 1.0 4LD - - 4LD 0 G
e
TABLE 5.0-4 (continued)
ENVIR0letENTAL RADIOLOGICAL MONITORING PROGRAM QuaRTEdLY 5trouRY Nome of Factitty Byron Nuclear Power Station Docket No. 50-454, 50 a55 Location sf Facility Ogle, 111tnets Reporting Perted 2nd Quarter 1987 (Leenty. State)
Indicator Locatten with Nighest Centrol Sample Type and Lacettens Quarterly Mean Lecettens Num6er of Type Number of Meena Meen Meena Non-reetine Analyses Range Location Range Range Results (Units) LLD A p tte vegetatten Gross Seta 2 1.0 4.5 (1/1) Sy-12. Oregon Peel 4.5 (1/1) 4.3 (1/1) 0 (pCf/g wet) - of Rock River - -
4.5 mi e 213*
Gemma spec. 2 Cs-134 0.1 4LD - - ALD 0 0.1 <LLD 0
$ 4LD - -
Cs-137 Other Gemmes 0.2 4LD - - 4LD 0 Gross Beta 2 1.0 23.7 (1/1) Sy-12. Oregon Pool 23.7 (1/1) 16.6 (1.1) 0 Sottom Sedfaents (pC1/g dry) - of Rock afver - -
4.5 et 9 213*
Gamma spec. 2 Cs-134 0.1 4LD - - 4LD 0 Cs-137 0.1 1.3 (1/1) Sy-12. Oregen Pool 1.3 (1/1) 0.2 (1/11 0 of Rock River 4.5 et 9 213* ,
Othea Gemmes 0.2 (LD - - 4LD 0
- Mean and range based en detectable measurements only. Fractions indicated in perentheses.
teveneer - April LLD = 1.0; May October LLD = 0.5 pCf/1.
, LLD value dependent en volume of semple available for enelysts.
TABLE 5.0-5 ENVIR01stDITAL RADIOLOGICAL MONITOR 1tG P90ERAM QUARTERLY 5LsetARY Mame of Factif ty Byron Nucleer power Station Decket No. 50-454. 50-455 Location of Fact 11ty Ogle. 111tnets Reporting Perted 3rd Quarter 1987 (County. 5 tate)
Indicator Locatten with Nf9 hest Centrol Sample Type and Locattens Quarterly Mean Locattens W of Type Ilumber of Meena noen steens hen-reettne (Units) Analyses LLD Ran9e Location Ran9e Range Reamits Air Particulates Gross Beta 156 0.01 0.027 (117/117) Sy-24. Onstte 0.65 0.030 (13/13) 0.027 (39/39) 0 3
(PCf/m ) (0.010-0.043) of 9 229* (0.022-0.043) (0.011-0.041)
Gamma Spec. 12 0.01 (LD - - <LLD 0 Sr-89 12 0.01 4LD - - <LLD 0 3r-90 12 0.01 4LD - - ALD 0 Airborne lodine 1-131 156 0.07 <LLD - - <tLD 0 (pCf/m3)
Gamma Back9round Gamma Dose 12 3.0 15.3 (9/9) Sy-22, Onstte 19.3 (1/1) 14.7 (3/3) 0 00 (TLos) (sst/0tr.) (11.9-19.3) 0.3 el 9 101* -
(13.2-16.7) g Milk 1-131 24 0.5 4LD - - 4LD 0 (pCf/1)
Gassna spec. 24 Cs-134 5.0 <LLD - -
<LLD 0 Cs-137 5.0 <LLD - - 4LD 0 Other Gammes 10.0 4LD - - ALD 0 Sr-89 24 10 <LLD - - ALD 0
$r-90 24 2 2.6 (18/18) By-15. Reeverts Def ry 2.7 (6/6) 2.2 (6/6) 0 (2.1-3.4) Farm. 3.2 el 9 108* (2.3-3.4) (1.8-2.8)
Precipitation Gross beta 11 12.3b 35.0 (3/8) By-20, Seebeld Fare 77.6 (1/2) (LD 0 (6.2-77.6) 2.5 et 9 134* - -
Ganna spec. 4 20 <LLD - -
ALD 0 Trftfue 4 200 223 (1/4) By-16 Kenneth Druf en 223 (1/4) ALD 0 (223) Farm, 3.3 et 9 134' (223)
Er-89 4 10 4LD - -
<LLO O Sr-90 4 2 <LLD - -
ALD 0 6
TABLE 5.0-5 (continued)
ENVIRouMENTAL RADIOLOGICAL MONITORING PA0GU9t QUARTERLY Sif91ARY m.m. of rectitty syren mucieer re-er Station Decket me. s0-454. So-4ss Location of rectitty Ogle, Illinets Reporting Period 3rd Quarter 1987 10eunty, 5tatel Indicater Locatten with Highest Centrol Type and Locattens Quarterly Mean Locattens number of Sample gg,,,,,,gg ,
Meena Reen Meena Type humber of Analyses Range Lacetten Range Range Results (Units) LLD 2.3 9.2 (13/13) By-11. Discherpe 9.2 (13/13) 4.3 (12/13) 0 Cooling Water Gross Dete 26 (pC1/1) (5.3-15.11 at Station (5.3-15.11 (2.3-7.2)
Genne Spec. 6 10 4LD - - 4LD 0 Cs-134 10 (LD - - 4LD 0 Cs-137 4LD #
Co-58 10 4LD - -
Other Geeses 20 ALD - - 4LD 0 to 41,906 (3/3) 4LD "o Tritf ue 6 200 41,906 (3/3) By-11. Discharge 1 (202-115.112) at Station (202-115.112)
Sr-89 6 10 <LLD - - 4LD 0 Sr-90 6 2 4LD - - 4LD 0 sueface Water Gross Deta 39 1.7 3.0 (26/26) Sy-12. Downstroom of 3.4 (13/13) 3.1 (12/13) 0 (PCf/1) (1.4-5.3) Oregon Dee (2.3-5.31 (2.1-4.7) 4.6 et 9 213' Genes spec. 9 Cs-134 10 4LD - - <LLO O Cs-137 10 ALD - - <LLD 0 Other Gaunes 20 C LD - - <LLD 0 Trftium 3 200 279 (1/;) By-12. Downstream of 279 (1/1) (LD 0
- Oregen Dee -
4.6 et 9 213*
Sr-89 3 10 4LD - - ALD 0 Sr-90 3 2 4LD - - <tLD 0 d
TABLE 5.0-5 (continued)
ENVIRONMENTAL RADIOLC4? CAL eich!TORING pn0 gust GunnTERLY stpowtv me Of rectitty syren m.cieer pe ee stetten Decket see. 50-454, 50 ass j Lecetton of Fact 11ty Ogle 111tnets Reporting perted 3rd Quarter 1987 40eunty 5tatel Indicator Lecetten with Highest Centrol Sample Type and Lacettons Quarterly Mean Lecettens thumber of Type slumsber of Means n,,, n,,,e g,,,,,,gge. l 2esults (Units) Analyses LLD Range Lacetten Itenge Range l
Well Water Gross Sete 2 2.4 6.4 (1/2) Sy-18. McCoy Fernsteed 6.4 (1/1) Isene 0
-(pC1/11 - 1.25 of e 23s* -
Gemme spec. 2 Cs-134 10 (LD - - mene O Cs-137 10 4LD - - mene 0 Other Gennes 20 ALD - - stone 0 Tritfun 2 200 4LD - - None 0 l Sr-89 2 10 4LD - - scene 0 O Sr-90 2 2 ALD - - None 0 Fish Gross sete 5 1.0 2.2 (2/2) By-12. Oregon pool 2.2 (2/2) . 1.8 (3/3) 0 (pCf/s wet) (2.2-2.2) f ,g gr. (2.2-2.23 (1.4-2.2)
Gemme spec. 5 Cs-134 0.10 ALD - - 4LD 0 Cs-137 0.10 ALD - - 4LD 0 Other Gemmes 0.13 4LD - - 4LD 0 sr-89 5 0.1 4LD - - 4LD 0 sr-90 5 0.1 (LD - - ALD 0 Cattlefeed 8 Grass Gross Sete 4 1.0 7.5 (3/3) Dy-20. Seebeld raru 8.6 (1/1) 7.2 (1/1) 0 (pCf/g met) (6.0-8.6) 2.5 mi e 41* - -
Gemme Spec. 4 Cs-134 0.1 ALD - - ALD 0 Cs-137 0.1 4LD - - 4LD 0 Other Gennes 0.2 (LP - - 4LD 0 Sr-89 4 1.0 ALD - - 4LD 0
$r-90 4 1.0 (LD - - <LLD 0
~
O TABLE 5.0-5 (continued)
ENVIRONMENTAL RADIOLOGICAL 840NITORING PROGUM QUMtTERLY 5tpetutf syren muciear re ec station Decket no. 50-454, 50-4ss me of Factitty Location of Factitty Ogle, 1111aels Reporting perted 3rd Quarter 1987 Keunty, statel Indicator Locatten with Highest Centro 1 Quarterly Mean Locations mueer of sample Type and Locations steena Non-routine Meena Reen Type Nuder of Locattog Range Range Results Analyses LLD Range (Units)
Dy-12. Oregon pool of 3.9 (1/1) 2.0 (1/1) 0 A w tic vegetatten Gross Beta 2 1.0 3.9 (1/1) -
(pCf/g wet) - Rock Rfeer -
4.6 of 9 213' Gmune spec. 2
- - <LLD 0 Cs-134 0.1 (LD
- <tLD 0 Cs-137 0.1 4LD -
- <tLD 0 Other Gammes 0.2 <LLD -
By-13. Upstream of 9.2 (1/1) 9.2 (1/1) 0 Bottee sediments Gross Beta 2 1.0 5.0 (1/1?
e Oregon Dam 5 -
- fpCf/g dry) 4.3 et 9 213' Gamma spec. 2 4LD 0 Cs-134 0.1 4LD - -
- .LD 0 Cs-137 0.1 4LD -
- (LLD 0 l Other Gammes 0.2 (LD -
By-19-1. 966 East 3.2 (4/4) home 0 i Wegetables Gross Beta 8 1.0 2.9 (8/8)
(1.5-s.0) Weld Sart Asad (1.7-5.0)
Gamma Spec. 8 none O Cs-134 0.1 4LD - -
- mene 0 l Cs-137 0.1 <tLD -
- None 0 Other Gammes 0.2 (LD -
- hene 0 Sr-89 8 0.1 <LLD -
- None 0 sr-90 8 0.1 4LD -
- None 0 1-131 1 0.06 <LLD -
4
- Mean and range based os detectable measurements only. Fractfens indicated in parentheses.
LLD value dependent on volume if sample available for analysts.
J
TABLE 5.0-6 ENVIR0is4 ENTAL RADIOLOGICAL MONITORING M 0 GRAM QUARTERLY 5tstuRY Name of Factitty Dyron Nuclear Poner Station Docket No. 50-454. 50-455 Location of Factitty Ogle 1111refs Reporting Perted 4th Quarter 1967 (County. 5tatel Indicater Location with Highest Centrol sample Type and Locattens Quarterly Mean Locations atumber of Type Number of 90eana Reen lesens Non-routine (Unfts) Analyses LLD Range I.ecation Range Range Results AfrPart{culates Gross Beta 156 0.01 0.028 (117/117) Sy-02, 5tt11 man Valley 0.031 (12/13) 0.029 (30/39) 0 (pC1/r) (0.000-0.049) 6.2 et 8 56* (0.013-0.048) (0.012-0.048)
Gasma Spec. 12 0.01 (LD - - <LLD 0 Sr-89 12 0.01 ALD - -
<tLD 0 3r-90 12 0.01 ALD - -
4LD 0 Afrborne ledfne I-131 156 0.07 <tLD - -
<LLD 0 (pCf/m3)
Gauna sackground Gauna Dose 12 3.0 16.9 (9/9) Dy-22. Onstte 0.3 19.4 (1/1) 16.5 (3/J) 0 (TLDs) (udt/Qtr.) (13.5-19.4) of e 101* -
(15.2-17.6)
Milk I-131 16 0.5 4LD - - (LD 0 (pCf/1)
Gauna Spec. 16 Cs-134 5.0 4LD l - -
<tLD 0 Cs-137 5.0 ALD - -
4LC 0 Other Gammas 10.0 4LD - -
<LLD 0 Sr-89 16 10 4LD - -
4LD 0 Sr-90 16 2 2.4 (12/12) Dy-16. Drufen Defry 2.8 (4/4) 2.4 (4/4) 0 (1.8-3.8) Farm. 3.3 et 9 134' (1.9-3.8) (2.1-2.6) precfpftation Gross Beta 12 12.9b 4LD - -
<LLD 0 Gauna Spec. 4 20 <LLD - -
4LD 0 Tritium 4 200 <LLD - -
4LD 0 Sr-89 4 10 <LLD - -
4LD 0 Sr-90 4 2 4LD - -
<LLD 0 e
TABLE 5.0-6 (continued)
EmVIROWIDITAL RADIOLOGICAL MoulTORinG PROGRmt QUARTERLY SIpetutY meme of rectitty syren m.ciear peser Station Docket me. 50-454, so-4ss Location of rectitty Ogle, 111tnets Reporting Period 4th Quarter 1987 (0.ownty, statel Indicator Location with mighest Centrol Locations Quarterly Hean Locations w of Sample Type and g,..,,,g g ,
Meena noen Meana Type number of Range mesmits Analyses LLD Range Location Range (Units) 8.7 (13/13) 3.4 (13/13) 0 cooling Water Gress Beta 26 1.6 8.7 (13/13) By-11.Discharp (pC1/1) (4.4 19.4) 2.3 mi 9 283 (4.4-19.4) (2.4-5.4)
Gamma spec. 6 4LD - - <tLD 0 Cs-134 10 Cs-137 10 4LD - - ALD 0 20 ALD - - 4LD 0 Other Gammas Trf tf ue 6 200 170,140 (3/3) By-11.Discherp 170.140 (3/3) 4LD 1
$ (148-499.642) 2.3 el 9 283 (148-499.642) 6 10 <LLD - - <LLD 0 Sr-89
- 4LD e
$r-90 6 2 <LLD -
Gross Beta 37 1.7 2.6 (22/24) Sy-12. Deenstream 3.2 (13/13) 2.5 (13/13) 0 Sus "ace Water
( Cf/1) (1.4-3.9) of Oregon Dam (2.6-3.9) (1.5-4.1) 4.6 et 0 213*
Gamma Spec. 9 Cs-134 10 443 - - 4LD 0 Cs-127 10 <LLD - - <LLD 0 Other Gennes 20 (LLD - - ALD 0 Tritfue 3 200 4LD By-12. Donostream 267 (1/1) 267 (1/1) 0 of Ore 9en Dam 4.6 at 9 213*
Sr-89 3 10 <tLD - - 4LD 0 sr-90 3 2 4LD - - <LLD 0 s
1 i
TABLE 5.0-6 (continued)
ENVIROWIENTAL RADIOLOGICAL MONITORING pA0GIUWf QMRTERLY SIMWtY m e of rectif ty syren misc 1oor re er Station Decket me. 50-4s4, 50-4ss Location of rectif ty Ogle, I111aefs Reporting perted 4th quarter 1987 t
(county, State)
Indicator Locatten with Mfghest Centrol Sample Type and Locattens Qiserterly Mean Locattens W of Type Mr of Meena pee , nonna Iden-routine (Units) Analyses LLD Range Locatten Range Range Results ve11 water Gross seta 2 2.4 10.0 (1/2) sy-le, McCey Famstead 10.0 (1/1) mene 0 (pCf/1) - 1.0 of e 235* -
Gamune Spec. 2 Cs-134 10 4LD - - Mene O Cs-137 10 4LD - - Isene 0 Other Gemmes 20 ALD - - Isone 0 Trftfun 2 200 (LD - - 16ene 0 g Sr-89 2 10 4LD - - None 0
$r-90 2 2 4LD - - None O Cattlefeed a Gross Gross seta 4 1.0 8.1 (3/3) By-1s. Reeverts Defry 12.6 (1/1) 9.9 (1/1) 0 (pCf/g wet) (4.5-12.6) Form. 3.2 el 9 108' - -
Gauna Spec. 4 Cs-134 0.1 (LD - - <tLD 0 Cs-137 0.1 4LD - - 4LD 0 Other Gemmes 0.2 (LD - -
<LLD 0 Sr-89 4 1.0 ALD - - <LLD 0 Sr-90 4 1.U 4LD - - <LLD 0
O TABLE 5.0-6 (continued)
ENVIROIMENTAL RADIOLOGICAL MONITORING PROGAmt QUARTERLY SlpMARY 4
Nome of Fact 11ty Byron Nuclear peuer Statten Do.ket No. 50-454, 50-455 Location of Facility Ogle, Illinet s Reporting perfed 4th Quarter IW,7 fcounty, statel 1
Indicater Lecetten with Highest Centrol
' Sample Type and Locattens Quarterly Mean Locattens Iluster of neon Heena g,,,,,,gg ,
Type Number of Meena Analyses Range Location Range Range Assults (Units) LLO 1.0 4.1 (1/1) By-13, upstream of 5.3 (1/1) 5.3 (1/1) 0 4 A p tic vegetation Gross Beta 2 1 (pC1/g met) - Intake. - -
2.6 at # 302*
Gamma Spec. 2 0.1 4LD - - <tLD 0 Cs-134 0.1 4LD - - <tLD 0
, Cs-137 0.2 <tLD - - 4LD 0 Other Gemmes Setten Sedfsents Gross 6ete 2 1.0 5.4 (1/1) By-13 Upstrfram of 6.9 (1/1) 6.9 (1/1) 0 (pCf/g dry) - Intake - -
2.6 et 9 302*
Gamune Spec. Z l
0.1 (LD - - <tLD 0 Cs-134 0.1 (LD - - 4LD 0 Cs-137 0.2 ALD - - ALD 0 j Other Gammes ,
j
- Mean and range based on detectable messerements only. Fractions indicated in parentheses.
LLD value dependent on volume of sample evellable for anslysts.
I 2
1 P
4 e -
e
Table 5.1-1 GAMMA RADIATION, AS MEASURED BY THERM 0LUMINESENT 00SIMETERS (TLDs)
STANDARD RADIOLOGICAL MONITORING PROGRAM 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 12-29-86 03-30-87 06-30-87 09-28-87 Date Removed: 03-30-87 06-30-87 09-28-87 12-28-87 Days in the Field: 91 92 90 91 Location Average mR/Qtr.
Offsite Indicator Locations BY-01 Byron 11.910.7 11.3i0.7 12.810.8 14.lt0.4 BY Nearsite East 14.310.8 15.711.4 14.910.9 16.110.4 BY Paynes Point 14.110.7 16.0t0.8 15.Di0.8 17.710.3 BY Nearsite South 16.410.8 17.5i0.8 17.111.2 19.311.2 BY Oregon 12.310.7 13.010.9 13.3tl.0 15.110.4 Mean i s.d. 13.8tl.8 14.712.5 14.6tl.7 16.512.1 Onsite Indicator locations BY Onsite North 11.210.7 11.410.9 11.9i0.8 13.610.5 BY Onsite ESE 17.6fl.0 18.110.7 19.311.7 19.410.4 BY Onsite South 16.3tl.3 16.710.9 17.lil.3 18.810.3 BY Met. Tower 16.111.2 16.8tl.0 16.4tl.4 18.210.6 Mean i s.d. 15.3i2.7 15.at3.0 16.2i3.1 17.Si2.6 Background Locations BY Stillman Valley 13.210.9 12.5i0.8 13.210.9 15.210.6 BY Mt. Morris 14.010.8 15.710.8 16.7tl.6 17.610.7 BY Leaf River 13.310.8 la.7*1.1 14.211.1 16.7f0.7 Mean i s.d. 13.510.4 14.311.6 14.7tl.8 16.511.2 )
96
-,.--,,-__m- , ., , - , - . - - . - . . _ _ _ , _ , , , . - - __
O Table 5.1-1 (continued)
GAMMA RADIATION, AS MEASURED BY TLDs (continued)
SPECIAL PROGRAM Inner Ring, Near Site Boundary, Indicator Locations 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 12-29-86 03-30-87 06-30-87 09-28-87 Date Removed: 03-30-87 06-30-87 09-28-87 12-28-87 Days in the Field: 91 92 90 91 Location Average mR/Qtr.
BY-101-1 16.9tl.4 19.412.3 17.Sil.5 19.811.2 BY-101-2 16.lt0.9 16.210.7 18.3i1.0 18.0i0.4 BY-102-1 16.6tl.4 18.611.1 18.211.2 19.610.5 BY-102-2 16.211.1 16.011.3 18.7tl.0 17.0tl.1 BY-103-1 15.910.8 16.6t0.7 16.8t0.9 19.7tl.2 BY-103-2 15.6tl.4 15.710.9 16.7*1.0 17.7i0.2 BY-104-1 16.410.8 17.211.0 17.510.8 18.411.1 BY-104-2 16.910.9 16.110.8 17.8*1.0 18.4i0.4 BY-105-1 16.510.8 17.510.7 18.011.2 18.7i0.7 BY-105-2 16.110.8 16.410.7 18.611.2 19.0i0.5 BY-106-1 16.110.8 16.310.8 17.311.1 17.510.7 BY-106-2 15.110.9 15.210.8 17.311.7 16.811.1 BY-107-1 16.6i0.8 17.7tl.2 17.0f0.9 19.0f0.7 BY-107-2 17.0i0.9 17.li0.8 18.810.9 20.311.5 BY-108-1 16.510.3 17.910.7 17.8tl.0 18.710.6 BY-108-2 14.1*0.7 14.810.9 15.210.8 16.5t0.6 BY-109-1 14.910.7 15.710.8 15.510.8 18.0il.0 BY-109-2 15. 9tl . 3 14.010.8 16.811.6 16.110.9 BY-110-1 14. 9tl .1 15.410.8 15.3i0.8 17.Bi0.7 BY-110-2 15.210.9 13.810.9 16.310.9 15.910.6 BY-111-1 15.7t0.8 16.710.8 17.211.2 17.710.5 BY-111-2 16.010.8 15.810.8 17.511.0 17.0i0.7 BY-112-1 15.010.8 15.6t0.7 16.310.9 17.7tl.1 BY-112-2 14.811.0 13.6i0.8 16.5tl.5 15.6t0.6 BY-113-1 14.6t0.7 15.410.7 16.0i0.8 17.4i0.6 BY-113-2 13.Di0.7 12.7tl.0 17.1*1.6 14.8i0.5 BY-114-1 12.6i0.7 13.210.8 13.310.8 16.0il.0 BY-114-2 14.810.9 13.6f0.7 16.210.9 15.910.6 BY-115-1 14.510.8 15.110.9 15.810.8 17.010.6 BY-115-2 14.110.9 14.211.1 15.420.9 16.310.5 BY-116-1 13.Di0.7 13.510.8 14.0i0.9 15.510.7 BY-116-2 13.811.1 13.411.0 15.2iO.8 16.711.1 Mean i s.d. 15.411.2 15.611.7 16.7tl.4 17.5*1.4 97
Table 5.1-1 (continued)
GAMMA RADIATION, AS MEASURED BY TLDs (continued)
SPECIAL PROGRAM Outer Ring, Near 5 Hile Radius, Indicator Locations 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed: 12-29-86 03-30-87 06-30-87 09-28-87 Date Removed: 03-30-87 06-30-87 09-28-87 12-28-87 Days in the Field: 91 92 90 91 Location Average mR/Qtr.
BY-201-1 14.410.8 15.810.9 15.510.8 17.410.4 BY-201-2 17.110.9 15.810.8 18.410.8 17.310.9 BY-202-1 14.3f0.8 15.110.8 17.2tl.6 16. 9t0. 3 BY-202-2 15.7tl.0 15.610.9 17.410.9 17.6i0.6 BY-203-1 11.910.8 11.410.7 12.410.9 14.010.4 BY-203-2 15.010.8 14.7tl.2 16.2i0.9 16.6t0.5 BY-204-1 12.9t0.9 13.010.7 13.6t0.8 15.li0.4 BY-204-2 16.810.9 16.310.7 18.6t0.9 18.510.5 BY-205-1 17.0i0.8 16.Dio.8 18.4tl.4 17.110.3 BY-205-2 15.5i0.8 14.910.7 17.211.0 16.St0.7 BY-206-1 16.6i0.8 16.310.9 17.910.8 17.910.9
, BY-206-2 16.410.8 15.910.7 18.010.8 17.7t0.2 BY-207-1 17.010.9 17.0t0.8 19.011.6 19.0i0.4 BY-207-2 16.110.8 15.210.7 17.6*1.1 17.410.2 l
BY-208-1 17.811.0 17.4t0.7 19.110.9 19.0t0.7 BY-208-2 17.210.9 17.0tl.0 18.410.8 19.911.0 BY-209-1 16.0iO.8 16.610.8 17.710.8 18.710.8 BY-209-2 14.310.8 13.9i0.7 16.4fl.6 16.210.3 4
BY-210-1 16.711.1 15.910.7 17.510.8 18.3i1.0 BY-210-2 15.810.8 15.5i0.8 17.0t0.9 17.710.4 BY-211-1 15.510.8 14.5i0.8 16.410.9 16.3t0.6 BY-211-2 17.2i0.9 16.610.7 19.711.5 18.6i0.7 BY-212-1 16.5i0.9 16.310.8 21.110.8 18.510.9 BY-212-2 17.7tl.1 17.410.8 18.410.9 19.0t0.5 BY-213-1 16.510.9 14.910.8 19.8tl.4 16.6i0.3 BY-213-2 16.810.8 17.510.9 19.610.9 18.910.4 BY-214-1 15.510.8 15.2tl.2 17.5i0.8 15.810.7 BY-214-2 16.2i0.9 15.810.8 17,910.8 17.9i0.9 BY-215-1 16.711.0 16.310.9 19.811.1 18.0t0.5 BY-215-2 16.410.8 16.110.7 18.2il.1 18.210.6 BY-216-1 17.810.9 15.9i0.7 20.711.0 17.5i0.9 f BY-216-2 16.8tl.0 17.210.8 18.7f0.8 18.9i0.6 Mean i s.d. 16.111.3 15.711.3 17.811.8 17.611.3 i
98
h 4
l l
l l
l
\
l APPENDIX 11 METEOROLOGICAL DATA I
P 99 t
- 1. .
l BYRON NUCLEAR POWER STATION i PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 250-30 FT) l WINDS MEASURED AT 250 FEET j WIND WIND SPEED (IN MPH) i DIRECTION .8-3 4- 7 8-12 13-18 19-24 OT 24 TOTAL i l _________ _____
N 0 0 0 0 0 0 0 j NNE O O O O O 2 2 ,
NE O O O O 2 1 3 ENE O O 2 3 0 0 13 E O O O O O O O ESE O O O O O O O ,
SE O O O O 2 0 2 i SSE O O O O O O O S O O O O O O O SSW 0 0 0 0 0 0 0 ,
SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W O O O O O O O 0 i WNW 0 0 0 0 0 0 NW 0 0 0 1 0 0 1 NNW 0 0 0 0 1 O i VARIABLE O O O O O O O TOTAL 0 0 2 4 13 3 22 Hours of calm in this stability classt 0 Hours of missing wind measurements in this stability classt 0 Hours of missing stability measurements in all stability classes: O l
l 100 l
. l
. .I i
i BYRON NUCLEAR POWER STATION #
PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET l WIND WIND SPEED (IN MPH)
DIRECTION .0-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O o 0 0 0 0 0 i NNE O O O O O 1 1 NE o 0 0 0 3 1 4 .
ENE O O 2 3 1 0 6 E O 1 2 0 1 2 6 i
ESE O O O 1 1 0 2 SE O O O 1 2 1 4 4
SSE O O O O O O O S 0 0 0 0 0 0 0 SSW O O O O O O O SW G 0 0 0 0 0 0 WsW O O O O O O O !
W 0 0 0 0 0 0 0 i
WNW 0 1 0 1 0 0 2 l NW 0 0 2 0 1 0 3 (
! NNW 0 0 0 1 1 0 2 l
- VARIABLE O O O O O O O I I
TOTAL 0 2 6 7 to 5 30 l 1
Hours of calm in this stability class 0 l Hours of missing wind measurements in this stability class 0 [
j H ors of missing stability measurements in a11 stability classes 0 J
I 101
[
4 BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 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 OT 24 TOTAL N O 1 0 0 0 0 1 NNE O 1 0 0 0 0 1 NE O O O 3 1 1 5 ENE O O 2 4 3 1 10 E O 1 2 1 1 1 6 ESE O O 1 3 1 1 6 SE O O 1 0 1 2 4 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 1 0 0 1 SW 0 0 0 1 0 0 1 WSW 0 0 0 0 1 0 1 W 0 0 0 3 0 0 3 WNW 0 0 2 2 0 0 4 NW 0 1 4 1 1 0 7 NNW O 4 1 2 0 0 7 VARIABLE O O O O O O O TOTAL 0 0 13 21 9 6 57 I
Hours of calm in this stability class O Hours of missing wind measurements in this stability class O Hours of missing stability measurements in all stability classest 0 ;
102 l
l
SYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 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 OT 24 TOTAL N 3 12 21 16 9 0 61 NNE 2 0 7 4 11 21 45 i
NE o 1 5 11 46' 13 76 !
ENE 1 3 13 51 54 9 131 -
E 1 6 16 18 10 10 61 ESE 3 9 9 15 8 9 53 ;
SE 2 9 5 7 17 9 49 SSE 1 10 2 12 3 4 32
$ 1 13 12 20 16 6 68 .
SSW 3 11 12 31 19 2 78 i
SW 3 12 17 20 0 1 61 ,
WSW 1 5 12 20 11 0 49 i
W 5 16 25 42 19 0 107 WNW 3 15 13 33 21 6 91 i NW 2 12 29 57 18 7 125 NNW 2 9 24 33 30 14 112 l VARIABLE O O O O O O O }
l TOTAL 33 143 222 390 300 111 1199 i
Hours of calm in this stability class 0 ;
Hours of missing wind measurements in this stability class 0 j Hours of missing stability measurements in all stability classest 0 ;
i i
i t 103 :
. i s
i BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 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 OT 24 TOTAL l N 1 2 4 6 1 0 14 NNE 1 6 9 10 1 0 27 NE O 5 5 5 3 0 18 l ENE 1 2 8 23 15 2 51 E O 1 2 13 28 27 71 ESE O O O 2 6 5 13 l
l SE 1 3 5 1 12 2 24 SSE O 2 3 6 5 2 18 S 0 2 7 12 11 5 37 j SSW 0 2 9 14 7 1 33 SW 1 2 9 24 12 2 50 WSW 2 3 9 20 6 2 42 '
W 2 2 to 17 5 2 38 WNW 1 4 10 10 4 0 29 '
1 1 NW 2 9 18 16 5 0 50 l l
NNW 1 5 6 16 2 0 30 I i
l VARIABLE o 0 0 0 0 0 0 1
1 i
TOTAL 13 50 114 195 123 50 545 l
[
t j Hours of calm in this stability classt 0 Hours of missing wind measurement s in this stability classt 0 i l 0 I I Hours of missing stability measurement s in all stability classest l
I f
r i
104 f
L
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - MODERATELY STABLE (DIFF-TEMP 250-CO FT)
.)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 2 5 0 0 0 7 NNE O 2 2 2 O O 6 NE 1 0 2 5 1 0 9 ENE 1 2 0 2 1 0 6 E 1 1 3 5 22 5 37 ESE O 1 3 5 12 3 24 SE O O 3 8 4 0 15 SSE 1 1 4 7 6 1 20 S O 1 1 3 9 1 15 SSW 0 4 3 5 6 0 18 SW 0 1 3 6 1 0 11 WSW 1 3 6 3 0 0 13 W O O 7 8 O O 15 WNW O 5 4 1 0 0 10 NW 0 3 8 1 2 0 14 NNW 2 3 1 O O O 6 VARIABLE O O O O O O O TOTAL 7 29 55 61 64 10 226
-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: 0 105
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET l
l WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL l _____ ____ _____ _____
N O O 2 O O O 2 l
NNE O O O O O O O NE O O 1 1 1 0 3 ENE O O 1 1 1 0 3 E O O O 3 3 1 7 ESE O O 1 5 6 0 12 SE O O 4 6 0 0 10 SSE O 1 3 4 0 0 8 S 1 O O O 1 0 2 SSW O 2 0 2 2 0 6 SW 1 1 2 4 0 0 0 9
WSW i 0 1 4 4 0 10 W O O O 3 0 0 3 WNW 1 O O 2 O O 3 NW O O 1 2 O O 3 NNW O O 1 O O O 1 VARIABLE O O O O O O O TOTAL 4 4 17 37 18 1 81 Hours of calm in this stability class: O Hours of missing wind measurements in this stability classt O Hours of missing stability measurements in all stability classes 0 106
._ 4 . . . _
l BYRON NUCl. EAR POWER STATION l PERIOD OF RECOR ) - APRIL-JUNE 1987 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 OT 24 TOTAL l
l l
N O O O 6 4 1 11 NNE O O 4 1 4 2 11 NE O O 2 1 O O 3 ENE O 1 5 6 0 0 12 E O O 4 0 0 0 4 ESE O O O O O O O SE O O O O O O O SSE O O 1 0 4 0 5 S O O O 1 1 0 2 SSW O O O O O O O SW O O O 4 1 2 7 WSW O O O O 4 1 5 W O O O O O O O WNW O O 2 2 O O 4 NW O O O 1 2 0 3 NNW O O 1 O O 1 2 VARIABLE O O O O O O O TOTAL 0 1 19 22 20 7 69 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classes: 13 107
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 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 1 6 1 1 9 NNE O O 1 4 0 2 7 NE O O 1 O O O 1 ENE O O 2 6 1 0 9 E O O 1 2 O O 3 ESE O O O O O O O SE O 1 O O O O 1 SSE O O 2 3 1 0 6 F S O O O 4 0 0 4 k:
I'I.
SSW O O 2 2 O O 4 SW O O 1 ! 5 3 0 9 WSW O O O O 2 0 2 W O O 1 1 1 0 3 WNW O 1 4 5 0 0 10 NW O 1 4 2 3 3 13 NNW O O 1 2 0 1 4 VARIABLE O O O O O O O TOTAL 0 3 21 42 12 7 85 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classes: 13 I
1 l
108
4 BYRON NUCLEAR POWER STATION i I
PERIOD OF RECORD - APRIL-JUNE 1987 STABILITY CLASS - SLIOHTLY UNSTABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH) I DIRECTION .8-3 4- 7 8-12 13-18 19-24 'GT 24 TOTAL
----- ----- ----- i N O 1 2 5 1 1 10 NNE O O 3 1 1 0- 5 NE O O 1 2 2 1 6 ENE O O 1 2 i O 4 E O 3 4 4 0 0 11 ESE O 1 0 3 0 0 4 SE O O 2 1 0 0 3 SSE O O 3 4 2 0 9 S 0 0 2 7 1 2 12 -
1 SSW O O 1 4 1 1 7 SW O 1 5 5 2 0 13 WSW O O 1 0 3 1 5 W O O 1 2 2 1 6 WNW 0 1 6 3 5 0 15 NW O 2 6 2 4 2 16 NNW O 1 0 1 O O 2 VARIABLE o 0 0 0 0 0 0 TOTAL 0 10 38 46 25 9 128 Hours of calm in this stability classt 0 Hours of missing wind measurements in this stability class O Hours of missing stability measurements in all stability classes: 13 109
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 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 OT 24 TOTAL N 4 7 27 8 5 3 54 NNE 2 11 13 8 2 4 40 NE 1 8 8 4 13 6 40 ENE 1 10 22 34 46 5 118 E 1 5 26 24 11 1 68 ESE 1 5 14 10 4 1 35 SE 2 5 5 8 1 0 21 SSE 1 8 13 13 2 0 37 S 3 7 20 24 6 2 62 SSW 3 4 19 18 9 6 59 SW 2 6 23 26 12 3 72 WSW 1 6 9 11 9 0 36 W O 6 16 20 3 3 48 WNW O 2 15 19 12 3 51 NW 3 8 18 21 17 7 74 NNW O 8 18 17 6 3 52 VARIABLE O O O O O O O TOTAL 25 106 266 265 158 47 867 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class O Hours of missing stability measurements in all stability classes: 13 v
110
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I BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 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 OT 24 TOTAL N O O 4 11 9 0 24 NNE 1 4 9 15 6 0 35 NE O 2 1 16 13 0 32 ENE O 3 8 22 s 1 38 E 1 4 10 30 13 1 59 ESE 1 2 8 9 8 1 29 SE O 3 4 13 11 0 31 SSE 1 4 8 17 11 2 43 S O 3 5 29 12 0 49 SSW 1 2 9 36 28 1 77 SW 1 1 12 36 27 7 84 WSW 2 2 15 18 7 1 45 W 0 2 4 2 1 0 9 f
WNW 2 2 8 13 0 0 25 NW i 1 8 13 0 0 23 NNW i 2 3 11 3 1 21 VARIABLE O O O O O O O TOTAL 12 37 116 291 153 15 624 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 13 111
1 BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 .
STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4 */ 8-12 13-18 19-24 GT 24 TOTAL N O O 4 11 9 0 24 NNE 1 4 9 15 6 0 35 NE O 2 1 16 13 0 32 ENE O 3 8 22 4 1 38 E 1 4 10 30 13 1 59 ESE 1 2 8 9 8 1 29 SE O 3 4 13 11 0 31 SSE 1 4 8 17 11 2 43 S O 3 5 29 12 0 49 SSW 1 2 9 36 28 1 77 SW 1 1 12 36 27 7 84 WSW 2 2 15 18 7 1 45 W O 2 4 2 1 0 9 WNW 2 2 8 13 0 0 25 NW 1 1 8 13 0 0 23 NNW 1 2 3 11 3 1 21 VARIABLE O O O O O O O TOTAL 12 37 116 291 153 15 624 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 13 111
e BYRON NUCLEAR POWER STATION l PERIOD OF RECORD - APRIL-JUNE 1987 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 OT 24 TOTAL N O O 1 5 4 0 10 NNE 1 0 2 8 3 0 14 NE O 1 3 2 O O 6 ENE O 3 4 1 3 0 11 E O O 3 8 6 0 17 ESE O O 5 6 12 1 24 SE O O 2 6 14 0 22 SSE O O 3 10 6 1 20 S 0 1 3 11 17 2 34 SSW O O 4 22 26 1 53 SW O 1 3 11 5 0 20 WSW O 1 3 6 O O 10 W O 1 1 4 0 0 6 WNW O O 1 7 O O 8 NW 2 2 4 4 0 0 12 NNW O 1 0 8 2 0 11 VARIABLE O O O O O O O TOTAL 3 11 42 119 98 5 278 Hours of calm in this stability class O Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classest 13 112
O BYRON NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 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 OT 24 TOTAL N O 2 3 8 0 0 13 NNE O 1 0 0 0 0 1 NE O O O O O O O ENE O 1 0 4 0 0 5 E O 2 0 1 O O 3 ESE O O O O 5 3 8 SE O 2 0 4 7 2 15 SSE 1 3 4 2 8 0 18 S O 1 2 2 2 0 7 SSW 0 1 2 7 4 0 14 SW 1 0 1 10 2 0 14 WSW 1 2 0 0 0 0 3 W 1 0 0 0 0 0 1 WNW 0 1 0 0 0 0 1 NW i 3 0 1 0 0 5 NNW 1 3 5 2 0 0 11 VARIABLE O O O O O O O i
TOTAL 6 22 17 41 28 5 119 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: 13 113
'o BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 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 3 2 O O 5 NE O O 1 1 O O 2 ENE O O 1 O O O 1 E O O O O O O O ESE O O O O O O O .
SE O O 4 2 O O 6 SSE O O 3 0 0 0 3 S O O 3 4 0 0 7 SSW O O 2 6 0 0 8 SW O 1 1 1 1 0 4 WSW O O 3 9 1 0 13 W O O O 7 1 0 8 WNW O 1 0 3 0 0 4 NW 1 O O 4 1 0 6 NNW O 1 1 5 O O 7 VARIABLE O O O O O O O TOTAL 1 3 22 44 4 0 74 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classes: 1 114
O BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 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 2 O O 2 NNE- 0 0 2 2 O O 4 NE O O 1 O O O 1 ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O 1 O O O 1 SSE O O O 2 O O 2 S O O 2 1 O O 3 SSW O 1 2 O O O 3 SW O 2 2 O O O 4 WSW O O 4 1 O O $
W O O O 2 O O 2 WNW O 1 0 4 O O 5 NW O 1 1 1 O O 3 NNW O 2 3 4 1 0 10 VARIABLE O O O O O O O TOTAL O 7 18 19 1 0 45 T
Hours of calm in this stability class: O Hours of missing wind measurements in this stability classt O Hours of missing stability measurements in all stability classes: 1 l
115
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - SLIOHTLY 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 OT 24 TOTAL N O 1 0 3 0 0 4 NNE O 1 'O 2 O O 3 NE O O O 1 O O 1 ENE O 1 1 O O O 2 E O 2 O O O O 2 ESE O O 1 1 O O 2 SE O 1 1 6 0 0 8 SSE O O 6 6 0 0 12 S O 1 5 1 1 1 9 l
i SSW O 2 6 4 1 0 13 SW O 3 1 2 1 0 7 WSW O 3 2 0 1 0 6 W O 2 1 3 0 0 6 WNW O 2 3 10 0 0 15 NW O O 3 5 1 0 9 NNW O O O O 1 0 1 VARIABLE O O O O O O O TOTAL 0 19 30 44 6 1 100 i
Hours of calm in this stability class O Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classes: 1 116 n
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 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 5 10 17 3 0 36 NNE 4 4 7 17 1 0 33 NE 4 3 5 2 O O 14 ENE 1 8 6 6 0 1 22 E O 5 4 5 2 0 16 ESE O O 10 22 5 0 37 SE O 4 20 16 1 0 41 SSE O 6 19 13 3 1 42 S O 7 26 22 12 2 69 SSW O 17 24 31 4 2 78 SW O 18 36 48 3 0 105 WSW O 8 15 9 1 0 33 W 1 7 70 16 3 0 47 WNW O 12 14 23 4 0 53 NW O 13 17 13 4 1 48 NNW 1 5 19 19 6 0 50 VARIABLE O O O O O O O TOTAL 12 122 252 279 52 7 724 Hours of calm in this : ability class: O Hours of missing wind asurements in this stability class: 12 Hours of missing stabii 'y measurements in all stability classes: 1 117
e BYRON NUCLEAR FOWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 3 14 13 2 0 32 NNE O 3 9 3 1 0 16 NE 4 6 6 4 0 0 20 ENE 1 3 4 5 4 0 17 E 1 1 5 30 10 1 48 ESE 1 3 10 17 5 1 37 SE O 2 9 15 4 1 31 SSE O 2 6 16 11 3 38 S 1 3 10 19 30 1 64 SSW O 6 10 53 29 0 98 SW O 7 37 29 10 6 89 WSW 4 7 18 14 4 0 47 W 1 3 19 9 1 0 33 WNW O 6 18 16 0 0 40 NW O 2 21 37 0 0 60 NNW 1 6 14 25 0 1 47 VARIABLE O O O O O O O TOTAL 14 63 210 305 111 14 717 Hours of calm in this stability class O Hour s of missing wind measurements in this stability class: 13 Hours of missing stability measurements in all stability classes: 1 118
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 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 6 3 4 0 0 13 NNE O 2 2 2 1 0 7 NE 1 1 2 i O O 5 ENE 1 2 4 3 0 0 10 E 1 3 8 11 4 1 28 ESE 2 3 5 10 3 0 23 SE 2 0 5 11 7 0 25 SSE O 2 0 9 2 0 13 S O 3 1 14 22 0 40 SSW O 5 7 35 14 1 62 SW O 8 10 10 0 0 28 WSW O 3 1 8 2 0 14 W 1 1 5 11 O O 18 WNW 1 0 3 13 0 0 17 NW 2 2 5 20 0 0 29 NNW O 1 11 13 1 0 26 VARIABLE O O O O O O O TOTAL 11 42 72 175 56 2 358 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 stabiiity classes: 1 119
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 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 1 2 4 0 0 8 NNE O 1 1 O O O 2 NE 2 1 1 O O O 4 ENE 1 1 O O O O 2 E 1 2 3 4 1 0 11 ESE O 2 5 7 3 3 20 SE O 4 3 16 6 3 32 SSE O O 2 7 4 1 14 S 1 O O 8 9 0 18 SSW 2 0 1 6 10 0 19 SW O O 3 1 O O 4 WSW O O 3 1 O O 4 W O O 3 0 0 0 3 WNW O O 4 2 O O 6 NW O 1 2 3 0 0 6 NNW O O 1 1 O O 2.
VARIABLE O O O O O O O TOTAL 8 13 34 60 33 7 155 Hours of calm in this stability classt O Hours of missing wind measurements in this stability classt 2 Hours of missing stability measurements in all stability classes: 1 120
o BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 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 1 O O O 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 O O O O O SE O O O O O O O SSE O O O O O O O S O O 1 2 O O 3 SSW O O O 1 3 0 4 SW O O 1 1 0 3 5 WSW O O O O O O O W O O 1 1 1 1 4 WNW O O 3 1 1 0 5 NW O O 2 O O O 2 NNW O O 3 O O O 3 VARIABLE O O O O O O O TOTAL 0 0 12 6 5 4 27 Hours of calm in this stability class: O Hours of missing wind measurements in this stability class: O Hours of missing stability measurements in all stability classess 3 121
1
- 1
- s' I BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 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 1 O O 1 NNE O O 1 O O O 1 NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S O O 1 1 O O 2 SSW O O O 2 3 0 5 SW O O O 1 0 2 3 WSW O O O 3 0 1 4 W O O 2 O O 1 3 WNW O O 2 3 1 0 6 NW O O O O 3 0 3 NNW O O O O 1 0 1 VARIABLE O O O O O O O TOTAL 0 0 6 11 8 4 29 Hours of calm in this stability class O Hours of missing wind measurements in this stability class O Hours of missing stability measurements in all stability classes 3 122
a BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 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 3 2 O O 5 NNE O O 1 O O O 1 NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O 2 O O 2 SE O O O O O O O SSE O O O O O O O S O O O 4 0 0 4 s SSW O O 2 i O O 3 SW O O 3 2 O O 5 WSW O O O 3 0 0 3 W O O 1 O O 2 3 WNW O O 1 3 2 0 6 NW O O O O 5 0 5 NNW O O O 5 2 0 7 VARIABLE O O O O O O O TOTAL O O 11 22 9 2 44 I Hours of calm in this stability class: O Hours-of missing wind measurements in this stability class O 1
I Hours of missing stability measurements in all stability classes: 3 i 123 i
9 BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 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 12 18 38 15 10 93 NNE O 4 11 12 13 1 41 NE 1 1 4 23 7 7 43 ENE O 1 12 24 21 0 58 E 1 3 10 17 15 0 46 ESE 1 3 5 7 8 1 25 SE O 2 5 8 2 0 17 SSE O O 10 21 19 9 59 S O O 20 25 16 22 83 SSW O 1 15 27 18 12 73 SW O 2 19 16 11 12 60 WSW i 3 20 11 17 6 58 W 1 4 22 46 23 23 119 WNW O 3 17 47 65 26 158 NW 1 8 22 31 34 2 98 NNW O 3 16 35 13 6 73 VARIABLE O O O O O O O TOTAL 6 50 226 388 297 137 1104 Hours of calm in this stability class O Hours of missing wind measurements in this stability class: 18 Hours of missing stability measurements in all stability classes 3 124
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SPEED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 3 7 34 0 0 44 NNE 1 1 1 11 O O 14 NE 1 5 9 3 0 0 18 ENE O 2 1 0 2 4 9 E 2 1 1 7 11 4 26 ESE O 1 5 2 9 3 20 SE O 2 4 9 11 7 33 SSE O 5 2 17 28 13 65 S O 2 9 29 45 7 92 SSW 1 1 7 21 47 7 84 SW O O 9 27 35 5 76 WSW 1 1 6 20 7 3 38 W i 1 9 15 8 0 34 WNW O O 10 18 11 0 39 NW 1 1 22 27 10 2 63 i
NNW 0 4 17 33 1 1 56 VARIABLE O O O O O O O TOTAL 8 30 . 119 273 225 56 711 Hours of calm in this stability classt O Hours of missing wind measurements in this stability class 14 Hours of missing stability measurements in all stability classes 3 125
9 BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 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 1 5 7 1 0 14 NNE 1 1 1 4 0 0 7 NE O 2 2 O O O 4 ENE O 3 0 0 0 0 3 E O 2 1 1 1 2 7 ESE O 2 0 3 1 1 7 SE O 2 3 1 9 1 16 SSE O 1 0 2 5 1 9 S O 1 3 9 9 2 24 SSW O O 1 22 18 0 41 SW O O 5 18 1 0 24 WSW O O 4 1 O O 5 W .O _
1 O O O O 1 WNW O 1 0 5 0 0 6 NW O O 10 6 0 0 16 NNW 1 1 6 4 0 0 12 VARIABLE O O O O O O O TOTAL 2 18 41 83 45 7 196 Hours of calm in this stability class O Hours of missing wind measurements in this stability class: 3 Hours of missing stability measurements in all stability classes 3 l
126 1
BYRON NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 250-30 FT)
WINDS MEASURED AT 250 FEET WIND WIND SF'EED (IN MPH)
DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 0 1 1 O O 3 NNE O O 5 0 0 0 5 NE O O 1 O O O 1 l
ENE O 3 3 0 0 0 6 E O O 1 1 0 2 4 i
j ESE O O 2 1 2 0 5 SE O 1 0 1 1 0 3 SSE O O O 2 4 1 7 S 1 O O 2 0 0 3 SSW O O 2 2 1 0 5 SW 1 2 1 4 i O 9 -
WSW 0 1 0 0 0 0 1 W i 1 O O O O 2 WNW O O O O O O O I
NW O 1 O O O O 1 NNW O 1 3 0 0 0 4 i
VARIABLE O O O O O O O TOTAL 4 10 19 14 9 3 59 Hours of calm in this stability class O Hours of missing wind measurements in this stability classt O Hours of missing stability measurements in all stability classes 3 0
1 127
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i APPENDIX III LISTING 0F MISSED SAMPLES i
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128
I APPENDIX III LISTING 0F MISSED SAMPLES Expected Collection Sample Type Location Date Reason Airborne Particulates BY-02 11-30-87 AP Filter Missing Fish BY-12 4th Qtr. Not available.
BY-13 Several attempts to collect fish were unsuccessful, i
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h 129
B ADDENDLM 130
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l 3T305 W mam POWER STATION .
f, EFFLUENT A m IshSTE DISPOSAL S M -a m t. REPORT FOR JANUARY - JUNE, 1997
! annammness e
j A. Per Technical Specifications 3.3.3.9 and 3.3.3.10, tiee following is a sn===ry of of fluont monitoring i
instrumentation inoperable for a period of time greater than specified in the Technical Specifications:
1 1
1
- 1. Reactor Containment Pan Cooler Essential Service Water Outlet Radiation Monitors (IRE-PR002, 2RE-PR003) were inoperable for greater than 30 days. The extended period of inoperability was j
- due to faulty sample pumpe. A modification was initiated and new sample pumps have been installed into these monitors.
- 2. Component Cooling Beat Exchanger Water Outlet Radiation Monitor ((ORE-PR009) was inoperable greater than 30 days. The extended period of inoperability was due to a faulty sample pump
' as above. A modification was initiated and a new sample pump has been installed.
l i
j - 3. Station Blowdown Radiation Monitor (ORE-PRO 10) was inoperable greater than 30 days. Thw extended l U period of inoperability was due to a faulty sample pump, as in 1 and 2 above. Also, the monitor's sample point was upstream of complete mixing when using Unit-2 blowdown. The sample point was i moved downstream w*nere representative samples are now being taken and a new sample pump has I been installed.
1 i.
) B. Per Technical Specification 6.13.2, the following is a discussion of changes to the Process Control Program (PCP):
The formula for volume reduction solidification was modified. This chango was recoassended by 4
the manufacture of the volume reduction system, Stock Equipment Company. The revision does not impact the current criteria for solid wastes and was found acceptable by Onsite Review in j March of 1987.
1 C. There were no major changes to the liquid, gaseous, or solid Radweste Treatment Systems. There were j no liquid holdup tanks or gas decay tanks which exceeded the limits addressed in the Technical
] Specificationc.
l j
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s._ .__ _._ .. _ . . . _. . _ . . ._ .
BYRON NUCLEAR POWER STATION EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT FOR JULY-DECEMBER,1987 ADDENDUM A. Per Technical Specifications 3.3.3.9 and 3.3.3.10, the following is a summary of effluent monitoring instrumentation inoperable for a period of time greater than specified in the Technical Specifications:
- 1. Unit-2 Component Cooling Ileat Exchanger Water Outlet (2RE-PR009) was inoperable for greater than 30 days. The extended period of inoperability was due to a faulty sample pump. A modification was initiated and a new sample g pump installed.
B. There were no major changes to the Process Control Proysm (PCP). There were no major changes to the liquid, gaseous, or Solid Radwaste Treatment System. Byron Station coctinu '- to utilize Westinghouse-liittman for dewatering and solidification services. There were no liquid holdup ta. gas decay tanks which excee,ded the limits specified in the Technical Specifications.
9 A -
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Commonw:alth Edison Byron Nucint Station 4450 North German Church Road Byron, Illinois 61010 February 9,1988 FILE: 2.12.2200 LTR: BYRON 88-0120 Mr. A. Bert Davis Regional Administrator Directorate of Inspection and Enforcement Region III l U.S. Nuclear Regulatory Commission 799 Roosevelt Road Glen Ellyn, IL 60137
SUBJECT:
Byron Station Operating Report, NRC Dockets 50-454 and 50-455.
Dear Mr. Davis:
Enclosed is Part 3 of the Byron Station Operating Report, reporting results of Environmental Radiological and Meteorological monitoring. Part 1, facility operating experience was submitted under separate cover in February, and Part 2, radioactive effluents in February and August.
Two copies of the report are provided for your use. One copy each will be forwarded to Document Control and the NRC Resident Inspector.
Sincerely, R. E. Querio Station Manager Byron Nuclear Power Station l
REQ /SF/db
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Attachment /09
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