ML20153C766
| ML20153C766 | |
| Person / Time | |
|---|---|
| Site: | Braidwood  |
| Issue date: | 12/31/1987 |
| From: | Fitzpatrick E COMMONWEALTH EDISON CO. |
| To: | Davis A NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III) |
| References | |
| EEF-88-263, NUDOCS 8805060309 | |
| Download: ML20153C766 (119) | |
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BRAICWOOD STATION RADI0 ACTIVE WASTE AND ENVIRONMENTAL MONITORING ANNUAL REPORT 1987 l
APRIL 1988 f-l 8805060309 871231
/k g
PDR ADOCK 0500045C.
J R
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 CITE 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 Sample Collections......................
8 6.0 ANALYTICAL PROCEDURES.......................
8 7.0 MILCH ANIMAL CENSUS........................
8 8.0 NEAREST RESIDENT CENSUS......................
9 9.0 INTERLABORATORY COMPARIS0N PROGRAi RESULTS 10 APPENDIX I - DATA TABLES AND FIGURES,.................
33 Station Releases Table 1.1-1 Gaseous Effluents 34 Table 1.2-1 Liquid Effluents...................
42 iii
TABLE OF CONTENTS (continued)
Page APPENDIX I - DATA TABLES AND FIGURES StationReleases(continued)
Table 2.0-1 Solid Waste Shipments 46 Figure 3.1 Figure 3.1-4 Isodose and Concentration Contours..........
48 Table 3.1-1 Maximum Doses Resulting from Airborne Releases....
52 Table 3.2-1 Maximum Doses Resulting from Liquid Discharges....
53 knvironmentalMonitoring Figure 5.0 Figure 5.0-4 Locations of Environmental Radiological Stations...
54 Table 5.0-1 Environmental Radiological Monitoring Sampling Sites...................
58 Table 5.0-2 Environmental Radiological Monitoring Program 59 Table 5.0 Table 5.0-6 Environmental Sunnary Tables.............
67 Table 5.1-1 Gamma Radiation Measurements (TLD)..........
83 APPENDIX II - METEOROLOGICAL DATA 86 4
APPENDIX III - LIST OF MISSING SAMPLES................. 115 iv
INTRODUCTION Braidwood Station, a two-unit PWR plant, is located in Will County, Illinois, fif teen (15) miles south-southwest of Joliet, Illinois.
Each reactor is de-signed to have a capacity of 1120 MW net.
Unit No. I went critical on May 29, 1987, and Unit No. 2 went critical on March 8,1988.
The plant has been designed to keep releases to the environment at levels below those specified in the regulations.
Liquid effluents from Braidwood Station are released into the Xankakee River in controlled batches after radioassay of each batch.
Gaseous effluents are released. to the atmosphere after delay to permit decay of short half-life gases.
Releases to the atmosphere are calculated on the basis of analyses of 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 Regulatory Commission as required per Technical Specifications.
Airborne concentrations of noble gases, 1-131 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 Braidwood Station to measure changes in radiation or radioactivity levels that may be attributable to plant operations. If significant changes attributable to Braidwood Station are measured, these changes are correlated with effluent releases.
External garrma radiation exposure from noble gases and I-131 in milk are the most critical pathways at this site; however, an environmental monitoring program is con-ducted which includes other pathways' of less importance.
1
SUMMARY
Gaseous and liquid effluents for the period remained at a fraction of the Technical Specification limits.
Calculations of environmental concentrations based on effluent, Kankakee River flow, and meteorological cata for the period indicate that consumption by the public of radionuclides attributable to the plant are unlikely to exceed the regulatory limits.
Ganma radiation exposure from noble gases released to the atmosphere represented the critical pathway for the period with a maximum individual dose estimated to be 3.14E-06 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 EFFLUEN1S 1.1 Gaseous Effluents to the Atmosphere Measured concentrations and isotopic composit ion 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 2.81E-01 curies of fission and activation gases was released with e maximum release rate of 9.70 pCi/sec.
A total of 1.20E-05 curies of I-131 and I-133 was released during the year.
A total of 1.43E-06 curies of beta-gamma emitters and 5.36E-04 curies alpha emitters were released as airborne particulate matter.
A total of 4.44E-02 curies of tritium was released.
1.2 Liquids Released to the Illinois River A total of 3.85E+07 liters of radioactive liquid waste (prior to dilution) containing 5.00E-02 curies (excluding tritium, gases, and alpha) were discharged af ter dilution with a total of 1.63E+10 liters of water.
These wastes were released at a monthly average concentration of 3.67E-09 pCi/ml, discharged on an unidentified nuclide basis.
A total of 7.41E-03 curies alpha radioactivity and 41.2 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 No solid radioactive wastes shipments were made in 1987 (see Table 2.0-1).
3.0 DOSE TO MAN 3.1 Gaseous Effluent Pathways Gama Dose Rates Gama 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 (Tabl e 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 3.14E-06 mrem for the year, with an occupancy or shielding factor of 0.7 included.
The maximum gamma air dose was 6.74E-06 mrad.
Beta Air and Skin Rates The range of beta particles in air is relatively small (on the order of a few meters or less); consequently, plumes of gaseous effluents may be considered "infinite" for purpose of calculating the dose from beta radiation incident on the skin.
However, the actual dose to sensitive skin tissues is difficult to calculate because this depends on the beta particle energies, thickness of inert skin, and clothing covering sensitive tissues.
For purpos,es of this report d
the skin is taken to have a thickness of 7 mg/cm and an occupancy factor of 1.0 is used.
The skin dose from beta and garmia radiation for the year was 1.26E-05 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 1.50E-05 mrad.
Radioactive Iodine The human thyroid exhibits a significant capacity to concentrate ingested or inhIled iodine, and the radioiodine, 1-131, released during routine operation of the plant, may be made available to man thus resulting in a dose to the thyroid.
The principal pathway of interest for this radionuclide is ingestion of radioiodine in milk by an infant.
Calculation made in previous years indicate that contributions to doses from inhalation of I-131 and I-133, and I-133 in milk, are negligible.
Iodine-131 Concentrations in Ai_r_
The calculated concentration contours for I-131 in air are shown in Figure 3.1-3.
Included in these calculations is an iodine cloud depletion factor which accounts for the phenomenon of elemental iodine deposition on the ground.
The maximum off-site average concentration is estimated to be 2.47E-06 pCi/m3 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 3.40E-05 mrem during the year (Table 3.1-1).
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Concentrations of Particulates in Air Concentration contours of radioactive airborne particulates are shown in Figure 3.1-4.
The maximum off-site average level is estimated to be 2.57E-07 pCi/m3, Summary of Doses Table 3.1-1 summarizes the doses resulting from releases'of airborne radioactivity via the different exposure pathways.
3.2 Liquid Effluent Pathways The three principal pathways through the aquatic environment for 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 Comonwealth Edison Off-site Dose Calcu-lation Manual.
The maximum whole body dose for the year was 3.63E-04 mrem and no organ dose exceeded 6.49E-04 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' levels.
Data recovery for these measurements was about 98.6%.
S.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 Comission, Regulatory Guide 1.109 (Rev.1).
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5.1 Gamma Radiation External radiation dose from on-site sources and noble gases released to the atmosphere was measured at eight indicator and one reference (background) locations using CaSO :Dy thermoluminescent dosimeters 4
(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 59 were installed on March 30,1984, 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 monitoring 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 LLD of 0.07 pCi/m3 throughout the year.
Gross beta concentrations ranged from 0.006 to 0.057 pCi/m3 and averaged 0.027 pCi/m3, 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 gama-emitting isotopes.
Except for gross beta, all radioactivity was below the limits of detection, indicating that there was no measurable amount of radioactivity attributable to the station releases.
Annual mean gross beta concentrations measured 23.4 pCi/1, which is the level expected in precipitation samples.
Vegetables were collected in August and analyzed for gross beta, strontium-89 and -90, and gamma-emitting isotopes.
In addition, green leafy vegetables were analyzed for iodine-131.
Gross beta concentration ranged from 1.1 to 3.7 pCi/g wet weight and averaged 2.3 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 indicdating that there was no measurable amount of radioactivity attributable to the station releases.
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Cattle feed anti grass samples were collected quarterly from milk sampling locations and analyzed for gross beta, strontium-89 and -90 and gamma-emitting isotopes.
Except for gross beta, the level of radioactivity was below the detection limits.
Gross beta concen-trations were at the level usually encoetered in these samples.
Well water was collected quarterly fre one off-site well and analyzed for gross beta, tritium, strord s.en-89 and -90, and gama-emittinng isotopes.
The annual mean gross beta concentration was 24.8 pCi/1.
All other results were below the lower limits of detection.
5.4 Aquatic Radioactivity Surface water samples were collected weekly from four locations ano analyzed for gross beta content.
Monthly composites from the Kankakee River (upstream and downstream) were analyzed for gama-emitting isotopes, and quarterly composites were analyzed for strontium-89, strontium-90, and tritium.
Monthly composites from the Kankakee River near the intake and discharge pipes were analyzed for strontium-89, strontium-90,
- tritium, and gama-emitting isotopes.
In the Kankakee River, gross beta averaged 2.8 pC1/1 in upstream samples and 2.8 pCi/1 in downstream samples.
At the intake and discharge pipes, gross beta averaged 2.9 pCi/1 and 4.8 pCi/1, respectively.
Cesium-134 and -137 concentrations were below the LLO level of 10 pCi/1 in all samples.
Strontium-89 was below the LLD of 10 pCi/1, and strontium-90 was below the LLD of 2 pCi/1 in all samples.
Tritiura concentrations were balow the LLD level of 200 pC1/1 in all samples except in one quarterly composite (fourth quarter) sample from the Kankakee alver upstream (4530 pCi/1), one from a downstream sample (7005 pCi/1), and five monthly composites (September December) from the discharge pipe.
The presence of tritium in upstream samples is attributable to the lack of water flow in the I
river which resulted in the back-up from the discharge.
Tritium concentrations in samples collected at the discharge pipe ranged from 640 to 9080 pCi/1 and averaged 4326 pCi/1.
The presence of tritium in one downstream sample and at the discharge pipe is attributalbe to i
station opration.
Sediment samples were collected three times, from one control and one indicator location, and analyzed for gross beta and gama-emitters.
Mean gross beta activity in indicator samples measured 14.2 pCi/g and 20.2 pCi/g at control location.
Cesium-137 was detected in two samples (0.10 and 0.18 pCi/g).
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Collection sites, frequency, and analysis of aquatic vegetation were identical to those of sediments.
As expected, the gross beta n
conceMration was lower for aquatic vegetation than for sediments.
s All ghma-emitters were below the detection levels.
Levels of gama 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 2.6 pCi/g wet weight and was at the 3
s level expected in fish.
5.4 Milk
\\
Milk samples were collected monthly from November through April and bi-weekly from May through October and analyzed for strontium-89 and
~
r
-90, iodine-131 and gama-emitting isotopes.
Sr-90 concentrations were variable within the usual range for milk and Sr-89 was below the limit of detection.
Iodine-131 concentration was below the LLD level of 0.5 pCi/1 in all samples.
4 Cs-134 and, Cs-137 were below the LLD level of 5 pCi/1.
All other r
gama-emitting isotopes, except naturally-occurring K-40, were below
~
their respective LLDs.
There was no indication of the effect on the environment due to station operation.
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 III of the report for the period of January - December, 1985.
Procedures
, sed during the period covered by this report remained essentially unchang<t 7.0 MILCH ANIMAL i SUS A census of milch animals was conducted within five miles of the Station.
The survey was conducted by a "door-to-door" canvas and by information from Illinois Agricultural Ag er.t s.
the census was conducted by A. Lewis on August 29, 1987.
There is one dairy (80-11) within a five mile radius.
A 'ist of dairies that were surveyed follows.
8
80-11 Mack Dairy Farm Number of cows - 53 Number of fresh cows Diet consists of the following:
Ground feed
- 20 lbs./ cow / day Green chop Free choice
- Ground feed contains:
Corn r,ix 750 !bs.
Pre-mix 750 lbs.
Soybean meal 400 lbs.
Mineral.
15 lbs.
Salt 10 lbs.
80-12 Goodwin Dairy Farm Number of cows - 28 Number of fresh cows - 24 Diet consists of the following:
Pasture Free choice Ground feed
- 12 lbs./ cow / day
- Ground feed contains:
Corn 4000 lbs.
Soybean 200 lbs.
Salt 50 lbs.
Minerals 25 lbs.
8.0 NEAREST RESIDENT CENSUS A census of the nearcat residences within a five (5) mile radius was conducted by A. Lewis on August 29, 1987.
The location of residences remained unchanged from the previous census.
A list of the nearest residences follows.
9
Nearest Direction Residence N
0.5 miles NNE 0.7 miles NE 1.2 miles ENE 1.1 miles E
0.7 miles ESE 2.2 miles RSE 2.8 miles SSE 3.2 miles S
3.9 miles SSW 0.9 miles SW 0.7 miles WSW 0.4 miles W
0.3 miles WNW 0.4 miles NW 0.3 miles NNW 0.4 miles 9.0 INTERLABORATORY COMPARISON PROGRAM RESULTS Teledyne Isotopes Midwest Laboratory has participated in interlaboratory comaprison (crosscheck) programs since the formulation of its quality control program in December 1971.
These programs are operated by agen-cies which supply environmental-type samples (e.g., milk or watet )
containing concentrations of radionuclides known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent check on the laboratory's 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.
The results in Table A-1 were obtained through p3rticipation in the environmental sample crosscheck program for milk, water, air filters, 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 (TLDs) during the period 1976, 1977, 1979, 1980, 1984, and 1985-1986 through participation in the Second, Third, Fourth, Fifth, Seventh, and Eighth International Intercomparison of Environmental Dosimeters under the sponsorships listed in Table A-2.
10
Table A-3 lists results of the anal:es on in-house spiked samples.
Table A-4 lists results of the analyses on in-house "blank" samples.
Attachment B lists acceptance criteria for "spiked" samples.
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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 l
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 3.0 0.6 315.0 0.0-11.7 Gr. beta 6.7tl.2 615.0 0.0-14.7 STM-366 Milk June 1984 Sr-89 21i3.1 2515.0 16.3-33.7 Sr-90 1312.0 1711.5 14.4-19.6 I-131 4615.3 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.lil.1 615.0 0.0-14.7 Gr. beta
- 11. 912.4 1315.0 4.3-21.7 STW-369 Water August 1984 I-131 34.315.0 34.0i6.0 23.6-44.4 STW-370 Water August 1984 H-3 3003f253 28171356 2200-3434 STF-371 Food July 1984 Sr-89 22.015.3 25.0i5.0 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 2605t130 2379-2831 STAF-372 Air August 1984 Gr. alpha 15.311.2 1715.0 8.3-25.7 Filter Gr. beta 56.010.0 5115.0 42.3-59.7 Sr-90
- 14. i'.'. 2 1811.5 13.6-20.4 Cs-137 21.011.0 1515.0 5.3-23.7 STW-375 Water Sept 1984 Ra-226 b.li0.4 4.910.7 3.6-6.2 Ra-228 2.210.1 2.310.4 1.7-2.9 STW-377 Water Sept 1984 Gr. alpha 3.311.2 5.015.0 0.0-13.7 Gr. beta 12.712.3 16.015.0 7.3-24.7 STW-379 Water Oct 1984 H-3 2860i312 2810t205 2454-3166 STW-380 Water Oct 1984 Cr-51
<36 4015.0 31.3-48.7 Co-60 20.311.2 2015.0 11.3-28.7 Zn-65 15018.1 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 12
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
- 20c 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 16*1.5 13.4-18.6 I-131 41.713.1 4216.0 31.6-42.4 Cs-137 31.3t6.1 3215.0 23.3-40.7 K
1447166 1517*76 1386-1548 STW-384 Water Oct 1984 Gr. alpha 9.711.2 1415.0 5.3-22.7 (Blind) Sample A Ra-226 3.310.2 3.0f0.5 2.2-3.8 Ra-228 3.4tl.6 2.110.3 1.6-2.6 Uranium nae 0.0-15.4 Sample B Gr. beta 48.315.0 6415.0 55.3-72.7 Sr-89 10.7t4.6 1115.0 2.3-19.7 Sr-90 7.3tl.2 12*1.5 9.4-14.6 '
Co-60 16.3tl.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 18.7*1.2 1515.0 6.3-23.7 Filter Gr. beta 59.015.3 52i5.0 43.3-60.7 Sr-90 18.311.2 2111.5 18.4-23.6 Cs-137 10.3fl.2 1015.0 1.3-18.7 STW-388 Water Dec 1984 1-131 28.0i2.0 3616.0 25.6-36.4 STW-389 Water Dec 1984 H-3 3583i110 3182i360 2558-3806 STW-391 Water Dec 1984 Ra-226 8.4tl.7 8.6tl.3 6.4-10.8 Ra-228 3.110.2 4.110.6 3.0-5.2 STW-392 Water Jan 1985 Sr-89
<3.0 3.0f5.0 0.0-11.7 Sr-90 27.3*5.2 30.0*1.5 27.4-32.6 STW-393 Water Jan 1985 Gr. alpha 3.311.2 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 11.311.2 15.015.0 6.3-23.7 Sr-89 25.316.4 34.0i5.0 25.3-42.8 Sr-90 27.0t8.8 26.Dil.5 23.4-28.6 I-131 38.012.0 ?5.0i6.0 24.6-45.4 Cs-137 32.712.4 29.015.0 20.3-37.7 K
14101212 13021120 1174-1590 13
Table A-1.
(continued)
}
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis 12ac Is, N=1 Control Limits STW-397 Water Feb 1985 Cr-51
<29 4815.0 39.3-56.7 I
]
Co-60 21.313.0 2015.0 11.3-28.7 ll Zn-65 53.715.0 55 5.0 46.3-63.7 Ru-106
<23 2515.0 16.3-33.7 Cs-134 32.311.2 35f5.0 26.3-43.7 Cr.-137 25.313.0 2515.0 16.3-33.7 STW-398 Water Feb 1985 H-3 38691319 37961634 3162-4430 l[
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STM-400 Milk March 1985 I-131 7.312.4 9.010.9 7.4-10.6 STW-402 Water March 1985 Ra-226 4.6i0.6 5.010.8 3.7-6.3 Ra-228
<0.8 9.011.4 6.7-11.3 Reanalysis Ra-228 9.010.4 STW-404 Water March 1985 Gr. alpha 4.7i2.3 615.0 0.0-14.7 Gr. beta 11.3*1.2 1515.0 6.3-23.7 STAF-405 Air March 1985 Gr. alpha 9.3i1.0 10.0i5.0 1.3-18.7 Filter Gr. beta 42.Dil.1 36.015.0 27.3-44.7 Sr-90 13.311.0 15.0il.5 12.4-17.6 Cs-137 6.311.0 6.015.0 0.0-14.7 STW-407 Water April 1985 1-131 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.li0.6 3.1-5.1 Ra-228 nae 6.210.9 4.6-7.8 Uranium NA8 7.0i6.0 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 14.7i2.4 15.0tl.5 12.4-17.6 Co-60 14.712.4 15.015.0 6.3-23.7 Cs-134 12.Di2.0 15.015.0 6.3-23.7 Cs-137 14.0i2.0 12.015.0 3.3-20.7 14
1 Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
- 20c is, N=1 Control Limits STW-413 Water May 1985 Sr-89 36.0t12.4 39.0t5.0 30.3-47.7 Sr-90 14.314.2 15.011.5 12.4-17.6 STW-414 Water May 1985 Gr. alpha 8.3*4.1 12.015.0 3.3-20.7 Gr. beta 8.7tl.2 11.015.0 2.3-19.7 STW-416 Water June 1985 Cr-51 44.716.0 44.0f5.0 45.3-52.7 Co-60 14.3tl.2 14.0i5.0 b.3-22.7 Zn-65 50.3i7.0 47.0i5.0 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 22.712.4 20.0f5.0 11.3-28.7 STW-418 Water June 1985 H-3 24461132 2416f351 1807-3025 STM-421 Milk June 1985 Sr-89 10.314.6 11.015.0 2.3-19.7 Sr-90 9.0*2.0 11.011.5 8.4-13.6 I-131 11.711.2 11.016.0 0.6-21.4 Cs-137 12.7tl.2 11.015.0 2.3-19.7 K
1512i62 15251132 1393-1657 STW-423 Water July 1985 Gr. alpha 5.0t0.0 11.015.0 2.3-19.7 Gr. beta 5.0i2.0 8.0i5.0 0.0-16.7 STW-425 Water August 1985 I-131 25.7t3.0 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 13.0i5.0 4.3-21.7 Filter Gr. beta 46.011.0 44.0i5.0 35.3-52.7 Sr-90 17.7t0.6 18.0il.5 15.4-20.6 Cs-137 10.310.6 8.015.0 0.0-16.7 STW-429 Water Sept 1985 Sr-89 15.710.6
?0.015.0 11.3-28.7 Sr-90 7.0f0.0 7.011.5 4.4-9.6 STW-430 Water Sept 1985 Ra-226 8.210.3 8.911.3 6.6-11.1 Ra-228 4.110.3 4.6i0.7 3.4-5.8 STW-431 Water Sept 1985 Gr. alpha 4.710.6 8.015.0 0.0-16.7 Gr. beta 4.7tl.2 8.015.0 0.0-16.7 15 l
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-433 Water Oct 1985 Cr-51
<13 21.015.0 12.3-29.7 Co-60 19.310.6 20.0*5.0 11.3-28.7 Zn-65 19.710.6 19.0t5.0 10.3-27.7 Ru-106
<19 20.0i5.0 11.3-28.7 Cs-134 17.0*1.0 20.0i5.0 11.3-28.7 Cs-137 19.3 1.2 20.015.0 11.3-28.7 STW-435 Water Oct 1985 H-3 1957150 1974t345 1376-2572 STW-436 Water Oct 1985 437 (Blind)
Sample A
.Gr. alpha 53.011.0 52.0113 29.4-74.6 Ra-226 5.910.1 6.311.0 4.1-7.9 Ra-228 0.210.1 10.111.5 7.5-12.7 Uranium NA8 8.0i10.4 0.0-18.4 Sample B Gr. beta 85.7*2.5 75.015.0 76.3-83.7 Sr-89 21.3tl.5 27.0t5.0 18.3-35.7 Sr-90 10.310.6 9.0*1.5 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 18.015.0 9.3-26.7 STM-439 Milk Oct 1985 Sr-89 50.3i0.6 48.0f5.0 39.3-56.7 Sr-90 23.310.6 26.0il.5 23.4-28.6 I-131 45.7i3.2 42.016.0 31.6-52.4 Cs-137 60.7i0.6 56.015.0 47.3-64.7 K
1547129 1540177 1406-1674 STW-441 Water Nov 1985 Gr. alpha 5.310.6 10.0i5.0 1.3-18.7 Gr. beta 11.711.2 13.0i5.0 4.3-21.7 STW-443 Water Dec 1985 I-131 46.7f2.1 45.0*6.0 34.6-55.4 STW-444 Water Dec 1985 Ra-226 6.5t0.1 7.1tl.1 5.2-9.0 Ra-228 6.110.1 7.3*1.1 5.4-9.2 STW-445 Water Jan 1986 Sr-89 29.7*2.5 31.Di5.0 22.3-39.7 Sr-90 13.710.6 15.011.5 12.4-17.6 STW-446 Water Jan 1986 Gr. alpha 3.0i0.0 3.015.0 0.0-11.7 Gr. beta 5.310.6 7.015.0 0.0-15.7 16
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis 120c 15, N=1 Control Limits STF-447 Food Jan 1986 Sr-89 24.3i2.5 25.015.0 16.3-33.7 Sr-90 17.310.6 10.0il.5 7.4-12.6 I-131 22.712.3 20.016.0 9.6-30.4 Cs-137 16.3i0.6 15.015.0 6.3-23.7 K
927146 950*144 701-1199 STW-448 Water Feb 1986 Cr-51 45.0i3.6 38.015.0 29.3-46.7 Co-60 19.711.5 18.0i5.0 9.3-26.7 Zn-65 44.013.5 40.0*5.0 31.3-48.7 Ru-106
<9.0 0.0t5.0 0.0-8.7 Cs-134 28.312.3 30.0i5.0 21.3-38.7 Cs-137 23.710.5 22.015.0 13.3-30.7 STW-449 Water Feb 1986 H-3 5176148 52271525 4317-6137 STW-450 Water Feb 1986 U total 8.0f0.0 9.016.0 0.0-19.4 STNh451 Mil k Feb 1986 I-131 7.0f0.0 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 11.010.5 12.4fl.8 9.2-15.5 STW-453 Water March 1986 Gr. alpha 6.710.6 15.0*5.0 6.3-23.7 Gr. beta 7.310.6 8.015.0 0.0-16.7 STW-454 Water April 1986 I-131 7.010.0 9.016.0 0.0-19.4 STW-455 Water April 1986 456 (Blind)
Sample A Gr. alpha 15.011.0 17.015.0 8.3-25.7 Ra-226 3.110.1 2.9i0.4 2.1-3.7 Ra-228 1.5f0.2 2.010.3 1.5-2.5 Uranium 4.7i0.6 5.0i6.0 0.0-15.4 Sample B Gr. beta 28.7tl.2 35.015.0 26.3-40.7 Sr-89 5.710.6 7.015.0 0.0-15.7 Sr-90 7.010.0 7.Dil.5 4.4-9.6 00-60 10.711.5 10.Di5.0 1.3-18.7 Cs-134
- 4. 011. 7 5.015.0 0.0-13.7 Cs-137 5.310.6 5.015.0 0.0-13.7 17
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collec ted Analysis 120c 15, N=1 Control Limits 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 10.710.6 10.015.0 1.3-18.7 STU-458 Urine April 1986 Tritium 4313i70 44231189 4096-4750 STW-459 Water May 1986 Sr-89 4.3t0.6 5.015.0 0.0-13.7 Sr-90 5.0f0.0 5.0tl.5 2,4-7.6 STW-460 Water May 1986 Gr. alpha 5.310.6 8.015.0 0.0-16.7 Gr. beta 11.3tl.2 15.015.0 6.3-23.7 STW-461 Water June 1986 Cr-51
<9.0 0.0i5.0 0.0-8.7 Co-60 66.011.0 66.015.0 57.3-74.7 Zn-65 87.3i1.5 86.015.0 77.3-94.7 Ru-106 39.7f2.5 50.015.0 41.3-58.7 Cs-134 49.3t2.5 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 31251361 2499-3751 STM-464 Milk June 1986 Sr-89
<1.0 0.015.0 0.0-8.7 Sr-90 15.310.6 16.011.5 13.4-18.6 I-131 48.312.3 41.0f6.0 30.6-51.4 Cs-137 43.7tl.5
- 31. 0i5.0 22.3-39.7 K
15671114 1600i80 1461-1739 STLl-465 Water July 1986 Gr. alpha 4.710.6 6.015.0 0.0-14.7 Gr. beta 18.711.2 18.015.0 9.3-26.7 STW-467 Water August 1986 I-131 30.310.6 45.016.0 34.4-55.4 STW-468 Water August 1986 Pu-239 11.310.6 10.111.0 8.3-11.9 STW-469 Water August 1986 Uranium 4.010.0 4.016.0 0.0-14.4 STAF-470 Air Sept 1986 Gr. alpha 19.311.5 22.015.0 13.3-30.7 471 Filter Gr. beta 64.012.6 66.015.0 57.3-74.7 472 Sr-90 22.0il.0 22.015.0 19.4-24.6 Cs-137 25.711.5 22.015.0 13.3-30.7 STW-473 Water Sept 1986 Ra-226 6.010.1 6.110.9 4.5-7.7 Ra-2;8 8.711.1 9.111.4 6.7-11.5 18
Table A-1.
(continued).
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis 12oc 15, N=1 Control Limits STW-474 Water Sept 1986 Gr. alpha 16.3t3.2 15.0i5.0 6.3-23.7 Gr. beta 9.0il.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 Cc-60 31.0i2.0 31.0i5.0 22.3-39.7 Zn-65 87.315.9 85.0i5.0 76.3-93.7 Ru-106 74.7t7.4 74.0i5.0 65.3-82.7 Cs-134 25.710.6 28.015.0 19.3-36.7 Cs-137 46.311.5 44.Di5.0 35.3-52.7 STW-476 Water Oct 1986 H-3 5918160 5973tS97 4938-7008 SPW-477 Water Oct 1986 478 (Blind)
Sample A Gr. alpha 34.0t6.0 40.015.0 31.3-48.7 Ra-226 5.810.2 6.0i0.9 4.4-7.6 Ra-228 2.7tl.0 5.0i0.8 3.7-6.3 Uranium 11.0f0.0 10.016.0 0.0-20.A Sample B Gr. beta 38.7tl.2 51.015.0 42.3-59.7 Sr-89 5.0i0.0 10.015.0 1.3-18.7 Sr-90 3.010.0 4.0il.5 1.4-6.6 Co-60 24.7tl.2 24.0i5.0 15.3-32.7 Cs-134 11.012.0 12.015.0 3.3-20.7 Cs-137 9.3tl.2 8.0*5.0 0.0-16.7 STM-479 Milk Nov 1986 Sr-89 7.7tl.2 9.0i5.0 0.3-17.7 Sr-90 1.010.0 0.0*1.5 0.0-2.6 1-131 52.313.1 49.016.0 38.6-59.4 Cs-137 45.7t3.1 39.015.0 30.3-47.7 K
1489i104 1565i78 1430-1700 STU-480 Urine Nov 1986 H-3 5540*26 52571912 4345-6169 STW-481 Water Nov 1986 Gr. alpha 12.014.0 20.015.0 11.3-28.7 Gr. beta 20.Di3.5 20.015.0 11.3-28.7 STW-482 Water Dec 1986 Ra-226 6.710.2 6.811.0 5.0-8.6 Ra-228 5.210.2 11.111.7 8.2-14.0 STW-483 Water Jan 1987 Sr-89 19.715.0 25.015.0 16.3-33.7 Sr-90 21.0i2.0 25.011.5 22.4-27.6 19
Table A-1.
(continued).
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis 12ac 15, N=1 Control Limits STW-484 Water Jan 1987 Pu-239 17.0t2.3 16.7tl.7 13.8-19.6 STF-486 Food Jan 1987 Sr-90 36.014.0 49.0t10.0 31.7-66.3 I-131 78.0f3.4 78.018.0 64.1-91. 9 Cs-137 89.713.0 84.015.0 75.3-92.7 K
942156 980149 895-1065 STF-487 Food Jan 1987 SR-90 2.0i0.0 (Blank) 1-131
<3 Cs-137
<2 K
9931102 STW-488 Water Feb 1987 Co-60 49.010.0 50.0i5.0 41.3-58.7 Zn-65 96.017.2 91.015.0 82.3-99.7 Ru-106 92.0120.2 100.015.0 91.3-108.7 Cs-134 53.0i3.4 59.015.0 50.3-67.7 Cs-137 89.314.6 87.0i5.0 78.3-95.7 STW-489 Water Feb 1987 H-3 4130i140 42091420 3479-4939 STW-490 Water Feb 1987 Uranium 8.3*1.2 8.0i6.0 0.0-18.4 STM-491 Milk Feb 1987 I-131 10.0i0.0 9.0f0.9 7.4-10.6 STW-492 Water Mar 1987 Gr. alpha 3.7*1.2 3.015.0 0.0-11.7 Gr. beta 11.3fl.2 13.0i5.0 4.3-21.7 STW-493 Water Mar 1987 Ra-226 7.0iO.1 7.3tl.1 5.4-9.2 Ra-228 7.li2.3 7.5fl.1 5.5-9.5 STW-494 Water Apr 1987 I-131 8.010.0 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. beta 41.0i2.0 43.015.0 34.3-51.7 Sr-90 16.311.2 17.0il.5 14.4-19.6 Cs-137 7.0i0.0 8.015.0 0.0-16.7 STW-496 Water Apr 1987 497 (Blind)
Sample A Gr. alpha 30.711.2 30.018.0 16.1-43.9 Ra-226 3.9i0.2 3.910.6 2.9-4.9 Ra-228 4.9i0.9 4.010.6 3.0-5.0 Uranium 5.010.0 5.016.0 0.0-15.4 20 i
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis
- 2ac is, N=1 Control Limits STW-496 Water Apr 1987 497 (Blind)
Sample B Gr. Beta 69.3t9.4
- 66. 015.0 57.3-74.7 Sr-89 16.313.0 19.0i5.0 10.3-27.7 Sr-90 10.0i0.0 10.Dil.5 7.4-12.6 Co-60 8.313.0 8.0i5.0 0.0-16.7 Cs-134 19.0f2.0 20.0i5.0 11.3-28.7 Cs-137 14.7*1.2 15.0i5.0 6.3-23.7 STU-498 Urine Apr 1987 H-3 60171494 5620i795 4647-6593 STW-499 Water May 1987 Sr-89 38.016.0 41.0i5.0 32.3-49.7 Sr-90 21.0i2.0 20.Dil.5 17.4-22.6 STW-500 Water May 1987 Gr. alpha 9.013.4 11.015.0 2.3-19.7 Gr. beta 10.3tl.2 7.0i5.0 0.0-15.7 STW-501 Water June 1987 Cr-51 40.018.0 41.Di5.0 32.3-49.7 Co-60 60.313.0 64.Di5.0 55.3-72.7 Zn-65 11.315.0 10.0i5.0 1.3-18.7 Ru-106 78.316.4 75.0i5.0 66.3-83.7 Cs-134 36.7i3.0 40.015.0 31.3-48.7 Cs-137 80.3i4.2 80.0*5.0 71.3-88.7 STW-502 Water June 1987 H-3 2906186 28951357 2277-3513 STW-503 Water June 1987 Ra-226 6.9i0.1 7.3fl.1 5.4-9.2 Ra-228 13.311.0 15.212.3 11.2-19.2 STM-504 Milk June 1987 Sr-89 57.014.3 69.0i5.0 60.3-77.7 Sr-90 32.Dil.0 35.0il.5 32.4-37.6 I-131 64.012.0 59.0i6.0 48.6-69.4 Cs-137 77.7f0.6 74.0i5.0 65.3-82.7 K
1383i17 1525i76 1393-1657 STW-505 Water July 1987 Gr. alpha 2.310.7 5.015.0 0.0-13.7 Gr. beta 4.0il.0 5.015.0 0.0-13.7 STF-506 Food July 1987 I-131 82.714.6 80.018.0 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 I-131 45.714.2 48.0i6.0 37.6-58.4 STW-508 Water Aug 1987 Pu-239 5.810.2 5.310.5 4.4-6.2 21 y
Table A-1.
(continued)
Concentration in pCi/lb Lab Sample Date TIML Result EPA Resultd Code Type Collected Analysis t20C 15, N=1 Control Limits STW-509 Water Aug 1987 Uranium 13.310.3 13.0i6.0 2.6-23.4 STAF-510 Air Aug 1987 Gr. alpha 9.710.4 10.0i5.0 1.3-18.7 Filter Gr. beta 28.310.6 30.0i5.0 21.3-38.7 Sr-90 10.0f0.9 10.011.5 7.4-12.6 Cs-137 10.0tl.0 10.0t5.0 1.3-18.7 STW-511 Water Sept 1987 Ra-226 9.910.1 9.7tl.5 7.2-12.2 Ra-228 8.lil.4 6.3tl.0 4.6-8.0 STW-512 Water Sept 1987 Gr. alpha 2.010.6 4.Di5.0 0.0-12.7 Gr. beta 11.311.3 12.Di5.0 3.3-20.7 STW-513 Water Oct 1987 H-3 4473t100 44921449 3714-5270 STW-514 Water A Oct 1987 Gr. alpha 29.312.6 28.0i7.0 15.9-40.1 Ra-226 4.910.1 4.810.7 3.6-6.1 Ra-228 4.211.0 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 72.3f2.7 72.0f5.0 63.3-80.7 Sr-89 14.311.3 16.0i5.0 7.3-24.7 Sr-90 9.7t0.4 10.011.5 7.4-12.6 Co-60 16.7f3.0 16.0i5.0 7.3-24.7 Cs-134 16.7t2.3 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 80.3t17.5 70.015.0 61.3-78.7 Co-60 16.0i2.3 15.015.0 6.3-23.7 Zn-65 46.315.6 46.015.0 37.3-54.7 Ru-106 57.3115.4
- 61. 015.0 52.3-69.7 Cs-134 23.7*2.5 25.015.0 16.3-33.7 Cs-137 51.713.2 51.015.0 42.3-59.7 STU-517 Urine Nov 1987 H-3 7267i100 7432i743 6145-8719 STW-519 Water Dec 1987 I-131 26.013.0 26.016.0 15.6-36.4 a Results obtained by Teledyne Isotopes Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Intercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Laboratory, U. S. Environmental Protection Agency (EPA), las 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.
22
um m u-Table A-2.
Crosscheck program results, thermoluminescent dosimeters (TL0s).
mR d
Teledyne Average 12 o Lab TLD Result Known (all Code Type Measurement 12aa valuec partic f pants) b 2nd International Intercomparison CaF :Mn Field 17.011.9 17.1 16.417.7 115-2 2
Bulb Lab 20.814.1 21.3 18.817.6 e
3rd International Intercomparison CaF :Mn Field 30.713.2 34.914.8 31.513.0 115-3 2
m Bulb Lab 89.616.4 91.7114.6 86.2124.0 4th International Intercomparisonf CaF :Mn Field 14.111.1 14.111.4 16.019.0 115-4 2
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 CaF :Mn Field 31.411.8 30.016.0 30.2114.6 l
115-5A 2
l 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
Table A-2.
(Continued) mR d-Teledyne Average 120 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 i
beginning Lab at 85.4111.7 88.4i8.8 90.7131.2 the end h
7th International Intercomparison l
115-7A Lif-100 Field 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 CaF :Mn Field 71.512.6 75.816.0 75.1129.8 115-78 2
Bulbs Lab (Co-60) 84.816.4 79.914.0 77.9127.6 Lab (Cs-137) 78.811.6 75.013.8 73.0122.2 CaSO :Dy Field 76.812.7 75.816.0 75.1129.8 115-7C 4
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
+
Table A-2.
(Continued) mR d
Teledyne Average 120 Lab TLD Result Known (all Code Type Measurement 12oa valuec participants) i 8th International Intercomparison 115-8A Lif-100 Field Site 1 29.511.4 29.711.5 28.9112.4 Chips Field Site 2 11.310.8 10.410.5 10.119.06 Lab (Cs-137) 13.710.9 17.210.9 16.216.8 CaF :Mn Field Site 1 32.311.2 29.711.5 28.9112.4 115-8B 2
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 CaSO :Dy Field Site 1 32.310.7 29.711.5 28.9112.4 4
Cards 01 Field Site 2 10.610.6 10.410.5 10.119.0 Lab (Cs-137 18.110.8 17.210.9 16.216.8 i
1 a Lab result given is the mean 12 standard deviations of three determinations.
I b Second International Intercomparison of Environmental Dosimeters conducted in April of 1976 by the Health and Safety Laboratory (GASL), New York, New York, and the School of Public Health of the University of Texas, Houston, Texas.
c Value determined by sponsor of the intercomparison using continuously operated pressurized fon chamber.
d Mean *2 standard deviations of results obtained by all laboratories participating in the program.
e Third International Intercomparison of Environmental Dosimeters conducted in sunener 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 sunener 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 anc' 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.
h Seventh International Interccmparison of Environmental Dosimeters conducted in the spring and sunener of 1984 at Las Vegas, Nevada, and sponsored by the U.S. Department of Energy, the U.S. Nuclear Regulatory Commission, and the U.S. Environmental Protection Agency.
j Eighth International Intercomparisen of Environmental Dosimeters conducted in the fall and winter of 1985-1986 at New York, New York, and sponsored by the U.S. Department of Energy.
4
Table A-3.
In-house spiked samples.
Concentration in pC1/1 Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision 1s, n=3a QC-MI-6 Milk Feb. 1986 Sr-89 6.011.9 6.4t3.0 8.7 Sr-90 14.2il.7 12.9f2.0 5.2 1-131 34.213.8 35.2i3.5 10.4 Cs-134 32.011.8 27.3t5.0 8.7 Cs-137 35.812.1 35.015.0 8.7 QC-W-14 Water Mar. 1986 Sr-89 1.6i0.4 1.611.0 7.1 Sr-90 2.410.2 2.4f2.0 4.2 QC-W-15 Water Apr. 1986 I-131 44.9i2.4 41.517.0 10.6 Co-60 10.611.7 12.1*5.0 7.lb Cs-134 30.212.4 25.8i8.0 7.lb Cs-137 21.911.9 19.915.0 7.lb QC-MI-7 Milk Apr. 1986 I-131 39.7i3.3 41.517.0 10.4 Cs-134 28.7f2.8 25.8t8.0 8.7 Cs-137 21.212.8 19.915.0 8.7 SPW-1 Water May 1986 Gross alpha 15.81'.8 18.0i5.0 Sc QC-W-16 Water June 1986 Gross alpha 16.2f0.7 16.9t2.5 8.7 Gross beta 33.4i3.5 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 33.013.4 36.115.0 8.7 Cs-137 38.512.8 39.0i5.0 8.7 SPW-2 Water June 1986 Gross alpha 16.811.8 18.015.0 Sc SPW-3 Water June 1986 Gross alpha 17.7i0.8 18.0i5.0 Sc QC-W-18 Water Sep. 1986
.Cs-134 34.715.6 31.3f5.0 8.7 Cs-137 51.li7.0 43.318.0 8.7 QC-W-19 Water Sep. 1986 Sr-89 13.614.1 15.6t3.5 7.lb Sr-90
- 6. 4fl. 6 6.2i2.0 4.2b 26
' ~ ~ ~ - - ~ ~. _.
Table A-3.
In-house spiked samples (continued)
Concentration in pCi/l Lab Sample Date TIML Result Known Expected Code Type Collected Analysis n=3 Activity Precision 1s, n=3a QC-W-21 Water Oct.1986 Co-60 19.2t2.2 18.Si3.0 8.7 Cs-134 31.7i5.2 25.618.0 8.7 Cs-137 23.8tl.0 21.6t5.0 8.7 QC-MI-11 Milk Oct 1986 Sr-89 12.311.8 14.313.0 8.7 QC-W-20 Water Nov.1986 H-3 3855i180 3960i350 520b QC-W-22 Water Dec.1986 Gross alpha 9.811.4 11.2i4.0 8.7 Gross beta 21.7tr.0 23.8i5.0 8.7 QC-W-23 Water Jan. 1987 I-131 29.812.5 27.913.0 10.4 QC-MI-12 Milk Jan. 1987 I-131 36.Sil.3 32.615.0 10.4 Cs-137 32.614.2 27.418.0 8.7 SPM-13 Milk Jan 1987 SP-89 10.4f2.1 12.214.0 8.7 Sr-90 14.6fl.6 12.613.0 5.2 1-131 49.511.2 54.9i8.0 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 24.7*3.6 25.9i5.0 8.7 Sr-90 23.913.8 22.Bi8.0 5.2 SPW-25 Water Apr 1987 I-131 28.011.9 29.315.0 10.6 SPM-14 Milk Apr 1987 I-131 25.Di2.2 23.9i5.0 10.4 Cs-134
<2.1 0.0 8.7 Cs-137 34.212.0 27.2i7.0 8.7 SPW-26 Water Jun 1987 H-3 3422i100 3362*300 520 Co-60 24.B:1.4 26.5t7.0 8.7 Cs-134
<2.0 0.0 8.7 Cs-137 21.210.5 21.6t7.0 8.7 SPW-27 Water Jun 1987 Gr. alpha 8.511.9 10.114.0 8.7.
Gr. beta 22.6tl.9 21.2i5.0 8.7 SPW-28 Water Jun 1987 Gr. alpha 8.7tl.3 10.114.0 8.7 Gr. beta 12.215.2 9.413.0 8.7 j
27 1
Table A-3.
In-house spiked samples (continued)
Concentration in pCi/l Lab Sample Date TIML Result Known Ex pected Code Type Collected Analysis n=3 Activity Precision 15, n=3a SPW-29 Water Jun 1987 Gr. alpha 16.411.3
- 18. 9t5.0 8.7 Gr. beta 15.9t4.0 11.814.0 8.7 SPM-15 Milk Jul 1987 Sr-89 19.411.6 18.8t3.5 5.2 1-131 43.510.7 45.3f7.0 10.4 Cs-134 17.912.2 16.015.3 8.7 Cs-137 25.411.8 22.7t5.0 8.7 SPW-30 Water Sep 1987 Sr-89 17.513.0 14.315.0 8.7 Sr-90 18.4i2.2 17.Si2.2 5.2 SPW-31 Water Oct 1987 H-3 2053193 2059t306 520 b n=3 unless noted otherwise.
a n=
2.
c n=1.
28
Table A-4.
In-house "blank" samples.
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66o)
(4.66o)
BL-1 D.I. Water Nov. 1985 Gross alpha
<0.1
<1 Gross beta
<0.4
<4 BL-2 D.I. Water Nov. 1985 Cs-137 (gama)
<1.9
<10 BL-3 D.I. Water Nov. 1985 Sr-89
<0.5
<5 Sr-90
<0.6
<1 BL-5 D.I. Water Nov. 1985 Ra-226
<0.4
<1 Ra-228
<0.4
<1 SPW-2265 D.I. Water Apr. 1985 Gross alpha
<0.6
<1 Gross beta
<2.2
<4 Sr-89
<0.2
<5 Sr-90
<0.4
<1 I-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 D.I. Water June 1986 Gross alpha
<0.4
<1 BL-9 D.I. Water June 1986 Gross alpha
<0.3
<1 SPW-3185 D.I. Water Jan 1987 Ra-226
<0.1
<1 Ra-228
<0.9
<1 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.
29
Table A-4.
In-house "blank" samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collected Analysis (4.66a)
(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 (gamma)
<2.2
<10 Cs-137 (gama)
<2.4
<10 Ra-226
<0.1
<1 Ra-228
<1.0
<1 Np-237
<0.04
<1 Th-230
<0.05
<0.1 Th-232
<0.02
<0.1 V-234
<0.05
<0.1 U-235
<0.03
<0.1 U-238
<0.03
<0.1 SPS-4023 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 0.I. Water Jun 1987 Sr-89
<0.4
<5 Sr-90
<0.4
<1 1-121
<0.1
<1 Co-60
<3.8
<10 Cs-137
<5.7
<10 Ra-226
<0.1
<1 Ra-228
<0.9
<1 SPW-4627 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
<S 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 concentration in milk is not unusual.
30
l-e Table A-4.
In-house "blank" samples (continued).
Concentration in pCi/1 Acceptance Lab Sample Date Results Criteria Code Type Collec ted Analysis (4.66o)
(4.66o)
SPS-4848 D.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.I. 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 I-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 SPS-5386 Milk Jan 1988 I-131
<0.1
<1 SPW-5448 "Dead" Water Jan 1988 H-3
<177
<300 l
31
TIML-8 LINO-01 Revision 0, 12-29-86 A_TTACHMENT B ACCEPTANCE CRITERIA FOR "SP!KE0" SAMPLES LABORATORY PRECISION:
ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa One Standard Deviation Analysis level for Single Determination Gama Emitters 5 to 100 pCi/ liter or kg 5 pCi/ liter
>100 pCi/ liter or kg 5% of known value Strontium-89b 5 to 50 pCi/ liter or kg 5 pCi/ liter
>50 pCi/ liter or kg 10% of known value Strontium-90b 2 to 30 pCi/ liter or kg 3.0 pCi/ liter
>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) =
159.85 x (known).0933
>4,000 pCi/ liter 10% of known value Radium-226,
<0.1 pCi/ liter 15% of known value Radium-228 Plutonium 0.1 pCi/ liter, gram, 10% of known value or sample lodine-131, b
<55 pCi/ liter 6 pCi/ liter Iodine-129
>55 pCi/ liter 10% of known value Uranium-238,
<35 pCi/ liter 6 pCi/ liter Nickel-63b,
>35 pCi/ liter 15% of known value Technetium-99b Iron-55b 50 to 100 pCi/ liter 10 pCi/ liter 10% of known value a From EPA publication, "Environmental Radioactivity Laboratory Intercompari-I son Studies Program, Fiscal Year 1981-1982. EPA-600/4-81-004.
b TIML limit.
32
8 -
G APPENDIX 1 DATA TABLES l
l f
i 33
e f
TABLE lel-1 taalthe00 nutttaa peda Station Malaansaat Littutat etP0et tpt maY ta Amt. tute (saMput tritutett. Sweistim or att ettgaut I tatit t m i fra i ma s i. u tras un i
m, i
a
,2a w n ;
a, tiesten ene actt et6ea ses seteeses 1.
f atai Aalaata Actimits i
ft i
f I
l i
f a i t h.
I e tia j
e it_a i
2_
a.ai-ami-Lia I.z uur I I
l l
l 1
I 1
l s.
n af suf ama tuiti..
a_
taata nada fine aram/ maar t I
i i
f f
I l
t g
g g
g g-lg m.
tain mens arms.airi i
s l
I i
1 I
I 1
[
g e_
1 af 1Ef kid Limitt a.
- -- Lartarl a 11 araal 1
g g
m_
hau Lartarla fla ara.tl 1
g g
- j**
g" n_
e--
-- 1 sia meami 1
e a
'3]{
a_
am u - - 1 e ra ar aa n s
e e
.. io. a. eio....
t_
fatal f.111 and 1.113 As t i n i t s i
ft l
t t
l 1
i e LLD l
a 118 l
e i f_
1 af IMf a28/1Kf aia L iat t aa
~ "
- laltle) Crittsellt, stop it. IMt 1 et it(fett iteils it bened on the assima reteese rate f or the persed seasleered.
- Isetee. perticolete ead teltles 16e6ts are espressed et a tote) 14eit, lee $tes (,
e LLB he colette6te activity e6e.e borterev s.
no a
I r
t 34
TABLE 1.1-1 (continued) smaltam0 auttlaa e9ste $lation
$(nlanosAt (f f ty(st f(post (0e Nu le arrrata_ inat f.aSIOUS E f f tutett. Suseint t0e 04 att 4(Lt4 Sin 1 tm!?1 1 Jut t
I ti p i ira fLaattat Off I
act t
are f ata metry a,
f.gie.as act6,eties ras teleases I
fa f a.aar.1 1 a. itt.1 t t. a it.2 1 2 Pv.2 I a. aar.1 1 a ut.2 e t. aer. t i 1 tar. i g.1,1 m,1.na artt.it.
l uf t /ta r I 1.11.2 l a.1?r.1 l 4.nar.t I a _171.1 l
- a. IM.t l
1.1 )r ea I g. 7m aa
] a _ pag.a j_
m.m ta taats mata 1.
1 af taf f ala t imitt**
- t. a. t us ar /. air s t
t i a _ na i s.ma t s aa i a na e a_na e
a ma e
a_na i
n.ma e
I t
I a_na I a na I a.na I a.ma 1
a na I
a_na I
a.ma i m[
n.
t.ia sman a, m aari a.
1 at taf f ata t imitt r -- lLar t a r1. It arasi t
a.ma a.M a. ma I
e as a.ta e_ma a.ma a.ma n.
anta e artarin sie arman 1
aM a.ta
- a. ma a_me e.ta a as e ma a.as l
r
- -- -1 t ia n, ma t i
a as e ma s_ea s na a. ma Ah J aa a ma _
....-1 t re arma n i
a na a ta a _ na a _ na a.ma a ma a.ma a _ aL
- ~
3.
teetne telestes t_
tatat 1.111 maa 1.111 ar t i.i t.
I et i sits..
I ette i 1. aar.a 1
- 1. aar.a f
atta I a _ att.a f
a tra t a _ att.a L 1 af laUa2aliacf asa t imitt.
- $ et 10(f tt0 liestl 46 Dened ea the eesima release rete f or the pertes centteeret, geeine, part6celete. and tetties Ita6tn are espressed as a total liest. See Stee (.
e e L LS. he eetettable ettleitt ebeve 1emer limit of detettica f or gew ttag reen 6egttweentellee.
a 35
a h
TABLE 1.1-1 (continued) dea 10h000 enKtIas posta liAtitpe
$f ninassajat (f flytet e(poet 700 mar ta Aas. Itaf Gait 0vS (f f ttdall. Stretal104 Of Att ettgasts I tafft i 3Am i fra 1 nas I la t nuaaf f a t are i
nav 1
Jim 12am m aattal C.
terticviete to 8 der k.18-16fel seteases 1.
forat a Ar t { w i t u i
fl 1
l l
1 l
I a LLD I i LLB l
a LLB f
1.
6,a.i a w m u.it.
I fi l
I I
I I
I 1.ast.e4 I i ear-ea I s.w.atl 1_
_ af IMf t1Af tMf tM t ialtaa
- o. Irit6. sei ies 1.
latal islaata attivit a i
ft i
f I
f 1
i e ilD i
a L18 l
a 110 l
2.
1 af iMf k28/18(f RM Limitna
(.
Som of testne. Part6celete (> 8 day half.14f el, sad f rit 6.e teleases 1.
fatal Artielte I
fl l
l 1
l I
f a itB i
e itB 1
e itB l
1.
1 af 1Mf R20 Liat t a.
Aas ornaa itMe aram/naart i
1 1
I I
f f
I e
i e
j e
l 1.
I af 1Mf tsa flat t a.
Aartart s Aasinan f ?.1 mraal i
1 i
f f
i f
f a
1 a
{J _
s.
-- i Am. e, man f is e a,-i l
1 I
I I
I I
I a
I a
I a
e i.e+ae, partie.iete, eae tritt it +ie are espresses es e tetet limit. See lie, t.
l 36
TABLE 1.1-1 (continued) saAIDwo00 WCttat powEt 5f All0m
$talwesuat Ef f Lutut 9170e1 foe ny to arrismia. teaf GA$t005 (f f tut' O. Smtlp4 Of ALL titt A515 t tatti i n i am t
tr > t 1,s cuanttat act I
new I
are f ath outaf f al C.
Particulate (> 8 dat half-life) Reidsses 1.
Cratt Actisite I
fi 1 attD 1 ettB t ettS I
<t t0 t
ettD t
1.4 11.6 1
e itB 1
- 1. 4 M 4 7.
Gratt Al alu Ar ti el t e I
fi l 4.91f.$ l d.9&f.5 l 1.14f.5 l 1.10E.4 l
tttD l 2.19f.%
l 1.07E &
I
- 1. 86f.%
1.
1 af tKf t24/lKf tt0 timitte C.
frititan Seleaset 1.
Tatal Emleats Activit e I
fl 1 etto f 1 AM.1 1 e itB 1 1 Mf.1 1 1 Mr.1 l
1.16f.2 i ? tir.P 1 d.?ar.7 l
?.
1 af 1Mf t2e/1Kitia timit ta
(.
Sea of ledine, Partlcolate (> e day half.) fe), and tritive teleases 1.
Tatal Artinite 1,
fi l attD 1 1 AM-1 1 1.4af.4 t l AM 1 0 % %f.1 f
1.ltf.2 1 2 Alt.2 1 4. 2at.2 j 2.
1 af 1Kfs2e timit a.
aan erna L 151 a m./ maar i l
1 1
e.no i 3.00 t
8.86 I e _M i
s co l
A.00 1
0.08 i
S.Ll 1.
1 af 1Ef tho _*.imi t Daaregr1 Ann Orr.an f ? A arant I
i 1
0 to 1 9.00 i S.to I G.to t
0.60 1
8.60 1
8.60 1
8.00 a.
t aa.ai inn e,ama f i t.e.r i
i r
i n.ne I a no I e_ no I a.ea i
n.no I
a.na e oa i
n.t sedi, particolate, and trit 6. lleits are neressed as a total 16.it.
See step t.
I 1
l l
l l
l I
I I
l 1
1 37
I
.l t
TABLE 1.1-1 (continued) teAlWOOD MUCLEAa POWtt 5f ail 0N 5tmlAmuat fif tutal etP0el f 0s naY ta Jtat. leal G45tous Eff tut 411 - vtut $fatt etLEAlt5 t tatti !
Jam i rta t man I ist Duaatral Are t
na, 1
Jtm 1244 cuaitrej f.
fiss6sa and Act6,atlee Gas teleases Em.111a fi e LLD t LLD e 110 ta.111a ft a ttB u 110 t LLD Em. llha ft i LLD t LLD t itD 1,.111 fl e itb a LLD e it$
1s.lis ft e itB e LtB e 110 trJha fi t LLB t tto e Ltu E *Ji ft e LtB a Lib c ttb__
Kr AF ft t LLD a 110 t ttS Kr Aa ft t itD e itD e 11D Ar.41 ft t 11D t LLD
< j(
Others (5pedfs) b.
lediae Releases 1.111 ft t it B e tio e #in f.112 ft t it0 e tto e (to 1.111 fi t 110 t 110 e 11 1.1 14 fi e itD e 118 i tt 9 1 111 ft t ttD t tta e itD Others (Spetilp) 38
TABLE 1.1-1 (continued) 6aa10wo00 inuttIas Powtr liai10m
$tatamuuat titLVtNT ttP0ef FOR AAY fB Dffisef t. Ita?
Ga$t0V$ [ff tutm1$. vtaf $1ACK ettta$t$
i tails I
.fut AoG 1 ur I 1re Duantist act i
now t
Dit leth Dtgl F.
f 6stlea and Activation 6et Seieas.s Ra.111a fl e (to e llD
< t! D e LLB
_E ttD e LtB e 110 e itB Ra. Ilia fi e LLD a t10 t LLD e t10 e t LD e tLD a ttB e 1LD 1a.915m fl t LtB e LLD e itD e LLD t LtB e LLD e LLD t LtD 1a,111 fl a LLD
- 1. 96[.3, 1.2 7f.2
- 1. E f f.2 1_ lif.2
- 1. 2 DE.2 13 t f.1 2.14[. y fi t ttD
- 1. o rf.1 e. ast.s t tu.i s.w.)
- 1. aDf.a 2 nf.1 a.ut.i a m. m fl a LLD e LLD t LtD e LLB e (LD t 110 e itD e ttD J,h ar.ag ft t iti t itD a tta e LLD e itD e LLD a itP e tin gr.A F fs i LE D e itD t LLD t tLD e
- to t itD e tLD t LtD g r.ag ft
._t itD e 110 t LLD
<ttD t it0 e 110 t itD e itD Ar.J t fi
- 6. 44f.1 e tf D 1.11 f.1 1.17f.1
- 6. 84f.1 1.11f.2
- 1. & t t.2 132f.2 Others ($peelfs)
I io..me..ie.,e.
fi e itD e itD
- 1. eaf.6 1.eaf.a
( ttD 4 3af.a a itD a Aar a t.i11 1 112 ft t LLD e LtD t LLD t LLD e LtB t itD t LtB t LLD 1.111 ft i itD e 110 e itD e 110 a tio 1.8 %f.4
_ a itD
- itS e tLD e LLD f itD
[.tM ft t t*
f L1D a LLD t LLD e (LD e itD e itD e itD 5
1.111 Others (S etif p) t 1
l l
l l
I l
l
?
39 I
D TABLE 1.1-1 (continued) taAIDw000 seJCLlat Powlt 5f att0m 5talansajat Ef fgutet tipoel FDe MY ta Jtad. ItR7 GAitov5 (f f tL4mf 5. vtaf 'f ACK attiasts I 12I1s 1 1AN i
ff A i
sER l lit DULEIf El APs l
MY l
3tm 12aa Dukat E R j n.
Particulate O 8 var half-16fel setesses nn. LJ fl e LtD e LLD e 110 I s.5%
ft t LLD e t iD e ( LD fa.%4 fi i ttD f LLB t ilD fa.5A ft t 110
( t ta a Lt0 M
ft
< it0 e itD
< LtB irJ4' fI tr.to*
fl v.as fi e LLD
< LLD e LLD to.131 fi e LLD e itD t LtB Am.llen f(
e LLD e LtD
- 110 f a.11a fi a itD e LLD a itB f t.116 ft t itD a 110 a 110 fa.117 ft t LLB
< i LD e itD am/t a.lae ft
< LLD e 110
., _uu f a. l ga fi e 110 e itD e itD Others (Specify)
- weltlag for analysis resvits. Data alli be preseated la en errata to the See6-Aanval tepert, l
i l
l l
40 1
t TABLE 1.1-1 (continued)
Dealtndooo anxttaa powta Station Simlaasdual tffLitthf tip0et foe July fB off tsf t. Itaf GA$t0US (ffLVtuf 5. vth! 51Act OtttA5tl I tatts I in I
aur.
I tr e t tra Staattal of t e
st9v i
Dr r fatatwinven[
m.
Perticolate (s 8 6ar half-life) Releases gen.id f4 i itD e tth
( LLB i LLD e tLD e LtB e LLB e LLD t s.51 ft i itB e itD e LtB e LLB e itD i ttD e itB e itD fe.it fi e it0 i LLD i 110 t LLD e LtB e LL i ttB C ttD f a.4A fl
( LLB
< L LD t itD e itD t LLD a Ltb e LtD t LtB f s h8 ft t L LD t 1t0 t itD t itD E LLD
< 110 it.At fi
< LLB tr.te f1 t LLD T.AA ft t LtB e 110 e ttD e LtB t ttB e itB i ttB e 110 k 1A1 ft t itB e it0 t LLD t ttD e itD e LtB e LLD e 110
&a.11De ft t LLB e itD t LLD t LLD t LLD 4 ilD 4 LLD f LLD f t.11A ft i ttD i itB
< itB e LLD t LLD e LLD e itD e LLD ts.116 fi
. LtB f LLD e LtB t LLD i itB e LLD i LLD e itB i t D_
fa.117 ft t itB i itD i 110 t LLD e LtD e Lib t itD a
kaft a. t ab fi e LtB
< LLD e itD -
t LLD e itB
< LLD e LtD i tte ts.144 ft t LLO t LtB 4 ttD t LLD t LLD e LLD i
e LtD t LLD Others (Specifr)
- 1. 4 X-6 1.431 6 Ev.106 Cl M^"
op e.
- Idatting for eaalytil reteltl
- Data =t11 k presented la an errata LS the $ set.Anaval Report.
41
c.
e TABLE 1.2-1
$4Af Dt400 84KLCAR POWER St&Ilou
$tMI Aa8EJAL (IflytNT ttP081 FOR MAY to JLad.1987 LIOVID (ffluth11 - SLMittion of ALL etttA$t$
l Emel11 l 3Am i
fft 1
MAR I ist OtAA T E t t APG l
MAY l
kaf
$2nd DuAnf[tl 1.
fission and AClivellem Pred, cts 1.
f atal Ar tinit e talaatad i
f6 1
I l
i 1
l t LtB l
e itD l
t itD l
2.
Avarama f aarmatratina talaated I ut6/mi I I
I l
l l
0 l
6 l
8 l
1.
I af loff tlo italit a.
Bartarle htm hade fl.1 meant 1
8 8
e h.
Barta rl s Ann Draan (1.8 nrant 1
8 0
e c.
a-1 tdhala hade f3 0 mrael 1
e o
e
-1 Anu Orman f 18.8 mram) 1 8
8 e
n.
a--
J.
Ifitl6e 1.
fatal Artivitu tal an t ed fi I
Averama faarmat rat ian Relaated ut i /a1 e LLD t itD e itD 1.
I af timit fif.) di/all 1
6 6
0 E.
Dissolved tentle Gasses 1.
f atal Artieliv talaated fl a LLD e Lib i LLD 2.
Amarama f aar aat. at i am Islaa ted uti/a1 i LLD t itD t itD 1.
I af timit f 2f.4 all/ml1 1
0 0
0_
L.
6 rest Alpha I.
f atal Attivits Enlaatad i
ft 1
I i
i l
1 e LtB 1
e itB I
i 110 2.
Ave rama f aarmat ralian talamaad l ufi/al l l
l l
l l
t LLD l
t 110 l
t (to M.
valm af tia la mata ta Ditcharma 1 11 tart I l
[
l l
i 4.84f a el I 4.12f * $6 1 6.11f a e6l IL valm af Bituttaa hier I Iltart i l
I I
I l 2.4Af a BA I 2.fif a 69 1 2.49 a og l r
l l
l I
I 42
TABLF 1.2-1 (continued) 04AlthdOOO seJCLEAA P9dtt 5f A110N SimlaweJat Ef flullel tippet (0e }Jt? TO D(ff ett.1987 L10ule tf f LVOill. Swest!0m of ALL DELEA5tl f 13:111 l JUL i
AllC 1
i*P I 1rd Ouattf t!
fjft I
taDY l
Off 14th Quattf t) 9.
f asstem and &ctivellte Predwitt t.
f at al At t l e t t e Emi a n taa i
ft 1 P.64f.% 1 2.t&f.1 1 1.14f.2 f I.&ef.2 l l _7 ef.2 1 g. 44f.1 1
&_7tf.1 t
1.1Et.y g
2.
Avaraae f aarantrattaa talantad l uf t tal l 1.61f.11! l.29f.9 I 6.09f-9 l
- 2. 40f.0 I 7.76f.9 I
- 4. 81f.9 l
2.90[.9 l
4.&4f.g l l
1.
I a f 16f f k'J t talt t a.
Quartarle mais hade fl.1 mrant 1
0_M e.M G.00 0.M e.01 0.81 0.00 8.02 h.
Quart arlo Aan Oraan (L.0 areal 1
9.00 0.00 0.00 0 00 0.01 9.60 8.00 9.61 e.
Annual Whala Rade f 1.8 mrant 1
0.00 0.60 0.00 0.00 0.01 8.00 e.D0 a nl d.
Annual Ane Graan f 18.0 armai 1
0.00 0.00 e.60
- e. no 0.00 e eI a.00 e.et J.
Ifillum 1.
fatal Activlte Raimatad ft
- 2. 0M.1
- 4. 57f.1 1 2.14f ea 1.50f ea 7_41t h f. itJ e l 1.B Ff el 1.77{gL 2.
Averans f aarent ralian Ralmated ufi/m1 R. ?M.a 4.1M.7 ! 1.06[4 1.1M. 7 1.29[ L y t.4 7.99f.6
%.4 3R 1.
1 af timit fif.1 JI/all 1
6 to 0.91 I 0.84 0 no 0.11 0.17 8.77 0.t8 E.
D6ssalved hobie Esses l.
f atal Ar ti oits Relam ^=a ti e itD e LLD e itB e tLD e itB e 110 a 110 t tLD 2_
Amaraas f aar amt rat t aa talantad dt/mi i LLB e tib c LLO e 11D t ttD e itD e tiO a ttD 1_
1 af Llat t (2f.4 Ji /mi t 1
G.M G. 80 4 ha A.M A &&
8 Ga A_60 9.60.
L.
Gr$65 Alpha 1.
f atal attivit e talaated I
ft 1 2.21f.1 I t LLB f i ttD 1 7.21f.1 I i 110 i
e itD t 1 tFf.4 1
1.g 7f.4 _
e LtB I
S.42f.11 l
R.421.11 2.
A.a rama f aarmat rat t aa tal amana l di/m1 l 1.htf.4 l e itD l t itB !
- 1. tel.4 l < 110 l
se. Wai m af Limaid Watta ta Distkarna l litart I %.Rif ee f 1.2Ve4 t 4.e tf ee i
- 1. tM e ? 1 4.11E s k I 4.111 6 f 6.9sf ee i 1.44f e 7 l al. Veln af Bilattan warar i 11 tart t 2.34fet i 2.16fet f 2.20 fat i 1 naret 1 7.2&f at l 2.14f 9 t 2.14fet i 6,44f at l 43
a I'n TABLE 1.2-1 (continued) saa!0h400 seJCitAa Mbit 5fA~I0m
$(m1AssaAt Ef f tutN1 t(Pont 700 n&Y ta Aad. Ita7 t! QUID (f f tUthfl t tan tit i lam i fra i saa I tit Duaatta!
APs t
nav i
Jtas 12.4 maa t t a l S.
Ligeld Ef f tveats t,m.
Et ir.ta=
fi f>M fi
< LLD e t to a LLD fM fi e LLB e LtB e LLB f t.lla fl e L LD i LLD
< 110 f t.111 fl e itD e L LD a LtB ft.117 ft
< 11D a tio a ttD f.131 ft t itD t LLD
< Lto I.111 fi i LLB e tio e itD RA/LA-lad fi e LLD e itD e itD 1a.111 ft a LLB e LLD e itD Ra.1 H fi e itD e 110 e sto Olbrs (SpetlI )
J
- tsalting for analysis results - Data vill be presented la em j
errata to tk Semi.4aaeal beteet.
l l
l l
l I
l l
i I
I 44 1
~
TABLE 1.2-1 (continued)
DAAlth000 ARJCttat pedt 5f Aflou
$tMIAascat trrtutNT tip0tf FOR Juty to Offfmf a. itaf LIQUID (f ftutw15 I talft t Jut I
AUG I
UP f ird DuAAf f al Df f 1
edW l
Df f 14th Dtaa f f t l
- o. Liws (filwats it.no ft e (tB e
t,.ee fi
< 110 e
fa.Sa ft 7.adf.i
- 2. Sef.1 1.82f.2 1.29f.2
- 1. 21f. 2
%. %ef.1
- 1. Pu.1 2.1 tl.2 f a.e.a fi e L t_B
- 1. Sif.1
- 2. 2 &f.4 2 Laf.4
- 2. La f.4
- 1. 7 7f.4 6.alf.1 7 aM.4 f t.114 fl
< LLD e LLD e LLD e LLD e LLD t LLD e ttD
< 110 ft.116 fl i ttB a LLD E L1D i LLD R _ daf 4
< 1t0 e itD a. def 4 ft.117 fi t itD
- 1. htf i S 71f 4 2_ laf.%
1 gef.a 1.111 ft a ttB d.71f 4
& _ a&f.4 A tif-d 1.dif.1
<up_ y t4 1_ nas.1 f.t11 ft i LLB e itD e itD e LLD t LtD 4.14t 4
- 1. %g.4
- 1. h31.4 ha/t a-len fl e LLB e LtB 1.51f.4 1 11f i
- 1. 71f.4 e LtB
%.t.8f 4
- 1. 79f. 4 1a.111 fi e itD e itD e 110 t LLD A.22f.S t itD
< itB a 77E.h ta.11%
fl e itD a ttB d itD e itD e itD e itD t itB e LLB Others 15pecifyl
% 54 Cl 3.661 4 2.121 3 2.4X.3
- 2. 56t.3 3.811 3 t.let.3 6.718 3 he.24 Cl 1.89t.$
1.14t.4 1.37t.4 2.32t.4 4.91t.4 1.590 3
- 2. 3 t t.3 Sr.42 Cl
- 1. l et-5 8.14t.5 Fe.59 Cl 2.10t.S
- 2. I M.S 7.1M.4 7.lM 4 Er 44 Cl 3.94t.S 3.94b5 Ov.Its C6 I.9 M.S 1.9 M.6 2r.97 Cl 1.071 4 1.071 4 wetting for saa1 sis results. Data vill be preseeted la an 7
errata to the Seat-Anaval Report.
l l
45
}
s 4
4 TABLE 2.0-1 taAlet400 IEJCttAA MWit $ fallen Stmlasuuat (ff tutui tip00f f48 isar ta Amst. test 50tt0 RA0!JClivt Isallt sesetn U29. UM ytaa 1987 Dispostt6en of Meterial 3
suff f ehattriat taa. flata f ama
- talist isina Ammat saada af f r=amart nettinattaa valine par hiammat fit I turian par ihlammat een kadueste shipmeant evenag the aseths of my ead June, 1987.
4 e
l _
1
, [ s' N O
g t,
A i s.
4,
!ll
!J sesitav 10ful 6 ft3 0 Cl 5
I-I i
46 l
TABLE 2.0-1 (continued)
MAltw300 uuCLEAe,guta statteu
$(ntagenAAL (ffLWN1 atPtst fee Jutt to Mtiaefa. IM) 50Lto anotenClivt inallt semin 11G'.12/11 y( Aa. lMF et..iii., =t.,i.i 3
haTf f heit t tat ima. flata fmaa
'talieifaina Amat saada af f rantnari Da a t I nat i an Valm Per ih iameni ift i fariea Par ine ansat
=
- t..ni, ni...
t6.
sm..e 2.i, tu, eu-,.
B e
leu 1MLY 101ALS S It3 9 Ci 47
Figure 3.1-1 Estimated Cumulative Gama Dose (in mrem) from the Braidwood Station for the period 4
4ET January-December 1987
- J$$
5 N l}
Isopleth Labels
'u 7
l Small figure - multiply by 10 8 Large figure - multiply by 10-4 4[r 65,X y
f T_.
t, ORwo 25 I
m's 5
\\
10 E
so 9_ _
p 5
55
\\..
l p* D PS 80 od
,,,,,,g,,
00 gig 0
g Wilmingion Cool City' 0 id" d Wolon Won' eno WD 100 o ye,en.
61 0 Gordn 25
+
owl 9II
- 11 8 -
g
'\\
2.s
\\
x%
s
?....?
'P
'p 2pmi
,g
j-Figure 3.1-2 Estimated Total Concentrations (in pCi/m3) p of Noble Gases from the Braidwood Station for the period January-December 1987
- 4"" %9 Isopleth Labels 50 Small figure - multiply by 10-4 55 l
g Large figure - multiply by 10-5 5001 100 I
0
~' g5 80 9
? *i 50 55 o
\\
f.
50
/
e ONPS j
80 "I'
so wo hew l
Wsimi f
Cool City
- 1 0
(
l y,,,,,
B wood waren
,no m
750
(
[
250 I
p
- Go or
/
+i**
s r
\\
rNs l
/
~
Dee 25 1
o
)!
\\
O 5
10 15 2O rni 49 i.....
i i
Figure 3.1-3 3
Estimated Total Concentrations (in pCi/m )
.c of Iodine from the Braidwood Station for jgsC)p the period January-December 1987 d? jig Le ll50D Isopleth Labels Small figure - multiply by 10-8 33 g
Large figure - multiply by 10-9 h
,200 ( 100
~
1 E0 jff x
=
80 9-2 ai
/
Q+ :rs=**
oNPS 80 3:
poi' 50 Wdmi on I
h cooi ( Ity erai a
roy uan r
(
.o
- ~
100 l
0G dne 4i ir_
/
]
f
(
j"
=-
,,si o n.m l
15 c.
0...
5 10 15 20 mi 50 i
i
l l
l Figure 3.1-4 3
Estimated Total Concentrations (in pCi/m ) of Particulate Matter from the Braidwood Station avaihet for the period January-December 1987 RtL"d 74 "'
I/)
2 25 Isopleth Labels
-c 50 Small figure - multiply by 10-09 33 Large figure - multiply by 10-10 l
N l
200 d
V I-i j
100 k
25 25 9
? *i
/
10 E l'a 8, 1
DHPS j
j 80 -
V wist e.' b nw
,w 25 Wilmmgtor ool city 250 I
o 25 8i d
- 100 **y' Woron y,,,,,,
i
'*e o
o vw a.
u ord N,
\\
i 5
/
tr As I
Dwipt 10 4r f
o cows 0...
5 10 15 20 mi 51 i
i i
TABLE 3.1-1 PRAIDWOOD UNI? ONE 1987 AN40*'. REPORT
.M DOSES RESULTING FROM AIRBORNE RELEASES PERIOD 0F
- iASE - 01/01/07 TO 12/31/87 CALCULATED 02/11/88 1ST 2ND 3RD 4TH TYPE QUARTER QUARTER QUARTER QUARTER ANNUAL JAN-MAR APR-JUN JUL-SEP OCT-DEC OAMMA AIR 0.00E-01 0.00E-01 5 56E-07 6 19E-04 6.74E-06 (MRAD)
(
)
(
)
(W
)
(W
)
(W
)
DETA AIR 0 00E-01 0.00E-01 1.22E-06 1.37E-t5 1 50E-05 (NRAD)
(
(
)
(W
)
(W
)
(W
)
TOT. 90DY 0.00E 0 00E-01 2.40E-07
- 2. 8 8 E -(16 3.14E-06 (MREM)
(
)
(
)
(W
)
(W
)
(W
)
SKIN 0.00E-01 0.00E-01 1.05E-06 1 15E-05 1.24E-05 (MREM)
(
)
(
)
(W
)
(W (W
)
ORGAN 0.00E-01 0.00E-01 2.30E-05 1.10E-05 3 40E-05 (MtEn>
(
)
(
)
(E
)
(E
)
(E
)
THYR 0!D THYROID THYROID THIS IS A W PORT FOR THE CALENDAR YEAR 1987 COMPLIANCE STATUS - 10 CFR 50 APP. I l
I 0F APP !. -------------
QTRLY 1ST OTR 2ND OTR 3RD OTR 4TH QTR YRLY I 0F OBJ JAN-MAR ePR-JUN JUL-SEP OCT-NOV OBJ APP.
SAMMA AIR (MRAD) 50 00.00 00.00 0 00 0.00 10 0
- 0. 0' DETA AIR (MRAD) 10.0 00 00 00.00 0 00 0 00 20.0 0.0-TOT. BODY (MREM) 2.5 00.00 00.00 0.00 0.00 50 00 SKIN (MREM) 7.5 00.00 00.00 0 00 0 00 15 0 0.0 ORGAN (MREM) 7.5 00.00 00.00 0 00 0 00 15.0 0.0 THYROID THYROID THYROI RESULTS BASED UPON ODCM REVISION 11 UPDATE CS118 FEBRUARY 1986
.i l
52
l J6,
TABLE 3.2-1 BRAlowOOD UNIT ONE 1987 ANNUAL REPORT MAXIMUM DOSES (MREM) RESULTING FROM LIOUID EFFLUENTS PERIOD OF RELEASE - 01/01/87 TO 12/31/87 CALCULATED 04/12/88 IST 2ND 3RD 4TH DOSE TYPE QUARTER QUARTER OUARTER QUARTER ANNUAL JAN-MAR APR-JUN JUL-SEP OCT-DEC TOTAL 0.00E-01 0.00E-01 2.55E-05 3.38E-04 3.63E-04 BODY INTERNAL 0.00E-01 0.00E-01 1.61E-04 4.94E-04 6.49E-04 ORGAN GI-LLI THYR 010 GI-LLI THIS IS A REPORT FOR THE CALENDAR YEAR 1987 COMPLI ANCE STATUS - 10 CPR 50 APP. I
- - - -- - - - - - - - - - % O F A P P !. - - - -- - - - - - - - -
QTRLY 1ST QTR 2ND QTR 3RD OTR 4TH QTR YRLY
% OF OBJ JAN-MAR APR-JUN JUL-SEP OCT-N0V OBJ APP.I TOTAL 800Y (MREM) 1.5 00.00 00.00 0.00 0.02 3.0 0.01 CRIT. ORGAN (MREM) 5.0 00.00 00.00 0.00 0.01 10.0 0.01 GI-LLI THYROID GI-LLI RESULTS BASED UPON 00CM REVISION 11 UPDATE CS118 FEBRUARY 1986 53
BRAIDWOOD STATION Figure 5.0-1 Nearsite and Offsite Air Sampling and TLD Locations F.
e
~
$ttlieced i
T 20 t
39 e 21 6 e sulowooo
/ odley STATION "N
C Steceflfle toute tot en
- s
,seriew
-[ Esses d
El-I1 we og e
l Seeth vanigte.
SCALE l
Air Samplers L _1
/
P f
A ms l
1 - Braidwood 6 - Godley 2 - Custer Park 19 - Nearsite Northwest l
3 - County Line Road 20 - Nearsite North i'
4 - Essex 21 - Nearsite Northeast 5 - Gardner l
l-TLDs l
l Same as air samplers plus a sufficient number of additional dosimeters placed l
near the site and near five (5) miles to assure that one dosimeter is located l
at each range in each of the sixteen (16) meteorological sectors.
l 54
BRAIDWOOD STATION Figure 5.0-2 Inner Ring TLD Locations l
& *4 l
5 iT$
\\
IL 113
/
f e1021
- 122 101 2
'4
.i 1
iu'i';/;li4?'i.=>
1136 2
- 11 1136 1 162
\\
v'8 112 2 Ceco titrence 112 113e.2 1116.th III*
111b.1 1116 1 Braidwood Station
/
- /
\\ )
- 1.
+f r
c
, no.
//
s 3
e 1,.7.1 liti:
'H1 2
8 NS00W 10 1 e
e i.e a.s "
55 e
i
BRAfDWOOD STATION Figure 5.0-3 Outer Ring TLD Locations N
26-2 20f; h ad
\\
e 2'S '
2o31 i
Braidwood 2. g IL113
<g.:
t e21 aos.
e 213 1 L'i8
/
e WBraidwood I
odf*y Station
/<,,
g
@Y E
mt I
=
aos.
8+
Bracoville 8
a,s.,'l+
w County Line Rd.
212 3 37l B3 e att.t s
Gardner ace a a Essex e l 1
n Rice Rd.
d um a
South tio t 20s 1 2i&2 Wilmington 8
1 3
3 4
S. m
'8 56
BRAIDWOOD STATION Figure 5.0-4 Environmental Radiological Monitoring Locations i
7 I
et Breidwood e2 Custer Park 03 County Line Reed
.. e e
s 04 Essex OS Gardner 86 Godley 97 Kenkekse River Monitoring genaenes Site ti (upstrees) 10 Konkokee River Monitoring gre w e
. m..e, it "3
' '8 31te SS (downetrese) 11 Morris rare T
.e 13 Breldweed City Mail Well
\\.
14 Pinnick rer.
a is.iret r.r.
e,
~-
/ /
!!I;;it.?;".rer.
~
a is ure's r.r 19 Neer Site Northwest 28 Neer Site North v
S,ecenne 21 Near Site Northeast
- 9 a
Cevaty Line me s
e.
. se,ees, Esses n
m.coad's 1
~
Seven w*n.neien
,/
l
. =
nn:smesummk=:demud==d
? ! !
?
?
f
?"
l 57
BRAIDWOOO 5fAfl0N Table 5.0-1 ENylRONMENTAL RADIOLOGICAL blTURING 5AMPLING SITES MEDIA t
i T
4 O
E s
t U
1 b
d 8
5
~
t u
~
3 ~e 4 :.
3 5
2, 2,
y y
1 3
6 m
g 6
Loc ation Location E # 7 0 5
1 E 2 J
A I
~
v a
e Code Typea Location a
80 01 eraidwood 1
I 8D-02 Custer Park I
X BD-03 C
County Line Road I
I 80-04 Essen I
X B0-05 Gardner X
X 80-06 Godley I
I 8 D-07 C
Upstream at $1te No.1 I
I X
X BD-08 C
Braidwood Intate Pipe, Site No. 3 I
80-09 Braidwood Distnarge Pipe, Site No. 4 I
80-10 Downstream at Site No. 5 I
I I
I 80 11 Morris f are I
I I
I 1
80-12 C
Goodwin Fars I
1 1
I I
80-13 Braldwood City Hall X
80-14 Pinnick Fara X
B0-15 Girot Fara X
80-16 Clark Fara X
80-18 81ros Fara X
80-19 nearsite hw I
I 8D-20 hearsite N X
X 80 21 Nearsite NE I
I l
80-17 frotter's Fara X
SD-101 1,2 I
through I
80-116-1,2 8D 201 1,2 through I
80-216-1,2 a Control (Dackground) locations are indicated by a 'C' in this column. All otner locations are indicators.
1
r e
BRAIDWOOD STATION TABLE 5.0-2 ENVIRONMENTAL RADIOLOGIAL MONITORING PROGR#1, SAMPLING LOCATIONS 1.
AIR SAMPLERS Distance Direction Site Codea Location (miles)
(*)
BD-01 a.
Braidwood
- 1. 5 34 80-02 b.
Custer Park
- 5. 0 80 B0-03 (C) c.
County Line Road 6.2 12 0 B0-04 d.
Essex
- 4. 8 165 BD-05 e.
Gardner
- 5. 5 225 BD-06 f.
Godley
- 0. 5 245 2.
TLDs a.
Same as % 1.
b.
Special TLD Saglers Distance Direction
_evised Site Codeb Previous Site Code (miles)
(*)
R BD-101-1 BD-102-1
- 0. 6 9
l BD-101-2 BD-102-2 0.62 10 BD-102-1 BD-103-1
- 1. 2 32 i
8D-102-2 BD-103-2 1.1 33 BD-104-1,2 Same
- 0. 7 76 BD-105-1,2 Same
- 1. 5 85 l
BD-106-1,2 Same
- 1. 7 120 l
B0-107-1,2 Same
?.0 135 BD-108-1,2 Same
- 2. 0 148 BD-109-1 Same
- 2. 5 190 BD-110-1,2 Same
- 1. 8 205 l
BD-111a-1 80-111-1
- 1. 4 218 BD-111a-2 BD-111-2
- 1. 4 218.5 l
BD-111b-1 80-112-1 1.1 234 BD-111b-2 80-112-2 1.1 235 BD-112-1 BD-113-1
- 0. 7 252 8D-112-2 B0-113-2
- 0. 7 253 BD-113a-1 80-114-1
- 0. 5 263 BD-113a-2 80-114-2
- 0. 5 264 B D-113b-1 BD-115-1
- 0. 4 237 I
o BD-113b-2 BD-115-2
- 0. 4 276 Control (reference) locations are denoted by a "C" after site code.
All 3
other locations are indicator, l
b Effective August 1, 1985.
59
BRAIDWOOD STATION Table 5.0-2 (continued)
ENVIRONMENTAL f1ADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS U
2.
TLDs (continued) b.
Special TLD Samplers (continued)
Distance Direction Revised Site Codeb Previous Site Code (miles)
(*)
80-114-1 B0-116-1 0.4 294 80-114-2 80-116-2 0.4 298 80-116-1 B0-101-1 0.4 342 B0-116-2 B0-101-2 0.5 346 BD-201-1,2 Same 4.2 11 B0-202-1,2 Same 4.8 20 80-203-1 Same 4.9 45 B0-204-1,2 Same 4.3 67 8D-205-1 Same 4.0 86 80-206-1,2 Same 4.5 112 B0-207-1,2 Same 4.1 113 BD-208-1,2 Same 4.5 155 BD-209-1 Same 4.8 185 BD-210-1,2 Same 4.9 195 80-211-1 Same 4.8 220 80-212-1,2 Same 4.7 240 q
BD-213-1,2 Same 4.5 260 80-214-1,2 Same 4.3 287 80-215-1 Same 4.5 315 BD-216-1,2 Same 4.4 330 3.
MILK Distance Direction Site Codea Location (miles)
(*)
80-11 a.
Morris Farm 2.4 95 BD-12 (C) b.
Goodwin Farm 7.7 67 80-17 c.
Trotter's Farm 4.8 315 80-18 d.
Biros Farm 10.5 270
~ '
l 4.
PRECIPITATION
)
Same as No. 3 I
a Control (reference) Scations are denoted by a "C" af ter the site code.
All other locations are indicators.
b Effective August 1, 1985.
60 o
BRAIDWOOD STATION Table 5.0-2 (continued)
ENVIRONMENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS 5.
VEGETABLES Distance Direction S_ite Code Location (miles)
(*)
BD-14 a.
Pinnick Farm 1.8 360 80-15 b.
Girot Farm 1.4 360 BD-16 c.
Clark Farm 2.3 78 6.
CATTLEFEED AND GRASS Same as No. 3.
7.
WELL WATER Distance Direction
(
Site Code Location (miles)
(*)
BD-13 Braidwood City Hall 1.7 30 L
8.
SURFACE WATER I
Distance Direction Site Code Location (miles)
(*)
BD-07(C)
Upstream 5.4 88 BD-10 Downstream at Site No. 5 5.0 76 9.
COOLING WATER Distance Direction Site Codea Location (miles)
(*)
BD-08 (C) a.
Braidwood intake pipe /
5.0 82 Site No. 3 BD-09 b.
Braidwood discharge 5.0 80 pipe / Site No. 4 a Control (reference) locations are denoted by a "C" af ter the site code.
All other locations are indicators.
61 1
BRAIDWOOD STATION Table 5.0-2 (continued)
ENVIRONMENTAL RADIOLOGIAL MONITORING PROGRAM, SAMPLING LOCATIONS
- 10. FISH Distance Direction Site Code Location (miles)
(*)
BD-07(C)
Kankakee River Upstream 5.4 88 B0-10 Kankakee River Monitoring 5.0 76 l
Site No. 5
- 11. A00ATIC PLANTS Distance Direction a
Location (miles)
(*)
Site Code BD-07(C)
Upstream at Site No.1 5.4 88 BD-10 Downstream at Site No. 5 5.0 76 12.
BOTTOM SEDIMENTS Same as No. 11.
Control (reference) locations are denoted by a "C" after the site code.
All a
other locations are indicators.
62 i
uRAIDW000 STATI088 TABLE 5.0-2 (continued)
ENVIRONMENTAL RADIOLOGICAL MUNITORING Pit 0GNAM SAMPLE COLLECTION AND ANALYSLS Location Collectfon Type of Frequency Sample Media Lode =
5ste Frequency Analysts of Analysts Remarks 1.
Airborne 80-41 Braidwood Continuous Gross beta Weekly
> all samples.
Particulates 80-02 Custer Park operation Gamma Isot Quarterly on quarterly composttes from esca location.
80-03 (C)
County Line acad for a week Sr-89.-90 quarterly On quarterly composstes from e.ca location.
80-04 Essen t
80-05 Garener Non-routine Reporting ieveIs 80-06 Godley CS-134 10. Cs-137 20 pct /m3 80-19 Nearsite NW BD-20 Nearsite Il BD-21 Nearsite NE 2.
Airborne Same as 1.
Cont tn.ws I-131 utweekly
> all samples.
Iod1ne operation for two Non-routtne Neporting leveis weeks U.9 PCl/m3 c) 3.
TLD Same as 1.
Quarter?y Gamma Quarterly Two sets of all AP locations. One set read quarterly. Second set reae If regwaree 8D-101 1.2 Inner Ring by Commonwealth Eelsen. At otner loca-tions, all sets remo t.varterly, Menlaum 102 1.2 104 1.2 of two TLDs per set.
threugh 106 1.2 109 110 1.2 lila 1.2 Illt 1.2 112 1.2 113a 1.2 1136 1.2 114 1.2 116 1.2 8D-201 1.2 Outer Ring 202 1.2 203 1 204 1.2 205 1 206 1.2 207 1.2 208 1.?
209 1
- Control (reference) locations are denoted by a "C" in this column. All otner locations are indicators.
b Average concentration over calendar quarter.
IRAIDWOOO STATI0ll TAetE 5.0-2 (continued)
EnvlR0esCETAI. RADIOLOGICAL MOIIITORIssG PROGtApl. WIPLE CutLECTION Amp AmALY5E5 tocation Collection Type of Frequency
$ampts piedle code =
dite Fre?macy
. Analysis of Analysts samarks 4.
TLDs (continued) 80.-210 1.2 Outer Ring (continut1) 211 212 1.2 213 1.2 214 1.2 215 216 1.2 5.
Milk 8D-11 Morris Farm Weekly:
1-131 Weekly in all samples. LLD:
1.0 pct /I.
80-12 (C)
Cooewin Fara May through Gamma isot.
Monthly
@ montnly composttes.
80 17 Trotter's Farm October Sr-89.90 Monthly th monthly composttes.
8D-18 8tros Fare Monthly:
1-131 Monthly On all samples. LLD:
1.0 pct /I.
hovester Gamma Isot.
Montnly
> all samples.
thre*agh Sr-89.90 Monthly on all samples.
m Aprt1 4
mon-routine steporting Levels
- I-13' 3. Cs-134 60. Cs-137 70. sa.te-lev 300 pCl/l
,m 6.
Prectpttation Sa.se as 5.
Monthly Gross oeta pontnly
@ all samples.
Trittwo
@arterly
@ quarterly campasite from esca locassen.
Gamma Isot Quarterly Ori que'terly composite from esca Iecatsen.
5r-69.-90 Quarterly On guarterly compostte from eacn locStian.
7.
Vegetables 80-14 Ptnnick Fare Annually Gross beta Annually Four sartettes (at st one green leafy 80-15 Strot Fora Gamma Ifot Annually vec,tiple) from eaci.
- stion as avastante 80-16 derta Fare V -89.-90 Annually at marvest. (I-131 - green leafy I-131 Arrwally vegetasies.)
8.
Cattle Feed Same as 5.
@arterly Gross beta Quarterly Grass: Sw - May to octecer.
Gamma Isot Quarterly Feee: usater - seovemoer to April.
and Gran i
Sr-89.-90
@ eterly l
S.
Well Water.
80-13 Braidwood City Hall ideekly Gross beta Quarterly
@ all samples.
Offstte Well Tritium Querterly Gamma Isot Quarterly Sr-89.-90 Quarterly All other locations are tnetcators.
, Control (reference) lo:sticas are denoted by a "C" in this column.
Avtrage Concentration ever Caleeder quarter.
ORAIDWOOO STATION TABLE 5.0-2 (continued) i ENVIRONMENTAL RAOIOLOGICAL MoulTORIns rit0WtAM. SAMPLE COLLECTION Ago AWYSES tocation Collection Type rf frequency Samole Media code =
5ste Frequency Analysts of Analysts meneras j
- 10. Su-face Water 80-07(C)
IL.akakee River Weekly Gross beta Weekly 03 all samples.
(upstream)
Trttlum Cuarterly Quarteely analysis of weekly congesetes.
80-10 Kantakee Rtver Gassna Isot Monthly on all samples.
Monttoring Site Sr-89.-90 Quarterly Quarterly analysts of weetly composites.
80s. 5 (townstream)
Non-routtne hepert ang ieveIst
($ee feetnote *c.")
i
- 11. Cooling Water 80-08(C)
Intake pipe Weekly Gross beta Weekly es all samples.
I 60-09 Discharge pipe Trttlum Men'hly peonthly analysts of eseemly composttes.
Gamune Isot Monthly Monthly analysts of weetly compostles, c1 Sr-89.-90 Monthly Montaly analysts of weekly causesstes.
- 12. Fish BC-07(C) l* stream Three times Gross beta Three times From Kantatee utver seonttoring Site see. 5; a year.
Gamma Isot a year.
on selete porttons only; et least tuo i
80-10 Dow.estream Sr-89.-93 species.
hon coutine deporttag tevelst sei.54 3:10 ; Fe-59 Isled; Co-Se Jalud-8 Co-601s10 - 2n-65 2s10 ; Cs-13a IstoI; 8
8 3 pct /s, wet wetgat.)
Cs-137 2s10 i
- 13. Aquatic Piants 8D-07(C)
Ibstream Three times Gross beta Three times if avallante.
BD-10 Downstress a year if
(,anana Isot a year available 14.
Sotton Same as 13.
Three times Gross beta Three times Ost all samples.
Sediments a year r.;,amma Isot a year i
- Control (reference) locations are eenotee by a "C' In this column. All other locations are indtaators.
, Avera9e qoncentration over calender quarter.
3 2
2 2
2 2
' H-3 2x10*. Mn-54 1m10. Fe-591:10. Co-!rl (wi10. Co-60 2x10. In-65 2x10. Zr-le-95 4s10.1-131 2. Cs-134 30. Cs-137 50, sa-Ls-1401:102 oct/l.
~
RAlm STAT 10s:
TABLE 5.0-2 (continud)
ENY.A08stENTAL RADIOLOGICAL Montf(Ming PROGt#1. 54tPLE COLLECTION AnD ANALYSE 5 (continued)
Locatic..
Collection Type of Frequency Sample Media
__ Co. tea 51te Frequency Arslysis of Malysis menar6 s s.
Enumeration by a door-Annually aering yasing wesen.
- 15. Detry Census a.
$1te boundary to 2 miles to-door or equivalent counting technique.
b.
Enumeration by using Annually Ouring yazing season.
b.
2 miles to 5 miles referenced In'ormation from county artcultural agents or other reliable sources.
c.
Inquire as to feeding Annually (naring yarsag seasoa.
C.
At dalries listed in Item 5.
practices:
(1) Pasture only.
(2) Feed and chop only.
(3) Pasture and feed; if both, ask f armer to estimate f rar* ton of food from pasture:
<255,25-505, 50-755, or >751.
2
- 16. hea est in all 16 sectors.
Annually y
Destdence Census l
l hm
Table 5.0-3 ENVIR01840 ITAL RADIOLOGICAL MONITORING PROGUut O'JARTERLY SLpetARY meme of fact 11ty Bralesood Nuclear Power Station Docket No.
50-456, 50-457 Location of Fact 11ty Bracewflie Illinois Reporting Period 1st Quarter 1987 (county. 5 tate) l Indicator Location with Highest Control S qie Type and Locations Quarterly Mean Locations Number of 1)re Number of Means Mean feeana Non-routtne (Un1ts)
Analyses LLD Ran9e Location Range Range Results Af r Particulates Gross Beta 108 0.01 0.027 (96/96)
B0-19. Nearsite W 0.029 (12/12) 0.026 (12/123 0
(pCf/m3)
(0.013-0.043) 0.3 et 9 314*
(0.013-0.041)
(0.013-0.035)
Gaussa Spec.
9 0.01 4LD
<LLD 0
Sr-89 9
0.01 4LD
<LLD 0
$r-90 9
0.01 4LD
<tLD 0
Afrborne Iodine 1-131 108 0.07 4LD
<tLD 0
3 (pct /m )
Gaussa Background Gauuna Dose 9
3.0 14.0 (8/8)
B0-05 Gardner 17.1 (1/1) 13.3 (1/1) 0 (TLDs) (udt/Qtr.)
(12.4-17.1) 5.5 at 9 225*
Milt 1-131 12 0.5 4LD 4LD 0
fpCf/1)
Gessna spec.
12 Cs-134 5.0 ALD 4LD 0
<LLD 0
Cs-137 5.0
< LLC
<LLD 0
} Other Gausses 10.0 (LD Sr-89 12 10
<LLD
<LLD 0
Sr-90 12 2
2.5 (3/6) 80-11. 14 orris Fars 2.5 (2/3) 2.4 (2/6) 0 (2.4-2.6) 2.4 et 9 95*
(2.4-3.6)
(2.0-2.7) 0 SD-17. Trotter's Detry 2.5 (1/3) 4.8 et 9 315*
Precipitation Gross Beta 8
<11.7 19.6 (3/6)
BD-12. Goodwin Faru 49.7 (1/2) 49.7 (1/2) 0 (16.8-49.7) 7.7 of 9 67*
Gausna Spec.
4 20
<LLD
<LLD 0
Trftfum 4
200
<LLD (LLD 0
Sr-89 4
10
<LLD
<LLD 0
Sr-90 4
2
<LLD
<LLD 0
Table 5.0-3 (c ntinued)
ENVIRONENTAL RADIOLOGICAL MONITORING PROGRAM QUARTERLY StestARY Neme of Factitty Braidwood Nuclear Power Station Docket No.
50-456. 50-457 Location of Factitty precevtile, 1111 nots Reporting Period 1st Quart 9 1987 (County, State) lNummerof Indicator Location with Highest ContM1 Sasple Type and-Locations Quarterly Mean Locatfoes TyM member of Meana Mean Meena Non-routine (Units)
Analyses LLD Range tocation Range Range Results i
Cooling Water Gross Beta 25 1.3 4.3 (13/13) 8D-09. Discharge Pipe 4.3(13/13) 2.2 (12/13) 0 (pC1/1)
(2.2-5.4)
P.Statton (2.2-5.41 (1.8-3.3)
Gasma Spec.
6 Cs-134 10
<LLD
<tLD 0
<LLD 0
Cs-137 10
<LLD
<LLD 0
Other Gammes 20
<LLD Trftium 6
200 (LLD
<LLD 0
<LLD 0
Sr-89 6
10
<tLD Sr-90 6
2
<LLD (LLD 0
g Surface Water Gross Beta 26 1.3 2.0 (12/13) 80-07. Kankekee River 2.1 (13/13) 2.1 (13/13) 0 (ptt/1)
(1.4-2.8)
Upstream, 5.5 at 8 (1.3-2.8)
(1.3-2.8) 85*
Gamma Spec.
6
<LLD 0
Cs-1'44 10
<LLD 0
Other Ws 15
<tLD
<LLD 0
Tritfum 2
200
<LLD
<LLD 0
Sr-89 2
10
<LLD
<LLD 0
Sr-90 2
2
<LLD
<LLD 0
w,
Table 5.0-3 (continued)
ENtIR01sENTAL RADIOLOGICAL sq0NIMING pt0GANI QUARTERLY SLSOMAY '
Name of Fact 11ty Bralemood leuclear power Station pocket No.
50-456. 50-457 Location of Facility Orac-v111e, 1111 nets Reporting period 1st Quarter 1967 (County. State)
Indicater Location with Highest Control Sample Type and Locatic7s Quarterly seean
.ecations semeer of Type Number of stearia yteen steena lion-routine (Units)
Analyses LLD Range Location Range Range Results Well Water Gross Beta 1
2.2 10.8 (1/1) 90 *3. Bretemood City 10.8 (1/1)
None 0
(pCf/1)
Hall Well,1.7 et 9 30' Gesuma Spec.
1 Cs-134 10 4LD Neee O
Cs-137 10 4LD Isene 0
Other Gesumes 20 4LD None 0
m Ilone 0
T:Itium 1
200 4LD Sr-89 1
10
<tLD Isone 0
Isone O
Sr-90 1
2 4LD Cattlefeed a Grass Gross Beta 12 1.0 11.1 (9/9) 90-11,9torris Fare 13.9 (3/3) 8.8 (3/3) 0 (pCf/g wet)
(3.0-31.4) 2.4 et 9 95*
(3.0-31.4)
(3.1-19.1) h Spec.
12
<tLD 0
Cs-134 0.1 4LD Cs-137 0.1 4LD 4LD 0
Other Gammes 0.2
<LLD 4LD 0
~
<L Ln 0
Sr-89 12 1.0
<LLD
$r-90 12 1.0
<LLD
<LLD 0
a teen and re. ige based on detectable measurements only. Fraction indicated in parenthesis.
s S
,ee
.. n n
Tabic 5.0-4 ENVIR0 MENTAL RADIOLOGICAL MONITORING Pn00UM QUARTERLY SipetARY Name of Factitty Braidwood asuclear Pomer station Docket No.
50-456, 50 857 Location of f xility traceville,111t not s Reporting Period 2nd Quarter 1987 Kounty, state)
A Indicator Location with Highest Control Sample Type and Locations Quarterly Mean Locations Isusewr of a
Ison-routine Type Mus6er of IIeans mean Meen (Units)
Analyses LLD Range Location Range Range Results Air Particulates Gross Beta 117 0.01 0.024 (104/104) 80-04. Essen. 4.8 at 0.027 (13/13) 0.024 (13/13) 0 (pCf/m3)
(0.006-0.045) 9 165*
(0.012-0.045) iv.013-0.043)
Gasuna spec 9
0.01
<LLD
<LLD 0
Sr-89 9
0.01
<LLD
<LLD 0
$r-90 9
0.01
<LLD
<LLD 0
<tLD 0
Airt>orne lodine I-131 117 0.07 (LLD y
3 o
(pC1/m )
Gassna Background Gamma Dose 9
3.0 12.7 (8/8) 80-05, Gardner 14.8 (1/1) 12.8 (1/1) 0 (TLDs) (aft /Qtr.)
(11.4-14.8) 5.5 mi 9 225*
<LLD 0
M11k I-131 40 0.5
<LLD (pCf/l)
Gamma Spec.
40
<tLD 0
Cs-134 5.0
<tLD
<LLO O
Cs-137 5.0
<tLD Other Gansoas 10
<LLD
<tL3 0
<LLD 0
Sr-89 12 10
<LLD Sr-90 12 2
2.6 (5/6) 80-12. Goodwin Fare 3.5 (3/3) 3.0 (6/6) 0 l
(2.2-3.1) 7.7 at 67*
(2.7-5.1)
(2.1-5.1)
I i
N W
t e
fn oistt rul eou 0
0 0 0 0 0
0 0 0 0 0 0 trsAe-s u n.
M ks s
)
l n
))
3 o oa e 32 1) rimg
/
D D
D D
/5 D D D D D D
ttan 36 L
L L
L 3
L L
L L
L L
L L
4 nara (3
14 L
L A
L 4 A 4
ocMR
( -
Co 67 6
L 5.1 76 1(
2(
789 1
)
)
6
)6 3
5 r
e 3
11 4
e ng
/8
/2 t
an 34 3
0 r
ea
(
15 5
a t
mR 2
( -7
- 0. 9 42 u
s
, Q e
6 h
02 5
d gn 4(
4(
l 0
M 4
n i a Y
2 He W
5 hty e
d il p
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wr S
i e
e n
r nt r
eo Y
e or a*
gi L
.P a
F0 rt i a tu 7
aa R
E og aQ t
s2 ht T
N e c
t o
cS R
f o
a r9 s
A t i L
c t
it
)
U e c o
Of Da
.o A
L d
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E o ;
85 9e W
u U
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0p
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T1 0P 8
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G t
N a
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(
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)
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t os e
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3 4
I e
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aing 96 D
D D
D 1)
D D D D D D
N w
l t
ctan
/
L L
L L
/2 L
L L
L L
L O
o l
a i aea 88 (4
A 4 4 4 4 4 4 4 L
4 3.
0 15 MuMR M
P I
t
( -
s 48 7
5 L
r I
A a e
- 4. 2 C
e 1
y 84 I
l 1
t 2(
4(
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c 1
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O u
v u l
b L
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C o
a O
s E(
D 2
3 I
d a
T D
o r
L A
o B
L 2
0 0
0 2
1 0
0 0 0 0
2 R
w 1
1 0
1 1
1 2
0 1
d 2
2 L
f A
a T
r I
B 2
4 4
4 4
6 6
6 6
6 O
y 1
2 M
t u
t o
i R
yt f
I t c dos s
V i a n e e
N l F ars n
E i
ey a
c a
c n
cf e6l t
e t
e e
ao pma e
p e
p G
F yun B
S m
s S
4 7
e n
TNA u
3 3
r u
f o s
a I
9 0
s a
1 1
e f
9 0
oi s
m t
8 9
s m -
h t
8 9
t o
s i -
o m
s s
t i -
ea r
a r r r r
a C
C O
r r
r mc G
G T
S G
G T
S S
ao d L n
r
)
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i t
l et t
a pPi a
w) m yn t
1 aTU t
g/
S
(
p nf t
iC c
l p o(
e o
r C
P
~~
I ll 1
ll
1 1
lllI) e f n oistt rul eou 0
0 0 0 0 0 0
0 O 0 0 0 O 0 mrs u
e s nR nI on s
)
l n 3
e 1) o e a. g 4
D D
D D
D D
e e e e e e e rt
/
L L
L L
n n n n n n n tt a
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GL L
t L
L L
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lo o o lo Co 6
I I
l I
I 6o o
na 14 e
l
(
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( -
L 7.1 2(
769 1
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7 3
)
5 r
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e ng
/4
/
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1 t
.,a 14
(
9 r
5 a
t yR
(
-6 6
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, Q e
7.1 9
6 h
5 d
gn 2(
2 4
n i a Y
2 He R
0 M
m 5
h r
y ty e
t 8
d il v8 1
8 o
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Ct 1$
i e
Rt e
r nt e
d Y
e or e
o7 L
P ia n
e5 o.
R tu e
k w1 E
og aQ t
a5 d
T N n c
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a n,
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c am rl
)
U er o
Ka Be Q
k o L
e W '
d I
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1l3
+
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DU8 DH8 i
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P o
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G c
II t
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s
(
R S
f rs O
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)
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tose 3
)
4 l
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e aing 1)
D D
D D
D D 1
D D D D D D l
w 1
t ctan
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L L
L L
L
/
L L
L L
L L
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1 a
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t t
L L
t L
1 -
L L
L L
L L
P 1
t dcleR 14
(
(
(
0 I
5 no
( -
L r
IL 3
6 5
A a e 6.1 9
C e
1 y
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1 t
2(
2 o
G c
f n
l O
u w u O
le e o L
b c C a
I d
a (
D i.
2 T
D e r L
A e B L
1 0
0 5
0 0
2 1
0 0
0 0
0 2
s 1
1 1
0 1
1 1
2 0
1 R
e 2
2 L
t A
e T
r N
B 6
6 2
2 2
1 1
1 1
1 E
y 2
t S
i IO l
R yi f
I t c dos s
s V
i a n e a
a m
N l F ars m
u u
a c
s E
i ey a
c s
t e
e t
e e
cf edl ao p
a e
p G
e p
G 7
m B
S 4
7 m
F yun B
S A
3 r
u 3
3 r
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TloA
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9 0
s a
1 1
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9 0
f o s
e oi s
m h
t 8
9 s
s h
t 8
9 u
s t
o s
s s
t a
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s s t
i -
e a r
e C
C O
r r r
a C
C O
r r
r mc G
G s
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(
cf Wf aC C
f p l p r(
l(
u e
s W
Tabic 5.0-4 (continued)
ENVIR00pENTAL RADIOLOGICAL MONITORING PROGRAM QUARTERLY StpetARY Name of Facility Brafemood Nuclear Power Station Dociet No.
50-456. 50-457 Location of Factitty Bracewf11e, 1111 nots Reporting Period 2nd Quarter 1987 (county, statel I
Indicator Location with Highest Centrol Sample Type and Locations Quarterly Mean Locatfans W of Type Number of Meena Rean Means gen. routine (Units)
Analyses LLD Range Location Range Range Aesults Fish Gross Beta 4
1.0 3.0 (2/2) 90-07 Kankakee River 3.1 (2/2) 3.1 (2/2) 0 (pCf/g wat)
(2.7-3.a)
Upstream. 5.5 at 0 (3.0-3.2)
(3.0-3.2) 8$'
G:mmaa Spec.
4 Cs-134 0.1 4LD
<U O O
Cs-137 0.1 4LD ALD u
Other Gesumas 0.13 ALD ALD 0
Sr-89 4
0.1 4LD 4LD 0
Sr-90 4
0.1 4LD 4LD 0
- sttlefeed & Grass Gross Beta 4
1.0 19.2 (3/3) 90-11, Morris Fars 24.3 (1/1) 11.3 (1/1) 0 (pCf/g wet)
(12.8-24.3) 2.4 at 0 95*
Gaussa spec.
4 None O
Cs-134 0.1 (LD Cs-137 0.1 4LD None 0
Other Gennas 0.2 4LD None O
Sr-89 4
1.0 ALD None O
Sr-90 4
1.0 ALD None 0
a uu.
dL-
Tcblo 5.0-4 (continued)
DIVIR0ioIENTAL RADIOLOGICAL MONITORING PROGRAM QUARTERLY 58JotARY Mame of Factif ty Brefeseed buclear pouer Station Docket No.
50-456, 50-457 Location of Facility Braceutile, Illinets Reporting period 2nd Quarter 1967 (County. state:
Indicator Location with Highest Centrol Sample Type and Locattens Quarterly mean Locattens number of Type Number of neana Mean gesena W,-routine (Units)
Analyses LLD Rang Location Range Range Results Agustfc Vegetation Grost-Beta 2
0.6
<LLD BD-07. Kankakee R1ver 5.6 (1/1) 5.6 (1/1) 0 (pC1/g met)
Upstream, 5.5 of 9 85*
Gamma spec.
2 Cs-134 0.1
<LLD
<LLD 0
Cs-137 0.1 4LO
<tLD 0
Other Gammes 0.2 4LD
<tLD 0
N 4
Bottom Sedfaents Gross Beta 2
1.0 8.0 (1/1) 90-07. Kankakee R1ver 23.3 (1/1) 23.3 (1.1) 0 (pC1/g dry)
Upstream, 5.5 et 9 85*
Gamma Spec.
2 Cs-134 0.1 4LD
<LLD 0
Cs-137 O.1
<LLD BD-07 Kankakee Rfver 3.10 (1/1) 0.10 (1/1) 0 Upstream 5.5 of 9 85*
3 Other Gammas 0.2
<tLD
<tLD 0
a Mean and range based on detectable measurements only. Fractions indicated in parentheses.
Table 5.0-5 ENVIR0eMENTAL RADIOLOGICAL MONITORING PROGRAM OUARTERLY SlfMARY
(
meme of Facility Braf dmood nuclear Power Station Dcchet No.
50-456. 50-457 Location of Factitty graceville, Illinof s Reporting period 3rd Quarter 1987 (county. State)
Indicator Location with Hf host l
Control 9
Sample Type and Locations Quarterly Mean Locations numeer of Type Number of Meena mean Means non-routine (Units)
Analyses LLD Ran9e Location Range Ran9e Results Air Part{culates Gross Beta 126 0.01 0.027 (112/1123 80-19. Nearsite NW 0.028 (14/14) 0.028 (14/14) 0 (pCf/m3)
(0.006-0.057) 0.3 al 9 314' (0.012-0.057)
(0.306-0.052) ca-a spec.
9 0.01 4LD
<LLD 0
Sr-89 9
0.01 4LD
<LLD 0
Sr-90 9
0.01 4LD 4LD 0
Atrborne lodine 1-131 126 0.07 4LD (LLD 0
(pCf/m3)
Gesuna Background Ga m Dose 9
3.0 15.3 (8/8) 83-01. Bralduood 18.3 (1/1) 15.0 (1/11 0
(TLDs) (udt/Qtr.)
(13.1-18.3) 1.5 et 9 34*
<tLD 0
Milk I-131 52 0.5 4LD (pCf/1)
Gasuna Spec.
52 Cs-134 5.0 4LD
<LLD 0
Cs-137 5.0 ALD 4LD 0
4LD 0
Other Gassmas 10.0 4LD
$r-89 12 10 4LD
<LLD 0
Sr-90 12 2
2.4 (6/6)
BD-12, Goodwin Fam 2.7 (3/3) 2.0 (6/6) 0 (1.2-3.1) 7.7 at 0 67*
(2.5-3.11 (1.0-3.1)
Precfpitation Gross Beta 11 7.0 25.5 (6/8) 8D-11, norris Fam 39.1 (2/3) 14.5 (2/3) 0 (6.5-55.01 2.4 d 9 95*
(23.2-55.0)
(10.2-18.8)
Gamma Spec.
4 10 ALD
<tLD 0
Tr1 tium 4
200 4LD
<tLD 0
Sr-89 4
10
<LLD
<tLD 0
sr-90 4
2 4LD
<LLD 0
l
'e 1 w ',.
e,y n
~.
~
Table 5.0-5 (continued)
ENVIR0leIDITAL RADIOLOGICAL Mou1TORING PROGRMI QUARTERLT St99Wlf Name of Facility tratesood meclear Power Station Docket No.
50-456, 50-457 Location of Facility traceville, 111tnots Reporting Period 3rd Quarter 1987 (County: Statel Indicator Location with Highest Control Sample Type and Locations Quarterly Mean Locations number of Type leunder of Meena Reen Meena Ison-rowtIne (Units)
Analyses LLD Range Location Range Rar.y Results Cooling Water Gross Beta 25 1.3 5.2 (13/13) 80-09. Discharge 5.2 (13/13) 3.5 (13/13) 0 (pCf/1)
(3.7-6.3)
Pfpe, at Station (3.7-6.3)
(2.3-4.4)
Gamma Spec.
6
<LLD 0
Cs-134 10 4 LD CA.137 10 ALD
<tLD 0
Other Gasmaas 20 (LD
<LLO O
Tritium 6
200 1,005 (2/3) 80-09, Discharge 1,005 (2/3)
(LD 0
(640-1,370)
Pipe,at Station (640-1,370)
<LLD 0
Sr-89 6
10 (LLD
<tLD 0
Sr-90 6
2
<LLD N
CD Surface Water Gross Beta 76 1.3 3.2 (13/13) 80-10. Kankakee River 3.2 (13/13) 3.0 (13/13) 0 (pCf/11 (2.4-3.8)
Monitoring site #5, (2.4-3.8)
(2.5-3.9)
(Downstream), 5.0 at 9 46*
Gaussa Spec.
6 Cs-131 10
<LLD
<LLD 0
Cs-137 10 ALD
<tLD 0
Other Gammas 15
<tLD
<LLb 0
Tritiur 2
200
<LLD
<LLD 0
Sr-89 2
Sr-90 2
2 4LD 4LD 0
w
Table 5.0-5 (c:ntinued)
ENVIROWEENTAL RADIOLOGICAL MONITORING PROGUM r>RTERLY 5(feuRY Name of Facility tratesood Nuclose Power Statfor Dt;ket No.
50-456. 50-457 Location of Fwility traceville, Illinois R eporting period 3rd Quarter 1987 (County, state)
Indicator Location with Highest Control Sample Type and Locations Quarterly Mean Locations Nummer of Type Number of Means no..
pe, na non. routine (Units) -
Analyses LLD Range Location Range Range Results Nell Water Gross Beta 1
1.2 27.8 (1/1) 80-13, Brefduced City None 0
Hall Well,1.7 si # 30 '
(pCf/1)
Game Spec.
1 Cs-134 10 4LD None O
Cs-137 10 ALD None 0
Other Gaumes 20 4LD None 0
None 0
Trittum 1
200 ALD Sr-89 1
10 ALD Mone 0
a -90 1
2 4LD None 0
e y
Fish Gross Seta 4
1.0 2.4 (2/2) 80-10. Kankakee River 2.4 (2/2) 2.2 (2/2) 0 (2.3-2.4)
Downstream, 5.0 of (2.3-2.4)
(1.9-2.6)
(pC1/g uet) 9 76*
Gassna Spec.
4
<tLD 0
Cs-s34 0.10 4LD
<tLD 0
Cs-137 0.10 ALD Other Gasses 0.13
<tLD
<LLD 0
Sr-89 4
0.1 4LD
<tLJ 0
Sr-90 4
0.1 4LD
<tLD 0
Cattlefoed & Grass Gross Beta 4
1.0 8.2 (3/3) 80-17. Trott*r's Dairy L7.0 !?./1) 11.0 (1/1) 0 (ptt/g met)
(2.3-17.0) 4.8 af 9 315*
Gamuna Spec.
4 Cs-134 0.1 4LD 4LD 0
Cs-137 0.1
<LLD 4LO O
Other Gesumes 0.2 4LD
<LLD 0
l Sr-89 4
1.0 ALD ALD 0
<LLD 0
Sr-90 4
1.0 4LD s
i
y
. e..,
3-Tcb12 5.0-5 (ca tinued)
ENVIR0ISIENTAL RADIOLOGICAL MONITORING Pam QUARTERLY SLS9WtY Maar of Factitty Breteseed heclear pouer Statten Docket no.
50-456, 50-457 Location of Fact 11ty traceutile,111t net s Reporting period 3rd Quarter 1987 f county, 5 tate)
Indicator Location with Highest Centrol Sample Type and Locations Quarterly Mean Locations Inseer of I
Type humber of Meena Mean fleans non-routine (Units)
Analyses LLD Range Location Range Range Results Agustic Vegetation Gross Beta 2
0.4 3.7 (1/1) 30-10. Kankakee River 3.7 (1/1) 4LD 0
Downstream, 5.0 af (pCf/g wet) 9 76*
Gasses Spec.
2 Cs-134 0.1 4LD 4LD 0
Cs-137 0.1 4LD 4LD 0
4LD 0
Other Gesumas 0.2 4LD Bottom Sediments Gross Beta 2
1.0 14.3 (1/1) 80-07. Kankakee River 19.2 (1/11 14.3 (1/1) 0 (pCf/g d y)
Upstream, 5.5 mt 9
, 85*
f Gesuma *,pec.
2 f
fs-134 0.1 4LD 4LD 0
Cs-137 0.1
- LD BD-07. Kanketee River 0.18 (1/1) 0.18 (1/1) 0 Upstream. 5.5 et 9 85*
Other Gennes 0.2 4LD 4LD 0
l Vegetables Gross Seta 12 1.0 2.3 (12/12) 60-14. Pinnick Fars 2.7 (4/4)
Ilone 0
(1.1-3.7) 1.8 mi 9 350*
(2.1-3.2)
Gaassa Spec.
12 Cs-134 0.06 4LD none 0
Isone 0
1 Cs-137 0.08 4LD other Gresses 0.2 4LD None 0
l
$r-89 12 0.1 4LD Ilone 0
Sr-90 12 0.1 (LD None 0
j 1-131 2
0.06 4LP Ilone 0
8-Wan and range based on detectable measurements only. Fractions ind' *ted in parentheses.
s
Tablo 5.0-6 j
=
ENVIROIBIENTRL RAD 15.0GICAL Mou!TORING PROGR44 QWRRTERLY SuletMtY Name of factitty Brefdweed gluclear Pomer Station Decket No.
50-4 %. 50-457 j
Lecetten of Factitty tracert11e.1111aots Reporting Period 4th Quarter 1987 (County, State)
Indicator Locetten with 8Hghest Centrol Sample Type and Locattens Quarterly steen Locattees inputer of Type Ilumber of lesene 14een 90sene Ilon-reettne Range Range Results (Units)
Analyses LLD Range Locat!en i
Air Particulates Gross Seta 117 0.01 0.031 (104/104) 80-03, County Line O.C32 (13/13) 0.032 (13/13) 0 (pCf/#)
(0.016-0.055)
Road. 6.2 at 9 120*
(0.017-0.052) 10.017-0.052) 4LD 0
Gemme Spec.
9 0.01 4LD Sr-89 9
0.01 4LD
<LLD 0
Sr-90 9
0.01 4LD 4LD 0
(LD 0
Afrtorne lodtne 1-131 117 0.07 4LD (pCf/m3)
Gemme Sectgrcund Gesume Dese 9
3.0 15.2 (8/8)
- 0-03 County Line 20.4 (1/1) 20.4 11/1) 0 (TLDs) (sdt/Qtr.)
(14.3-20.4)
Road,, 6.2 of 9 120*
w to Ittik 1-131 28 0.5 4LD 4LD e
(pCf/11 Gemme Spec.
28 ALD 0
)
Cs-134 5.0 4LD ALD 0
Cs-137 5.0 4LD 4LD 0
Other Gemmes 10.0 4LD Sr-89 12 10 4LD ALD 0
Sr-90 12 2
2.2 (5/6) 83-18, 8tros Fars 2.6 (2/3) 2.2 (2/6) 0 (1.5-2.7) 10.5 et 9 270*
(1.7-3.41 (1.5-3.4) j Precipitation Gross Seta 11 6.0 22.6 (4/9)
BD-11, Pierris Form 30.5 (1/3) 9.4 (2/2) 0 (4.9-30.5) 2.4 et 9 95*
(4.9-14.0)
Gemme Spec.
4 10
<LLD 4LD 0
Trftfue 4
200 4LD 4LD 0
l
<LLO O
$r-89 4
10 (LD Sr-90 4
2 ALD ALD 0
e
=r**W""h
+
-y.
.,,,,g,
g-..~. - -..
g g. g g h s,., %
_..m,
- Tabla 5.0-6 (continued)
- s ENVIRDIMENTAL RASIOLf,=ICAL MONITORING PROGUM QUARTERLY SLPetARY Mame of Fact 11ty Braidwood Nuc~est Power Station Docket No.
50-456, 50-457 Location of Fact) tty Bracev111e Illinois Reporting Period 4th Quar'er 1987 2
(come.j,5 tate)
Indtcator Location with Highest Control Sample Type and Locations Quarterly Mean Locations Number of Type Number of Meana Mean Mean8 Non-rGutine (Units)
Analyses LLD Range Location Range Range Results Coo 11ag Water Gross Beta 24 1.3 5.4 (13/13)
BD-09, Discharge 5.4 (13/13) 3.2 (13/13) 0 (pCf/1)
(4.4-6.6)
Pipe, at Station (4.4-6.6)
(2.3-4.6)
Gasuna Spec.
6 Cs-134 10
<LLD
<LLD 0
Dther Gansnas 20 (LD 4LD 0
Trfttus 6
200 6,540 (3/3)
BD-09. Discherge 6,540 (3/3) 4LD 0
(3,560-9,080)
Pf pe, at Station (3,560-9,080)
Sr-89 6
10
<tLD
<LLD 0
m o
Sr-90 6
2 4LD
<LLD 0
Surface Water Gross Beta 26 1.3 3.5 (13/13) 80-10. Kankakee River 3.5 (13/13) 3.2 (13/13) 0 (pC1/1)
(2.5-6.51 (Down. stream), 5.0 (2.9-6.51 (2.4-5.6) si 9 76*
Gaussa Spec.
- 6'
~
~
Cs-134 10
<tLD (LLD 0
Cs-137 10 ALD
<LLD 0
Other Gassuas 20 (LLD
<LLD 0
Tritfum 2
200 7,005 (1/1) 80-10. Kankakee River 7,005 (1/1) 4.530 (1/1) 0 (Downstream), 5.0 sf 9 76*
Sr-89 2
10 4LD
<LLD 0
Sr-90 2
2 413 ALD 0
Tablo 5.0-6 (continued)
ENNitu: MENTAL RADIOLOGICAL M041TORINC Pft0GtNI QUARTERLY SW8WlY Name of Facility Bref esood Nuclear Power Statten Decket No.
50-456, 50-457 Location of Tactitty Bracewf11e, Illinois Reporting Period 4th Quarter 1987 (County, statel Indicator Location with Highest Control Sample Type and Locations Quarterly Mean Locattens thsaber of Type Number of Meana Mean Meana lion-rovttne (Units)
Analyses LLD Range Location Range Range mesults tiell Water Gross Beta 1
1.2 30.9 (1/1) 80-13, Brafducod Cfty 30.9 (1/1)
None 0
Wall leell,1.7 et 8 (pCf/1) 30' Gesume spec.
1 None O
Cs-134 10 4LD Cs-137 10 ALD None 0
Other Gaammas 20 4LD None 0
Tritium 1
200 4LD None 0
. Sr-89 1
10
<tL3 None 0
Sr-90 1
2 4LD None O
co Fish Gross Beta 2
1.0 2.4 (1/1) 80-10 Kankakee River 2.4 (1/1) 2.3 (1/1) 0 Downstream, 5.0 of (pCf/g wet) 8 76*
Game spec.
2 Cs-134 0.1 4LD 4LD 0
<tLD 0
Cs-137 0.1 4LD
<LLD 0
Other Gassmas 0.13 4LD Sr-89 2
0.1 4LD ALD 0
Sr-90 2
0.1 4LD 4LD 0
Cattlefeed & Grass Gross Seta 4
1.0 6.6 (3/3) 8> 17. Trotter's Dairy 8.4 (1/1) 8.4 (1/1) 0 (pCf/g met)
(3.4-8.4)
Faru, 4.8 af 8 315*
80-12, Gooerin Faru 8.4 (1/1) 7.7 af 8 67*
r - a Spec.
4 Cs-134 0.1 4LD 4LD 0
Cs-137 0.1 4LD
<LLD 0
A J
Table 5.0-6 (continued)
ENVIR0leqENTAL RADI(LOGICAL M0u170 RING PROGRmt QUARTERLY 5(pet 4RY Eame of Fact 11ty Brateseed nuclear Pauer Station Docket No.
50-456, 50-457 Location of Facility gracevt11e, 111tnots Reporting Period 4th Quarter 1987 (County 5 tate)
Indicator Location wfth Highest Control sample Type and Locations Quarterly Mean Locations Itsaber of Type ilumber of Meana Maen lesena Ilon-routine (Units)
Analyses LLD Range Location Range Aange Results Cattlefced & Grass Other Gmunes 0.2 4LD
<LLD 0
(pCf/g vet)
(continued)
Sr-89 4
1.0
, <LLD ALD 0
Sr-90 4
1.0
<LLD 4LD 0
Aquatic Vegetation Gross Beta 2
0.4 2.2 (1/11 80-07. Kankakee River 2.9 (1/11 2.9 (1/1) 0 (pC1/g vet)
Upstream, 5.5 mi e l
85*
Gauna Spec.
2 Cs-134 0.1 4LD ALD 0
Cs-137 0.1 4LD 4LD 0
m to 4LD 0
Other Gmunes 0.2 4LD Bottom Sediments Grcss Beta 2
1.0 20.2 (1/1) 80-10. Kankakee Rfver 20.2 (1/1, 18.1 (1/1) 0 (pct /g dry)
Dounstream. 5.0 of e 76*
Gauna spec.
2 Cs-134 0.1 4LD 4LD 0
Cs-137 0.1 ALD
<LLD 0
Other Gammas 0.2
<LLD ALD 0
a Mean and range based on detectable measurements only. Fractions indicated in parwatheses.
~
Table 5.1-1 GAMMA RADIATION, AS MEASURED BY THERMOLUMINESENT 00SIMETERS (TLDs)
STANDARD RADIOLOGICAL MONITORING PROGRAM l
I 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed:
01-03-87 03-27-87 06-27-87 10-03-87 Date Removed:
03-27-87 06-27-87 10-03-87 01-01-88
[
Days in the Field:
83 92 98 90 Location Average mR/Qtr.
BD-01 12.410.7 11.410.8 18.313.4 14.410.8 BD-02 12.710.9 12.7t0.8 14.0i0.7 14.8i0.7 B0-03 13.3i0.7 12.810.7 15.0il.6 20.4*1.3 l
8D-04 13.9*1.0 12.310.8 16.1tl.7 15.210.6 BD-05 17.110.9 14.810.8 17.2il.2 17.410.8 1
BD-06
- 13. 9tl. 3 11.910.6 13.lil.1 14.3t0.9 BD-19 15.110.9 13.110.8 14.810.9 16.li0.9 BD-20 14.110.9 13.111.0 14.710.8 14.510.7 BD-21 13.110.8 12.310.8 14.210.7 14.SiO.7 Mean i s.d.
14.0tl.4 12.7tl.0 15.311.6 15.7t2.0 83
Td)le 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:
01-03-87 03-27-87 06-27-87 10-03-87 Date Removed:
03-27-87 06-27-87 10-03-87 01-01-88 Days in the Field:
83 92 98 90 Location Average mR/Qtr.
Code 8D-101-1 14.110.7 12.4f0.9 16.7f0.8 14.510.8 BD-101-2 12.410.8 12.110.8 13.2i0.8 15.110.9 BD-102-1 12.6*0.7 11.6i0.9 13.810.8 13.810.7 80-102-2 12.810.8 12.5i0.7 13.711.0 15.510.7 80-104-1 12.411.0 11.510.8 13.2fl.2 12.810.7 80-104-2 12.210.7 12.110.9 13.310.9 15.310.7 BD-105-1 12.710.7 12.611.0 14.410.8 14.310.8 BD-105-2 13.0f0.8 11.6t0.7 14.111.1 15.410.6 BD-106-1 12.810.8 12.810.9 14.Sil.2 14.1*0.7 BD-106-2 13.110.9 12.110.7 13.811.1 15.4fl.0 80-107-1 13.410.7 12.410.7 14.610.9 14.8tl.3 i
80-107-2 13.2i0.9 11.010.8 14.0f0.9 14.911.0 BD-108-1 12.210.6 11.210.7 13.7tl.0 13.3*0.7 BD-108-2 13.0f0.8 10.710.7 13.710.7 14.5*1.1 80-109-1 15.611.0 15.511.2
- 16. 9tl.1 16.9i0.9 BD-109-2 15.5fl.2 13.6t0.8 17.0*1.2 16.811.0 BD-110-1 13.311.1 12.810.9 15.5fl.4 15.lil.0 BD-110-2 14.0t0.7 14.310.7 15.6i0.8 17.5i0.8 BD-111a-1 11.610.7 12.610.7 12.5i0.8 15.410.8 BD-111a-2 12.6t0.7 12.6i0.8 14.0*1.0 16.210.9 BD-111b-1 11.610.7 11.310.9 12.7tl.0 13.810.8 BD-111b-2 12.510.9 12.410.8 14.210.9 15.710.8 B0-112-1 12.810.9 11.510.8 12.710.7 13.310.7 BD-112-2 11.8t0.8 11.2i0.6 12.610.7 14.5i0.7 BD-113a-1 13.210.8 12.010.7 13.3tl.0 14.611.0 BD-113a-2 12.910.7 12.710.9 13.710.8 15.410.8 BD-113b-1
- 12. 9io.8 12.810.9 12.710.9 14.810.8 BD-113b-2 13.210.8 12.810.8 14.lil.0 15.410.7 BD-114-1 13.310.8 13.311.2 14.0f0.9 15.4i0.8 BD-114-2 12.510.6 11.610.6 14.011.0 14.010.8 BD-116-1 13.110.8 13.510.9 14.410.9 15.9*1.0 t
80-116-2 13.910.9 11.910.7 14.710.8 14.410.8 Mean i s.d.
13.0t0.9 12.3*1.0 14.111.2 15.Dil.0 84
Table 5.1-1 (continued)
GAMMA RADIATION, AS MEASURED BY TLDs (continued)
SPECIAL PROGRAM l
Outer Ring, Near 5 Mile Radius, Indicator Locations 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed:
01-03-87 03-27-87 06-27-87 10-03-87 Date Removed:
03-27-87 06-27-87 10-03-87 01-01-88 Days in the Field:
83 92 98 90 Location Average mR/Qtr.
BD-201-1 18.0fl.5 17.511.2 18.110.7 18.0i0.8 BD-201-2 15.411.2 14.410.9 15.311.1 17.111.6 BD 202-1 13.6tl.2 13.8i0.8 14.4i1.0 15.2t0.8 BD-202-2 13.211.0 13.211.1 14.6tl.2 14.4*l.2 BD-203-1 13.2t0.8 14.1*0.7 14.910.8 16.2i0.7 BD-204-1 11.810.8 12.110.6 12.710.8 14.2i0.8 BD-204-2 12.710.7 11.010.9 13.810.8 14.0i0.7 BD-205-1 12.710.7 12.7*0.7 13.4i0.7 14.8tl.2 BD-206-1 13.210.6 14.310.7 13.9i0.7 16.2il.2 80-206-2 14.0f0.8 12.4i0.8 15.610.8 15.210.7 BD-207-1 12.510.9 12.610.9 13.910.8 14.610.7 80-207-2 12.710.8 12.010.7 14.511.6 14.7f0.6 BD-208-1 12.510.9 11.510.7 13.410.8 13.610.8 BD-208-2 12.610.8 11.510.9 13.7i0.9 14.910.9 80-209-1 17.6t0.9 16.410.7 19.110.8 17.610.9 BD-210-1 19.510.7 19.111.5 20.9i0.8 19.6t0.8 BD-210-2 19.311.0 17.910,8 20.111.1 19.9tl.0 BD-211-1 16.810.8 15.710.8 18.0i0.8 17.510.9 BD-212-1 15.3tl.4 13.710.6 16.8tl.4 15.710.9 BD-212-2 16.411.1 16.310.8 17.810.8 19.411.4 I
BD-213-1 13.610.9 12.510.7 14.510.9 15.0f0.8 BD-213-2 12.7tl.1 12.710.8 13.910.8 15.611.2 BD-214-1 15.211.4 13.210.8 16.010.9 15.310.9 BD-214-2 14.4t0.9 14.6i0.8 16.211.0 16.9tl.1 BD-215-1 12.610.7 11.0t0. 6 13.511.3 13.010.7 BD-216-1 13.810.9 12.8i0.6 14.910.8 14.710.7 BD-216-2 13.511.0 12.311.0 15.011.1 16.Dil.1 Hean i s.d.
14.412.2 13.812.2 15.612.2 15.9tl.8 85
9 6
N' 4
APPENDIX II METEOROLOGICAL DATA l
(
86
.x c:
~
~
?
.+ -
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET 4
4 WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
O O
O 1
O O
1 NNE O
3 1
O O
O 4.
NE O
1 3
7 0
0 11 ENE O
O 11 10 2
0 23 E
O ~
5 ~
8 10 10 5
38 ESE O
O 2
9 8
0 19 SE O
O 1
2 3
0
.6-l SSE O
O O
O O
O O
S O
O O
3 0
0
'3 SSW O
O O
2 O
O 2
i j'
SW O'
O O
O O
O
.O WSW O
O O
O O
O O
I W
O O
O O
O O
O WNW O
O O
4 2,
1 7
i NW O
O 4
1 O
O 5
t 1
i NNW O
O 4
4 1
0 9
VARIABLE O
O O
O O
O O
TOTAL 0
9 34 S3 26 6
128 Hours of calm in this stability class:
O Hours of missino wind measurements in this stability class:
O Hours'of missing stability measurements in all stability classes 6
87
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD --JANUARY-MARCH 1987 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS NEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.0-3 4-7 8-12 13-18 19-24 GT 24
-TOTAL N
O 1
0 1
1 0
3 NNE O
O 2
O O
O 2
NE-0 1
1 7
5 0
14 4
ENE O
3 3
5 0
0 11 E
1~
2 2
2 O
O 7-ESE O
2 3
1 3
0 9
SE O
1 7
1 1
0 10 SSE O
O 2
1 O
O 3
S O
O 3
2 2
0 7
SSW O
O 2
5 0
0 7
SW O
2 1
O O
O 3
WSW O
1 1
3 0
0 5
W' O
1 1
2 O
O 4
WNW O
O 1
3 1
0 5
NW O
5 5
0 2
0 12 NNW O
O 3
4 1
0 8
VARIABLE O
O O
O O
O O
TOTAL 1
19 37 37 16 0
110 Hours of calm in this stability classt O
Hours of missing wind measurements in this stability class:
O Hours of missing stability measurements in all stability classest 6
88
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
O 1
4 2
O O
7 NNE O
1 0
6 O
O 7
NE O
4 5
3 5
0 17 ENE O
3 3
6 7
0 19 E
O 1
1 3
0 1
6.
ESE O
5 2
0 2
0 9
SE O
4 2
1 2
0
?
SSE O
2 0
2 1
0 5
S O
3 5
3 4
0 15 SSW O
3 5
1 O
O 9
SW 1
0 2
3 0
0 6
WSW O
3 3
2 O
O 8
W O
1 3
4 1
0 9
WNW O
5 3
8 3
2 21 NW O
2 2
4 2
0 10 NNW 1
4 5
13 6
0 29 VARIABLE O
O O
O O
O O
TOTAL 2
42 45 61 33 3
186 Hours of calm in this s t at. i l i t y class:
O Hours of missing wind measurements in this statility class:
1 Hours of missing s t atii l i t y measements in all s t a tii l i t y classes:
6 89
An, n.
as a
~ m..
. ;, a es
~
.v BRAIDWOOD NUCL(AR POWER STATION PERIOD OF RECORD - JANUARY-MARCH 1987 STABILITY CLASS'--NEUTRAL (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND-SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
2 4
8 7
3 0
24
-NNE 2
9 13 8
8' 15 55 NE 2
11 8
35 37 0
9?.
ENE 2
2 20 40 14 0
78 E
O 4
24 29 29 12 98 ESE O
2 5
12 17 5
41 SE 2.
5 1
1 4
0 13 SSE 1
8 3
~6 7
0 25 S
1 7
9 16 18 12 63 SSW O
9 6
'1 19 4
59 SW 2
10 18 21 9
1 61 WSW 1
12 20 36 9
0 78 W
2 19 14 26 9
0 70 WNW 1
5 20 30 15 7
78 NW O
11 28 30 22 9
100 NNW O
11 19 28 23 4
85 VARIABLE O
O O
O O
O O
TOTAL 18 129 216 346 243 69
.1021 Hours of calm in this stability class:
O Hours of missing wind measurements in this stability clasta 1
Hours of missing stability measurements in all stability classest 6
90
O e
BRAIDWOOD NUCLEAR POWER STATION PERIOD GF RECORD - JANUARY-MARCH 1987 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
1 4
3 3
0 0
11 NNE 1
2 4
0 0
4 11 NE O
6 8
15 2
0 31 ENE O
9 10 7
0 0
26 E
1 4
13 12 8
0 38 ESE 1
3 5
11 6
0 26 f
SE O
O 8
21 10 0
39 SSE 2
2 3
12 4
0 23 S
1 0
7 9
11 4
32 SSW 1
4 3
24 17 4
53 SW 1
4 7
15 5
0 32 WSW O
3 9
7 2
0 21 W
1 7
7 4
4 0
23 WNW 1
3 14 11 4
1 34 NW 1
1 13 8
3 0
26 NNW O
2 7
4 0
8 21 VARIABLE O
O O
O O
O O
TOTAL 12 54 121 163 76 21 447 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:
6 91 k
--. _ = _ _ _ _ _ _ _ _ _ _ _ _ _ _ _.-_- _____ _ _ _ __.
,.,e
- gg BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JANUA~4Y MARCH 1987 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT.199 FEET WIND.
WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24-TOTAL N
O O
1 1
O O
2 NNE O
2 1
1 1
0 5
NE O
O 1
1 O
O 2
ENE 1
3 5
0 0
0 9
E O
3 3
10 1
0 17 ESE 2
2 7
9 O
O
'20 SE O
O 5
6 3
0 14 SSE O
1 5
2 O
O 8
S 1
1 3
5 0
0 10 SSW 1
1 0
5 7
0 14 SW 1
1 5
5 4
0 16 WSW 1
3 3
0 O
O 7
s W
O 2
3 6
0 0
11 WNW O
O 6
8 O
O 14 NW O
2 8
10 0
0
~20 NNW 1
3 3
1 O
O 8
VARIABLE O
O O
O O
O O
t TOTAL 8
24 59 70 16 0
177 Hours of calm in this stability classt O
Hours of missing wind measurements in this stability class O
Hours of missing stability measurements in all stability classest 6
92
..m.
-. w-t c;
,z au s,
i BRAIDWOOD NUCLEAR POWER STATION PERIOD.0F RECORD - JANUARY-MARCH 1987 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 19-24 GT'24 TOTAL
'_13-18 N
O 2
3 0
0 0
5 NNE O
O O
O O
O O
NE O
O O
O O
O O
ENE 2
O O
O O
O 2
E 1
O O
2 O
O
'3 ESE 1
0 4
5 0
0 10 SE O
O 6
6 0
0 12 SSE O
O 1
1 O
O 2
S O
O O
O O
O O
SSW O
O O
3 5
0 8
SW O
2 3
1 O
O 6
WSW O
3 1
6 O
O 10 W
1 2
4 5
0 0
12 P
WNW O
2 5
1 O
O 8
NW O
1 0
1 1
0 3
NNW O
1 1
O O
O 2
VARIABLE O
O O
O O
O O
TOTAL 5
13 28 31 6
0 83 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 6
)
93
- f,, ;; + +,, z.
, _.+ c.1; 1x s;
y, I
- u Ls
, :.:,y y
r; BRAIDWOOD NUCLEAR POWER STATION PERIOD OF-RECORD - APRIL-JUNE 1987
-STABILITY CLASS - EXTREMELY UNSTABLE
-(DIFF TEMP 199-70 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12' 13-18 24 OT 24
~ TOTAL
'N O
O 8
8 1
1 19 NNE O
O 6
6 0
0 12 NE 1
3 16 23 5
0 48 ENE O
3' 4
6 0
0 13' E-1 2
'12 3
2 0
20 ESE O
3 6
3 0
1 13 SE O
7 15 12 C
0-34 SSE O
8 11 6
0 0
25 S
O 3
16 9
0 0
28 SSW O
1 2
11 O
O 14 SW O
O 1
9 1
0 11 WSW O
O 2
6 1
0 9
W O
2 6
2 2
0 12 WNW O
O 5
12 5
1 23 NW O
O 15 8
9 2
34 NNW O
1 7
2 2
0 12 VARIAULE O
O O
O O
O O
TOTAL 2
33 132 126 28 5
326 Hours of calm in this stability class:
O Hours of missing wind measurements in this stability class:
2 Hours of missing stability measurements in all stability classes 4
94
- ]
v!.-
c BRAIDWOOD NUCLEAR POWER STATION PERIOD OF. RECORD - APRIL-JUNE 1987 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3
~4-7 8-12 13-18 19-24 OT 24 TOTAL N
O 3
5 3
2 1
14 NNE 1
0 6
1-1 0
9 NE O
1 2
8 6
0 17 ENE O
O 4
3 1
0 8
E 1
0 1
0
'O O
2 ESE O
O O
2 2
2 6
SE O
5 4
i O
O 10 SSE O
1 5
i O
O 7
s S
O 7
4 8
1 1
21 SSW O
3 2
6 3
1 15
.SW O
2 3
10 1
0 16 WSW O
1 4
7 1
0 13 W
O O
3 1
2 0
6 WNW O
O 7
9 3
0 19 NW O
3 7
4 0
2 16 NNW O
1 7
2 O
O 10 VARIABLE O
O O
O O
O O
TOTAL 2
27 64 66 23 7
189 Hours of calm in this stability class O
Hours of missing wind measurements in this stability classt 1
Hours of missing stability measurements in all stability classes 4
95
b_.
A 4;
-1
-a
=
1 c
as t
BRAIDWOOD NUCLEAR POWER STATION r
PERIOD OF RECORD - APRIL-JUNE 1987 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4--7 8-12 13-18 19-24 GT 24 TOTAL' N
O 1
6 2
1 2
12 NNE O
4 3
2 2
0 11 NE 2
2 2
3 11
.O 19 ENE O
4 6
4 2
0 16 E
O 1
1 O
O O
2 ESE O
O 4
3 0
2 9
-O 6
1 1
0 O
-8 SSE O
2 2
1 O
O 5
S 1
9 1
9 0
1 21 SSW' O
5 3
6 5
0 19 SW 1
3 6
9 2
0 21 WSW O
1 5
3 10 0
19 W
3 3
7 4
2 0
19 WNW O
2 7
5 1
0 15 NW O
O 8
5 2
0 15
~i NNW O
3 2
1 0
1 7
VARIABLE O
O O
O O
O O
TOTAL 6
46 64 58 38 6
218 i
Hours of calm in this stability class O
i Hours of missing wind measurements in this stability class:
2 Hours of missing stability measurements in all stability classes 4
c i
i i
i 96
- p u
+-.
> ~ -
.x s
i e
~
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 STABILITY CLASS - NEUTRAL (DIFF TEMP 199-30 FT) i WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL l
i i
N O
1 8
11 4
4 28 NNE 3
3 9
31 10 0
56 7
.i l
NE 1
4 25 46 19 2
97
.ENE O
9 24 30 2
0 65 j
I E
3 9
12 18 6
0
-48' ESE 1
4 7
14 5
1 32 SE O
5 16 7
2 0
30 l
SSE O
5 9
10 0
0 24 I~
S O
3 9
10 3
3 28 SSW 1
5 8
16 5
6 40
[
SW 3
6 9
23 5
0 46 WSW 2
5 18 28 5
0 58 I
r I-W i
7 20 11 4
0 41 i.
WNW 4
2 23 11 3
0 43 NW i
5 8
12 10 0
36 l
NNW O
1 6
10 1
1 19 VARIABLE O
O O
O O
O
.O I
(
211 288 84 16 693 TOTAL 20 74 l
l l
Hours of calm in this stability class O
Hours of missing wind measurements in this stabil.ty class:
9 Hours of missing stability measurements in all 8tability classes 4
{
i; i
1 i
e i-i 97
c.
ss I
a BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 S-12 13-18 19-24 GT 24 TOTAL b
N O
O 6
15 2
.O 23 NNE O
1 5
9 1
4 20 NE O
2 11 12 2
1 28 ENE 1
6 21 3
0 0
31 E
O 2
13 8
1 0
24 I
ESE O
7 11 6
0 0
24 SE 2
3 11 17 2
0 35 SSE O
2 7
17 1
0 27 i
S O
2 7
37 8
0 54 i
SSW O
1 13 33 13 2
62 SW 0
4 9
29 9
0 51 1
WSW 1
2 6
8 0
0 17 W
O O
6 0-1 0
7 WNW O
O 8
2 0
0 10 NW i
O 6
4 2
0 13 NNW O
1 5
5 4
0 15 VARIABLE O
O O
O O
O O
TOTAL 5
33 145 205 46 7
441 Hours of calm in this stability classt 0
Hours of missing wind measurements in th.is stability classt 6
Hours of missing stability measurements in all stability classest 4
r I
I 98
1 BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
O O
8 6
0 0
14 NNE O
1 1
1 O
O 3
NE 1
2 6
0 0
0 9
ENE O
O S
1 O
O 9
E O
O 1
2 O
O 3
ESE 1
2 14 7
1 0
25 SE O
2 16 11 O
O 29 SSE O
1 3
7 3
0 14 S
O 3
4 9
3 0
19 SSW O
1 3
10 4
0 18 SW O
2 2
6 5
0 15 WSW 1
1 5
5 0
0 12 W
O O
3 0
0 0
3 WNW O
O 9
7 O
O 15 NW O
O 8
2 O
O 10 NNW O
1 3
0 0
0 4
VARIABLE O
O O
O O
O O
TOTAL 3
16 93 74 16 0
202 Hours of calm in this stability classt O
Hours of missing wind measurements in this stability classt 0
f, Hours of missing stability measurements in all stability classes 4
1 99 1
1
m3y 4.
.e, 1
4 ps
.s=
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - APRIL-JUNE 1987 l
STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP.199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH) l DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL 4
i l
N O
2 1
3 0
0 6
NNE.~
O O
O 1
O O
1 NE O
O 1
.O O
O 1
j i
ENE O
O O
O O
O O.
E O
1 1
1 O
O 3
ESE O
O 5
2 O
O 7
O O
8 SE 1
1 2
t i
SSE-0 4
4 4
4 0
16 S
1 1
3 1
2
'O 8.
SSW O
2 0
0 2
0 4
i SW 2
1 2
O O
O 5
WSW 1
0 4
1 O
O 6
W 1
1 4
1 O
O 7
f WNW 1
1 4
2 O
O 8
NW O
1 2
2 O
O 5
NNW 1
0 4
1 O
O 6
i VARIABLE O
O O
O O
O O
-TOTAL 8
15 37 23 8
0 91 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 classest 4
i I
f 100 i
I
o ai BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
O 3
12 5
2 0
22 NNE O
8 8
1 O
O 17 NE 1
3 13 9
0 0
26 ENE O
4 9
0 0
0 13 E
O 7
12 O
O O
19 ESE O
7 13 6
O O
26 SE O
13 17 2
O O
32 SSE O
9 14 3
3 0
29 S
O 10 17 15 17 6
65 SSW O
4 14 29 10 0
57 SW O
O 9
10 0
0 19 WSW O
O 6
5 O
O 11 W
O 1
6 2
1 0
10 WNW O
3 7
12 O
O 22 NW O
1 11 13 O
O 25 NNW O
2 8
12 3
0 25 l
VARIABLE O
O O
O O
O O
TOTAL 1
75 176 124 36 6
418 t
Hours of calm in this stability classa O
Hours of missing wind measurements in this stability class O
Hours of missing stability measurements in all stability classest 6
101
1 BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
O 2
3 2
1 0
8 NNE O
3 3
1 O
O 7
NE O
2 6
2 O
O 10 ENE O
1 2
O O
O 3
E O
O 3
0 0
0 3
ESE O
O O
O O
O O
SE 1
2 3
2 O
O 8
SSE O
3 7
1 O
O 11 S
O 6
7 2
3 2
20 SSW O
4 13 6
3 0
26 SW O
7 3
4 2
0 16 WSW O
2 10 4
1 0
17 W
O 3
10 5
2 0
20 WNW O
4 6
4 1
0 15 NW O
7 1
7 O
O 15 NNW O
7 4
2 1
0 14 VARIABLE O
O O
O O
O O
TOTAL 1
53 81 42 14 2
193 Hours of calm in this stability classt O
Hours of missing wind measurements in this stability class O
Hours of missing stability measurements in all stability classest 6
102
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - SLIGHTLY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
O 4
2 i
O O
7 NNE O
5 3
1 O
O 9
NE O
1 5
2 O
O 8
ENE 1
0 1
O O
O 2
9 E
O 2
1 O
O O
3 ESE O
O 1
2 O
O 3
SE O
2 3
2 O
O 7
SSE O
3 0
0 0
0 3
S O
4 6
3 2
0 15 SSW O
6 5
7 0
0 18 SW O
3 10 3
0 0
16 WSW O
2 7
5 0
0 14 i
W O
3 1
7 1
0 12 WNW O
3 8
8 0
0 19 NW O
2 4
3 0
0 9
NNW O
5 4
0 0
0 9
VARIABLE O
O O
O O
O O
TOTAL 1
45 61 44 3
0 154 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 6
103
W BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - NEUTRAL (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
O 2
17 4
0 0
23 NNE 3
7 10 2
O O
22 NE O
6 11 6
1 0
24 ENE 1
2 15 2
O O
20 E
3 3
12 7
0 0
25 ESE 1
2 8
10 2
0 23 SE O
11 16 11 O
O 38 SSE 1
3 18 13 0
0 35 S
O 4
20 64 14 2
104 SSW 1
3 34 67 8
1 114 SW O
10 26 7
O O
43 WSW O
3 10 18 0
0 31 W
1 2
10 8
0 0
21 WNW O
13 18 12 O
O 43 NW O
2 11 10 1
0 24 NNil 1
8 24 13 1
0 47 VARIABLE O
O O
O O
O O
TOTAL 12 81 260 254 27 3
637 Hours of calm in this stability class:
O Hours of missing wind measurements in this stability class O
Hsurs of missing stability measurements in all stability cle.ssest 64 104
x.
I' BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
2 5
15 4
0 0
26 NNE 1
5 8
5 0
0 19 NE O
5 7
5 0
1 18 ENE 1
5 16 1
O O
23 E
O 7
28 3
0 0
38 ESE 1
2 15 9
1 0
28 SE O
4 15 13 1
0 33 SSE 1
9 15 12 O
O 37 S
1 2
20 38 2
0 63 SSW O
4 12 31 6
0 53 SW O
4 6
19 1
0 30 WSW O
2 10 11 O
O 23 W
O O
11 16 0
0 27 WNW O
2 8
5 0
0 15 NW O
4 10 8
0 0
22 NNW 1
4 25 6
0 0
36 VARIABLE O
O O
O O
O O
TOTAL 8
'64 221 186 11 1
491 i
Hours of calm in this stability classt O
Hours of missing wind measurements in this stability classt O
Hours of missing stability measurements in all stability classest 6
s 105
i 1
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
1 3
5 0
0 0
9 NNE O
3 5
2 O
O 10 NE 1
3 1
3 0
0 8
ENE 1
6 0
0 0
0 7
E O
3 3
2 O
O 8
ESE O
3 12 14 0
0 29 SE O
5 10 14 0
0 29 SSE O
6 4
3 0
0 13 S
1 0
3 18 0
0 22 SSW O
4 8
3 0
0 15 SW O
1 2
1 O
O 4
WSW O
3 1
3 0
0 7
W 0
3 1
5 0
0 9
WNW 1
5 3
15 O
O 24 NW O
1 14 6
0 0
21 NNW O
1 13 2
O O
16 VARIABLE O
O O
O O
O O
TOTAL 5
50 85 91 O
O 231 Hours of calm in this stability classt 0
Hours of missing wind measurements in this stability class O
Hsurs of missing stability measurements in all stability classest 6
106
i, 9
E BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - JULY-SEPTEMBER 1987 STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 199-30 FT)
WINDS NEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 0,T 2 4 TOTAL N
O 2
i O
O O
3 NNE O
3 0
0 0
0 3
NE 1
1 O
O O
O 2
ENE O
8 3
0 0
0 11 E
1 0
5 1
O O
7 ESE 2
1 4
5 0
0 12 SE O
5 2
3 0
0 10 SSE O
4 1
2 O
O 7
S O
1 O
O O
O 1
SSW O
O 1
1 O
O 2
SW 1
O O
O O
O 1
WSW O
O O
O O
O O
W O
1 O
O O
O 1
WNW O
O 1
5 0
0 6
NW 1
1 3
3 0
0 8
NNW 1
2 1
O O
O 4
VARIABLE O
O O
O O
O O
TOTAL 7
29 22 20 0
0 70 H3urs 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 6
107
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - EXTREMELY UNSTABLE (DIFF TEMP 199-30 FT) i WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH) 1 DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
O 2
5 4
0 0
11 NNE O
1 0
1 O
O 2
NE O
O 3
0 0
0 3
ENE O
O O
O O
O O
E O
O 2
O O
O 2
ESE O
O 8
2 O
O 10 SE O
O 9
2 1
0 12 SSE O
O O
O 1
0 1
S O
1 4
9 3
0 17 SSW O
O O
6 5
1 12 SW O
O 1
4 2
0 7
WSW O
O 6
O O
O 6
W O
O 4
4 0
1 9
WNW O
O 1
6 1
0 0
NW O
O 2
2 9
1 14 i
NNW O
O 5
5 4
2 16 VARIABLE O
O O
O O
O O
TOTAL G
4 50 45 26 5
130
(
i Heurs of calm in this stability classt O
Hours of missing wind measurements in this stability class:
O l
Heurs of missing stability measurements in all stability classest 38
[
l 4
108 i
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - MODERATELY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
O O
1 2
O O
3 NNE O
O 1
3 O
O 4
NE O
O O
O O
O O
ENE O
O O
O O
O O
E O
O O
O O
O O
ESE O
1 0
2 O
O 3
SE O
O 5
2 1
1 9.
SSE 1
O O
O 1
1 3
S O
O 2
4 3
3 12 SSW O
2 3
5 3
0 13 SW 1
0 1
4 2
0 8
WSW O
1 9
2 1
0 13 W
O 1
3 4
i O
9 WNW O
O 1
3 5
0 9
NW O
2 2
3 3
0 10 NNW O
2 2
3 2
2 11 VARIABLE O
O O
O O
O O
TOTAL 2
9 30 37 22 7
107 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 38 109
?
I BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - SLIOHTLY UNSTABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
O O
O O
1 0
1 i
l NNE 1
1 O
O O
O 2
NE O
2 2
O O
O 4
ENE 1
1 3
4 0
0 9
E O
2 1
O O
O 3
ESE O
O O
3 1
0 4
SE O
1 2
1 2
1 7
SSE O
O 1
0 1
1 3
S 1
1 1
5 7
1 16 SSW O
O 3
4 1
2 10 i
SW O
O 1
6 1
0 8
WSW O
3 5
4 1
1 14 W
O 1
6 10 7
3 27 WNW O
O 1
10 7
4 22 NW O
2 2
2 O
O 6
NNW 1
3 3
1 3
4 15 VARIABLE O
O O
O O
O O
t TOTAL 4
17 31 50 32 17 151 i
1 Hours of calm in this stability classt O
l Hours of missing wind measurements in this stability classt O
l Hours of missing stability measurements in all stability classest 38 l
t i
b 110
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - NEUTRAL (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
1 3
37 33 1
0 75 NNE O
1 12 18 2
0 33 NE O
5 11 16 3
1 36 ENE O
2 16 30 6
0 54 E
O 3
28 14 0
0 45 ESE O
O 2
19 1
0 22 SE O
1 6
20 8
1 36 SSE O
1 11 31 21 5
69 S
O 2
17 42 26 18 105 i
1 SSW O
3 12 35 27 12 89 SW O
3 11 33 8
3 58 i
WSW O
1 19 25 18 4
67 W
O 3
11 47 33 16 110 WNW 1
6 22 37 43 9
118 NW 1
6 13 32 17 5
74 s
NNW O
O 14 38 22 0
74 i
VARIABLE O
O O
O O
O O
TOTAL 3
40 242 470 2d6 74 1065 l
Hours of calm in this stability classt O
Hours of missing wind measurements in this' stability class 18 Hours of missing stability measurements in all stability classest 38 8
\\
l j
111
r _
f BRAIDWOOD NUCLEAR POWER STATION j
PERIOD OF RECORD - OCTOBER-DECEMBER 1987 i
STABILITY CLASS - SLIGHTLY STABLE (DIFF TEMP 199-30 FT) t WINDS MEASURED AT 199 FEET i
WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 OT 24 TOTAL N
O 3
11 9
0 0
23 NNE O
2 5
5 O.
O 12 NE O
2 0
1 O
O 3
ENE 1
4 6
4 0
1 16 E
O 4
4 3
0 0
11 ESE O
3 5~
10 6
0 24 SE O
O 1
13 13 2
29 SSE 1
0 7
13 13 1
35 S
O 2
5 65 20 3
95 SSW O
3 8
20 16 6
53 SW O
2 6
26 4
2 40 WSW O
3 4
21 2
0 30 W
O O
8 15 3
0 26 WNW O
2 6
15 3
0 26 NW O
2 14 7
8 0
31 NNW O
4 16 2
O O
22 VARIABLE O
O O
O O
O O
TOTAL 2
36 106 229 88 15 476 Hours of calm in this stability classt O
Hours of missing wind measurements in this stability classt 30 Hours of missing stability measurements in all stability classest 38 l
1 112
4
+
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 STABILITY CLASS - MODERATELY STABLE (DIFF TEMP 199-30 FT' WINDS MEASURED AT 199 FEET WIND WIND SPEED (IN MPH)
DIRECTION
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
O 4
10 2
0 0
16 NNE O
1 2
1 0
0 4
NE O
1 1
0 0
0 2
ENE O
O 2
0 0
0 2
s E
O 2
1 1
0 0
4 ESE O
O 3
10 0
0 13 SE O
O O
3 0
0 3
SSE O
O 1
1 2
0 4
S O
O 1
6 2
0 9
SSW 0
1 1
12 0
0 14 SW 0
3 0
10 3
0 16 WSW 1
1 1
3 0
0 6
W 0
0 4
6 0
0 10 WNW 0
0 0
10 0
0 18 NW 0
3 7
8 0
0 18 NNW 1
2 4
0 0'
O 7
t VARIABLE O
O O
O O
O O
TOTAL 2
18 46 73 7
0 146 Hours of calm in this stability class O
Hours of massing wind measurements an this stability class 4
Hours of missing stability measurements in all stability classes 38 I
113
f i'
BRAIDWOOD NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER-DECEMBER 1987 l
STABILITY CLASS - EXTREMELY STABLE (DIFF TEMP 199-30 FT)
WINDS MEASURED AT 199' FEET WIND WIND SPEED (IN MPH)
DIRECTION'
.8-3 4-7 8-12 13-18 19-24 GT 24 TOTAL N
0 1
4 0
0 0
5 NNE O
O O
O O
O O
l NE o
0 0
0 0
0 0
l ENE O
O O
O O
O O
1 l
E O
O 3
0 0
0 3
ESE O
O 1
0 0
0 1
SE O
O O
1 0
0 1
SSE O
O O
O O
O O
S O
O 2
0 0
0 2
SSW 0
0 2
0 0
0 2
SW 0
1 1
1 0
0 3
WSW 1
0 5
4 0
0 10 i
W 0
0 2
0 0
0 2
l WNW 0
1 3
0 0
0 4
l NW 0
1 1
0 0
0 2
NNW 1
0 4
1 0
0 6
. VARIABLE O
O O
O O
O O
TOTAL 2
4 28 7
0 0
41 Hours of calm in this stability classt 0
Hours of missing wind measurements in this stability class:
2 Hsurs of missing stability measurements in all stability classes 38 114
i APPENDIX III LISTING OF MISSED SAMPLES i.
l
[
i i
i i
i t
i 115
f i
I LISTING OF MISSED SAMPLES Expected i
Collection Sample Type Location Dates Reason l
Cooling Water 80-08 01-23-87 River frozen Precipitation BD-11 February Insufficient amount Precipitation BD-12 February Insufficient amount
[
Precipitation 80-17 February Insufficient amount
.i Precipitation 80-18 February Insufficient amount i,
Precipitation 80-18 July Insufficient amount I
Precipitation 80-12 October Insufftcient amount
[
t
(
I I
116 I
_ :? '
fjW/88-263
,y; N Commonwealth Edison -
)
y
- j. Brildwood Nuclsir Powtr Stitlin -
,, (/
- Routa C1, Box 84 -
'\\
.}f
~m Bracevil'e, Illinois 60407 l
.. Telephone 815/458-2001 l
February 11, 1988-Mr. A.Bert Davis Regional Administrator Directorate of Inspection and Enforcement Region III U.S. Nuclear Regulatory Con: mission 799 Rocaevelt Road Glen Ellyn, Illinois 60137
Subject:
Braidwood Station Operating Report, NRC Dockets STN 50-h56 STN 50-457.
Dear Mr. Davis:
Enclosed is Part 3 of the Braidwood Station Operating Report, reporting results of Environmental Radiological 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 l
Inspector.
k Sincerely yours, j
[
'I E. E. Fitzpatrick I
Station Manager Enclosure
/
EEF/KAR/mb 3
t1 V
4/
I (
a
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