ML20034E893
| ML20034E893 | |
| Person / Time | |
|---|---|
| Site: | La Crosse File:Dairyland Power Cooperative icon.png |
| Issue date: | 12/31/1992 |
| From: | DAIRYLAND POWER COOPERATIVE |
| To: | |
| Shared Package | |
| ML20034E883 | List: |
| References | |
| NUDOCS 9303020054 | |
| Download: ML20034E893 (78) | |
Text
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RADI0 ACTIVE EFFLUENT REPORT AND l
l RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT FOR THE l
LA CROSSE BOILING WATER REACTOR (LACBWR) dBk (January 1 to December 31, 1992) l l
1 DAIRYLAND POWER COOPERATIVE I
Docket No. 50-409 l
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9303020054 930225 PDR ADOCK 05000409 R
PDR i
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TABLE OF CONTENTS SECTION TITLE PAGE A.
Radioactive Effluent Report Introduction 1
1.0 Regulatory Limits 2
2.0 Maximum Permissible Concentration 4
3.0 Average Energy 4
4.0 Analytical Methods 4
5.0 Batch Releases 6
6.0 Abnormal Releases 7
7.0 Estimated Total Analytical Error 7
()
8.0 Offsite Dose Calculation Summary and Conclusions 13 9.0 Meteorological Atmospheric Dispersion 14 Constants 10.0 Errata for the 1990 and 1991 Radioactive Effluent Reports 15 B.
Environmental Report Introduction 32 1.0 Sample Collection 33 2.0 Results of the 1992 Radio-Environmental Monitoring Survey 34 3.0 Conclusions 37 4.0 Interlaboratory Comparison Program Results 37 O
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TABLES l
TABLE NO.
TITLE PAGE l
1A Effluent and Waste Disposal Caseous Effluent Release Summaries 8
l 1B Caseous Effluents - Elevated Release 9
2A Liquid Release Summary 10 2B Liquid Effluents 11 l
t 3
Solid Waste and Irradiated Fuel l
Shipments 12 4
Meteorological Atmospheric Dispersion 14 Constants 4A 1991 Joint Wind Frequency Data 16 5
Sample Frequency and Analysis of i
Radio-Environmental Samples (thru Feb.1992) 45 j
i
()
SA Sample Frequency and Analysis of Radio-Environmental Samples (thru rest of 1992) 46
[
6 Permanent Environmental Monitoring Station Locations 47 7
Environmental TLD Locations (1st quarter 1992) 48 7A Environmental TLD Locations (2nd, 3rd, and f
4th quarters 1992) 49 i
8 Radio-Environmental Samples Collected January-December 1992 50 9
Quarterly TLD Measurements in the LACBWR Vicinity (1st quarter 1992) 51 9A Quarterly TLD Measurements in the LACBWR Vicinity (2nd, 3rd, 4th quarters 1992) 52 10 Weekly Beta Air Particulates in the LACBUR Vicinity (thru Feb. 1992) 53 10A Weekly Beta Air Particulates in the LACBWR Vicinity (thru rest of 1992) 54 i
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TABLES - (cont'd)
TABLE NO.
TITLE PAGE 11 Air Particulate Composite Results 57 12 Results of Analysis of Mississippi River Water in the Vicinity of LACBWR 63 13 Reruits of Analysis of Mississippi River Sediment in the Vicinity of LACBWR 69 14 Results of Analysis of Milk Samples in the Vicinity of LACBWR 70 15 Fish Samples Activity in the Vicinity of LACEUR 71 16 Vegetation Samples Activity in the Vicinity of LACBWR 73
(~q
%.)
FIGURES No.
TITLE PAGE FIGURE 1 LACBWR Property Map 38 FIGURE 2 Permanent Environmental Monitoring Station Location (1st quarter 1992) 39 FIGURE 2A Permanent Environmental Monitoring Station Location (2nd, 3rd, & 4th quarters 1992) 40 l
FIGURE 3 LACBWR Environmental Dose Assessment l
Locations (1st quarter 1992) 41 1
FIGURE 3A IACBWR Environmental Dose Assessment Locations (2nd, 3rd, & 4th quarters 1992) 42 FIGURE 4 LACBWR Environmental Dose Assessment Locations (1st quarter 1992) 43 FIGURE 4A LACBWR Environmental Dose Assessment Locations (2nd, 3rd, & 4th quarters 1992) 44 iii
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SECTION A RADI0 ACTIVE EFFLUENT REPORT g
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INTRODUCTION:
I The La Crosse Boiling Water Keactor (LACBWR), also known as Genoa Station No. 2, is located on the east bank of the Mississippi River near i
Genoa, Vernon County, Wisconsin. The plant was designed and constructed by l
the Allis-Chalmers Manufacturing Company.
It was completed in 1967 and had a generation capacity of 50 MW (165 MW{th)). The reactor is owned by Dairyland Power Cooperative (DPC).
I The reactor went critical in July 1967 and first contributed electricity to DPC's system in April 1968. After completing full power tests in August i
i 1969, the plant operated between 60% and 100% full power, with the exception of plant shutdowns for 1:nintenance and repair.
1 In April of 1987 plant operation was ceased.
The reactor is presently defueled and in a SAFSTOR trode.
In August of 1987 a possession-only license was received.
In accordance with LACBWR Technical Specifications 6.8.1.1.d and in compliance with 10 CFR 50.36a(a)(2), this document is the Radioactive Effluent Report for the period January 1 through December 31, 1992.
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EFFLUENT AND WASTE DISPOSAL REPORT (Supplemental Information)
FACILITY: Lacrosse Boiling Water Reactor LICENSEE: DAIRYLAND POWER COOPERATIVE DOCKET NO. 50-409 1.
REGULATORY LIMITS l
a.
Gaseous Effluent Release Limits:
LACBWR's Technical Specifications for gaseous effluent releases of radioactive material limit the release rates of the sum of the
[
individual radionuclides, so that the dose rates to members of the public beyond the Effluent Release Boundary do not exceed 500 mrem / year j
to the whole body, 3000 mrem / year to the skin from noble gases, and 1500 mrem / year to a critical organ from H-3 and particulates with half-lives i
I greater than 8 days.
I Also, in accordance with 10 CFR 50, Appendix I, the Technical j
Specifications for gaseous effluent radioactive material limit the air i
l dose to a member of the public from noble gases in areas beyond the l
Effluent Release Boundary to less than 5 mrad gamma and 10 mrad beta per calendar quarter, and less than 10 mrad gamma and 20 mrad beta per calendar year. 'The dose limits from H-3 and particulates with half-l lives greater than 8 days are less than 7.5 mrem per calendar quarter, and less than 15 mrem per calendar year to any organ.
Cumulative dose contributions from gaseous effluent releases are determined in accordance with the LACBWR Offsite Dose Calculations Manual.
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2 h.
Liquid Effluent Release Limits:
()
LACBWR's Technical Specification limits for liquid effluent 4
releases are limited to those concentrations of individual radionuclides such that the diluted discharge does not exceed 1 MPC in a 168-hour week averaged over the calendar year. For dissolved or entrained noble r
gases, the concentration is limited to a total activity concentration of 6 x 10 pCi/ml. For alpha emitting radionuclides, t'.ne concentration is limited to a total activity concentration of 4.9 x 10~8 pCi/ml, based i
upon an actual alpha emitting radionuclide analysis performed on a representative water sample. The values reported in tables 2A and 2B, Liquid Effluents, are based on dilution with the combination of LACBWR and Genoa Station No. 3 condenser cooling water flow prior to discharge l
I to the Mississippi River. No credit is taken for further dilution in the mixing vene of the Mississippi River.
Also, in accordance with 10 CFR 50, Appendix I, the dose commitment to a member of the public from radioactive materials released in liquid effluents to areas beyond the Effluent Release Boundary are limited to less than 1.5 mrem whole body and 5.0 mrem organ dose per calendar quarter, and less than 3.0 mrem whole body and 10 mrem organ dose per calendar year via the critical ingestion pathway.
Cumulative quarterly and annual dose contributions from liquid i
effluent releases are determined for the adult fish ingestion pathway in accordance with the LACBWR Offsite Dose Calculation Manual.
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c.
Solid Radioactive Waste All solid radioactive wastes are handled in accordence with a I
Process Control Program as defined by LACEWR procedures in order to assure that all applicable transportation and burial site disposal j
requirements are met.
2.
MAXIMlW PERMISSIBLE CONCENTRATION (MPC)
The MPC esed to calculate permissible release rates are obtained from 10 CFR 20, Appendix B, Tables I and II.
In addition, the following values l
are used:
Tritium in i'etec = 3 x 10- 8 pCi/mi.
i Tritium in Air
= 2 x 10-' pCi/cc.
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3.
AVERAGE ENERGY The release rate limits for LACBWR are not based on average energy.
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i 4.
ANALYTICAL METHODS a.
Liquid Effluents Liquid effluent measurements for gross radioactivity are performed i
by Ge-Li gamma isotopic analysis of a representative sample from each l
l tank discharged.
In addition, each batch discharged tank is analyzed for alpha and tritium activity concentration. A composite sample is created by collecting representative aliquots from each tank batch discharged and is analyzed quarterly for Iron-55 and Strontium 90 by a contractor.
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l b.
Airborne Particulates Airborne particulate releases are determined by Ge-Li gamma isotopic analysis.
This analysis is performed by analyzing a glass fiber filter paper taken from the stack monitor (Eberline SPING) which continuously isokinetically samples and monitors the stack effluent.
l This filter is changed and analyzed on an approximate weekly basis and i
analyzed within 7 days after removal.
This filter is also analyzed for t
alpha activity. A quarterly composite of these filters is sent to a contractor for Sr 90 analysis.
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c.
Radioiodines l
l Since the plant shutdown in April 1987, the I-131/I-133 have decayed completely to stable elements.
Amendment 66 to the LACBWR i
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Technical Specifications, Table 5.7.2.2, no longer requires monitoring j
for iodine.
d.
Fission and Activation Gases The gaseous releases converted into concentration (pCi/cc) are continuously sampled from the stack release flow by two stack monitors, 1
which are in-line monitors. These gas concentrations (pCi/cc) are averaged by the monitors microprocessor and flowrate/ pressure compen-sated to obtain the daily gaseous release of the plant. Since the plant shutdown in April 1987, gaseous releases have been immeasurable. All i
fission gases except Kr-85 have decayed completely to stable elements.
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e.
Tritium Tritium releases are determined by taking a grab sample of the stack atmosphere at the effluent of t.he stack monitor. Tritium, as tritiated water, is removed from the sample st. ream by condensation, using a cold trap containing an organic compound and dry ice.
The condensed water vapor is then distilled and the distillate is analyzed for H-3 concentration, pCi/cc, by internal liquid scintillation spectrophotometry and the results are expressed in terms of tritium release rates.
The tritium grab samples are obtained on at. least a once/ month basis unless the upper reactor cavity is flooded, at which time the sampling frequency is increased to at least once per 7 days.
5.
BATCH RELEASES a.
Airborne All airborne effluent releases at LACBWR are from a single Continuous-Elevated Release Point.
b.
Liquid All liquid effluent releases at LACBWR are batch releases. This is summarized as follows:
(1) Number of Batch Releases:
15 (2) Total Time Period for Batch Releases:
157.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br /> i
(3) Maximum Time Period for a Batch Release:
21.8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> (4) Average Time Period for a Batch Release:
10.51 hours5.902778e-4 days <br />0.0142 hours <br />8.43254e-5 weeks <br />1.94055e-5 months <br /> (5) Minimum Time Period for a Batch Release:
4.67 hours7.75463e-4 days <br />0.0186 hours <br />1.107804e-4 weeks <br />2.54935e-5 months <br /> (6) Average Stream Flow Rate During Periods of Release of Effluent into a Flowing Stream: 39,670 ft /sec 8
O 6.
ABNORMAL RELEASES O
There were no abnormal releases of radioactivity in plant effluents as i
summarized as follows:
a.
Liquid 3
(1) Number of Releases:
None (2) Total Activity Released: N/A b.
Gaseous 3
(1) Number of Releases:
None (2) Total Activity Released: N/A 7.
ESTIMATED TOTAL ANALYTICAL ERROR i
The reported analytical results contain the following estimated errors:
l I
Counting Error i 1 Standard Deviation (S
Sampling Volume Error 1 54.
i
\\-)
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l The lower limits of detection (LLD) are expressed in terms of a 4.66 o I
as defined in Technical Specifications.
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TABLE 1A l
EFFLUENT AND WASTE DISPOSAL ANNUAL REPORT - 1992 GASEOUS EFFLUFRTS - SUMMATION OF ALL RELEASFS l
l l UNIT l QTR l
QTR l
QTR l
QTR l TOTAL l
)
f A.
FISSION & ACTIVATION GASES I
l
- 1. TOTAL RELEASE l
l l
l l
l l
l l
Ci l
0.00 l 0.00 l 0.00 l 0.00 l 0.00 l
l 2. AVERAGE RELEASE RATE l l
l l
l l
l FOR PERIOD l pC1/See l 0.00 l 0.00 l 0.00 l 0.00 l I
B.
IODINE I-131 - No longer analyzed for.
l C.
PARTICULATES l
- 1. PARTICULATES W/ HALF-l l
l l
l l
l l
LIVES > 8 DAYS l
Ci
!2.66E-7l1.92E-7l3.47E-5l1.68E-6!3.68E-5l l 2. AVERAGE RELEASE RATE l l
l l
l l
FOR PERIOD l pCi/See !3.53E-8l2.42E-8l4.37E-6l2.11E-7l l 3. GROSc ALPHA l
l l
l l
l l
RADI0 ACTIVITY l
Ci l7.07E-8l 0.00 11.40E-8!2.70E-7l
(}
D.
TRITIUM j 1. TOTAL RELEASE l
l l
l l
l l
l l
Ci l8.42E-2l3.02E-2l2.57E-2l5.35E-2!1.94E-1l l 2. AVERAGE RELEASE RATE l l
l l
l l
l FOR PERIOD
! pCi/Sec l1.10E-2l3.86E-3l3.25E-3l6.73E-3]
l E.
PERCENTAGE OF (APPENDII I) TECHNICAL SPECIFICATION LIMITS 1.
NOBLE GAS RELEASE l QTR l QTR l
GAMMA l
l 0.00 l 0.00 l 0.00 l 0.00 l 0.00 l l
BETA l
l 0.00 l 0.00 l 0.00 l 0.00 t 0.00 l 2.
H-3 AND ALL RADIONUCLIDES IN PARTICULATE FORM WITH HALF-LIVES GREATER THAN 8 DAYS l QTR l
QTR l
QTR l
QTR l YEARLY l j HIGHEST ORGAN l
l4.59E-4l1.70E-4l3.96E-2l3.40E-4l1.98E-2l O
l l l
TABLE 'B
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EFFLUENT AND WASTE DISPOSAL ANNUAL REPORT - 1992 j
GASEOUS EFFLUENTS - ELEVATED RELEASE F
h CONTINUOUS MODE l NUCLIDES RELEASED l UNIT l
QTW l
QTR l
QTR l
QTR l TOTAL l 1
i 1.
FISSION GASES e
l l
Ci l 0.00 l 0.00 1 0.00 l 0.00 l 0.00 l
2.
10 DINES - No longer analyzed for.
J
- l 3.
PARTICULATES I
l STRONTIUM-90 l
Ci l 0.00 l 0.00 l3.40E-5l 0.00 l3.40E-5l j
CESIUM-134 l
Ci l 0.00 l1.26E-7l 0.00 l 0.00 l1.26E-7l l
Ci l4.90E-8l2.22E-8l3.32E-7l 8.6E-7l1.26E-6l l
Ci l2.17E-7l4.40E-8l4.03E-7l7.81E-7l1.45E-6l l
Ci l 0.00
! 0.00 0.00 0.00 l 0.00 l
I l
ZINC-65 i
Ci l 0.00 l 0.00 l 0.00 l3.60E-8l3.60E-8j
(]}
l l
Ci l
l l
l l
l
?
l l
Ci l
l l
l l
l l
l Ci l
l l
l l
l l
TOTALS l
Ci l2.66-7 l1.92-7 l3.47-5 l1.677-6l3.687-5l i
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a
_9_
7
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TABLE 2A EFFLUENT AND WASTE DISPOSAL ANNUAL REPORT - 1992 LIQUID EFFLUENTS - SUMMATION OF ALL RELEASES l
l UNIT l
QTR l
! TOTAL l A.
FISSION & ACTIVATION PRODUCTS i
l
- 1. TOTAL RELEASE (NOT INCL l l
l l
l l
l l
l TRITIUM, GASES, ALPHA) !
Ci l9.90E-3l9.87E-3l1.93E-2!1.33E-215.24E-2l l
l 2. AVERAGE DJLUTED CONCEN-l l
l l
l l
l TRATION DURING PERIOD lpCi/ml l7.86E-9l6.67E-9l1.39E-8l1.45E-8l l
B.
TRITIUM l 1. TOTAL RELEASE l
l l
l l
l l
i l
l
! Ci
!4.51E-2!6.42E-2l5.91E-2l1.48E-2l1.83E-1l l
l 2. AVERAGE DILUTED CONCEN-l l
l l
l l
l l
TRATION DURING PERIOD lpCi/ml ll.49E-7!4.34E-8!4.25E-8l1.76E-8l C.
DISSOLVED AND ENTRAINED GASES
~'
l 1. TOTAL RELEASE l
l l
l l
l l
l
(])
i Ci l
0.00 !
0.00 l 0.00 !
0.00 l 0.00 l l
l 2. AVERAGE DILUTED CONCEN-l l
l l
l l
l TRATION DURING PERIOD lpCi/ml l 0.00 !
0.00 1 0.00 1 0.00 l 1
D.
GROSS ALPHA RADIOACTIVITY l 1. TOTAL RELEASE l
l l
l l
l l
Ci l8.42E-6!8.10E-6!2.22E-5l2.54E-5l6.41E-5l J
lE. VOLUME OF WASTE RELEASED l l
l l
l l
l l
(PRIOR TO DILUTION)
! Liters 15.62E4 16.80E4 l8.50E4 l5.99E4 l2.69ES l l
l lF. VOLUME OF DILUTION WATER l l
l l
l l
l l
USED DURING PERIOD l Liters l3.03E8 l1.48E9 l1.39E9 18.43E8 l4.02E9 l l
i G. PERCENTAGE OF (APPENDIX I) TECHNICAL SPECIFICATION LIMITS FOR LIQUID RELEASES l QTR l
QTR l QTR l QTR l YEARLY l l HIGHEST ORGAN i
7.
l4.96E-2l1.50E-2l4.92E-2l5.18E-218.28E-2l l WHOLE BODY l
! 0.11 l3.30E-21 0.11 l 0.11 l 0.18 l
0,
TABLF 2B EFFLUENT AND WASTE DISPOSAL ANNUAL REPORT - 1992 LIQUID EFFLUENTS l
l l NUCLIDES RELEASED l UNIT l QUARTER l QUARTER l QUARTER l QUARTER l
l STRONTIUM-90 l
Ci l 6.09E-5 l 6.56 E-5 l 0.00 l 5.35E-5 l
l CESIUM-134 l
Ci l
l l
l l CESIUM-137 l
Ci l 2.47E-3 l 3.40E-3 l 3.73E-3 l 3.39E-3 l
1 l_ COBALT-58 l
Ci l
l l
l l
l l COBALT-60 l
Ci l 4.36E-3 l 3.97E-3 l 1.14E-2 l 8.74E-3 l
l IRON-55 l
Ci l 2.98E-3 l 2.43E-3 l 4.10E-3 l 1.07E-3 l
l IRON-59 Ci l
l l
l l ZINC-65 l
Ci l
l l
l l
l MANGANESE-54 l
Ci l 2.46E-5 l
l 5.64E-5 l
l l CHROMIUM-51 l
Ci l
l l
l ZIRCONIUM-NIOBIUM-95 l
Ci l
l l
l l
l l MOLYBDENUM-99 l
Ci l
l l
l l
l l TECHNETIUM-99M l
Ci l
l l
l l BARIUM-LANTHANUM-140 l
Ci l
l l
l l
l l
l CERIUM-141 l
Ci l
l l SILVER-110M l
Ci l
l l
l l
Ci l
l l
l l
O l
l Ci l
l l
l l
i l
l Ci l
l l
l l
l TOTAL FOR PERIOD (ABOVE)l Ci l 9.90E-3 l 9.87E-3 l 1.93E-2 l 1.33E-2 l
I l KR-85 i
Ci l
l l
l l
l l
i l
l 0 l
i j
l TABLE 3 i
EFFLUENT AND WASTE DISPOSAL ANNUAL REPORT - 1992 SOLID WASTE AND IRRADIATED FUEL SHIPMENTS 5
SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL (NOT IRRADIATED FUEL)
A.
l l
l 6-MONTH l 6-MONTH l l
l 1. TYPE OF WASTE l UNIT l PERIOD l PERIOD l TOTAL l rn l
0 l
0 l
0 l
3 l
- a. SPENT RESINS, FILTER SLUDGES, l
l EVAPORATOR BOTTOMS, ETC.
l Ci l
0 l
0 l
0 l
l
- b. DRY COMPRESSIBLE WASTE, l m l
0 l
3.72 l
3.72 l 8
l CONTAMINATED EQUIPMENT, ETC.
l Ci l
0 l 4.36E-1 l4.36E-1l m
l 0
l 0
0 l
3 l
- c. IRRADIAIED COMPONENTS, l
l CONTROL RODS, ETC.
l Ci l
0 l
0 l
0 l
l
- d. OTHER (DESCRIBE) l m
l 0
l 0
l 0
l 8
l l
Ci 0
l 0
l 0
l l
l 2.
ESTIMATE OF MAJOR NUCLIDE COMPOSITION l
l 6-MONTH l 6-MONTH l (BY TYPE OF WASTE) l PERCENT l PERIOD l PERIOD l i
b.
Co-60 l 42.47 l l 1.85E-1 l Cs-137 l
2.22 l l 9.67E-3 l 4
Fe-55 l 46.97 l l 2.05E-1 l Ni-63 l
5.38 l l 2.35E-2 l Mn-54 l
1.83 l l 7.99E-3 l l
Pu-241 l
0.45 l l 1.94E-3 l
()
Fe-59 l
0.68 l l 2.94E-3 l Sr-90 l3.21E-3!
l 1.40E-5 l 1
)
- 3. SOLID WASTE DISPOSITION NO. OF SHIPMENTS MODE OF TRANSPORTATION DESTINATION 11 SOLE USE BARNWELL, S.C.
B.
IRRADIATED FUEL SHIPMENTS (DISPOSITION)
NO. OF SHIPMENTS MODE OF TRANSPORTATION DESTINATION l
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t O j I
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8.
OFFSITE DOSE CALCUIATIONS SLHMARY AND CONCLUSIONS:
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a.
Gaseous Effluent Releases The maximum quarterly offsite gamma dose due to nobic gases was j
0.00 mrad. The cumulative 1992 annual offsite gamma dose due to noble gases was 0.00 mrad.
The maximum quarterly offsite beta dose due to noble gases was 0.00 mrad.
The cumulative 1992 annual offsite beta dose due to noble gases was 0.00 mrad.
The maximum quarterly offsite dose to any organ from the release of H-3 and all radionuclides in particulate form with half-lives greater than 8 days was approximately 2.97E-3 mrem.
The cumulative 1992 annual maximum organ dose from these radionuclides was also approximately 2.97E-3 mrem, since the indicated release of Sr-90 in the third quarter was the controlling dose for the maximum annual dose.
O The highest historical monthly and annual average X/Q's for the period 1985-1987 for the worst case offsite receptor location, in i
accordance with the ODCM, were used to calculate these offsite dose l
I values.
b.
Liquid Effluent Releases The maximum quarterly organ dose from liquid releases was approximately 2.59E-3 mrem. The maximum cumulative 1992 annual organ dose was approximately 8.28E-3 mrem. The maximum quarterly whole body dose for liquid releases was approximately 1.65E-3 mrem, and the i
l cumulative 1992 annual whole body dose was approximately 5.40E-3 mrem.
l c.
Conclusion All calculated offsite doses were below Technical Specification limits.
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i 9.
METEOROLOGICAL ATMOSPHERIC DISPERSION CONSTANTS TABLE 4 l
l l
(1) l (2) l (3) l (3) l l
Receptor l
T l
'X' l
D_
l D
l l
Location l
<Q2 l
<q; l
Q l
a l
l l
l l
l l
l 600m ENE l
1.694 E-6 l
3.379 E-6 l
4.11 E-9 l
7.40 E-9 l
l l
l l
l l
l l
l i
l l
l l
1300m SSE l
1.026 E-6 l
1.594 E-6 l
3.59 E-9 l
1.03 E-8 l
l l
l l
l l
l l
l l
l l
l l
1000m D4E l
6.712 E-7 l
1.341 E-6 l
l l
l l
l l
l l
X D
I
- For quarterly offsite dose calculations, the Q and Q values from receptor location 600m ENE will be used.
This provides the most i
conservative dose commitments based on an annual maximum historical l
dispersion parameter.
i (1) sec/ma - maxbnum historical long-term (annual) dispersion parameters.
- maximum historical short-term (monthly) dispersion parameters.
(2) sec/m8 I
(3) m based upon historical meteorological data, using methodology of NRC Regulatory Guide 1.111 and Julich data.
3 The joint wind frequency data valid for LACBWR stack release for 1992 is not available at this time due to data logging probicas. The data vill be sent under separate cover when it becomes available. This wind data is collected from a mounted boom projecting out near the top of the vent stack.
The stability determination is based upon the temperature difference between the 10m surface meteorological tower and the 100m meteorological boom The 1
stability class is then ascribed following the method outlined in Reg. Guide j
1.23.
This will be the last year this data is provided due.to changes in LACBWR's Technical Specifications.
O 10.
ERRATA FOR THE 1990 AND 1991 RADIOACTIVE EFFLUFRT REPORTS Several computation errors were noted on Tables 2A and 2B of the 1990 report. The corrected portions of the report are listed below, i
Table 2A A.
FISSION & ACTIVATION PRODUCTS l
- 1. TOTAL RELEASE (NOT INCL l l
j l
j l
l l
TRITIUM, GASES, ALPHA) !
Ci l1.03E-212.28E-2l2.02E-2!1.53E-2!6.86E-2l l 2. AVERAGE DILUTED CONCEN-l l
l l
l l
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O RUN O*16:
1-26-93 DPC ENVIROMEN TAL 110Nl rORING SYSTEM PACCt 18 PERCENTAGE WIND FREQUENCY DISTIBUTION BY PASQUILL STABILITY CLASS
- SITE NAMEt LACBWR STACK PERIOD OF RECORD: 91-B1-91 THRU 12-31-91 PASQUILL CLASS C SAROAD NO S13622B24 STABILITY INSTRUMENTATION-DELTA TEMP SLIGHTLY UNSTABLE t
WIND SPEED (MPH)
PERCENT AVERACE DIRECTION B-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED 1
l N
B.BB B.43 B.63 B.14 B.BB B.89 1.28 12.2 NNE B.BB B.83 B.BG B.81 B.BB B.BB B.18 8.3 NE B.BB B.BB B.04 B.BB B.BB B.BB B.04 8.9 l
ENE B.BB B.Bl B.BB B.81 9.28 B.BB 2.03 18.3 E
B.BB B.81 B.BB B.BB B.BB B.BB B.01 6.9 ESE B.BB B.84 B.BB B.BB B.BB B.BB B.04 G.5 SE B.BB B.BB B.BG B.BB B.BB B.BB B.06 9.3 SSE B.BB B.BB B.29 B.99 B.01 B.BB B.19 12.8 S
B.BB B.26 B.58 B.52 B.85 B.B1 1.15 12.8 SSW B.BB B.94 B.88 0.13 B.11 B.91 B.37 15.2 SY B.BB B.BB B.11 B.BB B.BB B.BV B.11 9.1 MSV B.BB B.BB B.01 0.23 B.BB B.BB B.04 11.7 Y
B.BB B.BB B.BB 2.21 B.BB B.BB 2.21 12.9 MNV B.BB B.BB B.BB B.BB B.BB B.BG B.02 0.0 NY B.BB B.B3 B.14 B.13 B.81 B.BB D.38 12.0 NNY B.28 B.98 B.14 B.BG B.BB B.BB B.28 19.4 VARlABLE B.BB B.22 B.00 B.BB B.BB 2.BB B.BB 2.0 i
PERCENT TOTAL B.BB B.72 1.86 1.12 B.19 B.11 4.98 AVG SPEED B.B 6.1 9.9 14.8 29.8 27.2 11.6 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABTVE V".TH SLIGHTLY UNSTABLE STABILITY =
B.B
^
VALID READINGS =
318 t
i i
TABLE 4A i
j i
4
rub ATE:
1-26-93 DPC ENVIROMENTAL I4ux5TORING SYSTEM PAGE: 19 PERCENTAGE VIND FREQUENCY DISTIBUTION BY PASQUILL STABILITY CLASS SITE NAME: LACBVR STACK PERIOD OF RECORDe B1-81-91 THRU 12-31-91 PASQUILL CLASS D
- SAROAD NO 513628E84 STABILITY INSTRUMENTATION-DELTA TEMP NEUTRAL t
VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION 0-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
B.25 2.91 2.86 1.74 B.59 8.23 6.89 11.3 NNE 8.11 1.23 1.82 U.16 B.81 8.8B 2.34 7.8 NE B.84 B.79 B.53 B.16 M.BB B.BE 1.52 7.8 ENE F.89 9.44 B.45 8.11 8.81 H.8F 1.11 0.2 E
8.14 E.55 8.37 8.99 8.81 F.BB 1.16 7.4 ESE 8.54 s.69 s.71 8.11 8.83 8.89 1.57 S.2 SE 9.19 F.88 8.97 f.57 9.53 F.11 3.16 11.8 SSE 8.89 1.01 2.35 2.53 B.38 8.58 5.05 11.6 S
8.15 1.84 3.97 4.43 1.47 8.06 11.92 12.6 SSU F.11 1.16 1.18 8.64 9.18 8.85 3.32 19.1 SV 0.24 0.65 B.64 B.29 8.01 9.89 1.44 8.1 VSW 8.13 8.44 8.48 8.14 8.81 8.88 1.12 8.1 V
5.14 8.67 9.55 B.26 8.83 8.58 1.65 8.6 VNV B.16 9.77 1.93 F.74 8.99 9.28 2.88 19.2 NV 8.15 9.84 2.g8 1.85 8.26 B.88 5.19 11.4 NNY 9.25 B.99 1.44 1.35 8.49 9.88 4.52 11.3 VARIABLE B.BB B.BB B.BB B.28 B.BB B.80 B.20 B.B PERCENT TOTAL 1.99 14.78 19.76 14.48 4.18 S.45 55.57 AVG SPEED 2.7 5.8 9.9 15.1 28.7 29.1 19.8 4
PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH NEUTRAL STABILITY =
B.8 VALID READINGS = 4413 t
TABLE 4A a--
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O PAGE: 20 PA N t%IE:
1-26-93 DPC E1VIROMEN TAL HohlTORING SYSTEM PERCENTAGE WIND FREQUENCY DIST180 TION BY PASQUILL STABILITY CLASS PASQUILL CLASS E SITE NAME: LACBVR STACK PERIOD OF RECORD: 81-01-91 THRU 12-31-91 SLIGHTLY STABLE SAROAD NO S13622884 STABILITY INSTRUMENTATION-DELTA TEMP PERCENT AVERAGE VIND SPEED (MPH)
DIRECTION 0-3 4-7 8-12 13-18 19-24
>24 TOTAL SPEED N
B.28 1.28 B.86 B.38 0.13 B.25 2.88 8.7 NNE B.18 B.81 B.42 B.94 B.BB B.BB 1.44 6.4 NE B.B6 B.2G B.18 8.88 8.28 B.BB F.43 5.7 ENE B.15 B.2B B.10 B.21 B.BB B.BB B.47 5.7 E
B.16 B.29 B.85 0.83 0.01 B.BB B.45 5.3 ESE B.21 B.20 B.B8 B.98 B.08 9.99 E.57 5.8 SE B.25 8.48 9.28 8.34 B.88 B.21 1.44 9.2 SSE B.45 0.91 E.47 B.39 B.95 B.BB 2.18 7.4 S
B.55 1.27 2.14 2.52 B.48 B.B1 6.98 11.2 SSV B.39 B.68 B.78 B.24 B.23 6.BB 2.32 8.9 Su B.23 U.38 B.18 B.83 B.BB B.BB B.81 5.8 MSV B.19 B.43 B.23 B.BB B.BB B.BB U.64 4.3 Y
B.16 B.24 B.06 B.BB B.BB B.BB B.47 4.6 WNW B.33 B.42 B.14 B.81 B.BB B.BB B.89 5.1 NY B.30 B.GB B.34 B.BB B.BB B.BB 1.25 5.6 NNW B.50 U.72 B.49 B.13 B.BB B.81 1.85 6.4 VARIABLE B.00 B.BU B.BB B.BB B.BB B.BB B.BB 2.0 TOTAL 4.41 8.99 6.59 4.99 B.97 B.B9 25.24 PERCENT 8.2 AVG SPEED 2.4 5.4 9.7 15.0 28.6 27.2 STABILITY =
B.B I
PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH SLIGHTLY STABLE VALID READINGS = 1989 i
TABLE 4A
O O
O RUN DATE:
1-26-93 DPC ENVIROMENTAL MONITORING SYSTEM PAGE: 21 PERCENTAGE WIND FREQUENCY DISTIBUTION BY PAS 0 VILL STABILITY CLASS SITE NAME: LACBVR STACK PERIOD OF RECORD: 81-81-91 THRU 12-31-91 PASQUILL CLASS F
-SAROAD NO 51362B984 STABILITY INSTRUMENTATION-DELTA TEMP MODERATELY STABLE l
I VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION B-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
B.28 B.58 B.25 B.11 B.83 B.81 1.18 7.1 NNE B.23 B.35 B.28 B.BB B.BB B.BB B.65 5.9 NE B.16 B.B9 B.21 B.BB B.BB B.BB B.26 3.8 ENE B.14 B.B6 B.Bl B.BB B.BB B.BB B.21 3.5 i
E B.18 B.84 B.BB B.BB B.BB B.BB B.la 3.2 ESE B.14 B.19 B.Bl B.BB B.BB B.BB B.34 4.8 SE B.37 B.35 B.24
.B.84 B.BB B.BB B.99 5.6 t
SSE B.71 B.G8 B.18 B.BB B.BB B.BB 1.56 4.4 5
B.57 1.4G B.78 B.28 B.BB B.BB 3,21 G.4 SSV B.28 8.28 B.24 B.BB B.BB B.BB B.59 4.2 SV B.15 B.16 B.BB B.88 B.BB B.BB B.31 3.4 VSY B.11 B.14 B.BB B.BB B.BB B.BB B.25 3.5 V
B.99 B.16 2.BB B.BB B.BB B.BB B.25 3.7 VNV B.2B B.13 B.BB B.BB B.BB B.BB B.33 3.2 r
NY B.34 B.25 B.85 B.BB B.BB B.81 B.65 4.4 NNY B.23 B.28 B.13 B.BB B.BB B.83 B.58 6.1 VARIABLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B PERCENT TOTAL 4.88 5.85 1.78 B.35 B.23 B.85 11.33 AVG SPEED 2.4 5.2 9.4 14.4 22.4 28.7 5.3 l
l PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH MODERATELY STABLE STABILITY =
B.B VALID READINGS 988
=
i s
TABLE 4A i
t
1 n
DPC E;iVIROMEN TAL hq.s 6
TORING SYSTEM PAGE: 22 R uh.o a.1 L a t-26-93 PERCENTAGE VIND FREQUENCY DISilBUTION BY PASQUILL STABILITY CLASS i
- SITE NAME: LACBVR STACK PERIOD OF RECORD: 81-B1-91 THRU 12-31-91 PASQUILL CLASS G SAROAD NO 51362BBB4 STABILITY INSTRUMENTATION-DELTA TEMP EXTREMELY STABLE i
VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION 0-3 4-7 6-12 13-18 19-24
> 24 TOTAL SPEED e
i N
B.81 B.14 B.89 B.83 B.BB B.BB B.26 7.7
\\
NNE B.83 B.83 B.84 B.BB B.BB B.BB B.99 6.1 NE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B ENE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B E
B.91 B.84 B.BB B.BB B.BB B.BB B.85 4.4 ESE B.81 B.BB B.BB B.BB B.BB B.BB B.Bl 1.6 SE B.84 B.86 B.29 E.81 B.BB B.BB B.28 7.2 SSE B.83 B.14 B.13 B.BB B.BB B.BB B.29 6.7 S
B.BB B.18 B.21 B.15 B.BB B.BR B 54 9.3 SSV B 84 B.91 B.B6 B.91 B.BB B.BB B.13 7.1 SV B.B3 B.BB B.BB B.BB B.BB B.BB B.83 2.3 VSV B.83 B.BB B.BB B.BB B.BB B.BB B.23 2.2 V
B.Bl B.83 B.BB B.BB B.51 B.BB B.85 7.9 VNV B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B NV B.93 B.88 B.90 B.MB B.BB B.BB B.83 2.8 NNY B.83 B.B1 8.BB B.BB B.BB B.BB B.94 4.4
- VARISBLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B PERCENT TOTAL B.28 B.63 B.62 B.25 B.91 B.BB 1.74 i
AVG SPEED 2.5 5.7 9.4 14.4 19.3 B.B 7.6 4
PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH EXTREMELY STABLE STABILITY.*
8.8 VALID READINGS =
138 i
i l
TABLE 4A t
l
RUw-ATE:
1-26-93 DPC ENVIROMENTAL he<ITORING SYSTEM PAGE: 24 PERCENTAGE VIND FREQUENCY DISTIBUTION BY PASQUILL STABILITY CLASS
- SITE NAME: LACBVR SURFACE PERIOD OF RECORD: 81-B1-91 THRU 12-31-91 PASQUILL CLASS A
- SAROAD NO 513622885 STABILITY INSTRUMENTATION-DELTA TEMP EXTREMELY UNSTABLE VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION B-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
B.91 0.85 B.87 B.BB B.BB B.BB 2.13 7.7 NNE B.BB B.BB B.BB B.BB B.BB B.BB B.BB 2.8 NE B.BB B.BB B.BB B.BB B.BB 2.98 B.BB B.B ENE B.BB B.BB B.BB B.BB B.BB B.BB 2.80 B.B E
B.BB B.BB B.BB B.BB B.BB B.BR 2.98 B.B ESE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B SE B.BB B.BB B.BB B.BB B.BB B.BB B.BQ B.B SSE B.83 8.98 B.93 B.81 B.BB B.BB B.87 6.9 5
B.BB B.BB B.17 B.19 B.BB B.BF B.2B 11.3 SSV B.BB 2.03 8.89 B.88 B.BB B.BB B.83 6.3 SY B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B MSV B.BB B.Bl B.BB B.BB B.BB B.BB B.91 5.1 l
Y B.BB B.BB B.BB B.BB B.BB B.BB B.BB 2.8 YNU B.BB B.BB B.BB B.BB B.BB B.BB B.BB BB NU B.BB
.B.BB B.BB B.BB B.BB B.BB B.BB B.B NNY B.83 B.28 8.36 B.BB B.BB B.BB B.52 7.6 VARIABLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B PERCENT TOTAL B.97 B.29 8.56 B.12 6.BB B.88 1.84 AVG SPEED 2.5 G.5 9.2 13.1 B.B B.B 8.5 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH EXTREMELY UNSTABLE STABILITY =
B.B VALID READINGS =
79 i
TABLE 4A
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~-.- -. -
O O
O FVR DArds 1-26-93 DPC ENVIROMENTAL MONITORING SYSTEM PAGi 25 PERCENTAGE VIND FREQUENCY DISTIBUTION BY PASQUILL STASILITY CLASS
- SITE NAME: LACBUR SURFACE PERIOD OF RECORD: #1-01-91 THRU 12-31-91 PASQUILL CLASS B
- SAROAD NO 51362B895 STABILITY INSTRUMENTATION-DELTA TEMP MODERATELY UNSTABLE VIND SFEED (MPH)
PERCENT AVERAGE DIRECTION 0-3 4-7 8-12 13-18 19-44
> 24 TOTAL SPEED N
B.BB B.85 B.21 0.89 B.BB B.BB B.07 7.4 NNE B.00 B.BB B.BB B.BB B.BB B.BB B.BB 2.9 NE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B ENE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.8 E
B.BB 2.99 B.BB B.BB B.BB B.BB B.BB B.B ESE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B SE B.BB B.BB B.BB B.BB B.BB B.BB B.BB 2.0 SSE B.BB B.BB B.94 B.83 B.BB B.BB B.87 11.7 S
6.BB B.83 B.45 B.Ba B.BB B.BB B.51 19.2 SSV B.BB B.81 B.BB B.BB B.BB B.BB B.Bl 6.8 SV B.BB B.83 B.BB B.BB B.BB B.BB B.83 5.7 VSV B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B V
B.BB B.83 B.BB B.BB B.BB B.BB B.23 5.6 VNV B.BB B.BB 2.BB B.BB B.BB B.BB B.BB 2.0 NV B.BB 2.28 E.21 B.BB B.BB B.BB B.21 7.8 NNY B.BB B.35 B.22 B.01 B.BB B.BB B.59 7.3 VARIABLE B.BB B.20 B.BB B.BB B.BB B.BB B.80 B.B PERCENT TOTAL B.BB B.50 9.73 B.BB B.BB B.BB 1.31 AVG SPEED 2.0 6.3 9G 13.8 B.B B.B 8.6 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH MODERATELY UNSTABLE STABILITY
- B.B VALID READINGS =
1B0 TABLE 4A i
__________m________________
O o
o PAGE: 26 RUN DATE:
1-26-93 DPC ENVIROMENTAL MONITORING SYSTEM PERCENTAGE WIND FREQUENCY DIST!BUTION BY PASQUILL STABILITY CLASS SITE NAME: LACBVR SURFACE PERIOD OF RECORD: 91-B1-91 THRU 12-31-91 PASQUILL CLASS C
- SAROAD NO 513628885 STABILITY INSTRUMENTATION-DELTA TEMP SLIGHTLY UNSTABLE WIND SPEED (MPH)
PERCENT AVERAGE DIRECTION B-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
B.BB B.38 B.16 B.BB B.BB B.BB B.54 7.1 NNE B.BB B.BB B.BB B.BB
.B.BB B.BB B.BB B.B NL B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B ENE B.BB B.BB B.BB B.BB B.BB B.BB B.BB 2.8 E
B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B ESE B,BB B.BB B.BB B.BB B.BB B.BB B.BB B.B SE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B SSE B.BB B.88 B.28 B.93 B.BB B.BB B.38 9.1 5
B.BB B.28 B.93 B.18 B 01 B.BB 1.49 9.7 SSV B.BB B.98 B.88 0.98 B.BB B.BB B.16 7.5 SY B.BB B.28 B.BB B.BB B.BB B.BB 2.98 6.1 USY B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B u
B.BB B.25 B.BB B.BB B.BB B.BB B.25 5.4 VNV B.BB B.91 B.BB B.BB B.BB B.BB B.21 4.7 NY B.BB B.17 B.17 B.BB B.BB B.BB 2.34 7.G NNY B.BB B.75 B.35 B.18 B.BB B.BB 1.21 7.6 VARIABLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B 1
PERCENT TOTAL B.BB 1.87 1.89 B.31 B.91 B.BB 4.89 AVG SPEED B.B 6.1 9.4 14.1 19.3 B.B 8.3 PERCENTAGE FRE0VENCY OF CALMS DISTRIBUTED ABOVE WITH SLIGHTLY UNSTAELE STABILITY =
B.B VALID READINGS =
312 i
4 TABLE 4A e-==~--~.,-._._---....,-----s.
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RVII sT C 1-26-93 DPC LdVIROMENTAL if6-<kOP.!NG SYSTEH P ACI: t 27 V
PERCENTAGE WIND FREQUENCY DIST18UTION BY PASQUILL STABILITY CLASS
- SITE NAME: LACBWR SURFACE PERIOD OF RECORD 81-BI-91 THRU 12-31-91 PA50 VILL CLASS D
- SAROAD NO 513628885 STABILITY INSTRUMENTATION-DELTA TEMP NEUTRAL WIND SPEED (MPH)
PERCENT AVERAGE DIRECTION 0-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
1.14 3.99 1.68 E.89 8.BB B.BB 6.EB 6.1 NNE B.48 B.18 B.BB B.BB B.BB B.BB B.67 3.1 NE B.28 B.BB B.BB B.BB B.BB B.BB B.28 Zs2 ENE B.13 B.21 B.BB B.BB B.BB B.BB 2.14 2.4 E
B.12 B.83 B.BB B.BB B.BB B.BR B.14 2.4 ESE B.08 8.84 B.BB B.BB B.BB B.BC B.12 3.1 SE B.17 8.35 B.18 B.81 B.BB B.BB B 72 5.9 SSE B.31 2.69 4.29 B.92 B.BB B.BB 8.28 8.6 S
B.29 4.77 4.77 1.34 B.88 B.BB 11.24 8.6 SSW B.17 1.53 B.79 B.41 B.87 B.Bl 2.97 8.1 SY B.89 B.85 B.22 B.BB B.BB B.BB 1.17 5.7 MSV B.28 B.51 B.87 B.BB B.BB B.BB B.77 4.6 Y
B.38 B.73 B.85 B.BB B.BB B.BB 1.89 4.8 VNV B.39 1.66 B.38 B.BB B.BB B.BB 2.36 5.3 NW B.86 5.50 2.52 B.84 B.BB B.BB 8.58 6.3 NNV 1.72 6.95 2.42 8.37 B.21 B.BB 18.58 6.2 VARIABLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB 2.8 PERCENT TOTAL 6.74 28.48 17.28 3.17 B.16 B.81 55.76 AVG SPEED 2.8 5.5 9.4 14.4 19.7 29.5 6.9 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE WITH NEUTRAL STABILITY =
B.B VALID READINGS = 4255
]
TABLE 4A i
O O
O RUN DATE:
1-26-93 DPC ENVIROMENTAL MONITORING SYSTEM PAGE: 28 PERCENTAGE VIND FRE0VENCY DISTIBUTION BY PASQUILL STABILITY CLASS
- SITE NAME: LACBWR SURFACE PERIOD OF RECORD: 81-B1-91 THRU 12-31-91 PASQUILL CLASS E
- SAROAD NO 513628295 STABILITY INSTRUMENTATION-DELTA TEMP SLIGHTLY STABLE VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION 0-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
1.14 B.75 B.2B B.BB B.BB B.BB 2.28 3.9 NNE 1.11 B.29 B.BB B.BB B.BB B.BU 1.48 2.8 NE 1.19 B.89 B.BB B.BB B.BB B.BB 1.29 2.3 ENE B.85 B.27 B.BB B.BB B.BB B.BB B.92 2.1 E
1.26 B.16 B.89 B.BB B.BB B.BB 1.42 2.1 ESE 1.61 B.13 B.91 B.BB B.BB B.BB 1.76 2.1 SE 1.74 9.58 B.23 B.BB 9.BB B.BB 2.27 2.8 SSE 1.87 3.32 1.39 B.14 B.BB B.BB 6.72 5.6 S
B.62 1.76 B.84 B.14 B.BB B.BB 3.35 6.3 SSV B.28 0.21 B.17 B.83 B.BB B.BB B.GB 6.8 Su B.99 B.84 B.85 B.BB B.BB B.BB B.18 4.7 usu B.19 B.95 B.BB B.BB B.BB B.BB B.16 3.2
=
u B.87 B.83 B.BB B.BB B.BB B.BB B.89 3.8 UNV B.12 B.95 B.BB B.BB B.BB B.BB B.17 2.9 NY B.lB B.14 B.BB B.BB B.BB B.BB B.33 3.2 NNV B.86 1.32 B.12 B.Bl B.BB B.BB 2.32 4.4 VARIABLE B.BB B.00 B.BB B.BB B.BB B.88 B.BB B.B PERCENT TOTAL 13.83 8.90 2.8B B.33 B.BB B.BB 25.86 AVG SPEED 2.2 5.1 9.3 13.9 B.B B.B 4.2 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE WITH SLIGHTLY STABLE STABILITY =
B.B VAL 10 READINGS = 1912 TABLE 4A t
O O
O RUN 0,' 1 *:
1-26-93 DPC EiiV!ROMENTAL MON 1TORING SYSTEM PAGE: 29 PERCENTAGE VIND FREQUENCY DISTIBUTION BY PASOUILL STABILITY CLASS SITE NAME: LACBVR SURFACE PERIOD OF RECORD: 91-B1-91 THRU 12-31-91 PASQUILL CLASS F SAROAD NO 513622885 STABILITY INSTRUMENTATION-DELTA TEMP MODERATELY STABLE a
\\
t VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION B-3 4-7 B-12 13-18 19-24
> 24 TOTAL SPEED N
B.54 B.87 B.84 B.Bl B.BB B.BB B.G6 2.9 NNC B.58 B.BB B.BB B.BB B.BB B.BB B.58 1.6 NE B.41 B.BB B.BB B.BB B.BB B.BB B.41 1.5 ENE B.51 B.Bl B.BB B.BB B.BB B.BB B.52 1.G E
1.13 B.81 B.BB B.BB B.BB B.BB l.14 1.6 ESE 1.47 B.BB B.BB B.BB B.BB B.BB 1.47 1.6 SE 1.23 B.BB B.BB B.BB B.BB B.BB 1.23 1.7 SSE 2.86 B.31 B.BB B.Bt B.BB B.BB 2.33 2.6 5
B.64 B.67 B.BB B.BB B.BB B.BB 1.31 3.4 SSV B.BB B.BB B.BB B.BB B.BB B.BB B.BB 1.8 SV B.18 B.BB B.BB B.BB B.BB B.BB B.18 1.7 VSV B.85 8.88 B.BB B.BB B.BB B.BR B.25 1.5 Y
B.85 B.BB B.BB B.BB B.BB B.BB B.85 1.5 VNV B.95 B.Bl B.BB B.BB B.BB B.BB B.87 2.1 NV B.13 B.BB B.BB B.BB B.BB B.BB B.13 1.9 NNV B.71 0.37 B.23 B.B1 B.BB B.BB 1.11 3.5 VARIABLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B PERCENT TOTAL 9.66 1.45 B.87 B.84 B.BB B.BB 11.22 AVG SPEED 1.9 4.4 18.3 14.3 B.8 B.B 2.3 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE WITH MODERATELY STABLE STABILITY =
B.B VALID READINGS =
B56 l
TABLE 4A t
RUN A1 E s 1-26-93 DPC ENVIROMENTAL MON TORING SYSTEM PAGE: 30 PERCENTAGE WIND FREQUENCY DISTIBUTION BY PASQUILL STABILITY CLASS SITE NAME: LACBVR SURFACE PERIOD OF RECORDt 81-B1-91 THRU 12-31-91 PASQUILL CLASS G
- SAROAD NO 513622885 STABILITY INSTRUMENTATION-DELTA TEMP EXTREMELY STABLE
.a......................................................................................................
VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION B-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
B.14 B.81 B.BB B.BB B.BB B.BB B.16 2.1 NNE B.89 B.BB B.BB B.BB B.BB B.BB B.89 1.5 NE B.87 8.98 B.BB B.BB B.BB B.BB B.07 1.5 ENE B.24 B.BB B.BB B.BB B.BB B.BB B.94 1.7 E
B.Bl B.BB B.BB B.BB B.BB B.BB B.Bl 1.3 ESE B.84 B.BB B.BB B.BB B.BB B.BP B.24 1.2 SE B.18 B.BB B.BB B.98 B.BB B.BB B.18 1.7 SSE B.25 0.25 B.08 B.BB B.BB B.BB B.38 7.8 S
B.99 B.84 B.BB B.Bl B.BB B.BB B.14 3.G SSM B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B SY B.83 B.BB B.BB B.BB B.BB B.BB B.03 1.3 MSV B.91 B.BB B.BB B.BB B.BB B.BB B.81 1.3 U
B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B UNY B.65 B.BB B.BB B.BB B.BB B.BB B.B5 1.7 NV B.95 0.88 B.BB B.BB B.BB B.BB B.95 2.4 NNV B.31 B.12 B.BB B.BB B.BB B.BB B.43 2.8 VARIABLE B.BB B.BB B.BB B.20 B.BB B.BB B.BB B.O PERCENT TOTAL 1.38 9.22 B.BB B.01 B.BB B.BB 1.53 AVG SPEED 2.0 4.4 B.0 14.2 B.B B.B 2.4 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE WITH EXTREMELY STABLE STABILITY =
B.B VALID READINGS =
117 TABLE 4A I
1 O
O O
RUN 0.s1 :
1-26-93 DPC ENVIROMENTAL MONITORING SYSTEM PAGL: 31 PERCENTAGE VIND FREQUENCY DISTIBUTION BY PASQUILL S*\\BILITY CLASS
- SITE NAMEe LACBWR SURFACE PERIOD OF RECORD: B1-B1-91 THRU 12-31-91 PASQUILL CLASS ALL SAROAD NO 513628885 STABILITY INSTRUMENTATION-DELTA TEMP ALL VIND SPEED (MPH)
PERCENT AVERAGE DIRECTION B-3 4-7 8-12 13-18 19-24
> 24 TOTAL SPEED N
2.97 5.25 2.15 B.lf B.BB B.BB 18.43 5.5 NNE 2.19 B.47 B.BB B.BB B.BB B.BB 2.GG 2.6 NE 1.94 B.89 B.BB B.BB B.BB B.BB 2.23 2.1 ENE 1.53 8.89 B.BB B.BB B.BB B.BB 1.62 2.2 E
2.52 B.28 B.BB B.BB B.BB B.BB 2.71 1.9 ESE 3.28 B.17 B.81 B.88 B.BB B.BB 3.38 1.9 SE 3.25 B.05 B.21 B.91 8.88 B.BB 4.32 3.8 SSE 4.52 6.45 5.94 1.14 B.BB B.BB 18.84 6.6 S
1.64 7.54 7.16 1.82 B.99 B.BB 18.24 7.9 SSV B.45 1.86 1.84 B.43 8.87 B.91 3.85 7.6 SV B.31 1.BB B.28 B.BB B.BB B.BB 1.59 5.3 VSV B.37 9.58 B.07 B.BB B.BB B.BB 1.21 4.2 V
B.42 8.84 B.95 B.BB B.BB B.BB l.31 4.5 UNY B.G2 1.74 B.38 B.BB B.BB B.BB 2.66 5.8 NV 1.23 5.48 2.78 B.84 B.BB B.BB 9.37 6.1 NNV 3.63 9.16 3.45 9.51 B.81 B.BB 16.76 5.9 VARIABLE B.BB B.BB B.BB B.BB B.BB B.BB B.BB B.B PERCENT TOTAL 38.78 41.63 23.34 4.86 8.17 8.91 ISB.BB AVG SPEED 2.2 5.4 9.4 14.3 19.7 29.5 5.8 PERCENTAGE FREQUENCY OF CALMS DISTRIBUTED ABOVE VITH ALL STABILITY =
B.B VALID READINGS = 7631 TABLE 4A t
l l
l l
l 1 O i
SECTION B l
ANNUAL l
"^ ' '
^'
O ENVIRONMENTAL MONITORING REPORT January 1 - December 31, 1992 O
INTRODUCTION:
O The Radiological Environmental Monitoring (REM) Program is conducted to comply with the requirements of Technical Specifications and in accordance with 10 CFR 50 Appendix I.
The REN program provides measurements of radiation and of radioactive unnterials in those exposure pathways and for those radionuclides which could potentially lead to radiation doses to
?
Members of the Public resulting from plant effluents. Environtrental samples are taken within the surrounding areas of the plant and in selected control or background locations.
l i
The monitoring program at the LACBWR facility includes monitoring of liquid and gaseous releases from the plant, as well as environmental samples of surface air, river water, river sediment, milk, fish, and penetrating radiation.
The REM program theory supplements the Radioactive Effluent analyses by i
verifying that the measurable concentrations of radioactive materials and l
1evels of radiation are not higher than expected on the basis of the effluent I
measurements and nodeling of the environmental exposure pathways using the methodology of the Offsite Dose Calculation Manual (ODCM).
i 1
i An Interlaboratory Comparison Program is provided to ensure that independent checks on the precision and accuracy of the measurements of radioactive material in environmental samples are performed.
!O
, 1
l LACBWR was removed from the power generation rolls in April 1987 when DPC shut down the reactor and placed LACBWR in SATSTOR.
Since that time, the O
amount of radioactive naterial released to the environment has decreased significantly. Amendment 64 to the LACBWR Technical Specifications was issued in December of 1988 and eliminated the need to analyze environmental samples for I-131 due to the stabilization of all iodine at LACBWR.
Amendment 66 to the Technical Specifications was received in August of 1991 and significantly reduced the sampling and analysis requirements of LACBWR's environmental program.
LACBWR's inhouse piocedures were modified in February of 1992.
At that time LACBWR environmental program was reduced to match that listed in Tech.
Spec. Amendment 66.
This report for 1992 will describe these changes and the data tables will reflect the analysis reductions.
1.0 SAMPLE COLLECTION I
Environmental samples are collected from the area surrounding LACBWR at the frequencies outlined in the Technical Specifications. A series of figures and tables are included in this report to better show LACBWR's j
environmental program.
l FIGURE 1 This map includes the plant boundary, roads, other generation l
plants, and the relationship of the plant to the nearest local community.
FIGURE 2 This map shows the location of LACBWR's permanent environ-mental monitoring stations through February of 1992.
FIGURE 2A This map shows the location of LACBWR's permanent environ-mental monitoring stations after February of 1992.
FIGURES 3&4 These maps show the location of LACBWR's TLDs used for the first quarter of 1992.
O FIGURES 3A&4A These naps show the location of LACBWR's T1.Ds used for the 2nd, 3rd, and 4th quarters of 1992.
TABLE 5 This table shows the sampling frequency of the various environmental samples and the analyses performed on these samples through February 1992.
TABLE SA This table shows the sampling frequency of the various environmental samples and the analyses performed on these samples after February 1992.
i TABLE 6 This table shows the permanent monitoring stations used in LACBWR's environmental program.
TABLE 7 This table shows the TLD locations used for the 1st quarter of 1992.
TABLE 7A This table shows the TLD locations used for the 2nd, 3rd, and l
4th quarters of 1992.
TABLE 8 This table shows the number of various samples collected and analyzed during 1992.
2.0 Results of the 1992 Radio-Environmental Monitoring Surveys j
During 1992, activity levels in the local environment were normal, indicating no significant plant attributed radioactivity.
2.1 Penetrating Radiation l
The environmental penetrating radiation dose is measured by l
thermoluminescent dosimeters consisting of four lithium fluoride (LiF) chips. These TLD's are changed on a quarterly basis and are sent to an outside contractor for reading. The TLD results for the 1st quarter of 1992 are shown on Table 9.
Table 9A shows the results of the 2nd, 3rd, and 4th quarter of 1992.
O l
l l
2.2 Air Particulate Air samples are collected continuously from various sites (see Table 6) around LACBWR. An air sampler is also located 18 miles north f
f of the plant in La Crosse, Wisconsin, to act as a control station.
l Particulate air samples are collected at the rate of approximately l
30-60 1pm with a Gelman Air Sampler. The air filter consists of a glass fiber filter with an associated pore size of approximately 0.45 pm.
The i
particulate filters are analyzed weekly for gross beta activity with an internal proportional counter, and the monthly particulate composites are gamma analyzed for individual isotopic concentration.
TABLE 10 This table shows the weekly gross beta gamma activity j
concentration from the air particulate filters through 3
2/17/92.
l TABLE 10A This table shows the weekly gross beta gamma activity
()
concentration from the air particulate filters through the rest of 1992.
TABLE 11 This table shows the composite air particulate isotopic analysis.
[
Comparison between the control station at La Crosse and the other stations near LACBWR indicate that there was no significant plant attributable airborne particulate activity.
2.3 RIVER WATER River water is collected monthly. River water samples above, at, 1
and below the plant site are collected and are gamma analyzed for isotopic concentration. The river water ganna isotopic analysis results are shown in Table 12.
The results indicate that there is insignificant plant attributable radionuclides in the river water..
i I
2.4 SEDIMENT SAMPLES Sediment samples were collected twice per year above, at, and below the plant outfall. These samples were gamma analyzed and these results appear on Table 13.
They indicated that small amounts of plant l
attributed radionuclides have accumulated in river sediments near the I
outfall.
i 2.5 MILK SAMPLES Milk samples were collected monthly during the grazing season (May through September) from three dairy farms in the vicinity of LACBWR and gamma analyzed. These samples are listed in Table 14.
There has been no significant accumulation of plant attributed radionuclides in milk in j
the vicinity of LACBWR.
J 2.6 FISH Fish samples were collected quarterly above and below the plant
[
discharge. The results of gamma spectral analysis of edible portions of fish samples appear in Table 15.
There has been no significant accumulation of plant attributed radionuclides in fish in the vicinity l
of LACBWR.
1 2.7 VEGETATION Vegetation samples were collected from local gardens at the time of l
harvest. The results of the gamma spectral analysis of the vegetation samples appear on Table 16.
There has been no significant accumulation of plant attributed radionuclides in the vegetation.
O i i
3.0 CONCLUSION
S All environmental samples collected and analyzed during 1992 exhibited no significant contribution from LACBWt.
I 4.0 INTERLABORATORY COMPARISON PRDGPJJi PISULTS During 1992, interlaboratory comparison samples were obtained from an l
outside contractor. The equipment used to analyze the environmental samples was tested against the contractors results.
The following is the result of i
this comparison.
l l
LACBWR l
Contractor l
l Analysis l
Results (pCi/cc) l Results (pCi/cc) l I
I j
Gross Beta l
3.86 E-4 l
3.19 E-4 l
l Gross Alpha l
7.04 E-4 l
8.77 E-4 l
l Tritium l
1.45 E-3 l
1.37 E-3 l
l Cs-137 l
8.50 E-3 l
8.74 E-3 l
l Co-60 l
8.97 E-3 l
9.42 E-3 l
O l
l l
l O l
O f Wll A CE Of s
l
-..'L"2.'... i i
/,,e L ft U.S. Lt) Cat GENDA l
e cam wa s
/
j i
l E
I 4
LOT 't s73 w
i C/ e;,
t 1ill.
f/p?
o 29^28 o
b/
- p 32 ss gd fl i
?
EXCLUSIO!I BOUIIDAI i
LOCATION MAP O'/
1109 ft radius
[
t.or n SCALE OF FEET
/
j j
/
Pow g ]i^:i c won T. -lOI-N., R.-3 -W.
[i -
P ROPERTY OF THE Sth RM. -
JEFFERSON TOWNSHIP LINE
'Q**yiT
/
HOUSTON COUNTY, s
/
~
fo~.7
/
oT 2 J
LOT 5
- -stmoa souTM SEC. 7 1
rett towt
"" * ' E L'"8 SEC.IB N- /
J3 r
h*
l
/
/
e
/i WELL LOT S
/
gI
/
g[3 f
toy 3
. N., R.-7-W.
~
OF THE 4th RM.
//
g hoTOWN OF GENOA N [ "lr"t %
MEb -.? -.
VERNON COUNTY, 7
BOAT WISCONSIN 6,
y l
tawoina o
l ISLAND 876 f
LOT 7 LOT 4
/
s SFC 32 _ T-13_-N I
SEC. 5 T-I2-N.
l
/
/
)
kOTts est aND 826 IS UNDER THE JU R S S DiC T SON Of UPPER
/
8AIS S fS 5 8 ppt Rivt R w tL D to C D F ISM R( W.
ab 6 7 0 sN0iCat t s wetts aDOvt 1Mt WOUTM Of 1ME OM 60 Ravtm.
FIGURE 1 - LACBWR PROPERTY MAP REM 1,a c ros s e
+),mj.
y
\\ \\'
e3i m
x N
)
f 5
f 0
L f# v
/
4 in
(~N L
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)
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n NY R
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25
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l ii
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- N;t 2
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i n-5 l
4 wk 13 J
ex La N1
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g fx
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w gei;/
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-? L
^N L._
i A
- 1.5
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. E a.? *
- f Environmental g=
g.,-
{
(
Monitoring
'J -
//-
U, 1
s Station Locations
'w'~.~.
FIGURE 2 - PERMANENT ENVIR0hMENTAL MONITORING STATION LOCATIONS (Refer to Table 6)
(before March 1992)
REM O
[
t y
lh. ex N h t rt
~
a 1- & '.~-
\\
4
. h 9
N.
- v..
u.
.\\.
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e t
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i P{,erelf.
.+i{h g p Q
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tough j:
j l,.Jl
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yl O !?
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e W: A
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~
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- 6 13 k
gg v
x fayslolr yl ?
La f
' 19' N
1 K I
R'&'W 5 '*.
L~j
.G
- Ve. A-T
. Sample t
'Lak-
-k---
nuironmental E.% A~~'h $1/db, S E o
FIGURE 2A - PERMANENT ENVIRONMENTAL MONITORING STATION LOCATIONS (Refer to Table 6)
._ (after Feb. 1992)
I r@
O gN s,.. 4.4...
I 8888 i
I
'W Li 15 i
k
'S f
f-g o g g - - m m.
Ceno.
~
S
[g O
g a
-e.tp O
kr,G LAC 8L1 e
Cenoa - 3 Q b
y sss f
Trattee rack g\\
H o;
B e a s sis O
FIGURE 3 - IACBWR ENVIRONMENTAL DOSE ASSESSMENT LOCATIONS (before April 1992) REM
.l
1
~
/
1 O
~
/
}
i 11 e
I L'P
/
y j
) 5.
I I
Loi e
[
,1 f, V
i d
l TLD No.
Incation
/
1 La Crosse Main Office
/
()
2 Dam #8 12 3
Radio Tower l
hp 4
Trailer Court i
o,
/
llQ'
)
~~^*
/
/
""?
G a
/.
JD
/
7
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l g) i I
t il
{(,
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e 8
I acusts J
J o
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{l>
d' h
ce
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i
/
n 1
3 i
s FIGURE 3A L IACBk'R ENVIRONMENTAL DOSE ASSESSMENT ll) CATIONS O
(after March 1992) l l
1 l
[ / ff 4
~
O
]
~
o
.oo'
.oo E!&
j
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4 i
9 f
y
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g' L
I i.
i I.
(20
.s FIGURE 4 - LACBVR ENVIRONMENTAL DOSE ASSESSMENT LOCATIONS REM (before April 1992)
Y
-x a
I O
J6 lI
=
w l
4 4
(J o1 g
.s 21 a4 4
e
$E L.J
\\
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1 t
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f i
1 4
wil (li.
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c4 9
rv;
.s.
,g, 4
c@
i I
l n
u 1
FIGURE 4A - LACBWR ENVIRONMENTAL DOSE ASSESSMENT IDCATIONS (after March 1992)
O O
O TABLE 5 SAMPLE FREOUENCY AND ANALYSIS OF RADIO-ENVIRONMENTAL SAMPLES (prior to April 1992)
SAMPLE FREOUENCY ANALYSIS PERFORMED TLD (LIF) Dosimeters Quarterly Dose in mrem Particulate Air Glass Weekly Gross Beta and Gamma Spectroscopy of Fiber Filters Composites Monthly (HPGe-MCA)
Milk Biweekly during grazing season Gamma Spectroscopy Sediment Twice per year Gamma Spectroscopy Fish Quarterly Gamma Spectroscopy River Monthly Gamma isotopic analysis and tritium (Internal Liquid Scintillation Spectrometer)
Vegetation At time of harvest Gamma Spectroscopy !
l l
O O
O TABLE SA SAMPLE FREQUENCY AND ANALYSIS OF RADIO-ENVIRONMENTAL SAMPLES (after March 1992)
SAMPLE FREOUENCY ANALYSIS PERFORMED TLD (LiF) Dosimeters Quarterly Dose in mrem Particulate Air Glass Weekly Gross Beta and Gamma Spectroscopy of Fiber Filters Composites Monthly (HPGe-MCA)
Milk Monthly during grazing season Gamma Spectroscopy Sediment Twice per year Gamma Spectroscopy Fish Quarterly Gamma Spectroscopy River Monthly Gamma isotopic analysis and tritium (Internal Liquid Scintillation Spectrometer)
Vegetation At time of harvest Gamma Spectroscopy !
}
TABLE 6 PERMANENT ENVIRONMENTAL MONITORING STATION LOCATIONS THRU FEBRUARY 1992 (Refer to Figure 2) l IDCATION l
l AIR NO.
I LOCATION l
SAMPLE MILK l
1 Pedretti Farm x
x i
l l
2 P. Malin Farm l
x 3
A. Malin Farm x
l l
4 Gianoli Farm x
ll l
l 1
l 5
l Dam No. 8 l
x 1
I 6
Trailer Court l
x l
7 l
Crib House l
x j!
I l
l I
i Main Office l
x l
8 i
O l
i i
9 l
Radio Tower l
x l
l l
l l
l AFTER FEBRUARY 1992 (Refer to Figure 2A)
LOCATION l
l AIR l
NO.
l IDCATION l
SAMPLE l
MILK I
I 1
l Pedretti Farm l
x 1
I 1
l 2
l P. Malin Farm l
x I
I i
l 3
l A. Malin Farm l
l x
1 I
I l
4 l
Dam No. 8 l
l l
x l
l 1
5 l
Trailer Court l
l x
l 1
6 l
Crib House l
I l
l x
I I
I I
7 l
Main Office l
l x
i 8
l Radio Tower l
x l
I I
l.
TABLE 7 O
ENVIRONMENTAL TLD LOCATIONS (before March 1992) l LOC *.YION l
l NO.
l IACATION l
I L
l 1
l ACROSS RIVER FROM PIANT i
l 2
l ACROSS RIVER ACROSS FROM G-1 SITE l
3 i ACROSS RIVER W END OF DAM 48 l
4 I
BERRA RIDGE ROAD AND BEYER HILL ROAD l
5 I MOUND RIDGE ROAD & HWY 56 l
6 I AT TRAILER COURT SOUTH ON HWY 35 l
7 I ON FENCE ACROSS FROM FUEL TANK N OF G-1 SITE l
l 8
l S OF PEDRETTI ROAD. E OF SITE l
l 9
l E SIDE OF FISHERMAN'S ROAD l
l 10 I
G-3 CONTROL ROOM l
l 11 1 TOP OF BLUFF. EAST OF PIAfU 12 l COUNTY ROAD K AND HICKORY RIDGE ROAD 13 l COUNTY ROAD K AND COUNTY ROAD 0 l
14 l NW FROM KELSEY FARM l
15 l DAM #8 l
16 i GIANOLI FARM l
l 17 i HWY 56 AT ROMANCE l
l 18 i PEDRETTI FARM l
19 l ROAD ABOVE GENOA LEGION l
O 20 l
SW CATEPOST AT END OF C-3 DIKE l
l 21 l DPC SERVICE CENTER l
l 22 l MUNDSACK ROAD. 3 MI SE 23 l
S BAD AXE ROAD. 3.8 MI SSE 24 l
S BAD AXE ROAD AND WORMAN AND KUEHN ROAD 25 i
STODDARD l
l 26 I HARMONY SUBSTATION l
l 27 1 DE SOTO. OLD HWY 35 l
l 28 I 4 MI N
[
29 1
3.5 MI ENE 30 l VICTORY 31 1 RENO 32 l NEW ALBIN. IOWA j
33 l ACROSS ROAD FROM BECK'S FISH MARKET j
34 i APPROX.
.7 MILE N OF JUNCTION ON HWY 26 & 14
[
l
.l 35 APPROX. 3 MILES N OF NEW ALBIN, IOWA, ON HWY 26,
[
l MILLSTONE RECREATION AREA l
36 l ON HWY 26 N OF NEW ALBIN. IOWA l
37 l
FISH HATCHERY l
38 l
CALEDONIA l
39 l APPROX. 3.5 MI S OF NEW ALBIN ON HWY 26 l
l 40 l RED MOUND l
j l
41 1 VIROOUA l
<s i
U !
l TABLE 7A
^
E!NIRONMENTAL TLD LOCATIONS (after February 1992) l LOCATION l l
l NO.
I IDCATION l
l l
l 1
l 1
I IA CROSSE MAIN OFFICE AIR SAMPLER BOX l
l l
I I
l 2
l DAM #8 AIR SAMPLER BOX l
l l
l l
3 l RADIO TOWER BUILDING AT AIR SAMPLER l
I I
I l
4 l TRAILER COURT AIR SAMPLER BOX l
l l
5 CRIBHOUSE AIR SAMPLER BOX l
l l
6 l G-3 CONTROL ROOM l
l l
l l
7 i SW CATEPOST AT END OF G-3 DIKE l
l l
l l
8 i ON FENCE N. SIDE OF FISHERMAN'S ROAD l
l 1
ll 9
SITE ENTRANCE CUARD AREA I
1 I
10 l ON FENCE AT NE CORNER OF THE SWITCHYARD l
O i
i l
l 11 ON N. SITE AREA FENCE CATE l
i I
I I
l 12 I G-1 CRIBHOUSE l
i I
i l
l 13 l ON MOORING WAIKWAY WEST OF IACBUR #2 WAREHOUSE l
j i
i l
14 G-3 COAL UNIAADING CRANE l
l l
1 l
15 l POWER POLE ON BLUFF SIDE EAST OF PLANT l
l l
1 l
16 RESTRICTED AREA FENCE N. SIDE l
l l
l l
17 I RESTRICTED AREA FENCE E. SIDE l
l l
l l
l 18 RESTRICTED AREA FENCE S. SIDE l
l 19 l RESTRICTED AREA FENCE SW CORNER i
20 RESTRICTED AREA FENCE V. SIDE l
L I
I l
21 1 RESTRICTED AREA FENCE NW CORNER l
l 0 l
TABLE 8 RADIO-EtNIRONMENTAL SAMPLES COLLECTED JANUARY-DECEMBER 1992 TYPE OF SAMPLE NUMBER OF SAMPLES Penetrating Radiation (TLD's) 102 Air Particulate 268 River Vater 36 Sediment 6
Milk 12 8
Fish 8
l Effluent Split w/St. of Wisc.
24 r
Vegetation 2
t i
i O 1 e
g----wt
I I
l i
l i
O i
I i
l i
1 l
l l
l l
i 1
1 l
O J
1 l
i i
i I
l l
O l
i
TABLE 9 OUARTERLY THERMOLUMINESCENT DOS 1 METER DOSE MEASUREMENTS IN THE IACBWR VICINITY IST QUARTER 1992 l
l l
1st QUARTER l
l 1st QUARTER l l
STATION NO.
I mrem l
STATION NO.
I mrem l
l l
l l
1 (offsite)
I 15.0 4.7 l
l 22 (offsite)
I 17.6 + 6.9 l
l 1
1 1
ll 2 (offsite)
I 17.4 i 4.1 l
23 (offsite)
I 21.2 i 5.2 l;
I I
l 3 (offsite)
I 16.8 i 5.9 l
24 (offsite) 19.4 i 4.1 ll i
i l
i I
l 4 (offsite) 14.2 i-3.6 l
25 (control)
I 20.4 t 4.6 l
l 1
1 I
I I
l l
5 (offsite) 19.2 6.5 l'
26 (control)
I 22.0 3.5 ll I
I I!
I l
6 (offsite)
I 22.8 4.6 27 (control) l 20.0 i 6.9 l
l 7 (onsite)
I 21.0 + 4.5 l
28 (control) 17.4 5.8 l
l l
8 (offsite) 19.6 5.4 l
l 29 (offsite)
I 17.6 t 7.0 l
I I
I I
I 9 (offsite)
I 20.2 t 9.1 l
30 (control) l 31.0 t 7.9 1
10 (onsite)
I 15.2 0.9 31 (offsite) 22.0 4.7 l
l I
i 11 (offsite) 16.2 3.6 l
32 (control l
17.8 4.3 l
l 12 (offsite) 19.6 4.6 33 (offsite) 23.0 6.9 l
l l
ll
[
13 (control) 22.4 4.8 1
34 (offsite)
I 22.0 i 5.1 l
l L
I I
14 (offsite) 22.2 i 6.2 l
35 (offsite) 22.4 6.4 I
i i
15 (offsite)
I 23.8 i 4.3
)
36 (control)
I 19.6 2.3 l
l l
l l
16 (offsite)
I MISSING l
37 (offsite)
I 20.4 5.8 l
1 I
i 17 (offsite) l 19.2 i 6.5 l
l 38 (control) 18.0 t 6.2 l
l l
l I
I
)
18 (offsite)
I 20.4 i 5 l
l 39 (control) l 19.8 6.7 1
1 22.4 4.6 l
40 (control) 25.6 i 5.8 l
19 (offsite) l l
l 20 (onsite) l 21.2 i 4.3 l
'l I
I 41'(control) 43.0 10.5 l
I l
l 21 (control) l 19.8 i 4.1 l
l l
O All TLD's greater than 5 miles from the plant are considered control TLD's..
r-r
--f
I l
i TABLE 9A OUARTERLY THERMOLUMINESCENT DOSIMETER DOSE MEASUREMENTS J.N THE 1ACBk'R VICINITY 2ND, 3RD, 4TH QUARTERS 1992 i
1 l
l 1st QUARTER l 2nd QUARTER l 3rd QUARTER l 4th QUARTER i
l STATION NO.
I N/A l
mrem I
mrem I
mrem i
I I
I I
I e
1 l
l 16.2 i 7.0 l 15.8 9.1 1 19.0 i 4.0 l
l l
1 l
2 l
24.6 i 1.8 l 22.2 i 3.3 1 23.2 i 8.2 I
I I
I I
I 4
l 3
I I
20.4 i 3.0 l 19.6 i'7.9 l 20.0 i-4.9 l
I I
I I
I I
6 l
4 I
I 23.6 t 3.3 1 21.6 2.3 1 23.4 i 7.8 l
I I
I I
l 5
l 42.0 111.7 1 34.4 12.5 l 30.4 i 3.6 I
I I
L l
6 l
17.2 1 3.0 14.0 7.5 l 17.8 + 2.6 4
I I
I I
l 7
l l
21.2 i 2.6 21.4 i 3.9 l 21.6 6.1 1
I I
I I
)
l 8
I l
22.4 5.2 1 20.6 t 5.4 l 24.4 113.4 I
I l
l r
l O
i 9
3o+8o 8 2 + 9-34+
3 I
I I
I I
I 10 l
l 19.6 5.8 l 22.0 2.8 I 25.2 i 3.6 l;
I I
I I
(
l 11 1
22.0 5.8 I 21.0 i 3.7 1 20.3 3.8 l
l l
l l
l l
l 12 1
24.0 9.7 I 28.0 i 6.8 1 25.0 i 3.2 l
1 1
I I
I l
13 l
l 39.6 t 8.2 l 28.4 i 4.1 1 32.4 i 5.9 I
I I
I I
l l
14 l
l 20.0 + 6.6 1 15.8 i 2.2 1 19.0 i 4.5 l
l l
1 l
l l
l 15 l
31.2 7.9 1
30.2 i 4.8 l 28.8 i 4.3 l
1 I
I I
I l
16 I
l 73.4 i 8.2 1 75.6 113.5 I 67.6 i 8.1 J
l i
I I
I l
17 l
l 86.0 i?8.8 l 117.6 i 24 1119.2 126.9 I
I I
I I
l 18 I
I 72.4 i10.4 l 81.8 i11.4 I 86.6 116.5 I
I I
i 1
19 l
I 52.0 i 4.9 I 55.8 i13.7 1 53.2 i 3.0 l
l l
l 1
l 20 40.4 14.7 1 45.6 _-13.2 l 49.0 112.2 l
1 I
I I
l 21 49.2 11.7 I 60.2 t 7.8 I 62.8 ill.9 l
O All TLD's greater than 5 miles from the plant are considered control TLD's.
l l
i_
l 2
3 3
0 6
3 EL 0
0 0
2 0
0 O
SO 0
0 0
0 0
0 SR OT RN i
i i
i i
1 COC 5
9 4
6 5
8 A
3 4
4 7
4 2
L 0
0 0
0 0
0 M
l1 II II II II R
3 3
4 4
3 3
A 0
0 0
0 0
0 F
0 0
0 0
0 0
3 I m T/
i 1
1 i
i T1 EC 1
3 0
6 6
9 RD 3
4 4
4 3
2 D
0 0
0 0
0 0
Y E
T P
I 11 II N
I R
3 4
4 4
3 3
C E
0 0
0 0
0 0
I W
0 0
0 0
0 0
V g
)
Tm R
e
/
i i
i i
i W u O1 B
l IC 8
6 4
4 0
6 C
a D o 3
4 4
4 4
3 A V A
0 0
0 0
0 0
I R
l E
o i1 lI H
r T
t M
5 5
5 6
5 5
n R
0 0
0 0
0 0
N o
A 0
0 0
0 0
0 I
C
{
m S
s I/
i i
1 i
i E
e L1 0
T m
OC 0
8 0
5 1
7 1
A i
ND 5
5 5
6 5
3 L
t A
0 0
0 0
0 0
E U
I 3
OL C 0 G
5 B
I 1
A T
II T
R 3
4 3
3 4
3 A
0 0
0 0
0 0
P l
0 0
0 0
0 0
e g
R v
- m I
e
/
i i
i i
i A L Mi AC 4
7 5
6 7
3 A
g D o 4
5 3
3 4
2 T
n 0
0 0
0 0
0 E
i B
t r
I1 i1 S
o T
iI iI S
p R
2 3
3 3
2 2
O e U
0 0
0 0
0 0
R R O
0 0
0 0
0 0
G
(
g m
Y R/
i i
i i
L Ei K
LC 1
4 4
3 8
5 E
I o 3
3 3
3 2
2 E
A 0
0 0
0 0
0 W
RT I1 iI ii I1 T
4 4
4 3
5 5
f 0
0 0
0 0
0 0
0 0
0 0
0 P m/
t 1
i i
i Ri WC 4
0 4
1 8
6 B o 3
4 3
3 2
4 C
0 0
0 0
0 0
AL N
il II I1 O
I 2
2 2
2 2
2 T
9 9
9 9
9 9
/
/
/
/
/
/
ET 7
4 1
8 4
1 LA 0
1 2
2 0
1 O
LD
/
/
/
/
/
/
O 1
1 1
1 2
2 C
l i
O*
O O8s'.4 HSP-03 Issue 12 TABLE 10A WEEKLY GROSS BETA AIR PARTICULATES IN THE IACBWR VICINIIT (Reporting Level - 10 times Control Value)
COLLECTION 1ACBWR PpiT TRAILERg0URT l
DAM #g
}
RADIO TO'fER l
1A CROSSE I
DATE 1992 oCi/m oCi/m I
oCi/m I
oCi/m i
CONTROL 2/17
.038 i.003
.024
.002
.039 i.003
.039 t.003
.043
.004 2/25
.028
.004
.022 i.002
.030 i.003
.030
.003
.031
.004 l
3/3
.028 i.003
.023
.003
.033
.003
.030 i.003
.031 i.003 3/10
.025 i.003
.023 i.003
.027 i.003
.032
.003
.023
.003 1
3/17
.023 f.003
.020 i.002
.028 f.003
.032 i.003 I
.026 i.006 1
3/24
.021 i.003
.019 i.002
.0284 i.003
.030 i.003 I
NO SAMPLE I
I 3/30 I
.024 i.003 I
.020 i.002
.029 i.003
.031 i.003
.028 i.003 4/7
.018 i.003
.020 t.002
.030 i.002
.026 i.003
.028 i.003 l
l 1
4/14
.026 i.003
.023
.002
.033 i.003
.033 i.003 I
.028
.003 4/21
.013
.002
.015 i.002
.017 i.002
.021 i.002
.019
.002 1
4/28
.018 i.003 I
.013 t.002
.018 i.002
.023 i.003
.020
.002 1
5/5
.028
.003 I
.024 i.002
.034 t.003
.034
.003
.029 i.003 I
5/12
.029 i.003
.027 t.003
.030 i.003
.036
.003 I
.029
.003 l
5/19
.017
.002
.019
.002
.019 f.002
.023 i.003 I
.017
.002 I
I I
I 5/26
.020 i.003 I
.023
.002 I
.022
.003 I
.026 i.003 i
.017
.002 I
I 6/2
.027 i.003
.024 i.003 1
.030 i.003
.033 i.003 1
.031
.003 !
O O
Q,e 55 HSP-03.4 Issue 12 TABLE 10A WEEKLY GROSS BETA AIR PARTICULATES IN THE IACBWR VICINITY (Reporting Level - 10 times Control Value)
COLLECTION IACBWR P y TRAILERg0URT DAMgg RADIOT0yER LA CROSSE l
DATE 1992 oCi/m oCi/m oCi/m oCi/m CONTROL 6/9
.023 i.002
.031 i.003
.029 i.003
.027
.003
.023 i.002 l
1 I
i 6/16
.033
.003
.040 i.003 I
.038 i.003
.041 i.003 I
.031 i.002 l
l 1
6/23
.015 +.002
.018 i.002
<.001 I
.016 i.002
.014
.002 l
6/30 I
.016 i.002
.020 1.002
.024 i.003
.022 i.002
.920 i.002 7/7
.021 i.003
.023 i.002
.018 i.002
.020 i.001
.020
.002 7/14
.014 i.003
.022 i.003
.019 i.002
.016 i.003
.009 i.001 7/21
.011
.003
.013 i.002 I
.009 i.002
.011 i.003
.009 i.002 l
I 7/28
.018 i.002
.023 i.002
.018 i.002
.024 i_.003
.037 i.003 8/4
.019 i.002
.021 i.003
.023 i.002
.016 i.003
.017 i.002 8/11
.025 i.003
.028 i.003
.022 f.003
.030
.004
.024 i.002 l
8/18 l
.023 i.003
.023 i.003
.023 i.003
.020
.003
.021 i 002 1
8/24 I
.031 i.003
.037
.004
.035 i.003
.040 t.003
.012
.005 9/1
.016
.002
.018 i.002
.003
.001
.019
.002 NO SAMPLE 9/9
.021
.002
.029
.003
.026 f.003
.027 1.003
.018 i.002 9/15
.017 i.003
.023 i.004
.021
.002
.021
.003.
.014 i.002 I
I 9/22 l
.020 t.003
.030 t.003 NO SAMPLE
.024 i.003 I
.024
.002 !
t O
O age 56 i
HSP-03.4 Issue 12 TABLE 10A WEEKLY GROSS BETA AIR PARTICUIATES IN THE IACBWR VICINITY (Reporting Level - 10 times Control Value)
COLLECTION IACBWR P y TRAILERg0URT DAMfg RADIOTO3ER 1A CROSSE DATE 1992 oCi/m oCi/m oC1/m DCi/m CONTROL 9/29
.019 t.003
.021 i.003
.019 i.003
.019 i 003
.020
.002 10/6
.029 i.003
.041 i.003
.042 i.003
.039 i.003
.041 i.003 1
10/13
.021 i.003
.026 i.003
.023 i.003
.027 i.003
.027 i.002 10/20
.022 i.003
.026
.003 NO SAMPLE
.026 i.003
.024 i.002 10/27
.042 i.003
.059 i.004
.048 1.004
.062 i.004
.056 i.003 l
11/3
.015 1.002
.014 i.002
.015 f.002
.023 i.003
.017 i.002 11/10
.021 i.002
.021 i.002
.022 i.003
.019 i.002
.016 i.002 i
'11/17
.025 i.003
.027 i.003
.031 i.004
.028 i.003 l
.025 i.002 l
11/24 I
.015 i.002
.016 i.002
.020 i.003
.019 i.003
.013 i.002 12/1
.038 i.003
.037 i.003
.036 i.003
.036 i.004
.027 i.002 I
i 12/8
.028 f.003
.027 f.003 l
.028 i.003 I
.027 f.003
.027
.002 i
12/15
.033 1.003
.026 f.003
.041 i.003 I
.033 i.003
.029 f.002 i
i I
12/22
.045
.003
.045
.003
.036 i.003 I
.052 i.003 I
.046 i.003 12/29
.042 i.003
.054 i.003
.039 i.003
.053
.004
.044 i.003 I
I I
56 -
~
O O
O TABLE 11 AIR PARTICUIATE COMPOSITE RESULTS (Report Concentrations in pCi/m l
LOCATION:
GIANOLI RADIO TOWER PEDRETTI IACBWR TRAILER CRT*
DAM NO. 8 LA CROSSE 12 30/91 START DATE:
12/30/91 12/30/91 12/30/91 12/30/91 12/30/91 12/30/91 f
END DATE:
01/28/92 01/28/92 01/28/92 01/28/92 01/28/92 01/28/92 01/28/92 ISOTOPES /RL*
Cs-134/10
<1.34 E-3
<8.62 E-4
<8.34 E-4
<1.07 E-3
<6.14 E-4
<7.71 E-4
<1.25 E-3.
l I
Cs-137/20
<1.50 E-3 l <8.26 E-4
<9.45 E-4
<1.18 E-3
<6.15 E-4
<9.71 E-4
<1.39 E-3 I
I I
I l
IDCATION:
GIANOLI RADIO TOWER PEDRETTI IACBWR TRAILER CRT DAM NO. 8 LA CROSSE START DATE:
01/28/92 01/28/92 01/28/92 01/28/92 01/28/92 01/28/92 01/28/92 END DATE:
02/10/92 03/03/92 02/10/92 03/03/92 03/03/92 03/03/92 03/03/92 ISOTOPES /RL*
Cs-134/10
<2.67 E-3
<6.60 E-4
<1.95 E-3
<1.08 E-3
<4.90 E-4
<7.33 E-4
<9.32 E-4 Cs-137/20 1
<2.91 E 3
<7.38 E-4
<1.91 E-3
<1.06 E-3
<4.76 E-4
<6.74 E-4
<8.28 E-4
- RL - REPORTING LEVEL
- S7 -
ll lll lIl llll i
- l E
E O
S2 2
3 3
S2 2
4 4
S9 9
S9 9
O/
/
E E
O/
/
E E
R3 0
R0 8
C0 3
3 9
C3 2
5 7
/
/
4 4
/
/
7 3
A3 3
A3 4
1 0 0
1 1
1 0 0
7 7
l' 1l lll1 lI 82 2
4 4
82 2
4 4
9 9
9 9
./
/
E E
./
/
E E
O3 0
O0 8
N0 3
1 1
N3 2
0 5
/
/
6 0
/
/
7 9
M3 3
M3 4
A0 0
9 9
A0 0
8 8
D D
Il Il
' i II T
T R
R S
U U
T O2 2
4 4
O2 2
4 4
L m
C9 9
C9 9
U
/
/
/
E E
/
/
E E
S i
R3 0
R0 8
E C
E0 3
5 8
E3 2
0 4
R p
L/
/
9 8
L/
/
8 3
I3 3
I3 4
E n
A0 0
5 6
A0 0
5 6
T i
R R
I T
T S
s t*
O n
O1 P
o 8
1 M
i 5
O t
E C
a L
r B
E t
A T
n T
A e
2 2
4 3
2 2
4 4
I c
R9 9
R9 9
U n
W/
/
E E
W/
/
E E
C o
B3 0
B0 8
I C
C0 3
3 4
C3 2
1 5
T A/
/
2 0
A/
/
4 8
R t
I 3 3
I 3 4
A r
0 0
8 1
0 0
8 9
P op R
e I
R A
(
I1 I1 1I R
R E2 2
4 3
E2 2
4 4
W9 9
W9 9
O/
/
E E
O/
/
E E
T3 0
T0 8
0 3
8 2
3 2
7 6
O/
/
7 0
O/
/
6 9
I3 3
I3 4
D0 0
8 1
D0 0
8 8
A A
R R
LE l
lI VEL G
N L
L I
E R
E R
T T
/
0 0
T
/
0 0
R NAE S
1 2
NAE S
1 2
O ODT E
/
/
ODT E
/
/
P I
A P
4 7
I A
P 4
7 E
TTD O
3 3
TTD O
3 3
R O
AR T
1 1
AR T
1 1
CAD O
CAD O
OTN S
s s
OTN S
s s
LSE I
C C
LSE I
C C
LR
l IlI lll1Il E
E O
S2 2
4 4
S2 2
4 4
S9 9
S9 9
O/
/
E E
O/
/
E E
R8 2
R2 0
C2 0
1 5
C0 3
5 7
/
/
2 3
/
/
8 9
A6 6
A4 6
L0 0
4 5
I 0 0
5 5
II II 82 2
4 4
82 2
4 4
9 9
9 9
./
/
E E
./
/
E E
O8 2
O2 0
N2 0
2 7
N0 3
2 6
/
/
6 0
/
/
4 9
M4 6
M6 6
A0 0
6 7
A0 0
7 8
D D
T T
R R
S U
U T
O2 2
4 4
O2 2
4 4
L m
C9 9
C9 9
U
/
/
/
E E
/
/
E E
S 1
R8 2
R2 0
E C
E2 0
1 0
E0 3
9 5
R p
L/
/
9 6
L/
/
9 6
I4 6
I6 6
E n
A0 0
4 5
A0 0
7 7
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R R
I T
T S
s t
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1 P
o 9
O1 M
i II 5
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a L
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2 2
4 4
2 2
4 4
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R9 9
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W/
/
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B8 2
B2 0
I C
C2 0
7 7
C0 3
2 3
T A/
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8 6
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L4 6
I6 6
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0 0
6 7
0 0
8 9
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4 4
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4 4
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W9 9
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2 0
3 2
0 3
6 8
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8 5
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I4 6
I6 6
D0 0
6 6
D0 0
9 8
A A
R R
LEVEL G
N L
L I
E R
E R
T T
/
0 0
T
/
0 0
R NAE S
1 2
NAE S
1 2
O ODT E
/
/
ODT E
/
/
P I
A P
4 7
I A
P 4
7 E
TTD O
3 3
TTD O
3 3
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AR T
1 1
AR T
1 1
CAD O
CAD O
OTN S
s s
OTN S
s s
LSE I
C C
LSE I
C C
L R
llllIlllIl1l1l llj lll E
E O
S2 2
4 4
S2 2
3 3
S9 9
S9 9
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/
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O/
/
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R0 8
R8 1
C3 2
1 3
C2 0
5 6
/
/
3 4
/
/
8 1
a6 7
A7 9
l 0 0
5 6
10 0
1 4
II 11 I1 ll ll l
82 2
4 4
82 2
3 3
9 9
9 9
./
/
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./
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On 8
O8 1
N3 2
6 4
N2 0
3 1
/
/
1 6
/
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7 8
M6 7
M7 9
A0 0
8 8
A0 0
1 2
D D
II 1l ll ll I1 l1 T
T R
R S
U U
T O2 2
4 3
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3 3
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C9 9
C9 9
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R8 1
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8 2
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7 3
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9 1
A0 0
1 4
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s t
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1 P
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R9 9
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B0 8
B8 1
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C3 2
4 7
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5 8
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L6 7
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R E2 2
3 3
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3 3
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W9 9
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T8 1
3 2
3 3
2 0
4 8
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I7 9
D0 0
1 1
D0 0
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R R
L ll E
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/
0 0
T
/
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1 2
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1 2
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/
/
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/
/
P I
A P
4 7
I A
P 4
7 E
TTD O
3 3
TTD O
3 3
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1 1
AR T
1 1
CAD O
CAD O
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s s
OTN S
s s
LSE I
C C
LSE I
C C
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1 Il lll1I Il1 i
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4 4
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4 4
S9 9
S9 9
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/
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R1 9
R9 3
C0 2
7 2
C2 0
3 0
/
/
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/
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4 8
A9 9
A9 1
I 0 0
6 5
I 0 1
4 4
ll I!
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4 4
82 2
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9 9
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O1 9
O9 3
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9 2
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5 3
/
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/
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M9 1
A0 0
6 7
A0 1
8 9
D D
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T E
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5 S
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1 T
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4 4
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4 4
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C9 9
C9 9
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/
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R9 3
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9 8
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R9 9
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B9 3
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0 7
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I9 9
1 9 1
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0 0
7 8
0 1
7 6
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4 4
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4 4
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W9 9
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7 1
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1 2
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1 2
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/
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/
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4 7
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3 3
TTD O
3 3
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1 1
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1 1
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s s
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s s
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W9 9
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7 1
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L I
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T T
/
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T
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1 2
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1 2
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/
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/
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4 7
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3 3
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3 3
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O TABLE 12 E.E. SULTS OF ANALYSIS OF MISSISSIPPI RIVER VATER IN THE VICINITY OF IACBVR (Report Concentrations in pCi/ Liter)
SAMPLE #1 SAMPLE #2 SAMPLE #3 SAMPLE #1 SAMPLE #2 SAMPLE 43 l
COLLECTION DATE:
01/07/92 01/07/92 01/07/92 02/04/92 02/04/92 02/04/92 l
SAMPLE LOCATION:
VICTORY OUTFALL DAM #8 VICTORY OUTFALL DAM #8 1
ISOTOPES /RL*
i l
l l
l H-3/20000
< 254
< 254
< 254 1
282
< 244 1
320 i
Mn-54/1000
< 11.9
< 13.2
< 11.6
< 11.5
< 13.0 i
< 11.6 i
Fe-59/400
< 23.6
< 30.4
< 22.8
< 29.7
< 29.4 1
< 24.5 l
Co-58/1000
< 12.9
< 11.6
< 10.6
< 11.1
< 11.0 1
< 11.8 Co-60/300
< 20.8
< 19.3
< 19.3
< 23.9
< 23.7
< 21.3 l
l Zn-65/300
< 27.5
< 34.7
< 25.0
< 27.7 i
< 24.8
< 22.7 l
l Zr-95/400
< 20.3
< 23.3
< 19.8
< 20.5
< 20.0
< 24.0 I
Nb-95/400
< 13.8
< 12.8
< 11.4 i
< 11.5
< 10.C
< 11.4 l
Cs-134/30
< 13.6
< 12.3
< 12.4
< 13.6 1
< 10.1
< 11.5 L
i l
Cs-137/50
< 12.6
< 12.8 l
< 13.2
< l.2.8
< 12.6 1
< 13.2 Ba-140/200
< 54.6
< 45.3
< 55.7
< 47.8
< 45.8
< 52.8 La-140/200
< 13.7
< 14.1
< 19.2
< 16.6
< 15.1
< 12.5
- RL - REPORTING LEVEL llll l[
O 32
- 9Y/R 6
8 8
6 0
E7 O 7
L0T 4
0 0
1 0
3 P/C 2
1 2
2 1
1 M4I A0V S
ll Ii il R
22 W
- 9L B
/L 3
2 0
6 C
E7 A 7
5 A
L0F 4
0 3
7 2
3 L
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1 2
2 1
1 M4U F
A0O O
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C 12 I
- 98 V
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6
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2 1
1 iT t
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32
- 9L 2
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/L 9
5 3
0 0
1 E
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1 3
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3 E
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2 1
1 4
OL R
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0 5
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3 5
3 8
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1 3
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2 S
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1 2
2 1
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1 P/C 2
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3 1
1 M6I A0V S
lll1 lI l1 li II lI Il il II iI II 22 k
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/L 3
9 3
2 0
C E2A 1
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1 1
3 1
1 M6U F
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3 1
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R s
/R 5
1 9
6 8
1 E
n E5O 1
5 V
o L0T 0
1 9
5 1
1 E
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1 1
2 1
1 5
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t M5I 6
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A0V A
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c l1 lI S
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C 22 S
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2 4
1 8
M r E5A 7
o L0F 4
2 1
5 2
2 F
p P/T 2
1 2
2 1
1 r
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A0O S
(
S I
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12
- 98 F
/#
3 0
0 0
2 O
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1 2
4 2
3 S
P/A 2
1 2
2 1
1 T
M5D L
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0 0
0 0
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0 0
0 0
3 5
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0 1
3 3
/
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/
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2 4
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- 98/#
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3 P/A 2
1 2
2 1
1 M8D A0 S
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22 W
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/L 4
4 8
4 3
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1 2
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1 2
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1 1
2 1
1 T
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I
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p T
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- 98 2
R s
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5 1
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1 1
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1 E
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1 2
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R t
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a A0 A
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P t
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c 1I 1l lI S
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C 22 S
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/L 2
2 6
5 6
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1 0
1 3
2 F
p P/T 2
1 2
3 1
1 O
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A0O S
(
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- 9Y F
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4 5
9 0
O E7O 9
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3 1
6 0
2 S
P/C 2
1 2
3 1
1 T
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/
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0 0
0 0
3 5
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0 1
3 3
/
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/
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4 7
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2 4
0 5
3 3
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/
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6 1
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3 LM S
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1 2
2 1
1 M0D A1 S
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22 V
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7 1
6 6
C E6 A 5
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0 3
8 2
2 L
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2 1
1 M0U F
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1 2
2 1
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i 32
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R s
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1 2
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- 9Y F
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6 6
5 3
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3 9
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1 1
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2 4
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p P/C 2
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A1V S
(
S I
SY l1 lI LANA 12
- 9L F
/L 1
3 3
8 0
O E3A 2
L0F 4
1 0
2 0
2 S
P/T 2
1 2
2 1
1 T
M1U L
A1O U
S L
S E
E V
R l1 ll EL EN G
TO N
AI I
DT L
T A
R 0
R NC
/
0 0
0 0
0 O
OO S
0 0
0 3
5 P
IL E
1 3
3
/
/
E T
P
/
/
/
4 7
R CE O
4 0
5 3
3 EL T
5 6
6 1
1 LP O
3 LM S
n o
n s
s L
OA I
H M
C Z
C C
R O
I ll ll l1ll 1
1
+
E E
3 O
- 2L 3
3 9L 1
28 29 E/A
. +. +
L3F 4
E1 E1 P2T 1
M/U 4i 7i A7O
< 1 S0 2
8 6
ll lI II l1 l1 1I lI Ii 1
R
+
W M
E B
2 A
C
- 2E 1
A 9R 8
11 L
E/T
. +
L3 S 5
E1 F
P2N 2
O M/W 9i A7O
< 8 Y
S0D T
8 I
N lI iI I
C IV 1#2M E
9A 5
1 H
E/E 8
T L3R 2
)
P2T 1
7 N
g M/S I
K A7P
/
S0U T
i N C E
p l1 lI I1 M
I n
1 1
D i
+
+
E 3
E E
E S
n
- 2G 3
o 9R 3
36 28 1
R i
E/A
. +6
+5 E
t L7H 6
E E
E V
a P0C 1
3 2
9 L
I r
M/S 4
6 6
OB R
t A5I
< 0. + 9. f A
n S0D T
I e
2 8
P c
P n
iI I
o S
C S
M I
t 2
A S
r
- 2E S
o 9R 2
9 I
p E/T M e L7S 5
0 E
R P0N 1
1 L
F
(
M/W P
O A5O M
S0D A
S S
I Y
ii L
S iI ll l1 O
L R
A T
N 12M N
A
- 9A O
/E 9
3 C
F E7R 7
O L0T 2
S P/S 1
9 E
S M5P M
T A0U I
L S
T U
S 0
ER Ii 1
EN TO L
AI E
DT V
A E
NC L
OO S
IL E
G T
P 4
7 N
CE O
3 3
0 I
EL T
1 1
6 T
LP O
R LM S
s s
o O
OA I
C C
C P
O l
R CS E
[
TABLE 14 RESULTS OF ANALYSIS OF MIlX SAMPLES IN THE VICINITY OF LACBWR (Report Concentrations in pCi/ Liter) l SAMPLE l COLLECTION ISOTOPES / REPORTING LEVEL l LOCATION l DATE Cs.134 /60 l Cs-137/60 l
l l
l l
l l
l l A. MALIN I 1/14/92 l < 13.1 1 < 14.3 l
l l
l l
l l
l l
l PEDRETTI l 2/11/92 l < 10.1 l < 12.6 l
l ll l
l l
l l
1 l P. MALIN l 3/10/92 1 < 11.0 l < 12.4 l
l l
l l
I I
l l PEDRETTI l 4/14/92 1 < 12.0 l < 12. 6 l
l
[
l l
l l
l l
l PEDRETTI l S/12/92 l < 11.6 l < 11. 6 l
l l
l l
l l
l l
l P. MALIN 1 6/9/92 1 < 10. 9 l < 13.0 l
I l
l l
l l
l PEDRETTI l 7/14/92 l < 11.3 1 < 13 3 l
l l
l l
l l
l l
P. MALIN l 8/11/92 l < 14.4 l < 12.1 l
l i _ _.
I I
I I
I j A. MALIN I 9/9/92 l < 14.8 I < 12. 5 l
l I
I I
I I
A. MALIN l 10/13/92 i < 15.0 1 < 13.0 I
l O
l l
l 1
I
[ P. MALIN l 11/10/92 l < 14.1 1 < 13.1 l
l l
l l
l l
l I
l PEDRETTI l 12/8/92 1 < 9.58 I < 13.0 l
l l
i l
l l
l l
l
[
l I
I I
I I
l l
l 1
I l
l 1
1 I
I I
l l
i I
I I
l l
l l
l l
l l
l l
l l
l l
1 1
I I
l 1
1 I
I I
I i
I I
i I
i i
i I
I I
I I
i l
l I
I I
l l
l 1
1 I
l l
l l
l 1
1 I
I I
I I
I I
I I
I I
I I
I l
l 1
I I
I l
l I
I I
I I
l l
I 1
1 I
l
, O l
l l
2 O
- 2 9P 6
4 5
5 6
E/R 7
4 L4A 5
0 0
P2C 8
1 3
9 1
M/
A7 S0 Il l1 1l lI 1#2E 9Y 0
9 0
5 3
E/E L4L 1
4 8
0 0
P2L 1
1 2
1 1
M/A A7W S0 Il l1 II Il Il II R
W B
2 C
- 2 L
E/R 0
6 1
A 9P 4
1
)
L7 A 6
8 0
2 5
F g
P0C 1
2 4
1 1
O K M/
/
A5 Y
1 S0 T C I
p I
n II N
C i
I V
s 1
n
- 2E 5
E o
9Y 5
4 2
1 9
1 i
E/E 1
iT t
L7L 0
9 2
9 2
E a
P0L 2
3 5
1 2
1 L
N r M/A 7
O B
I t
A5W A
n S0 T
Y e
T c
I n
II V
o I
C TC t
2 A r
- 2 o
9P 0
0 4
9 8
E p
E/R 2
4 L
e L4A 9
4 0
P R P2C 8
1 2
9 1
M (
M/
A A3 S
S0 H
S Il Il I
F 1
- 2E9Y 5
0 8
9 2
E/E 9
8 L4L 8
9 0
P2L 9
1 2
9 1
M/A A3W S0 LEV l1 EL E
G T
N A:
I DS L
T E
R 3
3 R
NI
/
4 4
4 E
E O
OC S
E E
E 1
2 P
IE E
3 1
2
/
/
E TP P
/
/
/
4 7
R CS O
4 0
5 3
3 E
T 5
6 6
1 1
LH O
LS S
n o
n s
s L
OI I
M C
Z C
C R
O l
lllIIlIlllllllil1lIII lIlIl O
EL P
M A
S Il Il ll ll 1i 1l ll II II Il Il ELP M
A S
,1 Il II ll lI II II Il Il Il R
4'B C
A I
E
)
L F
g P
O K M
/
A Y
i S
T C
I p
N Il 1l n
I C
i I
V sn 5
E o
1 H
i E
T t
L E
a P
2 L
N r M
7 O
B I
t A
A n
S T
Y e
T c
I n
V o
Il I
C TC t
22 A r
- 9 o
/P 3
0 4
2 6
E p
E2R 9
8 6
L e
L2A 6
2 P
R P/C 9
1 2
8 8
M (
M0 A
A1 S
S H
S l1 lI II II II lI I
F 8
12 7
- 9E
/Y 1
8 9
7 5
E2E 3
0 L2L 7
5 i
P/L 9
1 2
9 M0A 7
A1W S
0 L
1 E
l1 VEL E
G T
N A:
I DS L
T E
R 3
3 R
NI
/
4 4
4 E
E O
OC S
E E
E 1
2 P
I E E
3 1
2
/
/
E TP P
/
/
/
4 7
R CS O
4 0
5 3
3 E
T 5
6 6
1 1
LH O
LS S
n o
n s
s L
OI I
M C
Z C
C R
O 1
li[I lil1l1i 1I O
EL P
MA S
ll Il I1 ll 1I EL P
M A
S RW Il ll Il II BCAL F
O E
)
L Y
g P
T K M
I
/
A N
i S
I C
C p
IV n
lI il ll i
E l
s iT n
6 o
1 N
i E
I t
L E
a P
3 L
Y r M
7 O
B T
t A
A I
n S
T V
e I
c T
n 1!
C o
A C E
t 2
Y L
r
- 2I T
P o
9T I
E D
M p
E/TM O
V V
A N
A e
L9ER N
I O
D U
S R P0RA T
B M
O
(
M/DF C
A F
N A9E A
O S0P I
TAT il lI lI E
G T
E 1
I Y
V
- 2P T
9 A
I E
D E/iO V
V A
N l
L9SN O
I O
D U
P0AE N
T B
M O
M/
C C
A F
A9Y A
S0L L
F EVE Il II li ll lI L
E G
T N
A L*
I D
T R
R N
/
O O
S P
I E
E T
P R
C O
E T
L O
L S
L O
I R
O C