ML20153G478
| ML20153G478 | |
| Person / Time | |
|---|---|
| Site: | Davis Besse  |
| Issue date: | 12/31/1985 |
| From: | Storz L TOLEDO EDISON CO. |
| To: | James Keppler NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III) |
| References | |
| NUDOCS 8602280313 | |
| Download: ML20153G478 (285) | |
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w/ E61 SON E 2.30.1.5 February 13, 1986 RR 2 P-2-85-02 Mr. James G. Keppler Regional Director, Region III Office of Inspection & Enforcement U. S. Nuclear Regulatory Commission 799 I'oosevelt Road Glen Ellyn, Illinois 60137
Subject:
Effluent and Waste Disposal Semiannual Report for the Period Fron July 1, 1985 through December 31, 1985 Davis-Besse Nuclear Power Station Unit 1.
Dear Mr. Keppler:
Enclosed find two (2) copies of the Effluent and Waste Disposal Semiannual Report for Davis-Besse Nuclear Power Station covering the third and fourth quarters of 1985. Included as attachments are the revised versions of the Offsite Dose Calculation Manual (ODCM) and the Process Control Program
,/~' s (PCP) per Davis-Besse's Technical Specifications Appendix A, Section
(,) 6.9.1.11. The applicable portions of Regulatory Guides 1.109, 1.111, and 1.113 have been used along with NUREG-0133 for dose calculations and meteorological modeling methodology to demonstrate compliance with Appendix I to 10 CFR Part 50. Sincerely. Louis F. Storz Plant Manager Davis-Besse Nuclear Power Station LFS/JB B602280313 851231 [ mj d/61 PDR ADOCK 05000346 R PDR Enclosures l cc: Mr. James M. Taylor Health Program Director Office of Inspection & Enforcement Ohio Department of Health Encl.: 25 copies Encl: 1 copy n
) Ohio Environmental Protection Agency Mr. James Greer w_/ Northwest District Office Ottawa County Disaster Services Encl: 1 copy Encl: 1 copy THE TOLEDO EDISON COMPANY EDISON PLAZA 300 MADISON AVENUE TOLEDO. CHIO 43S52 NRC Resident Inspector Encl: 1 copy
O EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT DAVIS-BESSE NUCLEAR POWER STATION UNIT 1 For the Period From JULY 1, 1985 - DECEMBER 31, 1985 Docket No. 50-346 License No. NPF-3 TOLEDO EDISON COMPANY 300 MADIFON AVENUE TOLEDO, OHIO 43652 l FEBRUARY, 1986 O
l l EFFLUENT AND WASTE DISPOSAL ( SEMIANNUAL REPORT DAVIS-BESSE NUCLEAR POWER STATION ; UNIT 1 JULY 1, 1985 - DECEMBER 31, 1985 TABLE OF CONTENTS PAGE TOPIC TABLE 1 Supplemental information 6 Gaseous Effluents - Summation of All Releases 1A 7 Gaseous Effluents - Elevated Releases 1B 8 Gaseous Effluents - Mixed Mode Releases 1C 9 Liauid Effluents - Summation of All Releases 2A 10 Liouid Effluents 2B 11 Solid Waste and Irradiated Fuel Shipments 3A i 4 12 Maximum Individual Dose Due to j Release of Noble Gas 1 13 Maximum Individual Dose Due to I Release of I-131, H3, and Particulates 2 with halflives > 8 daws 14 Population Dose Due to Release of Noble Gas 3 15 Population Dose Due to Release of I131, H3, and Particulates with 4 halflives > 8 daws 16 Population Dose Due to Liouid Releases 5 O
TABLE OF CONTENTS (continued) PAGE TOPIC TABLE 17 Maxium Individual Dose Due to Liouid Releases 6 18 Joint Freauenew Distributions, Third Quarter Continuous Releases, 7 35 ft. elevation 26 Joint Freauenew Distributions, Third Quarter Continuous Releases, 8 250 ft. elevation 34 Joint Freauenew Distributions, Fourth Quarter Continuous Releases, 9 35 ft. elevation 42 Joint Freauenew Distributions, Fourth Quarter Continuous Releases, 10 250 ft. elevation 50 Joint Freauenew Distributions, Third Quarter Batch Releases, 11 35 ft. elevation 58 Joint Freauenew Distributions, Third Quarter Batch Releases, 12 250 ft. elevation 66 Joint Freauenew Distributions, Fourth Quarter Batch releases, 13 35 ft. elevation 74 Joint Freauenew Distributions, Fourth Quarter Batch Releases, 14 250 ft. elevation 82 Hourlw Meteorological Data During 15 Third Quarter Batch Releases 84 Hourlw Meteorological Data Durins Fourth Quarter Batch Releases 16
)
lllI 1 1
4 EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT Page 1
,x Facility: Davis-Besse Nuclear. Power Station, Unit 1
{ ; Licensee: The Toledo Edison Company 'N ~/ Reporting Period: July 1, 1985 - December 31, 1985 Supplemental Information:
- 1. Regulatory Limits Liquid and Caseous Radioactive Effluent Limits LIQUID GAS ANNUAL DOSE <25 mrems total body or any organ COMMITMENT FROM 75 mrems thyroid URANIUM FUEL CYCLE SOURCES (40 CFR 190)
DOSE LIMIT Noble Gas I-131 Tritium & Particulates** Calendar quarter $1.5 mrem total body <5 mrad /qtr.* <7.5 mrems/qtr. any organ
<5 mrem to any organ <10 mrad
/qtr.*
I T x, ,jlendar year <3 mrem total body
<10 mrad /yr*
<l5 mrems/yr any organ
<10 mrem to any
<20 mrad /yr*
organ DOSE RATE <500 mrems/yr total <1500 mrems/yr any LIMIT body organ
<3000 mrems/yr skin MICR0 CURIES PER 10 CFR 20 Part 20.106 MILLIMETER LIMIT MICR0 CURIES PER MILLIMETER
_4 LIMIT FOR 2x10 microcuries/ml DISSOLVED OR ENTRAINED NOBLE GASES wAbsorbed Air Dose
*cWith half-lifes greater than 8 days
- 2. Maximum Permissible Concentrations - Limits used are specified in 10 CFR 20, Appendix B, Table II, Column 2.
( ) v
Paga 2
- 4. Measurements and Approximations of Total Radioactivitw
- a. Fission and Activation Gases
- 1. These gases, excluding tritium, are collected in a Marinelli twPe beakert sPeCiallw modified for gas samPlingt steel bombst or slass vials and counted on a sermanium detector for Principal samma emitters.
- 2. Tritium sas is collected using a bubbler apparatus and counted bw liauid scintillation.
- b. Iodines - are collected on a charcoal or zeolite cartridge filter, and counted on a sermanium detector.
- c. Particulates - are collected on filter Paper and Counted on a sermanium detector.
- d. Liouid Effluents - are counted in a bottle or Marinelli beaker on a sermanium detector.
- 5. Batch Releases
- a. Liouid
- 1. Number of batch releases: 35
- 2. Total time period for batch releases: 5.31E+01 Hours
- 3. Maximum time period for a batch release: 1.80E+02 Minutes
- 4. Averase time period for batch releases: 9.11E+01 Minutes
- 5. Minimum time period for a batch release: 7.50E+01 Minutes
- b. Gaseous
- 1. Number of batch releases: 5
- 2. Number of containment Purses: 3
- 3. Number of waste sas decaw tank releases: 2
- 4. Total time Period for batch .eleases: 1.15E+02 Hours -
- 5. Maximum time Period for a batch release: 2.22E+03 Minutes
- 6. Averase time Period for batch releases: 1.38E+03 Minutes
- 7. Minimum time Period for a batch release: 8.80E+01 Minutes
- 6. Abnormal Releases None O
, Page 3
- 7. Radiolosical Effluent Technical Specifications (RETS)
A Percent of Limits Specification Limit Percent
- a. Quarter 1w: Gaseous Third auarter, 1985 Noble gases (samma) 5 mrad /otr 7.46E-03 Noble gases (beta) 10 mrad /atr 1.10E-02 I-131, tritium, and radionuclides in Particulate form with half-lives areater than 8 daws 7.5 mrem / ate 2.76E-03
- b. Quarter 1w: Gaseous Fourth auarter, 1985 Noble gases (samma) 5 mrad / ate 4.14E-06 Noble gases (beta) 10 mrad / ate 2.34E-04 I-131, tritium, and radionuclides in Particulate form with half-lives sreater than 8 daws 7.5 mrem / ate 1.83E-03
- c. Calendar wear: Gaseous Noble sases (samma) 10 mrad /wr 3.73E-03*
Noble sises (beta) 20 mrad /wr 5.64E-03* I-131, tritium, and radionuclides in particulate form with half-lives greater than 8 daws 15 mrem /wr 2.29E-03
- d. Quarter 1w: Liauid Third ouarter, 1985 Total bodw 1.5 mrem / ate 9.99E+00 Anw orsan ( LIVER) 5 mrem /atr 4.27E+00
- e. Guarterive Liauid Fourth auarter, 1985 Total bodw 1.5 mrem /atr 9.89E-01 Anu organ ( LIVER) 5 mrem / ate 4.19E-01
- f. Calendar wear:
Total bodw 3 mrem /wr 5.49E+00* Anw orsan ( LIVER) 10 mrem /wr 2 34E+00*
- Value represents the percent of annual limit for the third and fourth quarters of 1985 since Davis-Besse's RETS went into effect during the second half of 1985.
. Page 4
- 8. Dose Assessment The followins is a list of the sources of input data
- a. Water usage - source:
Appendix I analvsis, NRC Docket 50-346, Evaluation of ConPliance with Appendix I to 10CFR50, June 4, 1976, Davis-Besse Nuclear Power Station Unit No. 1.
- b. 0-50 mile meat, milke vesetable Production, and Population data - source:
1982 Annual Environmental Operatins RePorte report entitled,
' Evaluation of Compliance With Appendix I to 10CFR50: Updated Population, Agricultura1r Heat-Animal, and Milk Production Data Tables for 1982'. This evaluation was based on the 1980 Censusi the Asricultural Ministrw of Ontario 1980 report entitled,
' Agricultural Statistics and Livestock Marketins Account, 1980*f the Asricultural Ministrw of Ontario 1980 report entitled "Asricultural Statistics for Ontario - 1980 Publication 21, 1980*l the Michisan Department of Agriculture, Julwe 1981 report entitled ' Michigan Asricultural Statistics, 1981'l the Ohio Crop Reportins Service, 1981 report entitled *0hio Asricultural Statistics, 1981'
- c. Gaseous and liouid source terms - sources: Tables 1A, 1C, 2 and 2B.
- d. Location of the nearest individuals and Pathwaws bw sector out to 5 miles - source:
1985 Annual Environmental Operatins Reporte report entitled,
' Land Use Census'.
Tables 1 and 3 Present the maxitum dQses coRPuted from the noble sas effluents for each ouarter. Tables 2 and 4 Present doses resulting from saseous iodine, and particulate effluents. Doses
.. resultins from liouid releases are Presented in Tables 5 and 6.
O
Pagn 5 (S 9. Inoperable RETS Equipment-I D] The following are explanations as to why certain monitoring equipment required under Davis-Besse's Radiological Effluent Technical Specifications were inoperable for more than 30 days,
- a. Waste Gas System Effluent Flow Rate Measuring Device's FT1821 and FT1821A were declared inoperable on 10/30/85 at 0000 hours.
These meters were found to be malfunctioning during calibration and were sent to a vendor for repair. The vendor has informed us that replacement parts are no longer available. New monitors have been ordered and we are currently awaiting shipment.
- b. Waste Gas System Oxygen Monitor AE5828B was declared inoperable on 11/8/85 at 0825 hours. Due to engineering difficulties this meter is still inoperable.
- c. Station Vent Stack Radiation Monitor Sample Flow Device FT4598AA was declared inoperable on 10/30/85 at 0000 hours.
The meter was returned to an operable state on 2/12/86 at 0200 hours. The delay in getting the meter back to an operable state was due to the implementation of newly acquired test equipment. The total days of inoperability was 105 days.
- d. Station Vent Stack Radiation Monitor Sample Flow Device FT4598BA was declared inoperable on 10/30/85 at 0000 hours.
O}- The meter was declared operable on 12/6/85 at 1650 hours. The delay was caused by the implementation of newly acquired test equipment. The total days of inoperability was 36 days. O v I
Rage 6 l TABLE 1A I I I I EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1985) i I GASEOUS EFFLUENTS - SUMMATION OF ALL RELEASES I I I UNIT 3RD 4TH EST. TOTAL QUARTER QUARTER ERROR, % A. FISSION & ACTIVATION GASES
- 1. TOTAL RELEASE CI 1.81E+01 2.07E-01 2.00E+01
- 2. AVERAGE RELEASE RATE FOR PERIOD UCI/SEC 2.27E+00 2.61E-02
- 3. PERCENT OF TECHNICAL SPEC. LIMIT (RETS) See Sect 7, Supe Information B. I-131, TRITIUM, PARTICULATES, and ALPHA
- 1. I-131, TRITIUM, AND PARTICULATES WITH HALF-LIVES > 8 DAYS CI 3.06E+00 2.76Ef00 2.00E+01
- 2. AVERAGE RELEASE RATE FOR PERIOD UCI/SEC 3.84E-01 3.48E-01
- 3. PERCENT OF TECHNICAL SPEC. LIMIT (RETS) See Sect 7, SUPP Information
- 4. GROSS ALPHA RADIO-ACTIVITY CI 1.36E-05 7.99E-06 l
1 l l O
l TABLE 13 Pcgs 7 EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (85-2) GASEOUS EFFLUENTS- ELEVATED RELEASE
- Muclides Released Unit SE$E' SV $[- Qgap- Qggg-
- 1. Fission gases krypton-85 Ci . E . E . E . E krypton-85a Ci . E . E . E . E krypton-87 Ci . Ei . E . E '. E krypton-88 Ci . E . E . Ei. E xenon-133 Ci . E . E . EI. E xenon-135 C1 . E . E . E I . E xenon-135m Ci . E . E . Ei . E xenon-138 C1 . E . E . E I. E Others (specify) Ci . E . E . E i. E Ci . E . E . E ! . E Ci . E . E I . E . E unidentified Ci . E . E . E . E Total for period Ci . E . E . E . E
; 2. Iodinas
! iodine-131 Ci . E . E . E .' E l iodine-133 Ci . E . E . E . E{
l iodine-135 Ci . E . E . E . E l Total for period Ci . E . E . E . E i l l 3. Particulates strontium-89 Ci . E . E . E . E strontium-90 Ci . E . E . E . E cesium-134 C1 . E . E . E i. E i cesium-137 C1 . E . E . E l . E I barium-lanthanta-140 Ci . E . E . E . E Others (specify) Ci . E . E . E . E Ci . E . E . E . E Ci . E . E . E . E unidentified Ci . E . E . E . E
- Not applicable; all releases are classified as mixed mode releases.
Page 8 l TABLE 1C 1 1 I I EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1985) i I GASEOUS EFFLUENTS MIXED MODE RELEASES I I I CONTINUOUS MODE BATCH MODE NUCLIDES RELEASED UNIT 3RD 4TH 3RD 4TH QUARTER QUARTER QUARTER QUARTER
- 1. FISSION GASES KR-85 CI 0.00E-01 0.00E-01 6.92E-03 2.07E-01 XE131M CI 0.00E-01 0.00E-01 7.85E-05 0.00E-01 XE133M CI 0.00E-01 0.00E-01 7.09E-02 0.00E-01 XE-133 CI 0.00E-01 0.00E-01 1.79E+01 0.00E-01 XE-135 CI 0.00E-01 0.00E-01 3.70E-02 0.00E-01 TOTAL FOR PERIOD CI 0.00E-01 0.00E-01 1.81E+01 2.07E-01
- 2. IODINES I-131 CI 2.55E-06 0.00E-01 0.00E-01 0.00E-M TOTAL FOR PERIOD CI 2.55E-06 0.00E-01 0.00E-01 0.00E-01
- 3. PARTICULATES l H-3 CI 2.91Et00 2.76E+00 1.47E-01 5.80E-04 TOTAL FOR PERIOD CI 2.91E+00 2.76E+00 1.47E-01 5.80E-04 l
l O l
. Page 9 l TABLE 2A i
\~ /
) i 1 I EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1985) l I LIQUID EFFLUENTS - SUMMATION OF ALL RELEASES I I I UNIT 3RD 4TH EST. TOTAL QUARTER QUARTER ERROR, %
A. FISSION 1 ACTIVATION PRODUCTS
- 1. TOTAL RELEASE (WITHOUT TRITIUM, GASES, ALPHA) CI 1.72E-02 8.53E-03 2.00E+01
- 2. AVERAGE DILUTED CONCEN-TRATION DURING PERIOD UCI/ML 2.64E-09 1.41E-09
- 3. PERCENT OF TECHNICAL SPEC. LIMIT, (RETS) See Sect 7, SuPP Information
- 4. PERCENT OF 10 CFR 20 LIMIT % 1 28E-02 2.87E-03 B. TRITIUM
- 1. TOTAL RELEASE CI 5 88E+00 2.02E+01 2.00E+01 0, 2. AVERAGE DILUTED CONCEN-TRATION DURING PERIOD
- 3. PERCENT OF 10 CFR 20 UCI/ML 9.01E-07 3.34E-06 LIMIT % 3.00E-02 1.11E-01 C. DISSOLVED 1 ENTRAINED GASES
- 1. TOTAL RELEASE CI 0.00E-01 0.00E-01 2.00E+01
- 2. AVERAGE DILUTED CONCEN-TRATION DURING PERIOD UCI/ML 0.00E-01 0.0.0E-01
- 3. PERCENT OF 2 E-4 UCI/CC LIMIT % 0.00E-01 0.00E-01 D. GROSS ALPHA RADI0 ACTIVITY
- 1. TOTAL RELEASE CI 0.00E-01 0.00E-01 2.00E+01 E. VOLUME OF WASTE RELEASED (PRIOR TO DILUTION) LITERS 3.33E+05 6.85E+05 2.00Et01 F. VOLUME OF DILUTION WATER
- 1. TOTAL RELEASE LITERS 6.53E+09 6.04E+09 2.00E+01
. Page 10 l TABLE 2B l l l 1 EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (1985) i I LIQUID EFFLUENTS I I I CONTINUOUS MODE
- BATCH NODE NyCLIDES RELEASED UNIT 3RD 4TH 3RD 4TH QUARTER QUARTER QUARTER QUARTER MN-54 CI 0.00E-01 2.12E-05 FE-55 CI 2.59E-03 4.73E-03 FE-59 CI 7.03E-06 5.35E-06 CO-58 CI 1.66E-03 4.82E-04 CO-60 CI 3.29E-04 1.33E-03 AG110M CI 4.17E-05 4.80E-05 SB-125 CI 6.10E-05 8.70E-05 CS-134 CI 2.85E-03 3 85E-04 CS-137 CI 9.66E-03 1.44E-03 CE-141 CI 0.00E-01 9.06E-07 O
TOTAL FOR PERIOD ABOVE CI 1.72E-02 8.53E-03
- NOT APPLICABLES ALL RADI0 ACTIVE LIQUID EFFLUENTS ARE RELEASED BY BATCH MODE.
I 1 l 0
TABLE 3A Page 11 EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT (85-2) SOLID WASTE AND IRRADIATED FUEL SHIPMENTS O ( A. SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL. (Not irradiated fuel) l
- 1. TwPe of waste i Unit i 6-month i Est. Total I I Error, I I Period i % l l________________________________________l_______g___________l__ __________g I a.Seent resins, filter sludges, 1 3 I I I I evaporator bottoms, etc. I M I 3.50 E+1 I I I I Ci I 3.76 E+0 1 1.0 l l________________________________________l_______l___________l_______E+1 _____l l b.Drw compressible waste, contaminatedl 3 I I I I eouie, etc. I H I 5.00 E+1 1 1 1 1 Ci 1 5.70 E-1 1 1.0 E+1 l l________________________________________l_______l___________l____________l 1 c. Irradiated components, control 1 3 I I I I rods, etc. I M l . E I 1 l l Ci I . E I . E I g________________________________________l_______l___________l____________l I d.0ther (describe) Dewatered 1 3 I I I I primarw swstem cartridge filters I M i 4.19 E+0 l I I l Ci 1 5.20 E+1 1 1.0 E+1 I l________________________________________I_______I___________1____________I 2 Estimate of major nuclide composition (bw twee of waste)
~~~ ~~~ " ~ ~ ~~
- a. Co-58 l % I 3 90 EII l f~s __________________________________i_______i___________i
( Co-60 1 % ' 2.10 E+1 1 __________________________________l_______t___________l Ni-63 I % i 2.10 E+1 1 __________________________________g_______g___________l
- b. Cs-137 I % I 4.60 E+1 1
__________________________________l_______l___________l Co-60 1 % 1 1.60 E+1 1 __________________________________l_______l___________l Cs-134 1 % i 1.80 E+1 1 __________________________________l_______g___________i
- c. N/A I % i . E I
__________________________________l_______l___________g
- d. Ni-63 1 % 1 6.40 E+1 1
__________________________________l_______l___________l Co-60 1 % 1 3.20 E+1 1 __________________________________l_______l___________l Cs-137 1 % i 1.00 Et0 1 __________________________________l ______I___________I
- 3. Solid Waste Disposition i
Number of Shipments Mode of Transportation Destination 11 ' Exclusive Use' Truck Barnwell Waste Msat Fac1. Barnwell, S.C. 29812 l B. IRRADIATED FUEL SHIPMENTS (Disposition) Number of Shipments Mode of Transportation Destination None N/A N/A L
. Table 1 Page 12 SEMIANNUAL MAXIMUM INDIVIDUAL DOSE TABLE (GASEOUS)
. JULY 1, 1985 THROUGH DEC. 31,1985 DOSE DUE TO RELEASE OF NOBLE GAS WHOLE BODY DOSE (MREM)
CRITICAL CRITICAL CRITICAL CRITICAL CRITICAL SECTOR DISTANCE AGE ORGAN DOSE THIRD QUARTER N 980.(M) NA W BODY 6.55E-07 FOURTH QUARTER H 0.(M) NA W BODY 0.00E-01 SEMIANNUAL TOTAL N 980.(M) NA W BODY 6.55E-07 SKIN DOSES (MREM) CRITICAL CRITICAL CRITICAL CRITICAL CRITICAL SECTOR DISTANCE AGE ORGAN DOSE THIRD QUARTER H 980.(M) NA SKIN 1.84E-06 FOURTH QUARTER N 0.(M) NA SKIN 0.00E-01 SEMIANNUAL TOTAL N 980.(M) NA SKIN 1.84E-06 O
Table 2 Page 13 SEMIANNUAL MAXIMUM INDIVIDUAL DOSE TABLE (GASEOUS) JULY 1, 1985 THROUGH DEC. 31,1985 DOSE DUE TO I-131e H-3, AND PARTICULATES WITH HALFLIVES > 8 DAYS WHOLE BODY DOSE (MREM) CRITICAL CRITICAL CRITICAL CRITICAL CRITICAL SECTOR DISTANCE AGE ORGAN DOSE THIRD QUARTER NNE 990.(M) CHILD W BODY 1.17E-03 FOURTH QUARTER NNE 990.(M) CHILD W BODY 9.50E-04 SEMIANNUAL TOTAL NNE 990.(M) CHILD W BODY 2.12E-03 f SIGNIFICANT ORGAN DOSES (MREM) O( ,/ CRITICAL CRITICAL CRITICAL CRITICAL CRITICAL SECTOR DISTANCE AGE ORGAN DOSE THIRD QUARTER NNE 990.(M) CHILD THYROID 1.54E-03 FOURTH QUARTER NNE 990.(M) CHILD THYROID 9.50E-04 SEMIANNUAL TOTAL NNE 990.(M) CHILD THYROID 2 49E-03 i N 1
Table 3 Page la SEMIANNUAL POPULATION DOSE TABLE (OASEOUS) JULY 1, 198E THROUGH DEO. 31,1985 DOSE DUE TO RELEASE OF NOBLE OAS l TOTAL INiEGRATED AVERAGE DOSE TO INDIVIDUALS POPULATION DOSE (MANREM) IN POPULATION (MREM) WHOLE BODY WHOLE BODY THIRD QUARTER 6.53E-04 2.93E-07 FOURTH QUARTER 6.36E-08 2.86E-11 SEMIANNUAL TOTAL 6.53E-04 2.93E-07 i O l l l l 1 0
Table 4 Page 15 SEMIANNUAL POPULATION DOSE TABLE (GASEOUS) JULY 1, 1985 THROUGH DEC. 31,1985 DOSE DUE TO I-131, H-3, AND PARTICULATES WITH HALFLIVES > 8 DAYS TOTAL INTEGRATED AVERAGE DOSE TO INDIVIDUALS POPULATION DOSE (MANREM) IN POPULATION (MREM) WHOLE BODY WHOLE BODY THIRD QUARTER 9.86E-04 4.43E-07 FOURTH QUARTER 8.04E-04 3.61E-07 SEMIANNUAL TOTAL 1.79E-03 8 04E-07 O i i I O
, Table 5 Page 16 SEMIANNUAL POPULATION DOSE TABLE (LIQUID)
JULY 1, 1985 THROUGH DEC. 31,1985 TOTAL INTEGRATED AVERAGE DOSE TO INDIVIDUALS POPULATION DOSE (MANREM) IN POPULATION (MREM) WHOLE BODY WHOLE BODY THIRD QUARTER 5.05E-01 2.27E-04 FOURTH QUARTER 1.30E-01 5.84E-05 SEMIANNUAL TOTAL 6.35E-01 2.85E-04 O O
Table 6 Page 17 SEMIANNUAL MAXIMUM INDIVIDUAL DOSE TABLE (LIQUID) I JULY 1, 1985 THROUGH DEC. 31,1985 CRITICAL RECEPTOR : 0.4 MILES NW OF DISCHARGE WHOLE BODY DOSES (MREM) SIGNIFICANT ORGAN DOSES (MREM) CRITICAL CRITICAL CRITICAL CRITICAL CRITICAL AGE DOSE AGE ORGAN DOSE THIRD QUARTER ADULT 1.50E-01 TEEN LIVER 2.20E-01 1 FOURTH QUARTER ADULT 1.48E-02 TEEN LIVER 2.14E-02 i SEMIANNUAL TOTAL ADULT 1.65E-01 TEEN LIVER 2.42E-01 O l l O
, CONTINUOUS RELEASES Page 18 Table 7 O
DAVI S - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/85 TO 9/30/85 l STABILITY CLASS: A ELEVATION: 35 FEET WIND- WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O O 0 0 0 0 0 ENE O O O O O O O E O O 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE O 0 0 0 0 0 0 SSE o 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 1 0 0 0 1 l SW 0 0 0 0 0 0 0 WSW 3 0 0 0 0 0 0 l W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 TOTAL 0 0 1 0 0 0 1 PERIODS OF CALM (HOURS): 0
-- -+ - -- --- -
CONTINUOUS RELEASES Page 19 Table 7 Continued O DAV IS - BESSE UN IT 1 JOINT FREGUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/85 TO 9/30/85 STABILITY CLASS: B ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O 4 0 0 0 0 4 NNE 0 0 0 0 0 0 0 NE O O 0 1 0 0 1 ENE 0 0 7 1 0 0 8 E 0 0 9 0 0 0 9 ESE O O O O O O O SE O 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 1 0 0 0 1 SSW 0 0 3 1 0 0 4 SW 0 0 1 1 0 0 2 WSW 0 0 1 1 0 0 2 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW- 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 TOTAL 0 4 22 5 0 0 31 PERIODS OF CALM (HOURS)! 0
CONTINUOUS RELEASES
. Page 20 Table 7 Continued O
DAVIS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/85 TO 9/30/85 STABILITY CLASS: C l ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5- , 3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 1 2 0 0 3 l NNE O 3 3 0 0 0 6 NE O 2 5 6 0 0 13 ENE 0 2 20 0 0 0 22 E O 10 4 1 0 0 17 ESE O 1 0 0 0 0 1 l SE O O O 0 0 0 0 l SSE O 1 0 0 0 0 1 S 0 3 3 0 0 0 6 SSW 0 3 17 1 0 0 21 l SW 0 2 13 2 0 0 17 WSW 0 2 7 6 0 0 15 W 0 0 0 1 0 0 1 WNW 0 0 1 0 0 0 1 NW 0 1 0 0 0 0 1 NNW 0 1 4 1 0 0 6 VARIABLE O O O 0 0 0 0 TOTAL 0 31 80 20 0 0 131 PERIODS OF CALM (HOURS): 0 l
CONTINUOUS RELEASES Page 21 Table 7 Continued O DAV IS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/85 TO 9/30/85 STABILITY CLASS: D ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 19 37 12 0 0 69 NNE 2 26 38 32 4 0 102 NE O 20 51 68 10 0 149 ENE 0 30 49 6 0 0 85 E 2 36 26 2 0 0 66 ESE 2 26 8 3 0 0 39 SE 1 12 6 0 0 0 19 SSE 2 15 8 1 0 0 26 S 1 25 20 1 0 0 47 SSW 3 41 59 6 0 0 109 SW 0 32 67 20 0 0 119 WSW 1 13 59 27 2 0 102 W 2 5 20 19 0 0 46 WNW 0 7 9 2 0 0 18 i NW 1 9 9 3 0 0 22 NNW 0 9 20 3 0 0 32 , VARIABLE O 0 0 0 0 0 0 TOTAL 18 325 486 205 16 0 1050 O PERIODS OF CALM (HOURS): 0 l t
CONTINUOUS RELEASES Page 22 Table 7 Continued O DAVI S - BESSE UN I T 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD 7/01/85 TO 9/30/85 STABILITY CLASS: E ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18 5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 8 0 0 0 0 0 8 NNE 1 2 0 2 0 0 5 NE 1 2 1 0 0 0 4 ENE 1 5 17 1 0 0 24 E 3 11 8 2 0 0 24 ESE 1 14 8 2 0 0 25 SE 8 39 5 0 0 0 52 SSE 12 39 1 0 0 0 52 S 16 37 6 0 0 0 59 SSW 4 66 42 4 0 0 116 SW 5 53 26 5 0 0 89 WSW 2 27 20 2 3 0 54 W 4 34 22 0 0 0 60 WNW 1 5 14 0 0 0 20 NW 0 5 5 0 0 0 10 NNW 1 6 4 1 0 0 12 VARIABLE 0 0 0 0 0 0 0 TOTAL 68 345 179 19 3 0 614 ) PERIODS OF CALM (HOURS)! O
CONTINUOUS RELEASES Page 23 l Table 7 Continued O DAV IS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATHOSPNERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/85 TO 9/30/85 STABILITY CLASS: F ELEVATION: 35 FEET WIND WIND SPEED (HPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 3 0 0 0 0 0 3 NNE O 0 0 0 0 0 0 NE O O O 0 0 0 0 ENE O O O 0 0 0 0 E O 2 0 0 0 0 2 O ESE O 2 0 0 0 0 2 SE 2 1 0 0 0 0 3 SSE 13 31 0 0 0 0 44 S 28 28 0 0 0 0 56 SSW 10 35 1 0 0 0 46 SW 9 48 2 0 0 0 59 .: I WSW 6 11 0 0 0 0 17 j W 3 15 1 0 0 0 19 WNW 0 3 0 1 0 0 4 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 74 176 4 1 0 0 255 PERIODS OF CALM (HOURS): 0
. CONTINUOUS RELEASES Page 24 Table 7 Continued O DAVIS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORDI 7/01/85 TO 9/30/85 STABILITY CLASS: G ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 0 0 0 0 0 1 NNE O O O 0 0 0 0 NE O O O O 0 0 0 ENE O 0 1 0 0 0 1 E O O 1 0 0 0 1 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 4 3 0 0 0 0 7 S 8 17 0 0 0 0 25 SSW 1 31 2 0 1 0 35 SW 3 7 3 4 0 0 17 WSW 3 7 1 0 0 0 11 W 1 6 1 0 0 0 8 WNW 0 3 0 0 0 0 3 NW 0 0 0 0 0 0 0 NNW 0 0 2 0 0 0 2 VARIABLE 0 0 0 0 0 0 0 TOTAL 21 74 11 4 1 0 111 PERIODS OF CALM (HOURS)! O
i
, CONTINUOUS REI. EASES Page 25 Table 7 Continued 1 O
DAVIS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/95 TO 9/30/85 STABILITY CLASS: TOTAL ELEVATION: 35 FEET ! WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18 5- , 3.4 7.4 12.4 10.4 24.4 >24.4 TOTAL i-N 13 23 38 14 0 0 88 , NNE 3 31 41 34 4 0 113 . NE 1 24 57 75 10 0 167 ENE 1 37 94 8 0 0 140 5 59 50 5 0 0 119 O E ESE 3 43 16 5 0 0 67 SE 11 52 11 0 0 0 74 SSE 31 89 9 1 0 0 130 I S 53 110 30 1 0 0 194 SSW 18 176 125 12 1 0 332 SW 17 142 112 32 0 0 303 WSW 12 60 88 36 5 0 201 W 10 40 44 20 0 0 134 WNW 1 18 24 3 0 0 46 NW 1 15 14 3 0 0 33 l NNW 1 16 30 5 0 0 52 VARIABLE 0 0 0 0 0 0 0 TOTAL 181 955 783 254 20 0 2193 PERIODS OF CALM (HOURS): 0 HOURS OF MISSING DATA: 15
COMTINCOUS RELEASES Page 26 Table 8 O DAV IS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/01/85 TO 9/30/85 STABILITY CLASS: A ELEVATIONt 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O O O 0 0 0 NE O O O O O O O ENE 0 0 0 0 0 0 0 E O O O O O O O ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 1 0 1 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 1 0 1 PERIODS OF CALM (HOURS)! 0 l
CONTISTOUS RELEASES Page 27 Table 8 Continued DAVIS - BESSE UNI T 1 i JOINT FREQUENCY DISTRIBUTION ] WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD! 7/01/85 TO 9/30/85 STABILITY CLASS: B ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 74 12.4 18.4 i 24 4 >24.4 TOTAL N 0 4 0 0 0 0 4 NNE O O O O O O O NE O O O i O O O O ENE 0 0 1 4 0 0 5 E 0 0 6 7 0 0 13 4 O ESE SE 0 O 0 0 0 0 0 0 0 0 0 0 0 0 SSE O O O O O O O i S 0 0 0 1 0 0 1 SSW 0 0 3 0 1 0 4 SW 0 0 0 1 0 0 1 WSW 0 0 0 3 0 0 3 ! W 0 0 0 0 0 0 0
- WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 i TOTAL 0 4 10 16 1 0 31
! O PERIODS OF CALM (HOURS)! 0 l
1 CONTINUOUS RELEASES Page 28 Table 8 Continued O DAVI S - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORDt 7/01/85 TO 9/30/85 STABILITY CLASSt C ELEVATI0H 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 35- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O O 0 3 0 0 3 NNE 0 2 3 0 0 0 5 NE O 3 2 3 2 0 10 ENE 0 2 14 9 0 0 25 E 0 5 11 1 0 0 17 ESE O 2 0 0 0 0 2 SE O 0 0 0 0 0 0 SSE O 1 0 0 0 0 1 S 0 0 1 1 1 2 5 SSW 0 4 2 14 2 0 22 SW 0 0 10 5 1 0 16 WSW 0 0 4 8 1 0 13 W 0 0 1 2 2 0 5 WNW 0 1 0 0 0 0 1 NW 0 1 0 0 0 0 1 NNW 0 0 4 1 0 0 5 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 21 52 47 9 2 131 PERIODS OF CALM (HOURS)! 0 I
, CONTINUOUS RELEASES Page 29 Table 8 Continued O
DAVIS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TENPERATURE (250FT-35FT) PERIOD OF RECORD! 7/01/85 TO 9/30/85 STABILITY CLASSt D ELEVATION! 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12 4 18.4 24 4 >24.4 TOTAL N 0 13 29 30 1 0 73 NNE 2 20 32 24 13 0 .91 NE O 21 35 40 44 3 143 ENE 0 12 48 29 9 1 99 E 1 17 20 16 4 0 58 ESE 1 17 23 4 1 2 50 SE 1 5 7 5 0 0 18 SSE 1 5 9 6 1 0 22 S 1 3 21 23 9 2 59 SSW 1 8 32 33 19 0 93 SW 0 11 24 49 18 0 102 WSW 2 6 34 51 23 2 118 W 1 4 12 20 12 0 49 WNW 0 3 6 7 5 0 21 NW 0 8 10 9 0 0 27 NNW 1 3 13 7 1 0 25 VARIABLE 0 0 0 0 0 0 0 TOTAL 12 156 355 355 160 10 1048 PERIODS OF CALM (HOURS)! O
CONT 1NU0CS RELEASES Page 30 Table 8 Continued O DAVIS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPNERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD 3 7/01/85 TO 9/30/85 STABILITY CLASSI E ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 4 4 0 1 0 9 HNE O 3 0 1 1 0 5 NE 1 3 2 2 0 0 8 ENE 1 1 3 16 1 0 22 E 0 6 7 6 0 2 21 ESE 2 5 15 18 1 1 42 SE O 8 17 24 0 0 49 SSE O 8 9 13 0 0 30 S 0 1 15 36 15 1 68 SSW 0 1 13 53 12 4 83 SW 0 3 17 55 18 0 93 WSW 0 8 21 36 2 3 70 W 0 3 16 30 3 0 52 WNW 1 3 11 14 7 0 36 NW 0 2 5 8 1 0 16 NNW 0 1 3 5 0 0 9 VARIABLE 1 0 0 0 0 0 1 TOTAL 6 60 150 317 62 11 614
}
PERIODS OF CALM (HOURS)! 0
. CONTINUOUS RELEASES page 31 Table 8 Continued O
DAVIS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPNERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD! 7/01/85 TO 9/30/85 STABILITY CLASS! F ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 1 1 0 0 0 3 NNE 0 0 0 0 0 0 0 NE O 1 0 0 0 0 1 ENE O O 1 0 0 0 1 E O 1 1 0 0 0 2 ESE 0 3 2 0 0 0 5 SE 2 10 5 0 0 0 17 SSE O 2 11 10 2 0 25 S 0 4 4 29 14 0 51 SSW 0 2 5 27 6 0 40 SW 0 2 4 25 2 0 33 WSW 2 2 7 22 0 0 33 W 0 1 7 12 0 0 20 WNW 0 2 2 6 2 0 12 NW 0 2 3 4 0 0 9 NNW 0 1 1 0 0 0 2 VARIABLE 1 0 0 0 0 0 1 ( TOTAL 6 34 54 135 26 0 255 PERIODS OF CALM (HOURS)! 0
)
l CONTINUOUS RELEASES Page 32 Table 8 Continued O DAVIS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS
- . 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) l PERIOD OF RECORD
- 7/01/85 TO 9/30/85 STABILITY CLASS! G ELEVATION! 250 FEET WIND WIND SPEED (MPH)
DIRECTION 0.7- 35- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 1 1 0 0 0 2 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 l ENE 0 0 1 0 0 0 1 i E 0 0 0 1 0 0 1 ESE O O O O O O O l SE O 4 3 0 0 0 7 SSE O 3 0 5 0 0 8 S 0 1 2 6 0 0 9 SSW 0 0 2 21 0 0 31 SW 0 0 1 18 3 1 23 - WSW 0 0 1 5 0 0 6 i W 0 0 1 2 1 0 4 WNW 0 3 1 1 0 0 5 NW 0 5 1 4 0 0 10 j NNW 0 0 4 0 0 0 4 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 17 18 63 12 1 111 l PERIODS OF CALM (HOURS)! O l
CONTINUOUS REI. EASES Page 33 Table 8 Continued O DAVIS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STACILITY CLASS 4 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORDI 7/01/85 TO 9/30/85 STABILITY CLASSt TOTAL ELEVATION! 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18 5-3.4 7.4 12 4 18.4 24.4 >24.4 TOTAL , N 1 23 35 33 2 0 94 NNE 2 25 35 25 14 0 101 NE 1 28 39 45 46 3 162 ENE 1 15 48 58 10 1 153 E 1 29 45 31 4 2 112 ESE 3 27 40 24 2 3 99 SE 3 27 32 29 0 0 91 SSE 1 19 29 34 3 0 86 S 1 9 43 96 39 5 193 , SSW 1 15 57 148 49 4 274 SW 0 16 56 153 42 1 268 ,, WSW 4 16 47 125 26 5 243 W 1 8 37 66 18 0 130 WNW 1 12 20 28 14 0 75 1 NW 0 18 19 25 1 0 63 l NNW 1 5 25 13 1 0 45 VARIABLE 2 0 0 0 0 0 2 TOTAL 24 292 647 933 271 24 2191 PERIODS OF CALM (il0URS ) ! O HOURS OF MISSING DATAt 17
CONTINUOUS RELEASES l Page 34 l Table 9 ' l DAVIS - BESSE UNI T 1 , JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS ' l 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD! 10/01/85 TO 12/31/85 STABILITY CLASS: A ELEVATION! 35 FEET WIND WIND SPEED (MPH) ! DIRECTION 0.7- 3.5- 7.5- 12.5- 18 5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 i E 0 0 0 0 0 0 0 ESE O 0 0 0 0 0 0 SE O 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 l l ! NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 I i TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS)! 0 l
CONTINUOUS RELEASES Page 35 Table 9 Continued
- O DAVIS -
BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE-(250FT-33FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: B ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0. 0 0 NE 0 0 0 2 0 0 2 ENE O 0 0 0 0 0 0 E 0 0 1 0 0 0 1 ESE O O 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 1 0 1 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 1 2 1 0 4 PERIODS OF CALM (HOURS): 0 l l
CONTINUOUS RELEASES Page 36 Table 9 Continued DAV IS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD! 10/01/85 TO 12/31/95 STABILITY CLASS! C ELEVATION! 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-34 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 O 1 0 0 0 1 NNE O 1 1 0 0 0 2 NE 0 0 0 3 0 0 3 ENE O 1 3 0 0 0 4 E O 0 3 2 0 0 5 ESE O 0 1 0 0 0 1 SE 0 0 0 0 0 0 0 SSE O 1 0 0 0 0 1 S 0 0 0 0 0 0 0 SSW 0 0 3 4 0 0 7 SW 0 0 0 1 0 0 1 WSW 0 0 6 3 2 1 12 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 1 0 0 0 0 1 NNW 0 0 2 0 0 0 2 VARIABLE C 0 0 0 0 0 0 TOTAL 0 4 20 13 2 1 40 PERIODS OF CALM (HOURS)! O
, CONTINUOUS RELEASES Page 37 Table 9 Continued DAVIS -
BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD! 10/01/85 TO 12/31/85 STABILITY CLASS: D ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3 5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 3 17 11 12 7 51 NNE 1 10 15 31 10 0 67 NE 1 11 37 60 27 1 137 ENE O 14 12 35 16 0 77 E 1 13 34 39 5 0 92 ESE 4 18 26 14 0 0 62 SE 6 15 7 7 1 1 37 SSE 10 17 1 1 0 0 29 S 4 14 8 15 0 0 41 SSW 6 14 48 40 3 0 ill SW 2 13 45 80 37 12 189 WSW 0 17 74 47 48 18 224 W 0 19 35 23 7 0 84 WNW 1 11 16 27 2 0 57 NW 3 5 37 14 2 0 61 NNW 2 8 36 20 6 0 72 VARIABLE O 0 0 0 0 0 0 TOTAL 42 202 448 484 174 39 1391 PERIODS OF CALM (HOURS): 0
CONTINUOUS RELEASES Page 38 Table 9 Continued DAVIS - BESSE UN I T 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: E ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 4 2 0 0 0 6 NNE O 1 0 0 0 0 1 NE 1 0 1 0 0 0 2 ENE O 5 4 0 0 0 9 E 3 20 7 8 0 0 38 ESE 4 17 12 14 0 0 47 SE 6 15 6 0 0 0 27 SSE 9 21 5 0 0 0 35 S 4 23 13 9 1 0 50 SSW 8 36 50 11 5 0 110 SW 2 29 53' 10 3 0 97 i WSW 5 23 44 8 1 0 81 W 0 6 18 3 1 0 28 WNW 1 4 4 0 0 0 9 l NW 1 2 5 1 0 0 9 ) NNW 0 5 4 0 0 0 9 VARIABLE 0 0 0 0 0 0 0 TOTAL 44 211 228 64 11 0 358 PERIODS OF CALM (NOURS): 0
CONTINUOUS RELEASES Page 39 Table 9 Continued < DAVIS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASSt F ELEVATION: 35 FEET WIND WIND SPEED (NPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 7.4- 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O 0 0 0 0 0 0 E 2 1 0 0 0 0 3 ESE 3 2 0 0 0 0 5 SE 4 8 2 0 1 0 15 SSE 10 14 0 0 0 0 24 S 7 13 1 0 0 0 21 SSW 1 20 1 0 0 0 22 SW 0 14 4 0 0 0 18 WSW 1 5 0 0 0 0 6 W 0 6 3 0 0 0 9 WNW 0 0 2 0 0 0 2 NW 1 0 1 0 0 0 2 NNW 0 0 0 0 0 0 0 1 VARIABLE 0 0 0 0 0 0 0 TOTAL 29 83 14 0 1 0 127 PERIODS OF CALM (HOURS): 0
i l CONIDCOUS RELEASES Page 40 Table 9 Continued 1 DAV IS - BESSE
- UN IT 1 l
l JOINT FREQUENCY DISTRIBUTION I WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS! G ELEVATION! 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O O O 0 0 0 0 l ENE 0 0 0 0 0 0 0 E 1 0 0 0 0 0 1 ESE O 1 0 0 0 0 1 SE O O 0 0 0 0 0 SSE 1 2 1 0 0 0 4 S 0 0 0 0 0 0 0 ( SSW 0 11 0 0 0 0 11 SW 0 4 0 0 0 0 4 WSW 0 0 0 0 0 0 0 W 0 1 0 0 0 0 1 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 2 19 1 0 0 0 22 PERIODS OF CALM (HOURS): 0 l
CONTINUOUS RELEASES Page 41 Table 9 Continued DAVIS - BESSE l UN IT 1 l JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/95 TO 12/31/95 STABILITY CLASS: TOTAL ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7 5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 7 20 11 12 7 58 NNE 1 12 16 31 10 0 70 NE 2 11 38 65 27 1 144 ENE O 20 19 35 16 0 90 E 7 34 45 47 5 0 140 ESE 11 38 39 28 0 o 116 SE 16 38 15 7 2 1 79 SSE 30 55 7 1 0 0 93 S 15 50 22 24 1 0 112 l SSW 15 81 102 55 8 0 261 3W 4 60 102 91 40 12 309 WSW 4 45 124 78 51 19 323 W 0 32 56 26 8 0 122 WNW 2 15 22 27 3 0 69 NW 5 8 43 15 2 0 73 NNW 2 13 42 20 6 0 83 VARIABLE O O 0 0 0 0 0 TOTAL 117 519 712 563 191 40 2142 PERIODS OF CALM (HOURS): 0 HOURS OF MISSING DATA: 66
CONTINU0US RELEASES Page 42 Table 10 DAV IS - BESSE UN I T 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) , PERIOD OF RECORDI 10/01/85 TO 12/31/85 STABILITY CLASS: A ELEVATION! 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O 0 0 0 0 0 0 NE O 0 0 0 0 0 0 ENE O 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 I S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 - W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O 0 0 TOTAL 0 0 0 0 0 0 0 PERICDS OF CALM (HOURS): 0 l
CONTINUOUS RELEASES Page 43 Table 10 Continued O I DAVIS - BESSE UN IT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: B ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 1 1 0 2 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE O 0 1 0 0 0 1 SE O O O O O 0 0 SSE O O O 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 l WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 1 1 l NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 1 1 1 1 4 PERIODS OF CALM (HOURS): 0
CONTINUOUS RELEASES Page 44 Table 10 Continued DAV IS - BESSE UN I T 1 JOINT FREQUENCY DISTRIBUTION WIhD SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: C ELEVATIOPt 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 1 0 0 0 1 NNE O 1 1 0 0 0 2 NE 0 0 0 0 2 0 2 ENE O O 3 2 0 0 5 E O 0 2 0 2 0 4 ESE 0 0 2 0 0 0 2 SE 0 0 0 0 0 0 0 SSE 0 0 1 0 0 0 1 S 0 0 0 0 0 0 0 SSW 0 0 0 3 3 0 6 SW 0 0 0 2 0 0 2 WSW 0 0 0 6 1 1 8 W 0 0 0 1 2 1 4 WNW 0 0 0 0 0 0 0 NW 0 1 0 0 0 0 1 NNW 0 0 2 0 0 0 2 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 2 12 14 10 2 40 PERIODS OF CALM (HOURS): 0 lh
I CONTINUOUS RELEASES Page 45 Table 10 Continued O DAVI S UN I T BESSE 1 l JOINT FREQUENCY DISTRIBUTION l WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/95 TO 12/31/85 STABILITY '. LASS: D ELEVATI0hi 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.s-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 4 12 9 10 23 59 NNE 1 6 8 21 10 7 53 NE 2 8 27 50 42 5 134 ENE O 6 11 15 33 21 86 E 2 7 10 15 37 22 93 ESE 1 5 13 25 21 3 68 SE 3 13 6 5 9 0 36 SSE 5 4 14 1 1 1 26 S 3 7 9 9 8 9 45 SSW 0 5 12 25 23 14 79 SW 0 7 6 53 38 23 127 WSW 1 5 17 71 81 80 255 W 1 8 17 43 28 17 114 WNW 1 4 27 21 18 5 76 NW 1 2 19 18 11 3 54 NNW 1 5 18 37 16 1 78 VARIABLE 0 0 0 0 0 0 0 TOTAL 23 96 226 418 386 234 1383 PERIODS OF CALM (HOURS): 0
C0h7INUOUS REL USES Page 46 Table 10 Continued DAVIS - BESSE UN I T 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: E ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 3 4 1 0 8 NNE 0 0 1 0 0 0 1 NE 0 1 1 0 0 0 2 ENE O 1 1 2 0 0 4 l E O 3 15 6 3 4 31 ESE 1 3 13 9 8 13 47 SE 1 6 6 8 2 1 24 SSE 1 1 10 9 2 0 23 S 1 2 7 23 14 6 53 SSW 1 5 9 29 31 14 89 SW 1 2 13 43 27 4 90 i WSW 0 4 16 50 17 3 90 W 0 2 8 27 6 1 44 WNW 0 2 6 13 3 0 24 NW 0 1 2 6 3 0 12 NNW 0 1 2 5 0 0 8 VARIABLE O 0 0 0 0 0 0 TOTAL 6 34 113 234 117 46 550 PERIODS OF CALM (HOURS): 0 0
CONTINUOUS RELEASES Page 47 Table 10 Continued O DAV IS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD! 10/01/85 TO 12/31/85 STABILITY CLASSt F ELEVATION! 250 FEET i WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O 0 0 0 0 0 0 NE O 1 1 0 0 0 2 ENE 0 1 0 0 0 0 1 E 0 1 0 0 0 0 1 ESE 0 1 2 1 0 0 4 SE O 1 5 5 1 1 13 SSE 0 0 2 7 2 0 11 S 0 1 2 14 4 1 22 SSW 1 1 5 9 3 0 19 SW 0 1 2 12 11 0 26 WSW 0 0 0 2 4 0 6 W 0 0 2 5 0 0 7 WNW 0 0 2 5 0 0 7 NW 0 1 0 6 0 0 7 NNW 0 0 0 1 0 0 1 VARIABLE 0 0 0 0 0 0 0 TOTAL 1 9 23 67 25 2 127 PERIODS OF CALM (HOURS)! O
CONTINUOUS RELEASES Table 10 Continued DAVIS - BESSE UNIT 1 JOINT FREGUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: 0 ELEVATION! 250 FEET WIND WIND SPEED UAPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18 5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O O 0 0 0 0 0 NNE O O O O 1 0 1 NE O 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E O 1 0 0 0 0 1 ESE O O O 0 0 0 0 SE 0 0 0 1 0 0 1 SSE 0 0 0 0 0 0 0 S 0 0 1 0 0 0 1 SSW 0 0 1 4 2 0 7 SW 0 0 0 5 0 0 5 WSW 0 0 0 1 1 0 2 W 0 0 2 1 0 0 3 WNW 0 0 0 0 0 0 0 NW 0 0 0 1 0 0 1 l NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O 0 TOTAL 0 1 4 13 4 0 22 PERIODS OF CALM (HOURS): 0 h
CONTINUOUS RELEASES Page 49 Table 10 Continued DAV IS - BESSE UNIT 1 JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/01/85 TO 12/31/85 STABILITY CLASS: TOTAL ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTICN 0.7- 3 5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 1 4 16 13 11 23 68 NNE 1 7 10 21 11 7 57 NE 2 10 29 51 45 5 142 ENE 0 8 15 19 33 21 96 E 2 12 27 21 42 26 130 3 ESE 2 9 31 35 29 16 122 SE 4 20 17 19 12 2 74 SSE 6 5 27 17 5 1 61 S 4 10 19 46 26 16 121 SSW 2 11 27 70 62 28 200 SW 1 10 21 115 76 27 250 WSW 1 9 33 130 104 84 361 W 1 10 29 77 36 19 172 WNW 1 6 35 39 21 5 107 NW 1 5 21 31 14 4 76 NNW 1 6 22 43 16 1 89 VARIABLE 0 0 0 0 0 0 0 i TOTAL 30 142 379 747 543 285 2126 PERIODS OF CALM (HOURS): 0 HOURS OF MISSING DATA: 82
Table 11 Page 50 DAVIS O BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: A ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O 0 0 0 0 0 NE O 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE O 0 0 0 0 0 0 SE O O O O O O O SSE O 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 1 0 0 0 1 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 l WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O 0 0 0 0 0 TOTAL 0 o 1 0 0 0 1 PERIODS OF CALM (HOURS): 0 l 1
Table 11 Continued Page 51 DAV I S - BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASSt B ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3 5- 7.5- 12 5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O O 0 0 0 0 0 E O O 0 0 0 0 0 ESE O O O O 0 0 0 SE O O O 0 0 0 0 SSE O 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VAWIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS): 0
I Table 11 Continued Page 32 O' DAVIS - BESSE UN I T 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 vo 9/30/85 STABILITY CLASS: C ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O O 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O 0 0 0 0 0 0 ENE O O O 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 S S's 0 0 1 0 0 0 1 F,W 0 0 0 1 0 0 1 . WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 1 0 0 0 0 1 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 1 1 1 0 0 3 PERIODS OF CALM (HOURS): 0
Table 11 Continued Page 53 i I O , DAVIS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: D ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 1 0 0 0 0 1 NNE 0 3 0 0 0 0 3 NE 0 1 3 0 0 0 4 ENE 0 1 2 0 0 0 3 i E 0 1 0 0 0 0 1 ESE 0 0 0 0 0 0 0 SE 0 2 0 0 0 0 2 a SSE 0 1 1 0 0 0 2 S 0 0 0 0 0 0 0 SSW 0 3 9 1 0 0 13 SW 0 1 3 1 0 0 5 ( WSW 0 0 0 0 0 0 0 l W 0 0 1 0 0 0 1 l WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 2 0 0 0 0 2 VARIABLE 0 0 0 0 0 0 0 l TOTAL 0 16 19 2 0 0 37 PERIODS OF CALM (HOURS): 0 _ . _ . _ _ . . _ , _ . - . _ , ~..,....__-r _ _ , _ _ . _ , _ . , _ _ . . _ _ _ , . . , _ _ , _ , _ _ . - _
. Table 11 Continued Page 54 O DAV IS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: E ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O O O O O O 0 NNE 0 0 0 0 0 0 0 NE O 0 0 0 0 0 0 EHE 1 0 1 0 0 0 2 E O O O 0 0 0 0 ESE 1 0 0 0 0 0 1 SE 0 1 0 0 0 0 1 SSE 0 0 0 0 0 0 0 S 1 5 0 0 0 0 6 SSW 0 6 8 0 0 0 14 SW 0 1 3 0 0 0 4 WSW 0 0 0 0 0 0 0 W 1 1 0 0 0 0 2 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 l VARIABLE O O O O O O O TOTAL 4 14 12 0 0 0 30 PERIODS OF CALM (HOURS): O l
i Table 11 Continued Page 55 O DAVIS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: F ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O O O 0 0 0 0 ENE O O O 0 0 0 0 0 E ESE 0 0 0 0 0 0 0 0 0 0 0 0 0 0 SE O 0 0 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 1 0 0 0 0 1 SW 0 0 1 0 0 0 1 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 i NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 1 1 0 0 0 2 PERIODS OF CALM (HOURS): 0
Table 11 Continued Page 56 O DAVIS - BESSE UN I T 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATHOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS! G ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7 5- 12.5- 19.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O O O O O O O E O O 0 0 0 0 0 ESE O O 0 0 0 0 0 SE O O O 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 1 2 0 1 0 4 SW 0 0 3 4 0 0 7 1 WSW 0 0 0 0 0 0 0 ) W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O l TOTAL 0 1 5 4 1 0 11 PERIODS OF CALM (HOURS)! O I
Table 11 Continued Page 57 O I DAVIS - BESSE ' UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS! TOTAL ELEVATION! 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 19.4 24 4 >24.4 TOTAL M 0 1 0 0 0 0 1 NNE O 3 0 0 0 0 3 NE 0 1 3 0 0 0 4 , ENE 1 1 3 0 0 0 5 E 0 1 0 0 0 0 1 f ESE 1 0 0 0 0 0 1 SE O 3 0 0 0 0 3 SSE O 1 1 0 0 0 2 4 S 1 5 0 0 0 0 6 SSW 0 11 21 1 1 0 34 SW 0 2 10 6 0 0 18 WSW 0 0 0 0 0 0 0 W 1 1 1 0 0 0 3 WNW 0 0 0 0 0 0 0 NW 0 1 0 0 0 0 1 NNW 0 2 0 0 0 0 2 VARIABLE 0 0 0 0 0 0 0 TOTAL 4 33 39 7 1 0 84 PERIODS OF CALM (HOURS)! O HOURS OF MISSING DATA: 3
Table 12 Page 58 O DAVIS - BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASSI A ELEVATION! 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ! ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O O O O O O 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 1 0 1 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 1 0 1 PERIODS OF CALM (HOURS)! 0
Table 12 Continued Page 39 O DAVIS - BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: B ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- /.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O O O O O O O t E 0 0 0 0 0 0 0 ESE O O O 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 t l NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 UARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS): 0
Table 12 Continued
. Page 60 DAVIS -
BESSE O UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: C ELEVATION: 250 FEET WIND DIRECTION 0.7- WIND SPEED (MPH) 3 5- 7.5- 12 5- 18 5- , 3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O 0 0 0 0 0 0 ENE O 0 0 0 0 0 0 E O O O O O O O ESE O O O 0 0 0 0 SE O 0 0 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 1 0 1 SW 0 0 0 0 1 0 1 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 1 0 0 0 0 1 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 1 0 0 2 0 3 PERIODS OF CALM (HOURS): 0
Table 12 Continued Page 61 O DAVIS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: D ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 1 0 0 0 0 1 NNE 0 1 0 0 0 0 1 NE 0 2 1 0 0 0 3 ENE O O 2 4 0 0 6 E 0 0 0 0 0 0 0 ESE 0 0 1 0 0 0 1 SE O 1 1 0 0 0 2 SSE 0 0 1 1 0 0 2 S 0 0 0 0 1 0 1 SSW 0 0 1 7 2 0 10 SW 0 0 2 4 1 0 7 WSW 0 0 0 0 0 0 0 W 0 0 0 1 0 0 1 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 2 0 0 0 0 2 VARIABLE O O O O O O O TOTAL 0 7 9 17 4 0 37 i PERIODS OF CALM (HOURS): 0 1
Table 12 Continued Page 62 DAV IS - BESSE O UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: E ELEVATION! 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 1 0 0 1 E O 1 0 0 0 0 1 ESE O 1 0 0 0 0 1 SE O 2 0 0 0 0 2 SSE O O O O O O O S 0 0 0 1 0 0 1 SSW 0 0 2 10 4 0 16 SW 0 0 2 3 1 0 6 WSW 0 0 0 0 0 0 0 W 0 1 1 0 0 0 2 WNW 0 0 0 0 0 0 0 i NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 5 5 15 5 0 30 PERIODS OF CALM (HOURS)* O I
Table 12 Continued Page 63 O DAVIS - BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: F ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O O O 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E O 0 0 0 0 0 0 O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 1 0 0 0 1 SW 0 0 0 0 1 0 1 . WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 l WNW 0 0 0 0 0 0 0 l NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 1 0 1 0 2 O PERIODS OF CALM (HOURS): 0 s l [
Table 12 Continued Page 64 O DAVIS - BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/85 STABILITY CLASS: G ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 19.4 24.4 >24.4 TOTAL l l N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O O O O O O O ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 1 1 1 0 3 l SW 0 0 1 3 3 1 8 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 2 4 4 1 11 PERIODS OF CALM (HOURS): 0
Table 12 Continued Page 65 O . DAV IS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 7/1/85 to 9/30/E5 STABILITY CLASS: TOTAL ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O 1 0 0 0 0 1 NNE 0 1 0 0 0 0 1 NE 0 2 1 0 0 0 3 ENE O O 2 5 0 0 7 E 0 1 0 0 0 0 1 , ESE O 1 1 0 0 0 2 SE 0 3 1 0 0 0 4 SSE 0 0 1 1 0 0 2 S 0 0 0 1 1 0 2 SSW 0 0 5 18 9 0 32 SW 0 0 5 10 7 1 23 WSW 0 0 0 0 0 0 0 W 0 1 1 1 0 0 3 WNW 0 0 0 0 0 0 0 NW 0 1 0 0 0 0 1 NNW 0 2 0 0 0 0 2 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 13 17 36 17 1 84 0 PERIODS OF CALM (HOURS): 0 HOURS OF MISSING DATA: 3
1 l Table 13 . Page 66 DAVIS - BESSE UN I T 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS: A ELEVATION: 35 FEET , WIND WIND SPEED (MPH) ! DIRECTION 0.7- 3 5- 7.5- 12 5- 18.5- 1 3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL l l N 0 0 0 0 0 0 0 ) NNE 0 0 0 0 0 0 0 l NE O 0 0 0 0 0 0 ENE O O 0 0 0 0 0 E O O 0 0 0 0 0 ESE O O 0 0 0 0 0 SE O O O O O 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS): 0
Page 67
- Table 13 Continued O DAVIS -
BESSE UNI T 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS B ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18 5-3.4 7.4 12.4 18 4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O O 0 0 0 0 NE O O 0 0 0 0 0 ENE O 0 0 0 0 0 0 E O O O O O O 0 ESE O O 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 ! W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS)! 0 [ ___ _. . _ - . _ - _ _ _ _ - - -
. Table 13 Continued Page 68 DAV IS - BESSE O UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS: C ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O O O O O O NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E O 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS): 0 -
, Table 13 Continued Page 69 O DAVIS -
BESSE UN I T 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASSt D ELEVATION! 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0
- NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE O O O O O O O SSE O 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 4 6 2 0 12 SW 0 0 3 11 0 0 14 WSW 0 0 2 5 0 0 7 W 0 0 1 0 0 0 1 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 10 22 2 0 34 PERIODS OF CALM (HOURS)1 0
Table 13 Continued Page 70 DAVIS - BESSE O UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF REC 0RD: 10/1/85 to 12/31/85 STABILITY CLASS: E l ELEVATION! 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 7.4 12 4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O 0 0 0 0 0 0 ENE O O O O O O O E O 0 0 0 0 0 0 ESE O 0 0 0 0 0 0 SE O O O 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 2 1 0 0 3 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 TOTAL 0 0 2 1 0 0 3 PERIODS OF CALM (HOURS)! 0
Table 13 Continued Page 71 l DAVIS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS: F ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL l 0 N 0 0 0 0 0 0 NNE O O 0 0 0 0 0 NE 0 0 0 0 0 0 0 i ENE O 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE O O O O 0 0 0 i SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 + SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 ! I W 0 0 0 0 0 0 0 l WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0
, NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS): 0
Table 13 continued Page 72 I DAyIg - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS! G ELEVATION! 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O O O O 0 0 NE O O O o 0 0 0 ENE O O 0 0 0 0 0 E O 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE O O O O O O O SSE O O O O 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS)! O h
Table 13 Continued Page 73 O DAVIS UN I T BESSE 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 35-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/11/85 STABILITY CLASS: TOTAL ELEVATION: 35 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 74 12.4 18 4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E O O O O O 0 0 ESE O O 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 i SSW 0 0 4 6 2 0 12 SW 0 0 5 12 0 0 17 WSW 0 0 2 5 0 0 7 W 0 0 1 0 0 0 1 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 12 23 2 0 37 PERIODS OF CALM (HOURS): 0 HOURS OF MISSING DATA: 0
~ _ . . . _ _ _ _ - . _ - . . _ _ _ _ . _ _ _ _ . _ _ _ _ _ _ . . . . . _ _ _ - - _ _ - . _ _ _ _ _ , . _ _ _ _ _ _ _ _ . _ . _ _ _ _ _ _ _ _ _ _ _
. Table 14 Page 74 DAV IS -
BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASSt A ELEVATIONt 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N O 0 0 0 0 0 0 NNE O 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 ( E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O O O O 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 l WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS)! 0 ll l
Table 14 Continued Page 75 O- DAVIS UNI T BESSE 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATh0 SPHERIC STABILITY 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OFCLASS: STABILITY RECORD: 10/1/85 to 12/31/85 B ' ELEVATION: 250 FEET WIND DIRECTION 0.7- WIND SPEED (MPH) 3.5- 7.5- 12.5-3.4 18.5-74 12.4 18 4 24 4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 ~ 0 0 NE 0 0 0 0 0 0 0 ENE O O O 0 0 0 0 E O O 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE O O O O O O O SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 l 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 i W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 0 i 0 0 PERIODS OF CALM (HOURS): 0 l O I
Table 14 Continued Page 76 DAVIS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS: C ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE O O O O O O O NE O O 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE O O O O O O O SE 0 0 0 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS): 0 h
-- . .= . _ ,
, Table 14 Continued Page 77 DAVIS -
BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASSI D ELEVATION 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE O O 0 0 0 0 0 ENE 0 0 0 0 0 0 0 , E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 3 4 7 SW 0 0 0 4 4 3 11 WSW 0 0 0 5 7 0 12 W 0 0 0 2 2 0 4 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 7 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 11 16 7 34 PERIODS OF CALM (HOURS)! O
. Table 14 Continued Page 78 DAVIS - BESSE UN IT a BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS: E ELEVATION! 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12 5- 18.5-3.4 7.4 12.4 18.4 24.4 >24 4 TOTAL N O O 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O O 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE O O O O O O 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 3 0 3 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 0 3 0 3 PERIODS OF CALM (HOURS)! 0
Table 14 Continued Page 79 DAV I S - BESSE UNIT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TENPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/21/85 STABILITY CLASS! F ELEVATION 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24 4 >24.4 TOTAL N 0 0 0 0 0 O 0 NNE O 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O O O O O 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O O O O 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 { SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 l l W 0 0 0 0 0 0 0 l l WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0
- TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS)! 0
Table 14 Continued Page 80 DAV IS - BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASS! G ELEVATION: 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3 5- 7.5- 12.5- 18 5-3.4 7.4 12.4 18.4 24 4 >24.4 TOTAL N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE O O O 0 0 0 0 E O O O 0 0 0 0 ESE O O 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 l l W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O 0 0 0 0 0 0 TOTAL 0 0 0 0 0 0 0 PERIODS OF CALM (HOURS)! 0
r--
, Table 14 Continued Page 81 i O DAVIS -
BESSE UN IT 1 BATCH RELEASE JOINT FREQUENCY DISTRIBUTION WIND SPEED AND DIRECTION BY ATMOSPHERIC STABILITY CLASS 250-FT WINDS AND DELTA TEMPERATURE (250FT-35FT) PERIOD OF RECORD: 10/1/85 to 12/31/85 STABILITY CLASSt TOTAL ELEVATIONt 250 FEET WIND WIND SPEED (MPH) DIRECTION 0.7- 3.5- 7.5- 12.5- 18.5-3.4 7.4 12.4 18.4 24.4 >24.4 TOTAL N 0 0' 0 0 0 0 0 NNE O O O O O O O NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 3 4 7 l SW 0 0 0 4 4 3 11 WSW 0 0 0 5 10 0 15 W 0 0 0 2 2 0 4 l ! WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 l NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0 TOTAL 0 0 0 11 19 7 37 PERIODS OF CALM (HOURS)! O HOURS OF MISSING DATAt 0
Page 92 TABLE 15 HOURLY METEOROLOGICAL DATA DURING BATCH RELEASES DAVIS-BESSE NUCLEAR POWER STATION JULY in 1985 - SEPTEMBER 30, 1985 35' WIND SPD 35' WIND T 250'-35' YR MONTH DAY HOUR (MPH) DIRECTION ( F) 85 7 1 1 10.7 69 -0.6 85 7 1 2 10 9 64 -0.7 85 7 1 3 9.6 59 -0.7 85 7 1 4 9.1 51 -0.8 85 7 1 5 8.2 54 -0.7 85 7 1 6 7.4 58 -0.8 85 7 1 7 7.1 51 -1.1 85 7 1 8 8.0 36 -1.3 85 7 1 9 6.0 33 -1.3 85 7 1 10 6.2 31 -1.3 85 7 1 11 4.0 17 -1.1 85 7 1 12 5.5 340 -1.3 85 7 1 13 4.9 326 -1.4 85 7 1 14 4.8 314 -1.9 85 7 1 15 6.5 353 -1. 85 7 1 16 6.7 94 -1 85 7 1 17 5.9 140 -0. 85 7 1 18 4.3 129 -0.3 85 7 1 19 3.6 114 -0.4 85 7 1 20 1.8 75 .2 85 7 1 21 4.4 133 -0.8 85 7 1 22 2.6 179 0.3 85 7 4 10 6.9 202 -1.7 85 7 4 11 8.6 219 -1.4 85 7 4 12 11.7 221 0.5 1 85 7 4 13 13.5 229 1.5 l 85 7 4 14 12.4 227 2.4 85 7 4 15 11.6 203 1.3
- 85 7 4 16 13.6 216 -0.3 85 7 4 17 13.9 214 3.2 l 85 7 4 18 13.6 216 2.3 85 7 4 19 10.5 204 0.2 85 7 4 20 10.4 200 -0.4 85 7 4 21 8.3 197 0.3 85 7 4 22 7.7 198 0.4 85 7 4 23 6.4 195 0.6 85 7 4 24 4.4 181 0.6 85 7 5 1 8.0 193 02 85 7 5 2 9.5 201 -0.4 85 7 5 3 7.6 194 -0.2 85 7 5 4 8.6 195 -0.
85 7 5 5 10.5 204 -0 85 7 5 6 10.4 224 -0
Page 83 TABLE 15 Continued HOURLY METE.OROLOGICAL DATA DURING BATCH RELEASES DAVIS-BESSE NUCLEAR POWER STATION JULY 1, 1985 - SEPTEMBER 30, 1985 35' WIND SPD 35' WIND T 250' - 35' YR MONTH DAY HOUR (MPH) DIRECTION ( F) 85 7 5 7 3.6 269 -0.2 85 7 5 8 4.0 198 -0.6 85 7 5 9 6.6 143 -1.4 85 7 5 10 8.9 162 -1.5 85 7 5 11 10.9 194 -1.7 85 7 5 12 15.1 212 -1 6 85 7 5 13 16.7 216 -1.8 85 7 5 14 **** *** **** 85 7 5 15 **** *** **** 85 7 5 16 8.9 318 -1.3 85 7 5 17 19.4 39 **** 85 7 5 18 **** *** **** 85 7 5 19 **** *** **** 85 7 5 20 **** *** **** 85 7 5 21 10.6 203 -2.5 85 7 5 22 10.5 207 -0.8 85 7 5 23 9.1 210 -1.0 7 5 24 200 0 85 85 7 6 1 7.1 6.3 215
-0.7
-0.7 85 8 6 9 11.8 197 -1.4 85 8 6 10 13.9 198 -1.7 85 8 6 11 12.9 200 -1.8 85 8 6 12 11.6 204 -1.3 85 8 6 13 9.8 206 -1.0 85 8 6 14 9.9 206 -1.2 85 8 6 15 11.2 210 -1.3 85 8 6 16 9.7 213 -1.3 85 8 6 17 7.2 212 -1.2 85 8 6 18 7.8 209 -1.1 *,
85 8 6 19 7.8 216 -0 6 85 8 6 20 11.8 220 -0.3
- 85 8 6 21 8.4 216 2.0 85 8 6 22 6.1 196 0.9
! 85 8 6 23 4.0 185 01 85 8 6 24 4.0 186 1.5 85 8 7 1 4.8 187 1.6 85 8 7 2 5.4 198 0.8 85 8 7 3 7.2 201 -0.1 85 8 7 4 6.0 222 0.0 85 8 7 5 5.6 202 -0.1 85 8 7 6 6.8 262 -0.1 85 9 28 17 10 1 249 -1.3 85 9 28 18 8.6 240 -0.7 85 9 28 19 6.5 236 06 v
*** Indicates unavailable data l
l
Paga 84 TABLE 16 1 HOURLY METEOROLOGICAL DATA DURING BATCH RELEASES DAVIS-BESSE NUCLEAR POWER STATION l OCTOBER 1e 1985 - DECEMBER 31, 1985 35' WIND SPD 35' WIND T 250'-35' YR MONTH DAY HOUR (MPH) DIRECTION ( F) 85 12 21 15 15.4 229 -1.4 85 12 21 16 15.4 232 -1.2 85 12 21 17 12.7 227 -0.9 85 12 21 18 11.6 225 -0.6 85 12 21 19 12.6 226 -0.5 85 12 21 20 12.3 224 -0.1 85 12 21 21 10.8 225 0.1 85 12 21 22 10.5 224 -0.7 85 12 21 23 12.6 226 -0.8 85 12 21 24 13.2 228 -0.8 85 12 22 1 12.1 218 -1.1 85 12 22 2 11.6 210 -1.0 85 12 22 3 12.3 209 -1.1 85 12 22 4 12.2 208 -1.1 85 12 22 5 12 4 198 -1.1 85 12 22 6 13.4 195 -1. 85 12 22 7 14.0 192 -1 85 12 22 8 15.2 196 -1 85 12 22 9 16.1 193 -1.0 85 12 22 10 18.0 194 -1.0 85 12 22 11 17.8 203 -1.0 85 12 22 12 20.0 210 -1.0 85 12 22 13 19.0 213 -1.0 85 12 22 14 17.7 217 -0.9 85 12 22 15 17.8 224 -0.9 85 12 22 16 16.6 226 -0.9 85 12 22 17 17.8 231 -0.9 85 12 22 18 15.4 226 -0.9 85 12 22 19 16.4 229 -0.8 85 12 22 20 17.2 237 -0.7 85 12 22 21 17.9 248 -0.8 85 12 22 22 13.5 253 -0.8 85 12 22 23 11.4 249 -0.8 85 12 22 24 11.9 252 -0.8 85 12 23 1 13.3 248 -0.8 85 12 23 2 13.6 252 -0.8 85 12 23 3 11.1 260 -0.8 O
3 I-i t . 4 , THE TOLEDO EDISON COMPANY t DAVIS-BESSE NUCLEAR POWER STATION OFFSITE DOSE CALCULATIONS MANUAL !
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, t i i ; Reviewed by i Revision No. Station Review Board Date ! l 1 S . u. Eb ? As s / 29/ s r , L r i. )- I f I
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\ t 4 I h r I 2 Attachnent 1
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i l 0FFSITE DOSE CALCUI.ATION MANUAL FOR DAVIS-BESSE NUCLEAR I%7.R STATION March 1984 , G l d i I f'-
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4 [V OFFSITE DOSE CALCULATION MANUAL TABLE OF CONTENTS Page INTRODUCTION . . . . . . . . . . . . . . .. .. . ..... ..y ;
; 1.0 LIQUID EFFLUENTS i 1.1 Liquid Effluent Monitor Setpoints .. ...... . 1.0-1 1.1.1 Liquid Radwaste Effluent Line Monitors . . 1.0-1 -
'1.1.2 Turbine Building (Floor Drains) Sump
, Effluent Line (Applicable Upon Completion
! of Modification) . . . . . . . . . . . . . 1.0-6 1.2 Dose Calculation for Liquid Effluents .. . ... . 1.0-10 l 1.3 Projected Personal Maximus Dose for Liquid Effluents. 1.0-12 1
, 1.4 References to 1.0 Liquid Effluents . . ..... . . . 1.0-13 2.0 GASEOUS EFFLUENTS 2.1 Gaseous Effluent Monitor Setpoints . . ...... . . 2.0-1 , 2.1.1 Station Vent Monitor . . . . . . . . . . . 2.0-1
'~~
{' 2.1.2 Waste Gas Decay System and Containment urge Monitors . .. . ... . . .... . . 2.0-3 l 2.2 Gaseous Effluent Dose Rate and Dose Calculations . . 2.0-5 t 2.2.1 Unrestricted Area Boundary Dose Rate . . . . 2.0-5 2.2.2 Unrestricted, Area Dose to Individual . . . 2.0-8
! 2.3 Projected Personal Maximus Dose for Gaseous Effluents. 2.0-11 2.4 Total Dose . . . . . . . . . . . . . . . . . . . . . 2.0-12 2.4.1 Compliance with 40CFR190 . . . . ... . . . 2.0-12 1 2.4.2 Calculations Evaluating Conformance with . 2.0-12 -
~
40CFR190 r 2.4.3 Calculation of the Total Body Dose. . . . . 2.0-12 2.4.4 Calculation of the Thyroid Dose . .. . . . 2.0-14 i t I DAVIS BESSE, UNIT 1 i i i c--- ,- - - - --..a.>._~.- -,, , --, - , , , . . . . . . , - , - - - - - . . - - - - - , - - - - - - , - - - - - . - - - -
, .. . . . . . . . - - -.. - ._. . - ~ . - - 9 0FFSITE DOSE CALCULATION MANUAL . (L) TABLE OF CONTENTS (Continued) Page 2.5 Meteorological Model . . . . . . . . . . . . . . . . 2.0-14 2.5.1 Long-Tern Atmospheric Dispersion . . . . . 2.0-14 2.5.2 Long-Tera Deposition . . . . . . . . . . . 2.0-18 2.5 Definitions of Gaseous Effluents Parameters . . . . 2.0-18 - 2.6 References to 2.0 Gaseous Effluents . . .. . . . . 2.0-24 3.0 RADIOLOGICAL ENVIRONMENTAL MONITORING 3.1 Land Use Census . . . . . . . . . . . . . . . . . . 3.0-1 3.2 Sample Analyses . . . .. . . . . . . . . . . . . . 3.0-2 4.0 REGULATORY GUIDE 1.21 - EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL REPORT 4.1 Technical Specification Limit Used for Gaseous Effluents. ................ .. . . . 4.0-1 1 ( 4.2 Technical Specification Limits Used for Liquid Effluents. . ........... . ... .. . . . 4.0-1 w DAVIS BESSE, UNIT 1 11 .
A 0FFSITE DOSE CALCULATION MANUAL . TABLE OF CONTENTS (Continued) Page APPENDIX A Figures
- 1. Calibration curve for Liquid Effluent Monitors . . . . A-1
- 2. Open terrain correction factor . .... .... . . . A-2
- 3. Plume ~ depletion effect for ground-level releases . . . A-3
- 4. Plume depletion effect for 30-m releases . ... . . . A-4
- 5. Plume depletion effect for 60-m releases . ... . . . A-5
- 6. Plume depletion effect for 100-m releases . . . . . . A-6
- 7. Vertical standard deviation of material in a plume . . A-7
- 8. Relative deposition for ground-level releases . .. . A-8
- 9. Relative deposition for 30-m releases . . .. .. . . A-9
- 10. Relative deposition for 60-m releases . .. . . . . . A-10
! . (~)'\
\
\. .
- 11. Relative deposition for 100-m releases . ... . . . . A-11
- 12. Map of sampling locations on the site periphery of the Davis-Besse Nuclear Power Station . . . . . . . A-12
- 13. Map of sampling locations greater than 1.5 miles from site .. ...... . . . . .. . . . . . . . . A-13
- 14. Davis-Besse Gaseous Discharge . . . . . . . . . . . . A-14
- 15. Davis-Besse Liquid Discharge . . .. . . . . . . . . . A-15 t
16-50. Maps of individual sampling locations . .. . . . . . A-16 1 i APPENDIX B Tables
~^
- 1. Bioaccumulation factors . . ... . . . . . . . . . . B-1 -
- 2. Ingestion dose factors for adults . . . . . . . . . . B-2
- 3. Site-related ingestion dose commitment factor . . . . B-5
- 4. Dose factors for exposure to semi-infinite cloud n) q of noble gases . . .. . . . . . . . . . . . . . . . . B-7 DAVIS-BESSE, UNIT 1 111
OFFSITE DOSE CALCULATION MANUAL TABLE OF CONTENTS (Continued)
'O . ' (s) Page
- 5. Pathway dose parameter factors for implementing 10 CFR Part 20 . . . ...... . . . . . . . , . . . . B-8
- 6. Pathway dose parameter factors for implementing 10 CFR Part 50 . . . . . . . . . ... . .. .... . B-20
- 7. Controlling receptors, locations, pathways and Atmospheric Dispersion Parameters . .... . ... . B-59
- 8. Sampling locations . ...... . . . ... . .. . . B-60 -
- 9. Type and Frequency of Sample Collection, Environmental Radiation Monitoring Program . . .. . . B-62
- 10. Sample Collection Codes .............. . B-64 APPENDIX J Justifications Safety Evaluation . . . . . . . . . . . . . . . . . . . . . J-1 Service Water System-Radiological Effluent Monitoring Requirements . . . . . . . .. .. . . J-4 m/ Radioactive Effluent Instrumentation - _
- Automatic Isolation Feature .. . . . . .. . . .. . . J-5 Technical Bases for Eliminating Curie Inventory Limit for Gaseous Waste Decay Tanks . . . . . . . . . . . . . . . . . . . . . J-6 Lower Limit of Detection-Decay Correction Factor . . . . . . . . . . . . . . . . . . . . . J-9 Waste Gas Decay System and Ventilation System-Operability Requirementa .. . . . . . . . . . . . . . . . . . . . . . J-16 Radiological Effluent Dose Analysis-Meteorology for Short Tern Releases ....... . . . . . . . . . . . . J-18
~'
Radiological Environmental _ Reporting Levels . . . . . . . . . . . . . . . . . . . . . J-19 Technical Basis for Eliminating Curie Inventory Limit of Outside Liquid Tanks . .. ... . . ... . . . . . . . . . . . . J-20 n v . DAVIS-BESSE, UNIT 1 iv
0FFSITE DOSE CALCULATION IfANUAL .
. TABLE OF CONTENTS (Continued) i Page
, _ Sampling Frequency for I-131: < Significance of Power Changes and Increases in Coolant Activity Levels . . . . . . . . . . . J-21 Condensate Damneralizer Backwash Receiving Tank - Radioactivity Control . . . . . . . . . . J-24 - Lower Limit of Detection, Definition and - - Application to Detection Capabilities for Ce-144. . . . . . J-26 l \i . 'x , i l 9 l i 1 l 1 l DAVIS-BESSE, UNIT 1 v I
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J
',, INTRODUCTION ,
O This OFFSITE DOSE CALCULATION MANUAL (ODCM) describes the methodology and parameters to be used in the calculation of offsite doses due to radioactive liquid and gaseous effluents and in the calculation of liquid and gaseous effluent monitoring instrumentatica alarm / trip setpoints. The ODCM also contains a list and graphic description of the specific sample locations for the radiological environmental monitoring program. The ODCM will be maintained at the Station for use as a reference guide ~ and training document of accepted methodologies and calculations. Changes in the calculational methods or parameters will be incorporated into the ODCM in order to assure that the ODCM represents the present methodology in all applicable areas. The methodology stated in this manual is acceptable for use in demonstrat-ing compliance with 10 CFR Part 20.106, 10 CFR Part 50 Appendix I, and . 40 CFR Part 190. Only the dose attributable to the Davis-Besse Nuclear i () Power Station is considered in demonstrating compliance with 40 CFR , Part 190. More conservative calculation methods and/or conditions (e.g., location and/or exposure pathways expected to yield higher computed doses) t'2an appropriate for the maximally exposed person may be assumed in the dose evaluations. l l For the calculation of individual doses from gaseous effluents, the receptor is selected on the basis of applicable exposure pathways identi-fied in the land use census. Methodologies and pathways considered in NUREG-0133 are consistent with those in the ODCM. I I For liquid releases, doses are evaluated for the drinking water and freshwater fish pathways. In the Great Lakes region, invertebrates do not constitute a direct ingestion pathway to man. O . DAVIS-BESSE, UNIT 1 vi 2 __ - - _
1.0 LIQUID EFFLUENTS , 1.1 Liquid Effluent Monitor Segpoints 1.1.1 Liquid Radwaste Effluent Line Monitors Liquid Radwaste Effluent Line Monitors provide alarm and automatic termination of release prior to exceeding the concentration limits specified in 10 CFR Part 20, Appendix B, Table II, Column 2 at the release point to the unrestricted area. To meet this specification, the alarm / trip setpoints for liquid effluent monitors and flow measurement devices are set to assure that the following equation is satisfied: cf <C, (1-1) F+f where: l m) - C = the effluent concentration limit (RETS, section 3.11.1) implementing 10 CFR Part 20.106 for the site, in pCi/al
=
- c = the setpoint, in pCi/ml, of the radioactivity monitor measuring the radioactivity concentration in the effluent line prior to dilution and sub-sequent release; the setpoint, which is propor-tional to the volumetric flow of the effluent line and inversely proportional to the volumetric flow of the dilution stream plus the effluent _,
I stream, represents a value which, if exceeded, I would result in concentrations exceeding the limits of 10 CFR Part 20.106 in the unrestricted area f = the flow setpoint as measured at the radiation monitor location, in volume per unit time, but in O. the same units as F, below DAVIS-BESSE, UNIT 1 1.0-1 _ - '~1_- _ _ _ _ _ _ . __ _
F = the dilution water flow setpoint as measured p - () prior to the release point in volume per unit time. At Davis-Besse Unit 1, the available dilution water flow (F) is constant for a given release, and the waste tank flow (f) and monitor setpoint (c) are set to meet the condition of Equation 1-1 for a given effluent concentra-tion, C. The method by which this is accomplished is as follows:
- 1) The isotopic concentration for a waste tank to be released is determined by the analyses required in RETS Table 4.11-1. The ratio of the concentration to the unrestricted ares MPC (10 CFR Part 20, Appendix B, Table II, Column 2) is calculated with the equation:
C (1-2) FMPC = I iQO) MPC g + , g - where: FMPC = fraction of the unrestricted area MPC i C g = concentration of each radionuclide i acasured ih each tank prior to release (pCi/al) MPC g = unrestricted area MPC for each radionuclide i from 10 CFR Part 20, Appendix B, Table II, Column 2. For dissolved and entrained noble gases a value of 2 x 10-4 pCi/al shall be - - i used. N DAVIS-BESSE, UNIT 1 1.0-2 .
.-m.,.-y- - - .--.,..~,->.n- -
..,--,...,,-.,_.,,7 . -,-- ,n. _- --. - . _ _ _ . . - - - . . , , - . , - . . - ., --....-,,.n_.,--
' .~
The total or gross beta or gamma activity alone may be j-~ ,, ( ,) used to conservatively determine the NPC fraction by the equation: C FMPC = t (1-3) 1x10-7 Where: Cg = the total or gross beta or gamma activity, 1 x 10~7 = MPC value for an unidentified mixture of radionuclides (from footnote 3.b to 10 CFR Part 20, Appendix B). .
- 2) The MPC fraction (FMPC) as determined for each batch used to calculate a Dilution Factor, D.F. , which is the ratio of total dilution flow rate to tank flow l
rate required to assure that the 10miting concentra-
s tion of 10 CFR Part 20, Appendix B, Table II, Column 2 -
are set at the point of discharge. D.F. = FMPC (1-4) S.F. where: D.F. = dilution factor S.F. = an administrative safety factor normally applied at Davis-Besse which causes the ,, calculated Dilution Factor to be 3.33 times - larger than the dilution factor required for compliance with 10 CFR Part 20 lLnits.
! DAVIS-BESSE, UNIT 1 1.0-3 i
-- -. - - . . _ . . _ - _ _ - . . , _ _ _ - - - _ _ . . - - . - . . ~ _ , . , . - . _ - . .,.- - -__ .. - -, .-. . . - - . _ - .
. \
l 4 I l' 3) The naminamn permissible waste tank flow rate, f 'd18 calculated based on a fixed dilution flow rate, E d fd= d+Ida d for dF >> Id F (1-5) D.F. D.F. 4 where: 1 T = 0.9 x (dilution flow rate), as readout in d control room
- f * **Xi8um Permissible waste tank flow rate d
1 l i
- D.F. = Dilution Factor from Step 2. l l
NOTE that the equation is valid only for D.F. >1; for J , D.F. <1, the waste tank concentration meets the limits - of 10 CFR Part 20 without dilution, and f may take on d , , any desired value. t .
- 4) The minimum dilution flow (F), and waste tank maximum l flow rate setpoint (f) are calculated as follows:
1 9 F=Td = 0.9 x actual dilution flow rate as observed l from the control room readout, i f = 0.9 x fd = 0.9 calculated maximum waste tank flow rate for the stated release conditions.* A control room alarm occurs if the dilution flow rate
~'
- falls below the preset flow rate, or if the tank flow rate exceeds 0.9 of the preset flow rate, and the i
release is terminated. !O l l DAVIS-BESSE, UNIT 1 1.0-4
1 2 ./ 5) The monitor setpoint may now be specified based on the i f values of F, and f which were specified to assure that releases are asistained below the concentrations of 10 CTR Part 20, Appendix B, Table II, Column 2. The monitor setpoint in counts per minute (cpe) is taken I j from the monitor calibration graph (e.g., Figure 1) to
! correspond to three times the concentration in the batch.
i S.P. = 3 x A (pci/al) (1-6) where: * ] , 5 S.P. = the monitor setpoint obtained from the : I calibration curve for the monitor (cpe) 3 1 A = total radioactivity concentration in the , ! batch i l ( I A=IC l
.i 31 .
or, if based on gross or total beta or gamma l j analysis, 1 A=C g Normally, only one liquid relesse is conducted at a i time. If more than one release of radioactive effluents l is conducted simultaneously, the setpoints for the ! individual radiation monitors for the combined reless-es will be set to prevent exceeding the concentrations of 10 CFR Part 20, Appendix B, Table II, Column 2 in - t t the environment. l NOTE that the setpoint contains a factor of conserva-l tise, even if the calculated setpoint tank flow rate , l l DAVIS-BESSE, UNIT 1 1.0-5 I i i
._--_ _.. _ . . _ . ___ , _ . , _ _ . - . _... . ,_,..._. _ ,._._ ., - ,m__ ___ _, , _ _ _ . _ , . . - .
is attained, since the calculated rate contains the O ij factors as shown: 0.3 x 0.9 x 3 = 0.81 _ fraction of limit for trip setpoint , _ multiplier for setpoint froe equation (1-4) waste tank rate margin - _ dilution factor margin In practice, the actual tank flow rate normally is many times less than the calculated tank flow rate, thus providing an additional safety factor during a release. 1.1.2 Turbine Buildina (Floor Drains) Sump Effluent Line
/ (Applicable upon completion of modification) .
The purpose of the monitor for the turbine building sump effluent line (or Unit Storm Sewer Outlet) is to detect abnormal radionuclide concentrations in the sump effluent system. Because the only sources to the sump effluent system are from the secondary steam system, activity is expected in the turbine building sump effluent system only if a significant primary-to-secondary leak is present. If a primary-to-secondary leak is present, the activity in the sump effluent system would be comprised of only those radionuclides found in the secondary system, but with
~ ' '
reduced activity from decay and dilution. Until activity is measured in the secondary system, it will not be practical to select radionuclides on which to calculate the setpoint of the inline monitor. The monitor O is, therefore, operated normally as a gross gamma detector DAVIS-BESSE, UNIT 1 1.0-6 t 9
< at the lowest practical activity level to prevent false O
alarms. The lowest practical level has been determined to be three times the background count rate of the monitor when filled with clean water. idhan activity above the level specified in RETS Table 4.11-1 is detected in the secondary system, the principal nuclide or anclides comprising a major fraction of the activity in the secondary system condensate will be identified by gamme ! ray spectroscopy in the laboratory. The monitor setpoint i will then be determined as follows:
- 1) The isotopic concentration for the turbine building i sump effluent is determined by the sampling and j analytical requirements per RETS Table 4.11-1 (only '
required when secondary system concentration exceeds q 10-s pCi/al). The ratio of the concentration to the unrestricted area MPC is calculated with the equation: O C
*i (1-7)
FMPC = I - - MPC L L Idhere: FMPC = fraction of the unrestricted area MPC i - I C gg a concentration of each radionuclide i measured in each grab sample l! l MPC g a unrestricted area MPC for each radionuclide i from 10 CFR Part 20, Appendix B, Table II, ,, , ! Column 2. For dissolved and entrained gases, l a value of 2x10'* pC1/el shall be used. i e DAVIS-8 ESSE, UNIT 1 1.0-7 A
-,-_,-.,_-..m,,,,_y -
.,__n_ , - , _ ,,,-__n,-,-mm -
r If based on gross or total beta or gamma analysis, the
; unrestricted area MPC fraction is simply:
C ( ~0} l 1x10-' t C ga the total or gross beta or gamma activity lx10~7 = MEC value for an unidentified sixture of radio-nuclides (from footnote 3.b to 10 CFR Part 20,- Appendix B).
- 2) The actual dilution factor from fixed flow rates of the turbine building sump effluent flow rate and dilution flow rate is as follow.:
I actual dilution factor = f + F f where:
; f = turbine building sump effluent flow rate (spa) q F = dilution flow rate (spa)
- 3) The concentration in the turbine building sump which corresponds to an unrestricted area MPC value after
. dilution is calculated from the previously defined quantities, and is:
~
^ ..
- f + F (1-9) e = FMPC f I
, DAVIS-BESSE, UNIT 1 1.0-8 I
.z=* . me s> w e mee a
-.-e -_ , . ~ . - . - . , , - - - , -, , - _ _ , _ _ , , . . - _ . , . , - _ _ _ . _ . ~ . - - _ - _ , , _ - . . . . . _ . _ , - - _ . , - , _ - . _ . _ _ _ _ . . . ~ - . , . _ . - , _ . . . _
__.~m.- -._ _.__..---.
/ where: O . N_) c = concentration corresponding to the unrestricted area MPC value after dilution A = total radioactivity concentration (pC1/al) A = T. C i 81 or, if based on total or gross beta or gamma analysis, A=C g The calibration curve for the monitor (g.g., Figure 1) is then used to determine the count rate (cpa) corre-sponding to the radionuclide concentration (c). The monitor setpoint is the sum of the calculated count k rate plus the observed background count rate of the , monitor. To simplify the determination of setpoint or in the event that the concentration of radioactive material in the sample from the turbine building sump is below measurable levels (i.e,., less than 5 x 10-7 pCi/mi for principal gamma emitters), the value of 1 x 10~7 pCi/el may be substituted for the factor A ( i_ . e_ . , A = 1 x 10~7). FMPC FMPC It may conservatively be assumed that the radionuclide , concentrations in the secondary system are identical to those in the turbine building sump. Therefore, the results of the sampling and analysis of the secondary system may be used in conservatively determining the values of FMPC and c, above. DAVIS-BESSE, UNIT 1 1.0-9
/
1.2 Dose Calculation for Liquid Effluents _ Technical Specification 4.11.1.2.1 requires that an assessment be l performed at least once every 31 days in any quarter in which radio-active effluent is discharged to determine whether the dose or dose commitment to a person offsite due to radioactive material released in liquid effluent calculated on a cumulative basis exceeds Specifi-cation 3.11.1.2. The requirement is satisfied by computing the accumulated dose commitment to the most exposed organ and to the total body of a hypothetical persor. exposod by eating fish and - drinking water taken from Lake Erie.
, The dose contribution from all radionuclides identified in liquid
! effluents released to unrestricted areas is calculated using the following expressions: l Dg =IA t I atg Cgg Fg i _f= 1 , where: D = dose or dose commitment to orgsa I, including total body (area). DF g , the site-related ingestion does commitment ! A =K w+U pBF I "! j { factor from radionuclide i (" ) (from j Table 3 of Appendix B). E Atg= length of the A time period over which C gg and Fg are i averaged for all liquid releases, in hours. 11 = average concentration of radionuclide i observed in undiluted liquid effluent during time period Atg from any liquid . release, in pCi/ml. Concentrations are determined 1 O DAVIS-BESSE, UNIT 1 1.0-10 l 2-- - - _ . -_-. -_ - -. - _ _ _ - _ . . . . - _ -_
',,, primarily from a gaussa isotopic analysis of a liquid effluent sample. For Fe-55, Sr-89, Sr-90, and H-3, the last measured value will be used in dose calculations. Fg = near-field average dilution factor for Cg during any liquid affluent release. Defined as the ratio of the average undiluted liquid waste flow during release to the product of the average flow from the site discharge structure to unrestricted receiving waters times the near-field dilution factor of 10 times the collection box factor of 1.0 . (Ref. 2). Fg = average undiluted lionid waste flow average flow from the site d2.senarge x 10 x 1.0 . K, a units conversiotr f actor 1.14 x 10 3 (10 8 x 1037" + 8,760 h) N) _ 11 , 3 adult water consumption (730 liters /yr) (Ref. 3)
= dilution factor from the near-field area within one-quarter D,
- sile of the release point to the potable water intake for adult water consumption. D, is (57/(10 x 1.0)) = 5.7, where 57 = lowest dilution factor corresponding to beach wells located approximately 966 m NW of the discharge point (Ref. 2). The near-field dilution factor of 10, represents the mixing effect of the discharge structure (Re!. 2).
tL = adult fish consumption (21 kg/yr) (Ref. 3). s - . 3F g = bicaccumulation factor for nuclide, t, in fish, in pCi/kg per pCi/ liter from Table 1 of Appendix B (taken from Reference 3, Table A-1). O v e
- DAVIS-BESSE,IDTIT 1 1.0-11
*' i e eh e e e m og e ._
*' 8 **
y
- . . - . - . ~ _ _ _ , _
DF g = dose conversion factor for nuclide, i, for adults in gs
\s preselected organ, t, in eres/pci, from Table 2 of Appendig B (taken from Reference 3, Table E-11).
1.3 Projected Personal Maximum Dose For Liquid Effluents 1 The dose commitment to a person offsite due to radioactive material released in liquid effluent may be projected by calcu-lating the extrapolated total body and most exposed organ dose commitments to a hypothetical person exposed by eating fish and drinking water. The potential dose commitments to organs and to the total body are computed separately. i
- The dose commitment to a maximally exposed hypothetical person will be projected by calculating the doses accumulated during the most recent three months according to the method described in Section 1.2 and by assuming that the result represents the
-s projected doses during the current month or quarter ! 'V Alternatively, the 31 day dose causitment may be projected by 1 using the equation:
Pz =TD g (1-11) X where: P g
= projected dose commitment (ares) to organ t (including total body) for the current quarter T = number of days in the projected time period 1 (i.e. 31 days 91 days). -
X = number of days to date in current quarter Dg = accumulated personal dose to data during the current {}
\' quarter via radioactive material in liquid effluent (mres).
, DAVIS-BESSE, UNIT 1 1.0-12
.._ ~ . - _ , - - _ _ __. .
1
1.4 REFERENCES
TO 1.0 LIQUID EFFLUENTS o - 1.4.1 J.S. Boegli, W.L. Britz, R.R. Bellamy, and R.L. Waterfield. I 1978. " Preparation of Radiological Effluent Technical j Specifications for Nuclear Power Plants," NUREG-0133, Office of Nuclear Reactor Regulation, U.S. Nuclear Regula-tory Commission, i 1.4.2 D.W. McDougall. 1980. " Aquatic Dilution Factors within 50 miles of the Davis-Besse Unit 1 Nuclear Power Plant."- Stone & Webster Engineering Corporation. 1.4.3 United States Nuclear Regulatory Commission. 1977.
" Calculation of Annual Dose to Man from Routine Releases of i Reactor Effluents for the Purpose of Evaluating Compliance a
with 10CFR50, Appendix I," Regulatory Guide 1.109, Revision 1. 4 4 l _ l t
~
t 1 i l l ( DAVIS-BESSE, UNIT 1 1.0-13
------m__ , _. n -
/ 2.0 GASEOUS EFFLUENTS 2.1 Gaseous Effluent Monitor Setpoints
.1.1 Station Vent Monitor The station vent is the only normal radioactive gaseous release point.
For the purpose of implementation of section 3.3.3.10 of-the RETS, the alarm setpoint level for the station vent noble gas monitor will be calculated as follows: 0.5 (Rg) 500 S, = the lesser of or (2-1)
~
0.5 (R,) 3000 a3 . idhere: S = count rate of station vent noble gas monitor at y alarm setpoint level (cpe) 0.5 = safety factor allowing 100*. margin for cumulative unce'rtainties of measurements (dimensionless) R = count rate per ares /yr to the total body
= count rate per ares /yr to the skin.
R, _ The values of Rg and R, are dependent on the radionuclide distribution and are derived by the equations: 1 I ( -2) C + [ X/QNG f i i)I i Rg , -
. DAVIS-BESSE, UNIT 1 2.0-1 ,
*/
( R, = C + [(X/Qyg) I (Lg+1.1M)k} g g (2-3) . L where: C = count rate of the station vent monitor corresponding to grab sample radionuclide concentrations (cpe) M= highest sector annual average atmospheric dis-
~
persion at the unrestricted area boundary ~
= 1.83 x 10~8 sec/m3 in the north-northeast sector Kg = total body dose factor due to gamma emissions from isotope 1 (ares /yr per pCi/m3 ) from Table 4 of Appendix B O 4g a rate of release of each noble gas radionuclide i identified by the sampling and analysis per RETS Table 4.11-2 (pci/sec)
Lg = skin dose factor due to beta emissions from isotope i ' ares /yr per pCi/m3) from Table 4 of Appendix B 1.1 = ares skin dose per arad air dose Mg = air dose factor due to gamma emissions from isotope 1 (arad/yr per pC1/m3 ) from Table 4 of Appendix B. ** O DAVIS-BESSE, UNIT 1 2.0-2
A more conservative setpoint may be calculated to minimize requirements for adjustment of the monitor by using the equations: R' = C' + [(X/%g)K) (2-4) R' = C' + [(X/Qyg)(L + 1.1M)] (2-5) where: R' = conservative count rate per stes/yr to the total body (Xe-133 detection, Kr-89 dose) R' = conservative count rate per ares /yr to the skin (Xe-133 detection, Kr-89 dose) C' = count rate of station vent monitor for an effluent concentration of Xe-133 corresponding d to 1.0 pCi/sec release rate of Xe-133 (cpe) , K = total body dose factor for Kr-89, from Table 4 of Appendix B L
- skin dose factor for Kr-89, from Table 4 of Ap.sendix B M = air dose factor for Kr-89, from Table 4 of Appendix B 2.1.2 Weste cas Decay System and Containment Purge Monitors ,
The weste gas decay tank releases and containment purges, in addition to being monitored by the station vent monitor, t are controlled individually to provide additional assurance Q that releases do not exceed the limits of Technical Speci-U fications 3.11.2.1. DAVIS-BESSE, UNIT 1 2.0-3
The setpoint level (S ) d r discharge through the waste gas b decay system monitor will be calculated in a corresponding manner:
~
0.5 (r g) 500 S = the lesser of or (2-6) d 0.5 (r s) 3000 where: S d
= count rate of waste gas decay system monitor at alarm setpoint level r = count rate per ares /yr to the total body g
r, a count rate per ares /yr to the skin The values of rgand r, are dependent on the radionuclide distribution and are derived by the equations: rg = e + (( MNG }I i iI , (2-7) i r, = c + ((U6 Nc )I (Li*l'I"t)d) i (2-8) i where:
.c = count rate of the waste gas decay system monitor for radionuclide concentrations to be discharged (cpe) d = rate of release of noble gas radionuclide i ,
(pCi/sec) ( ! DAVIS-BESSE, UNIT 1 2.0-4
-_ . _ . - - ~ . - - _ - -
i I 1 For a more conservative, simpler setpoint for the waste gas 4 system monitor, the equations are: i e' = c' + [(X/Q )K) (2-9) : NG c' = c' + [(X/Q )(L + 1.1M)] (2-10) NG i ] where: } . I = conservative count rate per ares to the total r{ ] body (Xe-133 detection, Kr-89 dose) l 1 1 c' = conservative count rate per arem to the skin ; i (Xe-133 detection, Kr-89 dose) l f c' s count rate of the waste gas decay system monitor 1
- for an effluent concentration corresponding to 4 +
1.0 pCi/sec release rate for Ze-133 i 1 The setpo- . level for the containment purge noble gas 1 monitor will be calculated using the same methodology as indicated for the waste gas decay system, utilizing the - ) appropriate corresponding count and release rates. ; l 1
- The calculated setpoint values will be regarded as upper ,
1 . bounds for the actual setpoint adjustments (ie, setpoint I l adjustments are not required to be performed if the exist-l ing setpoint level corresponds to a lower count rate than ) the calculated value), i 1 2.2 Gaseous Effluent Dose Rate and Dose Calculations i 1 j r 1 2.2.1 Unrestricted Area Boundary Dose Rate > .l i a. Technical Specification 3.11.2.la limits the dose rate j I in the unrestricted ares due to noble gas releases [ I DAVIS-BESSE, UNIT 1 2.0-5
, _ . , ~ - _ . . . _ . , - , _ _ . _ . . ~ .
_ , _ . . _ . _ _ , . _ . _ _ _ - _ . _ _ - _ , . . . . _ _ _ _ - ....,-..-.._..,--,__J
'n from the station to 1500 ares /yr, total body and 13000 '
ares /yr, skin. Radiation monitor alarm setpoints are i established to assure that these release limits are not exceeded. In the event any gaseous releases from the station results in the alarm setpoints being i exceeded, an evaluation of the unrestricted area dose rate resulting from the release shall be performed using the following equations: Dg = (2-11) (X/QNG) 1 I Ei i 4 D, = (X/Q3g) I (Lt+1.1M)k t g (2-12) i where: Dg = total body dose rate (ares /yr) , '( ' D, = skin dose rate (ares /yr) - X/Q = highest sector annual average atmospheric NG dispersion at the unrestricted area boundary i 3
= 1.83 x 10-8 sec/m in the north-northeast
~ sector
- b. For I-131, tritium and particulates with half-lives 1 greater than 8 days, Technical Specification 3.11.2.1.b limits the dose rate to 11500 ares /yr to any organ.
~^
To demonstrate compliance with this limit, an evaluation ~ is performed at a frequency corresponding to the a i V DAVIS-BESSE, UNIT 1 2.0-6
,,..,-r., --e--.. ,. --- , - - . - - . . . , - , , . - , - . - - - . , ,-em,_. - - - , - - + , , - - - - - - - - , , - - - - - - - - - - - - - + . . ~ , - - - - , - - - - - - - n.
*o sampling and analysis time period (e_.g., normally once V) per 7 days for I-131). The following equation may be used for evaluation:
D, = (X/Q ) I (Pg Q'g) (2-13) I i where: D, = average organ dose rate over the sampling time period (ares / year) , X/Q = controlling sector annual average atmos-pheric dispersion at the site boundary for the inhalation pathway. 3
= 1.68 x 10~8 sec/m in the north-northeast sector.
Pg = dose parameter for radionuclide i, (ares /yr per pCi/m3 ) for inhalation pathway from
~
Table 5 of Appendix B. Values for Pg are derived in accordance with the methods described in NUREG-0133.
= average release rate over the appropriate Q'1 sampling period and analysis frequency for isotope i, I-131 or other radionuclide in particulate form with half-life greater than eight days (pCi/sec).
By substituting 1500 mres/yr for D, (equation 2-13) and ,
~
solving for Q{, an allowable release rate for I-131 can be determined. Based on the annual average meteorological dispersion (1.68 x 10~8 sec/m 3
) and the child inhalation 7 3 pathway (Pg = 1.62 x 10 meen/yr per pCi/m ), the release rate for I-131 is 44.1 pCi/sec. An added conservatism DAVIS-BESSE, UNIT 1 2.0-7 .
/ x factor of 0.8 has been included in this calculation to x-- account for any potential dose contribution from other radioactive particulate material. For a 7 day period which is the sampling and analysis frequency for I-131, the emmulative allowable release is 26.7 C1. Therefore, as long as the I-131 releases in any 7 day period do not exceed 26.7 C1, no additional analyses are needed to verify compliance with the Technical Specification 3.11.2.1.b limits on allowable release rate.
- 2.2.2 Unrestricted Area Dose to Individual
- a. Technical specification 4.11.2.2 requires at least a monthly assessment of releases of noble gases to evaluate compliance with the quarterly dose limits of
<5 mrad, gamma-air dose and <10 mead, beta-air dose.
The following equations may be used,to calculate the gamma-air and beta-air doses: lO (
~
D = 3.17 x 10-s I M ((X/QNG) il (~ D p
= 3.17 x 10-s I Ng [(X/Q3g)6] f (2-15) where:
l D = air dose due to gamma emissions for noble j gas radionuclide i (arad) I s i/Q c dispersion parameter for unrestricted areas NG - t
= 1.83 x 10-8 sec/m 3 i
Q = cumulative release of noble gas radionuclide i over the period of interest (pC1) J
}
DAVIS-BESSE, UNIT 1 2.0-8
-fm D = air dose due to beta emissions from noble
~
gas radionuclide 1 (arad) Ng = air dose factor due to beta emissions from noble gas radionuclide i (mrad /yr per pCi/m3 ) from Table 4 of Appendix B. 3.17x10-s = conversion factor (yr/sec)
- b. Technical Specification 4.11.2.3 requires an assest-ment at least once per 31 days to evaluate compliance with the quarterly dose limit of <7.5 ares to any organ. The following equation may be used to evaluate the maximum organ dose due to releases of I-131, tritium and particulates with half-lives greater than 8 days. 1 D
p
= 3.17 x 10-8 IQ (R X/Q' + Ry D/Q') (2-16) where:
D = dose or dose commitment to organ p, includ-ing the total body, from I-131 and radio-nuclides in particulate form with half-life greater than eight days (arem) i X/Q' = 1.19 x 10-s 3,cy,3 for inhalation pathway
. and H-3 dose contribution via other pathways (from Table 7 of Appendix B)
D/Q' = -1.39 x 10-s ,-2 vegetation pathway (from , l Table 7 of Appendix B) O O DAVIS-BESSE, UNIT 1 2.0-9 i
inhalation dose factor for radionuclide i
-m Rinh = '
from Table 6 of Appendix B (ares / year per (v) pCi/m3 ). Values for the inhalation dose factor were derived in accordance with the methods described in NUREG-0133. R = vegetation pathways dose factor for radio-veg g nuclide i from Table 6 of Appendix B (m2 - ares / year per pCi/sec). Values for vegetation pathway dose factor were derived in accordance with the methods described in NUREG-0133.
= cumulative release of radionuclide i of Q't I-131 or material in particulate form in long-term releases over the period of interest (pCi).
The location of exposure pathways and the maximum - organ dose may be based on the available pathways in the surrounding environment of Davis-Besse as identified by the annual land-use census (Technical Specifica-tion 3.12.2). Table 7 of Appendix B will be supple-mented yearly by including in the Semi-Annual Radioactive Effluent Report the applicable exposure pathways as identified by the census.
- c. For the purpose of impl:.:menting RETS Technical Speci-fication 3.11.3 on the EPA environmental radiation dose standard and 6.9.1.13 on reporting, dose calcula- , , ,
~
tions will be performed using the above equations with the substitution of average or actual meteor,.ogical parameters for the period of interest and applicable pathways. d DAVIS-BESSE, UNIT 1 2.0-10
- - ~
2 - _ _,
2.3 Projected Personel Maximum Dose from Gaseous Effluents i Pg - U The dose commitment to a person offsite due t,o radioactive material released in gaseous effluent may be projected by calculating the air dose for gamma and beta radiation and the most exposed organ dose commitments to a hypothetical person. The dose commitment to a maximally exposed hypothetical person will be projected by calculating the doses accumulated during the most recent three months according to the method described in - Section 2.2.2 and by assuming that the result represents the projected doses during the current month or quarter. Alternatively, the 31 day dose commitment may be projected by using the equation: P = T_ D X (1-11) O where: and B radiation, P = projected air dose commitment (ares) from or dose to organ t (including total body). l T= number of days in the projected time period (i.e. 31 days, 91 days). X = number of days to date in current quarter D = accumulated personal dose to date during the current quarter via radioactive material in gaseous effluent ,
~
(arem) l O DAVIS-BESSE, UNIT 1 2.0-11 l
- 7 -- --
f' 2.4 Total Dose fs . s 2.4.1 Compliance with 40CFR190 Compliance with 40CFR190 as prescribed by Specification 3.11.4 will be demonstrated when one or more of Specifications 3.11.1.2a, 3.11.1.2b , 3.11.2.2a , 3.11.2.2b , 3.11.2.3a , or 3.11.2.3b has been exceeded by a factor of 2. Once this occurs, the Company has 30 days to submit a report in accordance with Specification 6.9.2. - 2.4.2 Calculations Evaluatina Conformance with 40CFR190 To perform the calculation to evaluate conformance with i 40CFR190, an effort will be made to develop doses that are realistic by removing assumptions that might lead to overestimates of dose to a member of the public. To accomplish this, the following general rules will apply:
- a. Environmental sampling data which demonstr.tes that no pathway exists may be used to delete a pathway to' man,
- b. Locations used to calculate coses to a member of the public will only be at actual residences.
- c. When doses via direct radiation are added to doses j via the inhalation pathway, they will be calculated for the same receptor location (i.e., the same distance in the same sector).
2.4.3 Calculation of the Total Body Dose i Estimates will be made for each of the following exposure pathways to the same location by age class. Only those j [h
\ a) age classes known to exist at a location are considered. i DAVIS-BESSE, UNIT 1 2.0-12 ~~
. a. Direct Radiation
("^s .
%s
. The compcnent of dose to a Member of the Public due to direct radiation will be determined by first estimating the direct radiation dose at or near the site boundary, in each sector, using direct radiation measurements or radiation transport methodology. The dose at the calculational location is then determined by extrapolating the dose at the Site Boundary to the calculational location. The following method will-be used.
L ,9 " B,0( B,0 (X 0) DB,0 = Direct radiation dose at the site boundary in sector 8. l l < C'
\s- D 0
= Dose at calculational location in sector 8.
~
X = Distance to the calculational location in 0 sector 8. 1 X = Distance to the site boundary (or TLD B,0
, location) in sector 8 in meters.
- b. Inhalation Dose The inhalation dose will be determined at the calculational locations for each age group according _ ,
~
to the methods outlined in Sections 2.2 of this manual. i i l DAVIS-BESSE, UNIT 1 2.0-13 i+mm.,e e.. y ~ - w - + _ ._, _ -- , ,7m
1 l
- c. Insestion Pathway The dose via the ingestion pathway will be calculated at the consumer locations for the consumers at risk.
- d. Other Uranium Fuel Cycle Sources 1
For purposes of the Special Report, it will be assumed tnat the contribution to the dose commitment from other Uranium fuel cycle sources is negligible. 2.4.4 Calculation of the Thyroid Dose The dose to the thyroid will be calculated for each sector as the sum of the inhalation dose and the milk ingestion dose (if existing). The calculational methods will be
- those identified in Section 2.2 of this, manual. .(s, 2.5 Meteorological Model 2.5.1 Lont-Tern Atmospheric Dispersion Atmospheric dispersion for long-term releases is calculated l
i using a mixed-mode, wake-split form of the straight-line d l t flow Gaussian dispersion model, referenesd in Regulatory Guide 1.111, Revision 1. x/Q = atmospheric dispersion (sec/m3 )
~
2.03 ko 1-E ~ h2~ # E (2-17) ~~ r u(7 *U uI - l \ DAVIS-BESSE, UNIT 1 2.0-14 l i
/ where:
O V k = open terrain recirculation factor at distance r from Figure 2 of Appendix A. 6 = plume depletion factor at distance r for appro-priate stability class and effective height from Figures 3-6 of Appendix A. (Note: This plume depletion factor applies only to releases of radioiodines. The depletion factor for noble - gases is unity.) E = fraction considered as ground level 1.0 for {10 2.58-1.58 v for 1.0< v $1.5 u u
. 0.3-0.06 v for 1.5< v 15.0 ,
u u i O for {>5.0 , v = station vent exit velccity (13.4 m/sec) t u = wind speed at vent height from the 75-m level of the main meteorological tower (m/sec) i u = wind speed at ground level from the 10-m level of the satellite meteorological tower (m/sec)
~'
a = vertical standard deviation of the plume at - distance r for effective height under stability category indicated by temperature lapse rate AT ('C/100m)- from Figure 7 of Appendix A. O DAVIS-BESSE, UNIT 1 2.0-15
_. ma _ 4-m_J 1-_a - % -- +.-------44--.Ad.m L_J +A--A1 4 -J-41. -- J m--. - - - - * - Aaa' -A4_a & J4 AI = temperature differential with vertical separation between the 10-m and 75-m levels of the main meteorological tower (*K/100m) h = effective height of release (a)
= hy +h -
hg p hy = height of station vent i = 75.3m h = additional height due to plume rise (a) Pr for stability classes A, B, C, D i 2/3 1/3 v r d -c the lesser of 1.44 y u d _ i or 3 d . . m u L. I i -
~ .
DAVIS-BESSE, JNIT 1 2.0-16 i
..-..----,..---.I _ . _,___ __ _ -.. . - - - - - - _ . _ _ - _ _ _ _ . _ _ . . _ ._ , _
e subject to, for stable conditions (AT > - 0.5 'K/100m): d - _ 1/4 _F the lesser of 4 _j_ or _ 1/3 _F -1/s 1.5 S d = diameter of station vent - -
= 2.12 a cy = correction for low vent exit velocity (a)
- ~
3 1.5 *- d for Iu< 1.5
- _ u_
=
0 for * > 1.5 momentum flux parameter (a4 /sec2 ) F = a
= ( )
S = restoring acceleration per unit vertical dis-placement for adiabatic action in the atmosphere 8.7 x 10~4 sec -2 for AT 5 1.5 (E) 1.75 x 10-3 sec -2 for AT $ 4.0 (F) 2.45 x 10-3 sec -2 for AT > 4.0 (G)
~~
hg = height of terrain at distance r in sector of - interest (a) r = downwind distance (a) 2.0-17 i i
-i -
I = vertical standard deviation of the plume with () building wake correction (m) _ 1/2
= the lesser of + (0.5) or
/3 Oz b = height of reactor building
= 73.5m 2.5.2 Lons-Tern Deposition r
Relative deposition per unit area for long term releases is calculated for a mixed mode release. i
. D/Q = relative deposition per unit area (m-2) 2.55k
! = r (1-E) De+ ED g (i~-18 ) where: ! = relative deposition rate for elevated releases D, from Figures 9 through 11 of Appendix A. l I i l D = relative deposition rate for ground level releases l 8 i from Figure 8 of Appendix A. l . 2.6 Definitions of Gaseous Effluents Parameters b = height of reactor building (m) (Section 2.3.1) V 2.0-18
l C = count rate of the station vent monitor corresponding to p grab sample radionuclide concentrations (cpa) (Section 2.1.1) C' = count rate of station vent monitor corresponding to a 1.0 pCi/sec release rate of Xe-133 (cpe) (Section 2.1.1) e = count rate of the waste gas decay system monitor for radionuclide concentrations to be discharged (cpe) (Section 2.1.2) - - c' = count rate of the waste gas decay system monitor corre-sponding to a 1.0 pCi/sec release rate of Xe-133 (cpe) (Section 2.1.2) cy = effective plume height correction for low vent exit velo-city (m) (Section 2.3.1) D, = relative deposition rate for elevated releases from Figure 6 , l of Appendix A (Section 2.3.2) i D = relative deposition rate for ground level releases from 8 Figure 7 of Appendix A (Section 2.3.2) Dg = average organ dose rate (ares / year) (Section 2.2.1.b) D = dose or dose commitment to organ p, including the total p body, from I-131 and radionuclides in particulate form, with half-life greater than eight days (mres)
- (Section 2.2.2.b)
D, = average skin dose rate (arem/ year) (Section 2.2.1.a) Dg = average total body dose rate (mrem / year) (Section 2.2.1.2) Ov 2.0-19 .
~. e ms .
F
, D = air.d'ose due to beta emissions from noble gas radionuclide i.(arad) (Section 2.2.2.a)
D = air dose due to gamma emissions from noble gas radionuclide 1 (arad) (Section 2.2.2.a) D/Q = relative deposition per unit area (m-2) (Section 2.3.2) d = diameter of station vent (a) (Section 2.3.1) 6 = plume depletion factor at distance r for appropriate stability class and effective height from Figures 3 and 4 of Appendix A (dimensionless) (Section 2.3.1) E = fraction of release considered as ground level (dimension-less) (Section 2.3.1)
= momentum flux parameter (m*/sec 2 ) (Section 2.3.1)
F, h = effective height of release (m) (Section 2.3.1) i hg = height of terrain at distance r in sector of interest (m) (Section 2.3.1) hy = height of station vent (m) (Section 2.3.1) h,p
= additional plume height due to plume rise (m)
(Section 2.3.1) K = total body dose factor for Kr-89, (mres/yr per pCi/m )3from Table 4 of Appendix B (Section 2.1.1) . Kg = total body dose factor due to gamma emissions from radio-nuclide (mrem /yr per pCi/m3 ) from Table 4 of Appendix B (Section 2.1.1) O 2.0-20
k = open terrain recirculation factor at distance r from
- Figure 2 of Appendix A (dimensionless) (Section 2.3.1)
L = skin dose factor for Kr-89, the most restrictive radio-nuclide, from Table 4 of Appendix B (ares /yr per pCi/m3) (Section 2.1.1) Lg = skin dose factor due to beta emissions from radionuclide 1 (arem/yr per pCi/m3 ) from Table 4 of Appendix B (ares /yr
; per pCi/m3 ) (Section 2.1.1) - .
i M = air dose factor for Kr-89, the most restrictive radio-nuclide, from Table 4 of Appendix B (arad/yr per pCi/m3 ) (Section 2.1.1) Mg = air dose factor due to gamma emissions from radionuclide 1 (arad/yr per pC1/m3 ) from Table 4 of Appendix B (Section 2.1.1) , Ng = air dose factor due to beta emissions from noble gas i radionuclide 1 (arad/yr per pCi/m3 ) from Table 4 of Appendix B (Section 2.2.2.4) Pg = dose parameter for radionuclide i, (mres/yr per pCi/m )3for inhalation from Table 5 of Appendix B (Section 2.2.1.b) dg = rate of release of noble gas radionuclide 1 (pCi/sec) (Section 2.1.1) {
= average release rate over appropriate sampling period of Q'g isotope i of I-131 or other radionuclide in particulate ,
~
j form, with half-life greater than eight (8) days (pci/sec) (Section 2.2.1.b)
; Qt = cumulative release of noble gas radionuclide i over the , period of interest (pC1) (Section 2.2.2.a) 2.0-21
9
= cumulative release of radionuclide i of I-131 or material Q'g in particulate form over the period of interest (pCi)
(Section 2.2.2.b) qg = rate of release of noble gas radionuclide 1 (pCi/sec) (Section 2.1.2) Rg= inhalation dose factor for radionuclide i from Table 6 of Appendix B (ares / year per pCi/m 3 ) (Section 2.2.2.b). Ry = vegetation pathway dose factor for radionsrlide i from Table 6 of Appendix B (a2 - ares / year per pCi/sec) (Section 2.2.2.b).
= count rate per ares /yr to the skin based on current isotope R,
distribution (Section 2.1.1)
,O Rg = count rate per aren/yr to the total body based on current isotope distribution (Section 2.1.1) .
i R', = conservative count rate per ares /yr to the skin (Xe-133 detection Kr-89 dose) (Section 2.1.1) R' = conservative count rate per arem/yr to the total body (Xe-133 detection, Kr-89 dose) (Section 2.1.1) i i r = downwind distance (a) r, = count rate per ares /yr to the skin based on waste gas decay system isotope distribution (Section 2.1.2) r : C unt rate Per ares /yr to the total body based on current l t waste gas decay system isotope distribution (Section 2.1.2) l l r' = conservative count rate per arem to the skin for waste gas decay system only (Section 2.1.2) 2.0-22 1
( ,) r'g = conservative count rate per arem to the total body for V waste gas decay system only (Section 2.1.2) S = restoring acceleration per unit vertical displacement for adiabatic motion in the atmosphere (see-2) (Section 2.3.1) t S = c unt rate f waste gas decay system noble gas monitor at d alarm setpoint level (Section 2.1.2) i S = count rate of station vent noble gas monitor at alarm - y setpoint level (Section 2.1.1) I = vertical standard deviation of the plume with building wake correction (m) (Section 2.3.1)
=
a, vertical standard deviation of the plume at distance r for effective height under stability category indicated by AT
,,s from Figure 5 of Appendix A (m) (Section 2.3.1) \. (
L _ AT = temperature differential with vertical separation ('K/100m) (Section 2.3.1) u = wind speed at vent height from the 75-s level of the main meteorological tower (m/sec) (Section 2.3.1) i i u = wind speed at ground level from the 10-m level of the satellite meteorological tower (m/sec) (Section 2.3.1) v = plant vent exit velocity (m/sec) (Section 2.3.1) 3 X/Q = atmospheric dispersion (sec/m ) (Section 2.3.1) - i X/Q = highest sector annual average atmospheric dispersion value at the unrestricted area boundary (sec/m3 ) (Section 2.1.1) 2.0-23 )
I X/Qy= controlling sector annual average atmospheric dispersion at the site boundry for the inhalation pathway (Section 2.2.1.b) highest sector annual average atmospheric dispersion at the X/QNG= unrestricted area boundary (sec/m3 ) (Secton 2.2.2.a)
- 2.7 References to 2.0 Gaseous Effluents i
2.7.1 J. S. Boegli, W. L. Britz, R. R. Belamy, and R. L. Waterfield. 1978. " Preparation of Radiological Effluent Technical Specifications for Nuclear Power Plants," NUREG-0133, Office of Nuclear Reactor Regulation, U.S. Nuclear Regula-tory Commission. l 2.7.2 United States Nuclear Regulatory Commission. 1977. J
" Methods for Estimating Atmospheric Transport and Disper- ,
sion of Gaseous Effluents in Routine Releases from Light-Water-Cooled Reactors," Regulatory Guide 1.111, Revision 1. 1 - I b, **- t ) !O - 2.0-2(. i
,, 3.0 RADIOLOGICAL ENVIRONMENTAL MONITORING
( )
%)'
Sampling locations as required in Section 3/4.12.1 of the Radiologi-cal Effluent Technical Specifications are described in Table 8 of Appendix B and shown on maps in Appendix A, pages A-12 and A-16 through A-50, 3.1 Land Use census A land use census shall be conducted annually for the purpose-of identifying changes in the use of the offsite area surrounding Davis-Besse which may substantially affect the radiological dose assessment or which may indicate needed adjustments to the Program. This census satisfies the criteria of 10 CFR Part 50, Appendix I, Section IV.B.3. The census will include land within 5 miles of Davis-Besse and will be conducted at least annually. It will be conducted by I (( s) either a door-to-door survey, aerial survey, or by consulting , local agricultural authorities or by a combination thereof. The locations of: 1) the nearest milk animal, 2) the nearest vegetable garden greater than 500 square feet, and 3) the nearest resident, within 5 miles of Davis-Besse in each of 16 sectors in cardinal compass point directions from the plant, are
~
to be identified in the census. If a milk animal is not identi-fied in a sector within 5 miles, one may conservatively assume l. l that one is located at the 5-mile distance for purposes of evaluating maximum potential organ dose and identifying the con-trolling pathway, except in those sectors over Lake Erie. l . If the land use census identifies a location (s) at which the dose or dose commitment calculated at the time is greater than the maximum calculated dose associated with the like pathway (s) j at a location where sampling is conducted as specified by the l "N monitoring program, then the pathways having maximum exposure l j ) 3.0-1 .
.~*O _ _,.
___ n_ ._ __ _ ,_ . _ , , , , _ _ , _ , _
1 potential at the newly identified location will be added to the program, if samples are reasonably obtainable at the new loca-tion. Like pathways monitored (sampled) at a location, exclud-ing control station location (s), having a lower associated calculated personal dose may be deleted from the program at the time the new pathway (s) and location (s) are added. 3.2 Sample Analyses Radioactivity in environmental samples described in Table 8 of Appendix B may be analyzed either at Davis-Besse or at an offsite laboratory. In order to provide a comparative check on the accuracy and precision of these analyses, the laboratory participates in the USEPA Interlaboratory Comparison Program by analyzing radioactive samples distributed for the purpose. Tables 9 and 10 of Appendix B identify the , type and frequency of environmental sample collection. 4 1 O 3.0-2
4.0 REGULATORY GUIDE 1.21 - EFFLUENT AND WASTE DISPOSAL SEMI-ANNUAL
/""} REPORT 4.1 Technical Specification Limits Used for Gaseous Effluents Since the -air dose is usually the most limiting for exposure to noble gases, this specification as shown in 3.11.2.2a will be used to determine the percent of limits reported in the Regulatory Guide 1.21 Report. The specification for the dose to a Member of the Public from I-131, tritium, and particulates with half-lives -
greater than 8-days is specified in 3.11.2.3.a for any organ. 4.2 Technical Specification Limits Used for Liquid Effluents The specification for dose to a MEMRER OF THE PUBLIC used to determine the reported percent of limit from liquid effluents is shown in 3.11.1.2.a for the total body and to any organ. l The limit for the concentration of radioactive material released to _ UNRESTRICTED AREAS from liquid effluents, other than dissolved or entrained noble gases, are those specified in 10CFR Part 20.106. T. S. 3.11.1.1 specifies 2 X 10-4 microcuries/ml as the concentration limit for dissolved or entrained noble gases. l
~
DBP 4306G 4.0-1
_,_ , _a,, - __a.- ---+ a, ma + - 4---L~m a--~.- s--a -..---_ -4 ar- a a 64 ..a --,,a. ..a
-- -,a m I
i r 't e I e I i S l l I APPENDII A 7Lataes (-? :. 1-I t 4 l-II 4 e O b S
~
~~'^*=ce-m,
j
- i. - 10 ..
E i y' l O ' l 1 11111 i e s iees e i . . : .. 1 I l i titti i i 111:111 l- I t s t ilil l I s e i s til i I ielle! 1 l lilli. I ilI II l. lllll IIli!!!!+ . Figure 1
+ ' ' ' ' "
for Liquid Effluent Monitors Cltifbration Curve * * * ' 3 o I ' ' " l lidil ' ' ,' (RE 1770 A & S. RE 1878 A & a) ' ' ' ' ' 'l
- i i il From Victoreen Instruction Manual I I I'III" l I I !!!I gg I ! Ill t I I l:'('lli .
l i i . e . .i . . . . . . . . , . . . . . . . , . . . . . . . . . , .. . . . . . . ,. I l l Ill: i i f Illi!! l l l l lill:1 l ' I l i t illi i l l i I II;I /t I i.. :: L iga I1. I I 111111 l I ll Ill l I lillli' I I lil!! r I I I!!!!! !
?
e e i e eine ... terr. e . . . ...:: . . . . . . ; f.' . ... . . . . . . , i l illil l I l !!lill i l i i lilli 1 i i liisi / I l lill:1 l l 1 :ll!.i e -
!ll lllll11 I Illi ii ! V I Illllli1 l !!!it w .= I0'3 ,
1.' 1 . . . . . . . . . .. . . . . .,- . . . ;
- j. f , ....e . . . . . . , . . . . . ..... .j,3...... . . . . . . . . . . . . ....
; g, ll l 11111l I i i ililli i L 6 i lilil A .tfl l I llit I l l I tilll I i l i fli t gg IIillll! IlllV i* I Illll!! IIlll11! Ii11!!!!!
Y . . .... . . ., . . .
.S. . e e . . . .e . . . ..ia .s . . ... . ......:, . . . . . . . . . . . . . . . .
I i Illl!! i i i i I!!;l I I I i litil / i i i i lill I i i i:::: i : i f:i!! 10-5 I II I I !!! !I I!O! !! ! I!!d I ! I N!O
^
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, .P O *m 1 BICACC3ELLTION FACTURS (pci/kg per pC1/ liter) ymmmarAm FI5R E 9.0E-01 C 4.6E+03 NA 1.0E+02 _
P 3.0E+03 C1 2.0E+02 MI 4.0E+02 FE 1.0E+02 CD 5.0E+01 ' NI 1.0E+02 C3 5.0E+01 25 2.0E+03 31 4.2E+02 EI 2.0E+03 2 3.0E+01 Y 2.5E+01
'. Z1 3.3E+00 l 33 3.0E+04 2 1.0E+01 -
TC 1.5E+01 IU l.0E+Cl M 1.0E+0L TZ 4.0E+02 I 1.5E+01 C3 2.0E+03 3A 4.0E+00 l 1.4 2.5E+01 CZ l.0E+00 F1 2.5E+01 3D 2.5E+01
'J 1.2E+03 NP 1.0E+01
'7alues in this Table are taken from Regulaccry Guida 1.109 .
except for Phosphorus which is taken from 3C3IC/C2-1336. - DA7IS-3E55Z, UN!! l 3-1
m O Table 2 Page 1 of 3 tactsf rcn Ocss
- Ac7 As 8cm acut.r$ -
Pese sen act smcasft:1 auct.Inf sCu t,: vee T.aCm funcf3 st =EY t.unc GI-s:.!
,* I 40 OATA t.JSE-C7 t . 'J E-o r t.05d-07 1.
- S E-4 7 1 05 E-47 1.*1!-47 1 *- 2 464-4e S.a4E-47 5.4 4 E-3 7 5.445-17 S .4 4 E-37 S.e4E-37 S.eas-47 MA 26 1.?:f-44 1.7CE-44 1.7N4 1.f:E-44 1.7:E-04 1.7*E-44 1.70E-04 _
8 32 L.93E-44 L.2:E-41 7. eE-4 4 40 OATA MC OATA 4C OATA 2.L71-45 CA St MC OATA 90 "ATA 2. eet *4 9 1.51E-49 S.444-t: 3 518-49 4.49E-37 m 56 10 QATA 6.57544 S.725-47 40 OATA t.34E-44 NC OATA 1 648-05 4N $4 ,MC OA TA 1.tjE-37 2.04N 8 MC OA7A 1.*44-07 10 OATA 3.475-04 ft SS 2.fSE-44 1 40E-Ce 6.6 s E-3 7 40 *ATA NC OATA 1.044-44 1.096-04 8 E 19 6.J44-44 1.025-45 3.9t!-44 40 OATA mc OATA 2.4SE-44 3.*CE-41 C2 $4 NC OA7A 7.*Si-47 1. 4 7T-0 4 MC OA TA 40 OA7A 4C OATA 1.SLE-CS 0" ec MC OATA 2.I* M e 4.72 N 4 NC OATA MC OATA NC OATA 6.022-45 MI 43 1.3C1-46 9.01E-44 6. 3 4 E-4 4 MC O A TA MC OATA MC OATA 1 485-44 Mt e3 S.236-47 e.444-43 3.13 E-4 s %c 2ATA NC :ATA 4C OATA 1 764-44 Ou **- 10 CATA 8.331-48 3. 91 E-4 4 MC OATA .10E-47 NC CATA 7 1 E-44 IM e5 6.444-44 1.344-05 e.1 4-4 4 40 OATA 1.03E-4S *C A7A 9. 7:E-44 c IN 69 t.03E-48 1.175-45 1.37?-09 NC OATA 1.23E-43 NC OATA 2.944-09
$4 33 40 ATA MC 04f4 6.025-48 40 *ATA MC :ATA NC OAfA S.795-03 ;
SR 36 10 OATA MC :sfA S.211-34 10 OATA 10 OA T A *C OATA *.09E-13 - 4A 35 NC OATA 10 OA T A 2.164-09 10 OATA 4C OA TA 40 OATA LT E-Z6 a8 44 40 0171 2.111-15 9.43E-34 *C CATA 4C CATA 9C *ATA *. tee-06 as is MC CATA 4. SE-48 1.215-08 MC OAfa 10 OATA MC OATA 8.344-11 49 39 *C OATA 6.31E-45 2.421-28 NC OATA MC :ATA NC OATA 2.33E-21 SA 39 3.J8E-46 40 OATA 3.36(=34 4C OATA MC :A TA MC OATA
- 6.944-45
$2 90 7.38E-43 10 OATA t.444-01 44 CATA MC OATA NC OATA 2.19E=46 SR 91 S. aft-44 MC *ATA 2.27t-4 7 4 OATA *C ATA sc OATA 2.7:E-45
$a 12 2.tSE-44 1C "ATA 9.3:E-38 40 OATA NC OATA 4C :ATA *.264-45 Y #C 9.e21-09 MC CATA 2 54E-t: MC OAfA MC "ATA 90 OATA 1.021-44
? 117 9.095-11 NC *ATA 3.32!-12 NC *ATA 10 O A TA 10 CATA 2.47E-10 Y *1 1.*t!=42 MC :ATA 3. 77b4 9 40 Afa NC *AfA MC OATA 7.76E-05
- 92 8.45E-1: MC *A T A 2.67!=tt 4C OAfA 10 ATA 40 OATA 1.64E-45
~-
Raferenes: Ranulatm r Gaida. 1.109. Table I-11 O CA7*5-BE552 ':3- 1 3-Z
)
s, f in i - M IE 2, conti:xued Page 1 of 3 Inca 37Icm ccsa Psc7C*s act toutfs ( ** Em att scr t CIsfto 4UCLICE SOME LIVER f.&CCY fMv9Ctc <!CMEY t.unc C1 %t,I y 93 2.444-C1 NC ATA 7.=4E LL NC 2ATA 10 3afA 60 OATA t.SQt-of ZM 19 3.364-48 1.713-49 e.e4E-49 NC CAfA L.318-48 MC OATA 3.399-45 2A 97 t.448-41 3 394-t0 L.SSE-tQ M QATA S.12E-LC W CATA 1.35E-46 Me 95 4.22E=49 3.644-49 1.444-39 40 CA TA 3.628-49 40 OATA 2.10E-45 "O 19 MC 3AFA 6 313-44 8.2cE-47 nc QA7A 9.744-44 40 3ATA 9.99t-44 TC 99# 2.675-to 4.145-10 3.499-49 MC QATA 1.C64-48 3.643-10 6 13E-47 , TC10L 2. W LQ 3.444-tc 3.394-49 40 CATA 4.394-49 1 871-to 1.1c8-21 I auLO3 L.aSG-47 10 QATA 7.971-48 40 3ATA 7.044-47 NC 3ATA 2 144-45 Aut03 L.344-48 Mu OATA 4. 38 E-41 40 QAfA 1.996-47 MC CATA 9.629-44 tut 04 2.758-44 10 3ATA 1.644-47 MC 3ATA S.318-44 NC 3ATA 1.788-46 AG110m L.e44-47 t.*48-47 S.796-48 *to 3ATA :.11E-47 10 CATA 4.064-45
. TE125# 2 498-44 9.71E-47 3 59E-4 7 S.348-47 L.394-45 50 CafA 1.379-4S 7t127= 4.771-44 2.621-44 S.2SE-3 7 1.736-44 2.754-45 90 3ATA 2.271-45 ft127 L .128-4 7 3.1SE-48 2.34848 8.135-48 6.646-47 mc OATA 4.446-44 I
ft1299 L.1SG-45 6 218-Ca 1. A294 4 3.1SE-44 6 305-45 NC OATA S.799-45 ftus 3.t64-4s t. Lag.48 7.as e-49 2. 6 t t-o s t.323-47 40 CATA 2.371-4s ,q\ 1 - itt31s 1.715-44 s.64E-47 7.cSE-4 7 L.344-ce t.371-44 50 OATA s.645-49 ftt31 L.971-ce 1.234-49 4 22349 1 421-48 3.43E-48 9C OATA 2.199-49 _ T9132 2.329-44 t.43E-44 1.334-44 L. Jct-44 1.571-45 'to CATA 7.719-45 I L30 7.344-47 2.219-44 8.409-07 1 899-46 3 644-44 s0 cart 1.921-44 i L31 6 144-44 S.1SE-44 3. 6 ta-4 4 1 119-43 1.321-45 nc OATA 1.371-44
! 132 2.4 3E-47 5.*3E-47 1. 94E-4 7 1 949-43 8.4SE-47. 10 CATA t .323-27 1 133 L.625-44 2.6ft-44 7.136-47 3.435-46 6.312-44 MC OATA 2.225-44 t 136 1.044-17 2.38E-37 1.01E-4 T 6.199-44 6 548-47 NC 3ATA 2.312-40 i ! 131 6.638-47 1.144-44 6.2SE-47 7.4SE-45 1.444-4A 4C OATA t.312-44 C3136 4.222-45 1.=4E-46 1.213-J6 40 OATA 6.79E-45 L.$91-35 2.59E-44 C3134 4.315-44 2.371-45 L. SS E-31 9C 2ATA 1.61E-45 1.944-44 2.922-44 03137 7.171-45 1.C99-46 f.164-4 5 90 OATA 3.70t-CS 1 23E-45 2 1LA-44 C3134 S.32E-48 1.C99-47 S.644-48 4 3ATA 8.013-48 7.911-49 6.ASE-13 sat 39 9.7et-4s 4. s ta- t i 2'.4*4-39 =0 cATA 4.644-tt 1. 922- L t 1.72s-47 t
F l 3-3 DAVIS-BESSI. ":s!"* 1
I till M II. 2, C W dm'ad ! Page 3 of 3 l l IN Z37TCM 0051 71CTCR5 *CR &Cutr5 l tutEM 8Et 8C1 INGESTEDI (IVER 7.3CCY ThYtC17 (ICMEV (UNG GL-tLL qac'.Ici SONE I 2.351-48 t . 3 3 E-0 6 40 OAfi t.afh-49 1.6ef-ca 6.t sE-45 . 5AL.4 2.0 3 C-43 2.021-It 2.222-t? agt.t 6.f13-48 1.SeE-tL t . 5 8 9-0 9 we O A f 4 3.3tE-(t
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- 9. Set-49 s.31E-C9 f. tit-LC NQ oaf 1 2 964-49 4C OAft 2. 25-43 1
- stet 1.229-46 t.3SE-to NC 3ATA 5.37E-10 MC OAfA 6.54E-45 03163 1.aSE-C1 C216. 6.A48-47 2.06{-47 2. A21-0 3 NC CATA 1.2 t &=47 NC Cafi t . A $ $-44 6.3e4=10 *C 3ATA 2.t34-49 MC 3Af4 6.03E-45' 34163 9.2CE-ce 3 491-41 1.235-LL L. S SE-11 40 OATA 7.2SE-12 *C DATA 6.J3e-t3
**16. 3 3t3-11 6.2SE-49 MC OATA 3.69E-43 NQ167 4.29f=49 7.275-49 6.3SE-10 90 3ATA 3 311-18 MC CATA NC 3ATA #C Cafa 2.825-45
- 197 t.33E-47 t.418-48 i
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l TABI.Z 3 l (continued) _ l SI"I 2dm C GESTION DOSZ CCMMI!MErr FACTCR 1: 1 (mram/hr per 1.C1/ml) ' Page 1 of 2 ) nuct.nt tout t.Ivtx riony muors sinwty wpe - st-u.I MC-** 0.00E-41 1.44tHO 3.14t+0 L 4 00E-41 3.7*T+4 4. 00 E-41 3.45EM:
*019M t.* t-42 3.33t-4 4.49t=3t 0.00t-41 1.3:t-41 t.?31-4 2.09t+41 RU-103 7.13t+00 0.001-41 3. 07tMO 0.00C-41 2.? tM1 0 048-41 1. 3*E M SU-104 1.04E+4 0.00t-41 1 34tH1 0.00E-41 2 05t+42 1.00E-41 6.34t+43 4ett0M 3. *:t H O a . f gEMO t . 77t H0 0.00E-41 5 . a 't *40 1.00t-41 "t .
- 1 E +4 3 C3115M 0.008-41 9.00t+4: 2. 4 7tM t 0.00t-41 7.*Ct+42 0.00C-41 38tM4
$3-t:4 4.71E+41 S.30E-41 1. 89tH L 0.00ta41 0.00C-41 3 70tH1 1 33E+43 ft-t! 2. 4CEH3 L.!Et+43 1. 49tM1 t . 7tt +43 1. 33 F+4 4 0.00t-41 7.30t+44
!=t31 2.10t+4 3.4 TEM: 1. 701H 9.45t+44 S.tSt+4* 4.00t-41 ?.93E+41 I-t3* t.03E+4L 2.74EMt *. 40 t HO 9.40t+4 4.3*T+41 1.00F-41 1.13t HO
- 1.1:1M:
t-133 ?.17t+41 1. .*3 t MO 3 80tMt 1 83E+44 .18 t+4: 0.00C-41
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.10F-31 3.33t-41 1.01t+03 LA-t*4 1.84E-41 9.35E-40 * . 48t-4* 3 00E-41 0. 0 0 E-11 1 00E-41 6. 89 t *4 3 0 00E-41 1.00t-30 1.00E-41 **.stg+4*
C1-141 1.!?t-41 1 088-41 1.*:1-42 CE-143 * . 30E-42 2 07t+41 2. ?t-43 0.00E-41 9 131-43 0.00C-41 ' . 7:t H C1=144 1. *?tM O 3 47tHO 4.431-41 0 00E-41 * . 04E+40 1.00E-41
- 30t+43 89-144 2.24t-43 *.311-44 1.14t-44 0.00E-41 S.::t-44 0.00E-41 3. 1-to Wa t S7' .97t+4
- 49tHO 9. 4 91H1 0.008-41 4.00C-41 1. 00 t-11 9.14 t M4 88- 7T t .3:tH e 0.00t-41 8.4 1+42 0.00t-41 3 43t+43 1 00C-41 t.!!E+43 .
. ' l-::S 1.a't*44 0. 00 t=) t 1.3 Z+4* 0.00E-41 3. 3*t M 1 1.00t-41 3 221643 W-:37 4. tt-4: 4 3tg-43 :.49t 43 C 40E-41 1. 4 t t-4
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3-4
r. 4 D . O TABLE a DOSE FACTORS FOR EXPOSURE TO A SEMI-INFINITE CLOUD OF N08LE GASES 3g119, TM,"( X) s-Skin =*(1.) y-Aie(M) s-41M(N) Kr-45m T.17Ee 1.46E+03 1.23E+03 1.97E+03 Kr-45 1.61E+01 1.34E+03 1. 72E+01 1.9EE+03 Kr-47 5.92E+03 9.73E+03 6.17E+03 1.03E+04 Kr-48 1.47t+04 2.37E+03 1.52E+04 2.93E+03 Kr-49 1.66E+04 1.01E+04 1. 7M+04 1.06E+04 Kr-90 1.56E+04 7.29E+03 1.63E+04 7.83E+03 4 Xe-131m 9.15E+01 4.76E+02 1.56E42 1.11E+03 Xe-133s 2.51E+02 9.94E+02 3.27E+02 1.48E+03 M h.'l Xe-133 Xe-135m 2.94E+02 3.12E+03 3.06E+02 7.11E+02 3.53E+02 3.36E+03 1.05E+03 7.39E+02 Xe-135 1.81E+03 1.86E43 1.92E+03 2.46E+03 ! Xe-137 1.42E+03 1.22E+34 1.51E+03 1.27E44 l Xe-1:38 8.82+03 4.1X+03 9.21E+03 4.75E+03 Ar-41 8.84E+03 2.69E+03 9.30E+03 3.28E+03
Reference:
tegulatory Guide 1.109 Table 3-1 and See:1on 2.1.1 of the l Offsite Does c= ' ~ t =:1oa hu t
- arad-e 3
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3 uGi-yr
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= M n e = = e p M M e N = C M a n = n N g 9 3 = d = = S = 0 & it u m e 29
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=0 2A% M et te rs M M o vt e ft e e c e .= Pa re R e e M
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' .) CONT 20LI.3G RECUTORS, LOCACCUS, PATJAIS, AND A20S7EERIC DIS 7E2SICN PARA.L'E"'Z25 .
e Distanca Sector 6seters) ?sthwavs Age Groun X/QI D/0 3* 870 Inhalacion Infant 3.76E-07 8.09E-09 55I 900 7egetation Infant 1.19E-06 L.39E-08 NE** 900 inhalacion Child 1.26E-06 1.38E-08 g3gwr _ - g** _ - _ Szww .-. ~ SE*** S000 Cow / Milk Infanc 3.43E-08 1.45E-10 SSE 2680 7egetacion. Child 7.38E-08 9.13E-10 , S 1990 vegetation Child 7.66E-08 1.29E-09 SSW 1000 7egscacion Child 1.92I-07 4.18E-00 SW 990 7egecation Child 3.10I-07 5.64E-09
'452 4250 Cov/ Milk Infanc 5.74 E-08 5.36E-10
. e
, 9. V 980 7egacacion Child 6.21I-07 9.58E-09 M 2500 7egetation Child 3.38E-08 8.612-10
{' 37 1160 7eger.acion Child 2.29E-07 1.97I-09 33W 1250 7egscation Child 2.51I-07 1.79E-09 (Cafault value, no vesetabla gardens 21:hin five nilas.
**3ase sectors are located over Laka Iris, so no ingascion pathways are present.
*** Default value, ;io real receptors wichin five niles.
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. 8 Paga L of 2 SKOLING LCCATICNS, DAVIS-3 ESSE NUl** m FCUE2 STA**CN Appendiz A Type of Code ?asta Raf aranca Location
- Location T-L A-16 I Sita boundary, 0.96 'ca NE of station, naar intaka canal.
T-2 A-17 I Site boundarf,1.44 'as E of Station. T-3 A-18 L Sita boundary, 2.24 'ca. ESE of statica, naar Tousaatst River and stars drain. T-4 A-19 I Sita boundary, L.28 *ca S of station, naar Locust Point and Toussaint River. T-5 A-20 I L'ain entrance to si:n, 0.30 'ca W of station. T-7 A-21 I Sand Beach,.1.44 'ca NNW of sita. T-8 A-22 I Earl L'cora Farm, 4.32 'em '45J of sica. T-9 A-23 C' Cak. Harbor,10.9 1ca SSW of si:n.
;-11 A-24 C Pore Clinton,18.4 'ca SE of sita.
T-12 A-25 C Toledo, 37.6 las LTJ of sita (watar samples are takan from an. intaka located 17.6 km N37 of site).
'.i h : .
I-17 A-26 I Irv Fick.'s vall en si:a,1.12 'ca SW of station. 9 - T-20 A-27 C Carl Gaach, 12639 2. *oussaint E Road, 7.20 'm '.
'JS*J of sica.
T-24 A-18, A-29 C 42ndn=ky, 39.3 Ica SE of si:a. T-25 A-30 I Millar Farm, 5.92 'ca S of si:a. T-27 A-31 C Mages Marsh, 8.48 'ca '4NW of si:a. T-23 A-32 I Unit i ersated and untrasted vacar supply, ons1:a.
;-33 A-33 I Laica Erie, vi:hin a 3.0 'ca radius of si:a.
- 35 A-34 C Laka F.ria, graatar than 16.0 'ca radius of sita.
T-37 *A-35 C Fruit stand,19.2 ica SW of station (or the farn 16 to 30 'ca from the sita in the least prevalant vind direc:1on).
;-38 A-36 I Si:a boundary 0.96 'ca ENE of station naar laka.
T-40 A-37 I Si:a boundary 1.12 'ca SZ of station naar ditch
- o Toussaint.
T-41 A-38 I Sita boundar7 0.96 'ca SSI of station naar ditch _ to Ioussaint.
* := Indicator locations; C= Control Locations ,
- i DA*T!S-3ESSI, TJI I 3-40 l
_ . ~ . - - .
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Pass 2 of 2 SAMPLI3G LOCATIONS. DA7IS-BESSE 'TUCI.ZAR PCWER STATION Appendix A Type of Cada Pasa Rafarence Location
- Location T-42 A-39 I Sita boundary 1.2S la SSW of station by ECO.
T-43 Ar-40 I Sica boundary 0.30 'ma SW of station along Routa 2 fance. T44 A41 I Sita boundary 0.30 la WSW of station by railroad tracks. d= T-65 A-42 I Sica W 7 0.30 km UNU of stacion on access
- road behind Cooling Tower.
- T-46 A-43 I Site boundary 0.30 kat NW of station along -
access road. T-47 A-4A I Site boundary 0.80 la 3 of station along access road by gata.
- T-48 A-45 I site 9-d-ey 0.80 las NNE of station along access road by laka.
T-50 A-46 I Eria Industrial Park 7.20 las SE of station by Water Tower.
" T-51 A-47 I Daup Farm, 600 Taccau Icad, Port Clinton, Ohio S.80 lam SSE of the station.
i *
, T-52 A-48 I . M*" ar Tarz 5.92 'an S of sita on West Camp Parcey Road W.
( T-34 A-49 I M. Saiar Tars 7.68 las SW of sits on G==== Road.- T-55 A-50 I K.ing Farms 8.0 'em W of sita on touca 2.
* != Indicator location; C= Control locations.
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- AVIS-BISSE, T.!!" 1 3-41
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** Type anal Frequency of St >ple Collection U Environmental ltadiation Monitoring Program (Continised)
N Y 3.ucation Type Weekly Honthly (}uarterly Semi-annually Annually 42 1 T!.D 4'l i TI.D I ! 44 I TI.D I 45 1 TLD 46 I TIJ) 47 i TLD y 48 I T1.D 0 M I TI.D
$I I TI.1) 52 I TI.D l $4 i TI.D l
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Table 10 Samole Collection Codes - t Code Description : AP Airtome Particulatas ! I AI Airborne Iodine TLD Themoluminescent Cosimeter M Milk . WW Well Water (Ground Water) GLV Green Leafy Vegetables , SWT Surfaca Watar - Treated S*n1J Surface Water - Untreated F Fish BS Sottan Sediments [3.h r CAV!!-GESIE, " NIT 1 3-44 0 v en- ~.e-- ,, . _ - - - . - _ _ . _ _ - - - - , - -_ - . _ _ _ _ _--. _ -_ _ - . _ _ - _ - _ _ , _ _
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l OFFSITE DOSE CALCULATION MANUAL . . t APPENDIX J 3 JUSTIFICATIONS l-i l DAVIS-BESSE, UNIT 1 l
(; q Safety Evaluation for the Davis-Besy Radiological Effluent Technical Specifications Amendment Overview Revisions to the Davis-Besse Appendix A and Appendix B Technical Specifi-cations are proposed which will implement the regulatory requirement of 10 CFR 50, Appendix I on ALARA for radioat:tive effluents and other NRC regulations and criteria on radioactive material monitoring instrumenta=
. tion, radioactive material control, and rrdiological environmental moni-toring. In keeping with NRC guidelines, all radiological requirements are being deleted from Appendix B and placed in Appendix A.
This proposed amendment is a revision to a previously submitted amendment to that NRC dated March 16, 1979 (Serial No. 488). The major areas that are addressed in the revised submittal are as
! follows: .
!
- Liquid and gaseous effluent monitoring instrumentation--operation and periodic operability checks;
- Liquid and gaseous radioactive material releases--maximum release rates, quarterly does limits and yearly dose limits;
- Sampling and analysis requirements on batch and continuous radioac- 1
! tive material releases; I l
- Operation requirements on the liquid radwaste treatment system; 4 9
- Curie inventory limit on outside temporary liquid storage tanks; i
[
- Maximum allowable oxygen concentration in the waste gas system; l-DAVIS-BESSE, UNIT 1 J-1 i
Requirements to assure all solid waste meets applicable burial site
. requirements;
- Radiological ~ environmental monitoring program--minor revisions to
- reflect current program and current NRC guidelines.
Changes have also been made to Section 6 of Appendix A to reflect the ) applicable administrative controls needed for the Section 3/4 revisions. A notable addition to the amendment is the inclusion of a requirement for an Off-site Dose Calculation Manual (ODCM) and a Process Control Program (PCP). The ODCM and PCP are not licensed documents but are referenced in the Technical Specification as presenting acceptable methods for evaluat-ing compliance with applicable Technical Specification requirements. The ODCM provides calculational methods for determining radioactive effluent instrumentation alarm setpoints, and for evaluating releases of radioac-tive effluents and corresponding doses. The ODCM also includes the 4 sampling locations for the environmental monitoring program. The PCP l () presents the methods used to verify that waste (dewatered resins) as processed for disposal meets appropriate shipping and burial ground 1 regulations. Changes may be made to these documents without NRC approval; review by the SRB is required. Safety Evaluation An evaluation of the revised amendment has been performed to assure that the revisions as proposed do not involve an unreviewed safety question as defined in 10 CFR 50.59. The three criteria of 10 CFR 50.59 for the unreviewed safety question determination are addressed below. 1 i) Probability of occurrence or the consequences of an accident or - i malfunction of equipment important to safety previously evaluated in the safety analysis report. O DAVIS-BESSE, UNIT 1 J-2
Except for the addition of the turbine building liquid effluent radiation monitor (for which an FCR has already been initiated), no plant equipment modifications are required by the proposed amendment. Certain procedural requirements will need to be developed but these address rout'ine radioac . tive material effluents and controls; no accident procedures are involved. 1 ii) Probability for accident or malfunction of a different type than any evaluated previously in the SAR may be created. 4 For reasons as stated in response to item (i) above, the proposed amend-ment does not directly or indirectly pose a probability for an accident or malfunction. The amendment will implement the NRC regulations for routine releases and controls of radioactive material. The amendment does not address any engineered safety features of the plant design. iii) Ifargin of safety as defined in the basis for any technical specifi-cation is reduced. l- The proposed amendment does not reduce the margin of safety. The proposed , amendment addresses routine releases and control of radioactive material; i ! except as noted in ites (i), no plant modifications are involved. Several -- operating procedure changes may be needed, but these changes will be only for routine operations and will have no impact on accident probability or , consequences. For the reasons discussed above for each of the criteria of 10 CFR 50.59, it is concluded that the amendment as proposed does not involve an unre-I viewed safety question. l l l . l O DAVIS-BESSE, UNIT 1 J-3 I - . - - _ _ . _ _ _ _ - _ _ _ _ _ _ _ - _ _ - _ _ - - _ - - . . . - - - _ . . _ - _ - . - .
- . Service Water System--Radiological Effluent Monitoring Requirements
-o ,
The service water system is classified as a non-radioactive system, being removed from radioactive systems by two boundaries. Radioactive systems are serviced by the component cooling water system interface; and, the
,, service water, system provides cooling to the component cooling water system through closed loop heat exchangers. Therefore, any leaks from radioactive systems into the plant water systems would first be identified by the monitoring of the component cooling water system prior to any -
^
additional unexpected leakage'into the service water system. As a prudent r
.i measure, the service water system is monitored in accordance with the NRC 1
dguidance of Standard Review Plan, Section 11.5. However, because this system is a non-radioactive system and is separated from radioactive syatens through two closed-loop boundaries, no Technical Specification requirements are needed for routine monitoring and analysis for radioac-tive effluents. b'd - DAVIS-BESSE, UNIT 1 J-4 ,
" ~ ~ ~ '
Radioactive Effluent Instrumentation--Automatic Isolation Feature
%J The radioactive effluent monitoring instrumentation at Davis-Besse does not include provisions as called for in the NRC Standard Radiological Effluent Technical Specifications for automatic isolation should any of the following conditions exist: circuit failure, downscale failure, or instrument not set in operate mode. Even though the automatic isolation features do not exist, administrative controls have been established such that should any of these conditions exist the control of radioactive .
effluents would not be significantly impacted. Essentially all releases of liquid radwaste are controlled as individual batch releases with predetermined allowable release conditions. Thereby the radiation monitor serves mainly as a back-up; primary control is established by the prerelease radiological analyses and evaluations. To assure the availability of the back-up monitoring, the status of the instruments is checked once per shift by the control room operators. Indicator lights on the instrument panel are checked to verify operability. An indicator would illuminate , should a failure occur such as the ones delineated above. Therefore, in addition to the administrative controls on allowable releases, the verifi-cation of instrument operability prior to releases of radioactive effluents and the "once.per shift" status check by the control room operators provides adequate assurance of the proper control of the radioactive effluents. O DAVIS-BESSE, UNIT 1 J-5
Technical Bares for Eliminating Curie Inventory
!( Limit for Gaseous Waste Decay Tanks The NRC Standard Technical Specifications include a limit for the amount of radioactivity that can be stored in a single waste gas decay tank.
This curie inventory limit is established to assure that in the event of a tank failure releasing the radioactive content to the environment the resulting total body dose at the site boundary would not exceed 0.5 rem. For Davis-Besse the inventory limit in the waste gas storage tank has been determined to be approximately 45,000 curies (Xe-133, equivalent). An allowable primary coolant radioactivity concentration is established by the Technical Specifications which limit the primary coolant radioactivity concentrations to 100/E with E being the average energy of the radioactiv-ity in Mev. This equation yields an upper primary coolant gross activity limit of about 200 pCi/ml. By applying this activity concentration limit to the total liquid volume of the primary system, a total activity limit can be determined. For Davis-Besse the primary system volume is about _ 56,000 gallons, which yields a limiting total inventory of approximately 41,000 C1. By assuming a typical radionuclide distribution an equivalent Xe-133 inventory can be determined. Table 1 provides the typical radionuclide (noble gases) distribution and the Xe-133 equivalent concentration. The equivalent concentration is determined by multiplying the radionuclide l concentration by the ratio of the nuclide total body dose factor to the Xe-133 total body dose factor. Summing all the individual radionuclide equivalent concentrations provides the overall Xe-133 equivalent concen-tration. For determining concentration in a waste gas decay tank, a conservative assumption of 48 hours decay in degassing the primary system -
~
has been used to correct the primary coolant concentrations. The data i show that the equivalent concentration (decay corrected) is less than the gross concentration (i.e., 16 pCi/gm total in primary coolant versus 12 pCi/gm equivalent). The resulting Xe-133 equivalent curie inventory j for WGDT input is approximately 31,000 Ci. DAVIS-BESSE, UNIT 1 J-6
.. Therefore, even if the total primary system at the maximum Tech Spec
"'\ .
allowable concentration was degassed to a single waste gas decay tank, the
*(Q tank curie inventory would be well below the 45,000 Ci limit. Based on this evaluation, the curie inventory limit on a single waste gas storage tank has not been included as a Technical Specification requirement.
i l i l 1 ! DAVIS-BESSE, UNIT 1 J-7
-, r,-, - ......_ ,. ,,, ...,.-- -..-- ,.., , ,..- ,, . . _.-,m,...--,.w,_, ._ . - .,_ _ _ __ ___
Table 1
'(D ' %_)
Xe-133 Effective Concentration Primary
- Half-life Concentration Reg Guide 1.109 Ratio Xe-133 Coolant @ 48 hr decay TB Dose Factor TB DF Effective Cone (pCi/GM) (pci/ml) area /yr Xe-133 DF @ 48 hr decay pCi/m 3 (pCi/ml)
Kr-83M 2.0-02 1.9 hr -- 7.6x10-s .. .. Kr-SSM 1.1-01 4.5 hr -- 1.2x10-3 4.1 -- Kr-85 7.4-02 10.7 yr 7.4x10-2 1.6x10-s 0.06 4.4x10-3 Kr-87 5.8-02 76.3 min -- 5.2x10~3 20. -- Kr-88 1.9-01 2.84 hr -- 1.5x10-2 52. -- Kr-89 4.8-03 3.16 min -- 1.7x10-2 57. --
%e-131M 8.4-02 12 days 7.5x10-2 9.2x10-s 0.32 2.4x10-2 1133M 2.0-01 2.2 days 1.1x10~1 2.5x10-4 0.86 9.5x10-2 %J Xe-133 1.5+01 5.3 days 1.2x10+1 2.9x10-4 1.0 1.2x10+1 Xe-135M 1.3-02 16 min --
3.1x10~3 11. -- Xe-135 3.3-01 9.1 hr 8.5x10-3 1.8x10-3 6.2 5.3x10-2 Xe-137 8.7-03 4 min -- 1.4x10-3 4.8 -- Xe-138 4.3-02 17 min -- 8.8x10-3 30 -- Tctal 1.6x10+1 1.2x10+1 1.2x10+1
*Ad pted from Davls-Besse Evaluation of Compliance with Appendix I to 10 CFR 50, June 4, 1976. -
DAVIS-BESSE, UNIT 1 J-8
Lower Limit of Detection--Decay Correction Factor
}OD' The equation and definition of the lower limit of detection in the NRC
- Standard Radiological Effluent Technical Specification include the term e 'which'is used to decay correct the analysis. The LLD is further defined as an a priori (before the fact) limit representing the capabilities of a measurement system and not an a posteriori (after the fact) limit for a particular measurement.
1 Providing a decay correction for an evaluation of the capabilities of a system does not appear appropriate. It may be appropriate to decay correct certain analyses of specific samples to determine radionuclide concentra-i
- tions at the time of release. Even in this case, such a correction is not appropriate for batch releases. Analyses are performed prior to any re-lease; and, the sample will be decaying at the same rate as the batch fron which the sample was taken. For continuous releases, decay correcting analyses of samples obtained over a specified sampling interval must take into account the accumulation of radioactivity in the sampling medium, the decay during the sampling interval and, especially.for short lived radio-nuclides, equilibrium or quasi-equilibrium conditions that may be achieved.
Short-lived radionuclides will tend to reach an equilibrium value in the sampling medium as a function of source input and half-life. A single decay correction to adjust for sampling interval will provide an unacceptable j overestimate. Equilibrium concentrations must be considered if analyses are i to be indicative of actual release quantities. Employing exp(-Mt) to adjust for radioactive decay between the end of sampling and the time of analysis is straightforward. However, to attempt i to use the same term to adjust for decay during the sampling period is not - -
~
proper. As a practical matter, when the half-life of a radionuclide is long relative to the sampling time and the time between sampling and analysis, l 1.e., minimal decay, the correction term will be near unity. In that event, l the correction term is relatively unimportant. DAVIS-BESSE, UNIT 1 J-9 _-__$.- . - _ . . , _ . , .__-_,ym.,, ,,,.y , ,.,.-_-,. , _-,
At the other extreme, when the half-life of}}