ML20081L991
| ML20081L991 | |
| Person / Time | |
|---|---|
| Site: | Callaway  |
| Issue date: | 10/20/1983 |
| From: | Grundstrom R UNION ELECTRIC CO. |
| To: | |
| Shared Package | |
| ML20081L984 | List: |
| References | |
| PROC-831020-01, NUDOCS 8311170012 | |
| Download: ML20081L991 (77) | |
Text
~.
DATE 10/20/83 PAGE 1
of 2
UNION ELECTRIC COMPANY CALLAWAY PLANT EMERGENCY PLAN IMPLEMENTING PROCEDURE INDEX HEALTH PHYSICS Procedure Date Deficiency Reno.
Number Title Rev.
Immued Pace Date Dent.
EIP-ZZ-00101 Clammification of 0
05/18/83 04/14/83 Hlth Phv Emeroenclem' EIP-ZZ-00102 Emeroencv Imol.ementina 0
04/29/83 04/20/83 Hith Phv Actions L
EIP-ZZ-00201 Notifications 0
04/29/83 04/20/83 Hlth Phy I:IP-ZZ-00202 Ca1.1.out of' Emeroency 07/18/83 06/20/83 Hlth Phy Oroanization EIP-ZZ-00203 Additional Ammistance
/ g Hlth Phv Oh[
(~'IP-Z Z -0 0 21.0 In-Plant Radiol.oaical 0
7 Hith Phy Controlm EIP-ZZ-00212 Protective Action 0
07/I8/83 Hith Phv Recommendations EIP-Z Z-00 21.3 Technical. Assessment 0
07/18/83 Elth Phv EIP-ZZ-00214 Personnel / Vehicle 0
04/29/83 04/19/83 Hlth Phv Monitorina and Decontamination i
EIP-ZZ-0021.6 Potassium Iodine 0
1.0/04/83 Ema. Prec Administration EIP-ZZ-00220 Emercency Team Formation 0
04/29/83 Hlth Phy EIP-ZZ-00221 Search and Rescue 0
04/29/83 Hlth Phv EIP-ZZ-00222 Emercency Reoair 0
04/29/83 Hith Phv EIP-ZZ-00223 Field :3nitorino 0
05/18/83 05/12/83 Hlth Phy L
EIP-ZZ-00224 Tranmoort of Contaminated 0
04/29/83 04/19/83 Hlth Phv Iniured/Il.1 Personnel EIP-ZZ-00225 Reentry 0
06/15/83 Hith Phy l
s r,
, -iP-ZZ-00230 Evacuation 0
07/18/83 06/24/83 Hlth Phy
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PAGE 2
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y REALTH PHYSICS Procedure Date Deficiency Resp.
Number Tit 1.e Rev.
Issued Pace Date Dent.
EIP-ZZ-00240 Activation of Technical 0'
07/18/83 06/18/83 Hith Phy Saccort Center EIP-ZZ-00241 Activation of Operathional 0
07/18/83 06/09/83 Hith Phv
. Suocort Center l
EIP-ZZ-00250 Communications & Records 0
05/18/83 Hlth Phv Keeoina
+
EIP-ZZ-00260 Recoverv 0
05/18/83 Hith Phy
- EIP-ZZ-01.21.1 Initial. Dose Ammessment 0
10/19/83 09/30/83 Ema Preo
- Z EIP-ZZ-02211 Intermediate Phase and 0
10/1.9/83 09/30/83 Emq Preo Suhaenuent Dome Ammemament
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EIP-ZZ-01211 September 30, 1983 Revision O.
'Q d
CALLAWAY PLANT 2
EMERGENCY FLAN IMPLEMENTING PROCEDURE EIP-ZZ-0121'.
INITIAL DOSE ASSESSMENT RESP. DEPT. /!-a, n.ev Mmum g PREPARED BY An,e Cauve rre.-
APPROVED BY bN hA DATE /#./-83 l
DATE ISSUED lO l4 $3 This procedure contains the following:
p.
Pages 1
through
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through 2
Appendices through Checklist through
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DEFICIENCY LIST Section Deficiency Description Constraints I
4.1
! Meteorological instrumentation ! None at
! is not and may not be' installed! this time
! in control room.
4.2, 4.3, 4.5,
! Sensitivity Correction Factors,! None 8.1.6, 8.1.7,
! isotopic mix and steam release !
TABLE 3.1, 3.2
! rate for a steam effluent and 3.3
! release not available.
I
+
r 4.3, 8.1.5,
! Isotopic mixes for the
! None 8.1.6, 8.1.7, I accident types have to be TABLES 3.1, 3.2,
! verified I
and 3.3 I
f 4.5, 8.1.8,
! Contingency Release Rate Table ! None TABLE 5.1
! has to be developed, Becthel
! has to verify and complete g.
! Technical Basis.
I r w I
~) TABLE 1.3 I Units may change to meters /sec ! None
! pending installation of I
! meterological equipment and
!.RRIS ATTACHMENT 2
! Information not available to
! None NOTE
! ensure correct Units 2B
! Steam release rate through I atmospheric release valves
! not Available.
I
~
TABLES 3.1, 3.2 i Sensitivity Correct Factor,
! None and 3.3
! Whole Body Dose Rate
! Factor, and Child Thyroid /
! Whole Body Ratio has to be
! calculated for Loss of I
! coolant accident.
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0 9
INITIAL DOSE ASSESSMENT I
1.0 PURPOSE AND SCOPE l
The purpose of this procedure is to provide a means of rapidly determining the initial off-site dose rates for a potential or ac-tual major release of radioactive material" to the environment, when the Radioactive Release Information System (RRIS) is not available.
This procedure shall be used until effluent samples have been taken and analyzed; at which time subsequent dose assessments will be in accordance with Intermediate Phase and Subsequent Dose Assessment, EIP-ZZ-02211.
2.0 RESPONSIBILITY The Health Physics Coordinator is responsi-ble for performing the initial dose assess-ment in accordance with this procedure.
f
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3.0 INITIATING CONDITION N.J This procedure shall be initiated when the RRIS is not available and, either of the following conditions exist:
3.1 An Emergency has been declared with the classification of ALERT or higher and a release of radioactive material has occurred or has the potential to occur.
r 3.2-As determined by the Health Physics Coordi-nator, or Emergency Co.ordinator.
4.0 PROCEDURE The Health Physics Coordinator shall perform the following steps utilizing Attachment 2, Dose Assessment Worksheet when any of the initiating conditions (3.0) occur:
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Determine the Meteorological Dispersion Fac-tor
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4.1.1 Fill in the information needed to complete Box 1A in Attachment 2 by obtaining the in-formation from the Control Room instrument'ation.
4.1.2 If the primary tower information is not available in the Control Room, utilize the secondary tower indications and complete Box 13.
4.1.3 If no meteorological data can be obtained from the Control Room, dispatch an individ-ual to the meteorological tower to relay the needed information.
First to the primary meteorological tower and then to the secon-dsry tower as an alternate, if needed.
~
NOTE If an individual is dispat-ched to either meteorologi-cal tower, ensure he has the te:lephone number to contact the Health Physics h'S Coordinator.
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4.1.4 Using the DELTA-T (90m-10m) determine the PASQUILL STABILITY CLASS from Table 1.1.
If DELTA-T (90m-10m) is unavailable use DELTA-T (60m-10m).
4.1.5 If aither DELTA-T values are not available, determine the PASQUILL STABILITY CLASS with the WIND DEVIATION (Sigma Theta) from the Secondary Tower using Table 1.2.
The o
Average Wind Speed must be greater than 2.24 mph to use this method.
.4.1.6 Record the STABILITY CLASS in Block 1C.
i.
4.1.7 Using Table 1.3 and the coirect STABILITY CLASS transfer the correct xp/Q values to the appropriate-block in column 4A.
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4.1.8 Transfer the Wind Speed (p ) from block 1 to the column 4B.
4.2*
DETERMINE THE RELEASE RATES Release rates can be determined for the Unit Vent, Radwaste Building Vent and Atmospheric Relief Valves following the appropriate steps below.
Dose Assessment for other release pathways should be in accordance with EIP-ZZ-02211.
4.2.1 From the P.adiation Monitoring Panel in the control Room obtain the monitor readings for the release pathway:
Unit Vent, Radwaste Building Vent, or Atmospheric Release Valves.
Record the readings in Block 2A.
NOTE If more than one release path exists, a separate at-tachment 2 has to be com-pleted for each path.
4.2.1.1 If the Radiation Monitoring Panel is inoper-ative or values cannot be obtained, go to (n1?
Step 4.5 for contingency calculations.
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'4.2.2 Transfer the monitor reading for the release path from Block'2A'to column 4C.
4.2.3 Determine the effluent flow rate utilizing one of the steps below.
4.2.3.1 Determine the unit vent exhaust flow rate utilizing information from the Control Room instrumentation.
Check on or off for each f
exhaust fan tag ID listed on Table 2.1, Determination of Unit Vent Flow Rate.
Add all design rated flows for fans which are operating.
Record flow rate on 2B and 4D.
I 4.2.3.2 The Radwaste Building vent exhaust rate is i
prerecorded in 23.
If the release is frcm the Radwaste Building vent, transfer the value to 4D.
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0
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4.2.3.3 The Steam Effluent Release Rate via the At-cospheric Releasa Valve is pre-recorded in 2B.
If the release is from this path, transfer'the value to 4D.
-4.3*
DETERMINE THE CORRECTION FACTORS AND RATIOS 4.3.1 Utilizing Table 3.1, determine the sensitiv-ity correction factor for the correct moni-tor and accident type.
Note the accident type in 3A and record the correct sensitiv-ity correction factor in 3B.
NOTE The sensitivity correction factor corrects the monitor t-readings, which is based on XE-133 calibration, for the various isotopic mixes caused by the different type accidents.
Select the acci-
~*
dent type which mc;c closely resembles the acciuent in
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4.3.2 Based upon the accident type, select the
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ble 3.2 and record the values in 3C and 4F.
4.3.3 Based on the accident type, select the cor-rect Child Thyroid /Whole Body Ratio from 3.3 and record in 3D and'4H.
4.4 CALCULATIONS 4.4.1 Perform the calculations in Box 4.
Column G results give the Whole Body Dose Rates.
Column G multiplied by Column H gives the Child Thyroid Dose Rate, Column I.
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4.5*
CONTINGENCY CALCULATION
- This step provides a method for estimating release rates, utilising conservative acci.
dont assucptions, in the event that no data is available from the Radiation Monitoring System.
This step should only be used until other data is available, as it is unlikely that an actual accident condition would be similar to those postulated.
4.5.1 Utilizing Table 5.1, Contingency Release Rate Table, determine the Noble Gas Release Rate for the accident type.
4.5.2 Substitute this value' for the monitor read-ing on 2A and 4C, and note "Yes" in 2C.
4.5.3 In the event that the indicators for the ex-haust fan ID are inoperable, utilize the total for the correct " Normal Fan Lin,e Ups" from Table 2.1, for the Effluent Flow Rate in 2B.
c 4.6 PROTECTIVE ACTION RECOMMENDATIONS (f
Upon completing the calculations in Attach-ment 2, assist the Emergency Coordinator in making any necessary protective action recommendations, in accordance with EIP-ZZ-
.00212, Protective Action Recommendations.
4.6.1 To make a Protective Action Recommendation, the Emergency Coordinator will need the fol-lowing information:
4.6.1.1 Projected Whole Body Dose Rate from Attach-ment 2, 4G.
4.6.1.2 Projecte[1. Child Thyroid Dose Rate from At-tachment 2, 4I.
~
4.6.1.3 Plume Travel Time and Affectsd Sectors; the Plume Travel Time can be determined utiliz-ing Table 6.1.
The Affected Sectors can be determined utilizing Figure 6.1.
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4.6.1.3.1 Plot the Plume Centerline on Figure 6.1 by plotting a point on the 10 mile radius 180 deg~ree from the direction the wind is from.
Draw a line from that point to the plant at' center of radius circle.
4.6.1.3.2 Protective Actions should be recommended for the sector in which the centerline lays and the adjacent sectors on each side.
5.0 F_INAL CONDITIONS 5.1 All. Initial Dose Assessments are completed.
5.2 Any subsequent Dose Assessments are being i
performed in accordan<:e with EIP-ZZ-02211.
6.0 QA RECORDS 6."1 Completed Dose Assessment Worksheet, Attach-t ment 2.
7.0 REFERENCES
.M..
7.1 EIP-ZZ-02211, Intermediate Phase and Subse-VN quant Dose Assessment
.a 8.0 ATTACHMENTS i
8.1 TABLES l
8.1.1 Table 1.1, Determination of PASQUILL Stabil-ity Class Using DELTA-T 9.1.2 Table 1.2, Determination of PASQUILL Stabil-ity-Class Using Wind Deviations 8.1.3 Ta.ble 1.3, Xp/Q Values 8.1.4 Table 2.1, Determination of Unit Vent Flow Rates 8.1.5*
Table 3.1, Sensitivity Correction Factor 8.1.6*
Table 3.2, Whols Body Dose Rate Factor T
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Table ' 3.3, Child Thyroid /Whole Body Ratio 1
8.1.8*
Table 5.1, Contingency Release Rate Table 8.1.9 Table 6.1, Plume Travel Time 8.1.10 Figure 6.1, 10-Mile Emergency Planning Zone 8.2, Dose Assessment Worksheet k
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TABLE 1.1 DETERMINATION OF PASQUILL STABILITY CLASS USING DELTA-T STABILITY CLASS i
DELTA-T (603-10m) 'C DELTA-T (90m-10m) *C A - Estres ly Unscable a T I.95 0
A T i -1.50 3 - Moderately Unstable
.95 < a T 1.85 C - Slightly Unstable
-1.50 < a T S -1.35
-D - Jeutral
.85 < a T 1.75
-1.35 < a T 1--1.20
.75 < a T "
.25
-1.20 < a T S
.40 E - Slightly stable
.25 < a T 1.75
.40 < a T 1 1.20 J:
F - Moderately Stable
.75 < a T 5 2.00 1.20 < a T 1 3.20 I
'G - Extremely stable 2.00 < A T 3.20 < a T TABLE 1.2 DETERMINATION OF PASQUILL STABILITY f*' AcS USING WIND DEVIATION STABILITY CLASS WIND DEVIATION - SICMA THETA (DECREES)
A - F.xtremely Upstable -
3 - Moderately Unstable SICHA THETA E 22.5 22.5 > SIGMA THETA 2 17.5 C - Slightly Unstaole 17.5 > SICMA THETA 1 12.5 D - Neutral 12.5 > SIGNA TROIA E 7.5 g_gs E - Slightly stable F - Moderately Stabla 7.5 > -SICMA THETA 1 3.8 C
Extremely Stabla 3,8 >-' SIGMA THETA 1 2.1 2.1 > SICMA THETA
- TABLE 1.3 E
3 Q VALUES (see-sph/a )
STABILITY CLASS DISTANCE A
B C
D E
F G
I EAR i
4.4E-6 2.6E*5 7.2E-5 2.5E-4 4.7E-4 1.1E-3 2.5E-3 1
2 Miles 1.2E-6 2.0E-6 1.5E-5 5.1E-5 8.9E-5 2.4E-4 6.0E-4
?
5 Miles 5.5E-7 7.1E-7 2.9E-6 1.3E-5 2.8E-5 7.2E-5 1.8E-4
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10 Miles 3.6E-7 4.2E-7 9.9E 4.9E-6 1.2E-5 3.2E-5 8.3E-3 D
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DETERMINATION OF UNIT VENT FLOW RATR u.
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EXilAUST FAN' EXHAUST SYSTEN
' TSIGN RATED' NORMAL FAN LINEUPS TAG ID ON OFF 1 FUEL SLDG.
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TOTAL 3.1227 2.64E7 2.03E7 3.8FET i
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0 L
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- TABLE 3.1 I
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SENSITIVITY CORRECTION FACTOR TABLE e
STEAM EFFLUENT WIDE RANOE CAS McKITOR TAG ID AND RANGE __ MONITO GT-iE-21B GT-RE-215 GT-RE-21B AB-RE-121 or GT-RE-103 of GT-RE-lCB or GT-RE-108 AB-F.E-111
- ACCIDEhT TYPE AB-RE-113 LOW RANGE MID-RANGE HIGH RANGE 7g FUEL RaNDLING ACCIDENT-REACTOR BLDG.
1.04.
9.89 E-L 9.94 E-1 FUEL HANDLING ACCIDENT - FUEL ELDC. -
1.04 9.89 E-1 9.94 E-1 MAIN STEAM BREAK 1.21 1.61 1.64
[
CVCS LLTDOWN LINE RUPTURE 1.21 1.61 1.64 WASTE GAS DECAY TANK RUPTURE 1.53 l' 05 1.09 LIQUID RADWASTE TANK FAILURE 2.16 6.12 5.33 ROD CLUSTER C0hTROL ASSEMBLY 2.63 6.46 6.50 LOCKED ROTOR ACCIDDIT S/G TUBE RUPTURE 2.63 6.44 6.48 LOSS OF COOLANT ACCIDEhT' 1.21 1461 1.64 ATMOSPHERIC RELEASE VALVE DUMP (Later)
(Later)
(Later)
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WHOLE BODY DOSE RATE FACTOR AND 7, 7 '
CHILD THYROID /WBOLE BODY RATIO TABLES
- TABLE 3.2
- TABLE 3.3 1
ACCIDENT TYPE DOSE RATE CEILD THYROID /
FACTOR WHOLE BODY (mrem-a3/uCi-hr)
RATIO FUEL HANDLING ACCIDENT INSIDE REACTOR BLDC.
FUEL HANDLING ACCIDENT INSIDE FUEL HANDLING BLDG, 3.24 E-2 3.1 El 3.24 E-2 3.0 E0 MAIN STEAM BREAK CVCS LETDOWN LINE RUPTURE 3.94 E-1 9.3 E2 2_
WASTE GAS DECAY TANK RUPTURE 2.78 E-2 1.0 El LIQUID RADWASTE TANK FAILURE 4.57 E-1 1.8 E-1 S/G TUBE RUPTURE 6.74 E-1 1.5 E-1 EOD CLUSTER CONTROL ASSEMBLY EJECTION 3.94 E-1 1.7 E-1 LOCKED ROTOR ACCIDENT 5.45 E-1 3.1 E-1 LOSS OF COOLANT ACCIDENT 5.45 E-1 3.4 E-1 ATMOSPHERIC RELEASZ VALVE DUMP (Later)
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TABLE 6.1 PLUME TRAVEL TIP_.E (M NUTES) TABLE t
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- WIND SPEED-DISTANCE (MILES).
(meh)
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_ DOSE ASSESSMENT WORKSHETT DATT TIME i.
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EIP-ZZ-02211 September 30, 1983 Revision 0-CALLAWAY FLANT EMERGENCY PLAN IMPLEMENTING PROCEDURE EIP-ZZ-02211 i
l INTERMEDIATE PHASE AND SUBSEQUENT DOSE AS$ESSMENT i-RESP DEPT. b re_su [#s.hreaa4c.t PREPARED BY Mwee 64-ogre,m
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APPROVED BY w -[
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2 DATE ISSUED IC l_Q D
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This procedure contains tt a following:
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' s?g DEFICIENC'i LIST I'
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Section Deficiency Description Constraints
! Stability class based on-
! None
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! justified.-
. Steps 1.4, 3.3
!. Subject to change upon purchase! None Table 1.4, 1.5-I and installation of new
!z
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!. Analog Strip Recorders not
! None Step 1.1
! installed in Control Room
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! Sentitivity fac*. ors are based
! None
! upon the Manufacturer's Table 3.1
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! factors may vary based upon
! installation and actual
! Calibration Factors (h. Table 3.2andI Whole Body Dose Rate Factors'
! None
~) 3. 3
! and Child Thyroid Whole Body
! Ratio are subject to change I based upon the outcome of I
! a Verification of Technical
! Basis 4.2.5 and
! Sensitivity Factors have to
! None Attachment ?
! be obtained from the
! manufacturer and the isotopic I mixture of the release has
! to be supplied by Bechtel 1
!-QS-22 not approved
! None
{.
I 4.2.7
. Will be completed upon
! None 1
! completion of Verificatior
! of Technical Basis and
! Reformatting 2
Table 10.1
! Populations in listed
! None
! population centers are
! not available at
! this time
. g'"; Tables 3.1,
! Calculations have to be
! None 3.2 and 3.3' I made for loss of I
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w Table of Contents Section Page Number
1.0 Purpose and Scope
1 2.0 Responsibilities 1
.- 3. 0 Initiating Conditions 1
4.0 Procedure 2
5.0 Final Ccnditions 8
6.0
. Records 8
,7. 0 References 9
8.0 Attachments 9
. - Determination of Meteorological Dispersion Factors (X/Q) and Plume Dimensions - Determination of Release Pathway and Effluent h(~ ) Attachment 3 -' Dose Ratie Projection Based on Noble Gas Monit
~
Flow Rates
- - Dose Rate Projection Based known on Effluent Isotopic Release Rate - Estimation of-Dose Rate Based on Field Monitoring Data - Estimation of Dcse Rate Based on Isotopic Analysis of Environmental Samples - Dose Rate Projaction Based on Steam Effluent Monitors
? - Dose Rate Projection Based on Isotopic Analysis of Containment Air Samples
- - Dose Projection / Assessment for Particulate Activity 0 - Integrated Dose Assessment
' Attachment 11 - Contingency calculations
-- 2 - Dose Assessment Summary Sheet 3 - Radiological Release Accident Flow Chart E
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.:, y INTERMEDIATE PHASE AND SUBSEQUENT DOSE ASSESSMENT 1.0 PURPOSE AND SCOPE The purpose of this procedure is to provide the methods for determining projected off-site dose rates during the intermediate phase of an emergency and for any dose.as-sessments which'are beyond the scope of EIP-ZZ-01211, Initial Dose Assessment.
This procedure is a backup-aeans of dose assess-ment when the Radioactive Release Informa-tion System (RRIS) is not available.
This procedure'also provides guidance in direct-
~ ing field monitoring team activities.
2.0
~ RESPONSIBILITIES 2.1 The Health Physics Coordinator is initially responsible for all actions contained in this procedure and giving directions to the Dose Assessment Coordinator upon his e,
arrival.
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2.2
.The Dose nssessment Coordinator is responsi-ble for the dose assessment and field moni-toring activities as outlined in this procedure.
The Dose Assessment Coordinator shall ensure that the dose projection calcu-lations are updated as needed, based on changes in radiological and meteorological data.
2.3 The R'diological Assessment Coordinator a
shall assume.the overall responsibility of the activities of this proc.edure, upon. acti-vation of the EOF.
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3.0 INITIATING CONDITIONS This procedure shall be initiated when a release of radioactive material has occured or has the potential to occur, the RRIS is not available and either of the following conditions exist.
3.1 An Emergency has been declared with the classification of ALERT or higher and dose assment is-beyond the scope of EIP-ZZ-01211.
-3.2 As determined by the Health Physics Coordi-nator, Radiological Assessment Coordinator, Emergency Coordinator or the Recovery Manager.
4.0 PROCEDURE The Health Physics Coordinator or Dose As-J.
sessment Coordinator shall perform dose as-sessment in accordance with this procedure when any of the initiating conditions (3.0) occur. 3, Radiological Release Accident Flow Chart, provides guidance for determining which activities should be E.- /
initiated.
This procedure is arranged in v
the most likely order that the activities will be implemented.
4.1 METEOROLOGICAL DISPERSION FACTOR (X/Q)
Dr Ir.,xMINATION
- i The Health Physics Coordinator / Dose Assess-l ment Caordinator shall determine 'the Meteor > logical Dispersion Factors (X/Q),
i Plume Dimensions and Affected Sectors using
', Determination of Meteorologi-6
- cal Dispersion Factors (X/Q) and Plume Dimensions, utilizing available meteorologi-l:
cal equipment.
Record the appropriate in-l>
formation on Attachment 12, Dose Assessment l;-
-Summary Sheet.
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si 4.2 DETERMINATION OF PROJECTED DOSE RATES I
The Health Physics Coordinator / Dose Assess-i ment Coordinator shall determine the Projected or Measured Whole Body Dose Rate and the Projected or Measured Child Thyroid Dose R' ate at the Exclusion Area Boundary (EAB), 2-mile, S-mile, and 10-mile zones or
.any other selected distances requested and record the results on Attachment 12, Dose Assecament Summary Sheet, using one of the following attachments:
NOTE The starting time for which l'
the data is applicable shall i
be noted as the " time" on the forms, in the attach-ments, where indicated.
(near performed by).
4.2.l* - Dose Rate Projection Based On Noble Gas Monitors This attachment provides a fast method to project the offsite Whole Body and Child
.t Thyroid Dose Rates, utilizing data -from the Wide Range Noble Gas Monitors in the Radia-tion Monitoring _ System.. This attachment should be used initially, if possible, until further detailed calculations or sampling
-can be performed.
4 2.2 - Dose Rate Projection Based On Effluent Isotopic Analysis
.This attachment provides the method to pro-ject Whole Body and Child Thyroid Dose Rates utilizing isotopic analysis of samples from the release pathway..
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0 4.2.3 - Estimation Of Dose Rate Based On Field Monitoring Team Data This attachment provides the methods for es-timating Whole Body'and Child Thyroid dose rates at various locations utilizing actual
. field measurements taken by the Field Moni-toring Teams at one location.
i 4.2.4 - Estimation Of Dose Rate Based On Isotopic Analysis Of Environmental Sam-ples.
. This attachment provides the methods for es.
timating the Whole Body and Child Thyroid Dose Rates, utilizing isotopic analysis of air saaples taken by Field Monitoring Teams.
4.2.5* - Dose Rate Projection Based On.
Steam Effluent Monitors This attachment provides the method for projecting offsite Whole Body and Child Thyroid dose rates, utilizing data from the Effluent Steam Monitors in the Radiation hl,y.
Monitoring System, for releases via the
'E-)
Secondary Side Atmospheric Relief Valves and Auxiliary Feedwater Turbine Discharge.
4.2.6 - Dose Rate Projection Based On Isotopic Analysis Of Containment Air Samples.
This attachment provides a method of projecting offsite Whole Body and Child Thyroid dose _ rates, utilizing data from Con-tainment Air _ Samples for unmonitored leakage r
from containment.-
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4.2.7* 1 - Contingency Calculations
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This attachment provides a method to project i
offsite Whole Body and Child Thyroid doses,.
utilizing conservative accident assumptions, f
in the event that no data is available from l~
the Radiation Monitoring System.
As it is unlikely that actual accident conditions e
1-would be similar.to those postulated, this 1
attachment should only be used until other i
data is available.
t 4.3 SURFACE CONT /MINATION DETERMINATION
~
I 4.3.1 The Health Physics Coordinator / Dose Assess-i ment Coordinator shall determine the projected or measured surface contamination a
levels and dose ratos from contaminated sur-faces using Attachment 9, Dose Projection / Assessment for Particulate Activ-ity, and record the results on Attachment 12, Dose Assessment Summary Sheet.
4.4 INHALATION / INGESTION DOSE COMMITMENT DETER-s.
MINATION
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- C f' 4.4.1 When isotopic analysis of environmental air samples taken by Field Monitoring Teams becomes available, the Health Physics
?
Coordinator / Dose Assessment Coordinator shall determine the critical Organ, the Critical Population Segment and the Inhala-tion Dose Commitment for the general public, from inhalation of particulate radioactiv-ity, using Attachment 9, Dese
' Projection / Assessment of Particulate Activ-
[
ity,.and record on Attachment 12, Dose As-1 sessment Summary Sheet.
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s 4.4.2 When isotopic analysis of environmental sam-ples (soil, vegetation, milk, drinking L.
water, foodstuffs, etc.) become available, the Health Physics Coordinator / Dose Assess-ment Coordinator shall determine the Criti-cal Organ, Critical Population. Segment and the Ingestion Dose Commitment for the gen-
.eral public from ingestion of contaminated
. milk, drinking water or foodstuffs, using, Dose Projection / Assessment of Particulate Activity.
Record the surface contamination levels, milk-or drinking water contamination levels, foodstuff con::amina-tion Levels, pasture grass contamination and the ingestion dose commitment on Attachment 12, Dose Assessment Summary Sheet.
4.5 PROTECTIVE ACTION RECOMMENDATIONS 4.5.1 The Health Physics Coordinator / Radiological Assessment Coordinator, using Attachment 12, Dose Assessment Summary Sheet, shall assist the Emergency Coordinator / Recovery Manager in making Protective Action Recommendations.
[l*t~
4.6 FIELD MONITORING TEAM DIRECTIONS
(. '
The Health Physics Coordinator / Radiological Assessment Coordinator shall direct Field Monitoring Team activity as follows:
4.6.1 Direct Field Monitoring Team (s) be formed per EIP-ZZ-00220, Emergency' Team Formation.
4.6.2 Direct the Dose Assessment Coordinator to:
a 4.6.2.1 Implement EIP-ZZ-00223, Field Monitoring.
4.6.2.2 Brief the Radiological Controls Coordinator J.
on offsite radiological conditions.
4.6.2.3 Determine the affected sectors to which L
Field Monitoring Teams should be dispatched.
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4.6.2.4 Instruct the Field Team Communicator to es-tablish communications with the Field Moni-toring Teams and dispatch teams to the af-
'fected sectors.
Provide the following to the Field Team Communicator:
f 4.6.2.4.1' Direct teams to don protective clothing, if warranted.
NOTE Protective clothing should.
not be used unless the gen-eral public has been evacu-ated or issued instructions.
4.6.2.4.2 Field Monitoring Locations to be sampled.
Locations are designated in EIP-ZZ-00223, Field Monitoring, Attachment 5, Field Moni-toring Sampling Location.
NOTE The initial sampling loca-tion should be that sampling location at the EAB nearest to the-plume centerline, in order to verify the jg emergency classification.
Subsequent locations should
^
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be chosen based on factors such as topographical feat-ures and wind direction changes, in order to locate the plume centerline (highest concentration).
Major population centers l
should be monitored as precautionary measure. a i:
H 1
4.6.2.4.3 The type of samples to be collected (i.e.,
air, water, vegetation, soil, etc).
4.6.2.4.4 The type of ' measurements to be taken (i.e.,
dose rate, count rate, I-131 analysis, etc).
4.6.2.3.5 Locations to which environmental samples shall be delivered if other than the EOF.
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1' 4.6.2.3.6 Debriefing instructicns.
4.7 CUMULATIVE EXPOSURE AND TOTAL POPUI.ATION EX-POSURE DETERMINATION 4.7.1 The Health Physics Coordinator / Dose Assess-
]
ment Coordinator.shall track the Cumulative Whole Body Exposure and Cumulative Child Thyroid Exposure in each affected sector in the EAB, 2 mile, 5 mile and 10 mile zones 4"
using Attachment 10, Integrated Doce Assess-ment, and record the results on the Dose As-Passment Status Board. -If requested, the Total Population Whole Body or Child Thyroid Exposure will also be calculated.
4.8 STATUS BOARD 4.8 The Health Physics Coordinator / Dose Assess-ment Coordinator shall ensure that all sig-
.+
~
nificant dose assessment information is recorded on the Dose Assessment Status Board, and updated as needed.
5.0 FINAL CONDITIONS fs 5.1 All necessary dose assessmenti calculations have been performed.-
5.2 All records have been handled in accordance with EIP-ZZ-00250, Communications and Records Keeping.
6.0 RECORDS 6.1 QA RECORDS Completed tables from 6.1.1, Determination of Meteorologi-cal Dispersion Factors (X/Q) and Plume Dimensions.
6.1.2, Dose Rate Projection Based on Noble Gas Monitors
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6.1.3, Dose Rate Projection Based on Known Effluent Isotopic Release Rates 6.1.4, Estimation of Dose Rate Based on Field f.onitoring Team Data 6.1.5, Estimation of Dose Rate Based l
on Isotopic Analysis of Environmental Sam-i ples f
.631.6, Dose Rate Projecticn Based on Steam Effluent Monitors 6.1.7, Dose Rate Projection Based on i
. Isotopic Analysis of Containment Air Samples 6.1.8, Dose Projection / Assessment for Particulate Activity 6.1.9 0, Integrated Dose Assessment
'6.1.10 1, Contingency Calculations 6.1.11 2, Dose Assessment Summary Sheet Cj;
7.0 REFERENCES
\\ *..)
7.1 USNRC Regulatory Guide 1.109, " Calculation of. Annual Doses to Man from Routine Releases of Reactor Effluents for the purposes of Evaluating Compliance with 10CFR50, Appendix I, Revision 1, October 1977."
7.2 USNRC Regulatory Guide 1.145, " Atmospheric Dispersion Models for Potential Accident Consequence Assessments at Nuclear Power Plants, Revision 1."
7.3 USNRC Regulatory Guide 1.23, " Meteorological ProcJrams in Support of Nuclear Power Plants, Revision 1."
7.4 SNUPPS, Final Safety Analysis Report, Chap-ters 2, 7, 11, 15 and 15A.
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7.5 EIP-ZZ-01211, Initial Dose Assessment 8.0 ATTACHMENTS, 8.1, Determination of Meteorologi-
. cal Dispersion Factors (X/Q) and Plum Dimen-sions 8.2, Determination of Release Path-way and Effluent Flow Rates 8.3~, Dose Rate Projection Based on Noble Gas Monitors 8.4, Dose Rate Projection tased on Known Effluent Isotopic Release Ratzt 8.5, Estimation of Dose Rate Based on Field. Monitoring Team Data 8.6 Attach:::ent 6, Estimation of Dose -Rate Based on Isotopic Analysis of Environmental Sam-ples 8.7, Dose, Rate Projection Based on y
.q Steam Effluent Monitors 1
- )
8.8, Dose Rate Projection Based on Isotopic Analysis Of Containment Air Samples 8.9, Dose Projection / Assessment for Particulate Activity 8.10 0, Inte. grated Dose Assessment 8.11 1, Contingency Calculations 8.12 At achment 12, Dose Assessment Summary Sheet 8.13 3, Radiological Release Accident Flow Chart It I
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0 4
J-DETERMINATION OF METEOROLOGICAL DISPERSION FACTORS (X/O)
AND PLUME DIMENSIONS This attachment provides a method for determination of meteorological dispersion factors and plume dimensions using onsite meteorological data from the Primary or Secondary Meterological Towers.
1.0 DETERMINE PASQUILL STABILITY CLASS 1.1*
Obtain the meterological data (previous 15-minute average) from the Control Room Analog Strip Recorders.
Record the primary tower'in-formation in the appropriate location on Form 1A and secondary tower-information if available.
^
1.2 If meteorological data is not$ available in the Control Room, obtain the information as follows:
1.2.1 Dispatch an individual to the shed at the pri-mary meteorological tower to relay this data from the analog strip recorder charts.
1.2.2 If information is' not availabic at the primary meteorological tower, dispatch an individual to Q'p j, the back-up shelter in the communications Equip-ment Room in the EOF to relay this data from the V.'
analog strip recorder (WIND SPEED, WIND DIREC-t TION and WIND DEVIATION (Sigma Theta) are r
available from the Secondary Meteorological Tower).
1.3 Using the DELTA-T (90m-10m) determine.the PASQUILL STABILITY CLASS from TABLE 1.2.
If DELTA-T (90m-10m) is unavailable use DELTA-T (60m-10m.)
1.4*
If either DELTA-T values are not available, 1
determine the PASQUILL' STABILITY CLASS with the
?
WIND DEVIATION (Sigma Theta) from the Secondary Tower using TABLE.1.3 The Average Wind Speed j'
must be greater than 2.24 mph to use this b
method.
i -
NOTE WIND DEVIATION (Sigma Theta) is the standard L
deviation of horizontal wind direction q
fluctuation.
bj 1.5 Record the STABILITY CLASS on FORM 1A.
H
/ _ 2.0 DETERMINATION OF X/O o
't
'.1 Using this STABILITY CLASS, determine the Xu/Q for each selected distance of interest from TAELE 1.4 and record on FORM 1A. Page 1 of 6.
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Procad. No.
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0 p
~l NOTE If a distance falls between two values, use the higher Xu/Q value.
2.2 Using the XE/Q values,' determine the METEOROLOGICAL DISPERSION FACTOR (S)-(X/Q) for each SELECTED DISTANCE by dividing.X_g by the WINDSPEED(E).
Q 2.3 Record X/Q on FORM 1A.
!~
3.0 DETERMINATION OF PLUME TRAVEL TIME AND PLUME WIDTH 3.1 Using the WIND SPEED (u), determine the PLUME TRAVEL TIME for each selected distance of interest from TABLE 1.5, and record on FORM 1A.
, NOTE If the wind speed or selected distance falls between two values,.use the lower plume travel time.
3.2 Using the STABILITY CLASS, determine the PLUME WIDTH for each selected distance of interest from TABLE 1.6 and record on FORM 1A.
NOTE The PLUME WIDTH is the perpendicular distance from the plume centerline to where the concentration is less than 10% of plume cen-pe%
terline ccacentration.
+,.}
V 3.3*
If the STABILITY CLASS is D, E, F or G and the wind speed is less than 13 mph, using the STABILITY CLASS and WIND SPEED, determine the PLUME WIDTH CORRECTION DISTANCE from TABLE 1.7 and add the PLUME WIDTH CORRECTION DISTANCE to the PLUME WIDTH.
Record on FORM 1A.
NOTE The PLUME WIDTH CORRECTION DISTANCE is added to the PLUME WIDTH to conservatively account for the combined effects of increased plume meander and building wake on diffusion in the horizontal crosswind direction under light d
wind end stable or neut.ral atmospheric j
conditions.
4.0 DETERMINATION OF AFFECTED SECTORS 4.1 Plot the Plume Centerline and PLUME WIDTH on the Status Board 10 mile EPZ map to determine affected sectors.
4.1.1 Draw the Plume Centerline by plotting the point '180 from where the wind direction is from on the 10 mile radius cir-cle, and draw a line from that point to the plant or center of radius.
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..d' 4.1.2 Plot the PLUME WIDTH from the Plume Centerline for several 4
j distances from the plant and connect the points to sketch the plume edges.
I 4.2 Record affected sectors on Attachment 12.
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TABLE 1.2 m
DETERMINATION OF PASOUILL STABillTY CLASS USING DELTA-T I
STABILITY CLASS DELTA-T (60m-10m)
- C DELTA-T (90m-10m) -'C A - Extremely Unstable aT<
.95 a T < -1.50 i
B - Moderately Unstable
.95 < a T I
.85
-1.50 < a T I -1.35 C - Slightly Unstable
.85 ( a T I
.75
-1.35 < a T T -1.20 0 - Neutral
.75 ( aT<
.25
-1.20 < a T <
.40 E - Slightly Stable
.25 < a T T
.75
.40 < a T I 1.20 F - Moderately Stable
.75 < a T < 2.00 1.20 ( a T < 3.20 G - Extremely Stable 2.00 < a T -
3.20 < a T ~
TABLE 1.3 DETERMINATION OF PA50 VILL STABILITY CLASS USING WIND DEVIATION 1
STABILITY WINO DEY!ATION - SIGMA THETA CLASS (DEGREES)
A - Extremely Unstable SIGMA THETA > 22.5 5 - Moderately Unstable
.22.5 > SIGMA THETA > 17.5 C - Slightly Unstable 17.5 > SIGMA THETA > 12.5
<.~
Q.
0 - Neutral 12.5 > SIGMA THETA 7.5 4j T - Slightly Stable 7.5 > SIGMA THETA > 3.3 F - Moderately Stable 3.8 > SIGMA THETA > 2.1 p
G - Extremely Stable 2.1 > SIGMA THETA.
- TABLE 1.4 Xu 3
Q VALUES (sec W h/m )
STABILITY CLASS H
DISTANCE A
B C
D E
F G
EA8 4.4 E-6 2.6 E-5 7.2 E-5 2.5 E-4 4.7 E-4 1.1 E-3 2.5 E-3 1 Mile 2.4 E-6 1.6 E-5 4.7 E-5 1.8 E-4 3.0 E-4 7.5 E-4 1.9 E-3 2 Miles 1.2 E-6 2.0 E-6 1.3 E-5 5.1 E-5 8.9 E-5 2.4 E-4 6.0 E-4 i
3 Miles 8.9 E-7 1.1 E-6 6.3 E-6 2.6 E-5 5.4 E-5 1.3 E-4 3.1 E-4 4 Miles 7.1 E-7 8.9 E-7 4.0 E-6 1.8 E-5 3.4 E-5 8.9 E-5 2.3 E-4 5 Miles 5.5 E-7 7.1 E-7 2.9 E-6 1.3 E-5 2.8 E-5 7.2 E-5 1.8 E-4 6 Miles 4.7 E-7 5.9 E-7. 2.2 E-6 9.8 E-6 2.2 E-5 5.4 E-5 1.4 E-4 7 Miles 4.2 E-7 5.1 E-7.1.8 E-6 8.2 E-6 1.9 E-5 4.8 E.5 1.2 E-4 8 Miles 4.0 E-7 4.7 E-7 1.4 E-f 7.4 E-6 1.6 E-:,
4 2 E-5 1.0 E-4 j9 Miles 3.7 E-7 4.6 E-7 1.2 E-6
-6.0 E-6 1.5 E-5 3.6 E-5 9.3 E-5 10 Miles 3.6 E-7 4.2 E-7 9.9 E-7 4.9 E-6 1.2 E-5 3.2 E-5 8.3 E-5
,er 12 Miles 2.7 E-7 3.2 E-7 6.8 E-7 4.2 E-6 9.5 E-6 2.6 E-5 6.5 E-5
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15 Miles 2.4 E-7 2.8 E-7 4.9 E-7 2.7 E-6 6.8 E-6 1.9 E-5 4.9 E-5 ATTACH!'ENT 1 Page j_ of 6_
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.. S PEED DISTANCE (Hiles),
j 1
(aph)
EAB 1
2 3
4 5
6 7
8 9
10
'12 15 a b['e$.
.5 90.0 120.0 240.0 360.0 480.0 600.0 720.0 840.0 960.0 1080.0 1200.0 ~
1440.0 1800.0 *
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1.0 ' 45.0 60.0 120.0
-180.0 240.0 300.0 360.0 420.0' 480.0-540.0-600.0 720.0 900.0' e
g 2).j 2.0 22.5 30.0 60.0 90.0 120.0 J 150.0 180.0
-210.0 240.0 270.0 300.0 360.0' 450.0 S.
4.0
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.15.0 30.0 45.0 60.0 75.0 90.0 105.0 120.0 135.0 150.0 180.0 225.0 i
j 6.0 7.5' 10.0 20.0 30.0
^40.0 50.0 60.0 70.0 80.0 90.0 100.0 120.0 150.0 l'
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15.0 22.5 30.0 37.5 45.0 52.5 60.0 67.5 75.0
'90.0 112.5
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10.0 4. 5, 6.0 12.0 18.0 24.0 30.0 36.0 42.0 48.0 54.0 60.0 72.0 90.0
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5.0 10.0 15.0 20.0 25.0 30.0 _
35.0 40.0 45.0 50.0 60.0' 75.0
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4.3 8.6 12.8 17.1 21.4
.25.7 30.0 34.3 38.6 42.8 51.4 64.3 16.0 2.8 3.8
' 7.' 5 11.2 15.0 18.8 22.5 26.3 30.0 33.8 37.5
' 4 5'. 0 156.3 E
18.0 2.5 3.4 6.7 10.0 13.3 16.7 20.0 23.3 26.7 30.0 33.3 40.0 50.0 a
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20.0 2.3 3.0 6.0 9.0-12.0 15.0 18.0' 21.0 24.0 27.0 30.0 3$ 0 45.0 r
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TABLE 1.6 PLUME WIDTH (MILES) TABLE g
STABILITY.
DISTANCE (Miles)
CLASS EAR 1
2 3
4 5
6 7
8 9
10 12 15
[
u
. p' A
0.31 0.40 0.80 1.07 1.33 1.73
.2.00 2.27 2.40 2.53 2.67 3.47 4.60 L
o B
0.24 0.29 0.60 0.87 1.07 1.33 1.60 1.87.
2.00 2.13 2.27 2.93 3.33 C
0.19 0.23 0.40 0.60 0.80 0.93 1.07 1.20 1.33 1.47 1.60 2.00 2.40 d
0 0.11 0.13 0.27 0.40 0.53 0.60 0.69 0.77 0.83 0.93 1.06 1.20 1.60
. j E
.0.08
-0.11 0.21 0.29 0.40 0.45 0.53 0.59 0.64 0.67 0.80 0.91 1.16
- j F
0.06
.0.07 0.13 0.21 0.27 0.31 0.37 0.40.-
0.44 0.49 0.53 0.64 0.80 Q 3-G 0.04 0.05 0.09 0.15 0.17 0.20 0.24 0.27 0.29 0.32 0.35 0.43 0.53
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. STABILITY WIND SPEED (HPH) -
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CLASS
- 0. 5 :-
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.08
.08
.08
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Procsd. No.
EIP-22-02211 Rev.
0 L
G I
DETERMINATION OF RELEASE PATEWAY AND EFFLUENT
[
FLOW RATES 1.0 RELEASE PATHWAY DETERMINATION
~
1.1 Determine the RELEASE PATHWAY for the particular monitor.of-interest using TABLE 2.1 and 2.2.
l' 2.0 EFFLUENT FLOW RATE DETERMINATION NOTE As there are no instruments'that measure the actual exhausting air flow, determine the FLOW RATE by adding the DESIGN RATED FLOW of each exhaust fan operating in the release pathway.
(
2.1 Request the Exhaust Fan Tag ID for each operating exhaust fan from the Control Room.
~
2.2 From TABLE 2.3 determine the Design Rated Flow (CFM) for each I-operating fan.
2.3 Add all Design Rated Flows for the operating fans and record on Attachment 12.
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IDENTIFICATION OF RELEASE PATilWAYS Allo DETECTORS i
Mjd 4
[d MONITOR DETECTOR TYPE OF j
RELEASE PATHWAY TAG ID H00EL H0.
DETECTOR HETii00 0F DETECT 10H'
- .1 Plant Unit Vent GT-RE-21 A R0-60-300
- Particulate Octa Scintillation
)
,,[sl.
' lodine Gaama Scintillation
~ 'lf ;.)
.;. -;[j i
Plant Unit Vent GT-RE-210 R0-52 Low Rar:ge Gas
~
Deta Scintillation t,
q R0-72-01 Hld Range Gas
. Gamina-Deta Scintillation R0-72-02 liigh Range Gas Gasma-Beta Scintillation
,9-Radwaste Vent Gil-RE-10A RD-60-300 Particulate Deta Scintillation 4
lodine Gasvaa Scintillation
.... g
.l Radwaste Vent Gil-RE-100 R0-52 Low Range Gas DeLa Scintillation p;y RD-72-01 Hid Range Gas Gaasaa-Deta Scintillation
- 1. f X A0-72-02 ffigh Range Gas Gamma-Deta Scintillation al
!i" Atmospheric Relief Valve AB-RE-Ill i, R0-12 Ganma Geiger Hueller 4! ' i jo AB-RE-Il2 l
iS AS-RE-Il3 l; N AB-RE-Il4 m
g I
I Auxiliary Feedwater FC-RE-385 RD-12 Ganma Geiger Hueller i
i I'
Turbine Di,scharge
- O Containment High GT-RE-59 RD-23 Gaama ionization Ehamber f'y Range Area Radiation GT-RE-60
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CClo3Ato ti g Aus/ Fuel Dadg edosmal Eshause
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CGno2 AID O I""I' ***
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STEAM AELIEF CC E 0 8 ^/D EFFLUENT
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BH-RE-52 f.f :,1
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aloG MAIN STEAM 7
DG 12 1.
EHcLOSURE, FUEL GLOG
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DETERMINATION Of EFFLUENT FLOW RATE _
a,
5;i
.i VENillATION EXHAUST FAN DESIGN RAiED FUEL BLDG.
A81X. BLDG.
CONTAINMENT
.Ja ",
EXilAUST SYSTEM TAG ID FLOW (CFM)
NORMAL FLOW ISOLATION ISOLATION PURGE 4
3^
1 Ilandi g B dg.
j (S [ Speed) y~l Normal Exhaust - Fast 30 32,000 Shutdown 32,000
[
i Fuel llandling Bldg.
CGG02A 9,000
-Q, ;
Emergency Exhaust CGG62B 9,000 Shutdown 9,000
' 9,000
$hutdown
~ fi Main Steam CGF03A 23,000
- .h.y Enclosure Bldg. Exhaust CGF038 73,000 23, 23, 23, M 23, M i
7 o
s j
cp q
Access Control Exhaust A
6, 5,
g
,000 6,000 6,000 6,000 6,000 S
Condenser Air CGE01A 1,000 j N Removal Flitration
-CGEGIB 1,000 1,000 1,000 1,000 1,000 r+
d t w rge Exhaust CGT01 20,000 Shutdown Shutdown Shutdown 20,000 a
g 3
Exhaust CGT02 4.000.
4.000 4,000 4.000' Shutdown fo p
66,000 56,000 43,000 82,000 si,
.E
'N Radwaste Bldg.
CGil-01A 12,000 j
txhaust CGil-OlB 12,000 lh000 M,000 12,000-
_l 0 000 i
1 NOTE DESIGN RATED FLOWS from Technical Specifications for RRIS (Radioactive Release Information System) for the C
o Standardized Nuclear Unit Power Plant System (Specification No.10466 J-314A).
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'W Procad.~No.
EIP-ZZ-02211 Rev.
0 I'
A w
DOSE RATE PROJECTION BASED ON NOBLE GAS MONITORS t
This attachment provides a fast method to project the offsite Whole Body and. Child Thyroid Dose Rates, utilizing data from the Wide Range Noble Gas Monitors in the Radiation Monitoring
. System.
This attachment should be used initially, if possible, until further detailed calculations or sampling can be performed.
1.0 DETERMINATION OF NOBLE GAS RELEASE RATE Determine (Q) - the NOBLE GAS RELEASE' RATE (Ci/sec),
follows.
as 1.1
~
Record the Noble Gas Effluent MONITOR TAG ID, RANGE (LOW, MID, HIGH) and READING (uCi/cc) on FORM 3A.
u 1.2 Record the RELEASE PAL \\Y and the EFFLUENT FLOW RATE (CFM)
['
- from Attachment 2, Determination of Release Pathway and Ef-fluent Flow Rates on FORM 3A.
l.3 Determine the SENSITIVITY FACTOR for the particular NOBLE GAS MONITOR and the ACCIDENT TYPE from TABLE 3.1 and record on FORM 3A.
hO
' Q 1.4 Complete the' calculation on FORM 3'A to determine the NOBLE GAS RELEASE RATE.
NOTE An isotopic mix of various noble gases is as-sumed in each of the accident classifications.
If no accident classification is possible, use the most conservative classification - MAIN STEAM BREAK.
2.0 DETERMINATION OF PROJECTED WHOLE BODY DOSE RATE Using the NOBLE GAS RELEASE RATE, determine the PROJECTED WHOLE P
BODY DOSE RATE for each selected distance of interest using the following data and FORM 3A.
2.1 Record the METEOROLOGICAL DISPERSION FACTOR (S)-(X/Q) from At-tachment 1, Determination of Meteorological Dispersion Factor (s) (X/Q) and Plume Dimensions, for each selected distance of interest and record on FORM 3A.
2.2 Determine the WHOLE BODY DOSE FACTOR, using the ACCIDENT TYPE and TABLE 3.2 and record on FORM 3A.
f
~
2.3 Complete the calculation on FORM 3A.
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o
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3.0 DETERMINATIO3 OF THE PROJECTED CHILD THYROID DOSE RATE l
-Using the PROJECTED WHOLE BODY DOSE RATE (S), determine the
[
PROJECTED CHILD THYROID DOSE RATE, using the CHILD i
THYROID /WHOLE BODY RATIO and LORM 3A.
3.1 Determine the CHILD TRYROID/WHOLE BODY RATIO for the particular Accident Type, using the TABLE 3.3 and record on FORM 3A.
3.2 Complete the calculation on FORM 3A.
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SENSITIVITY FACTOR TABLE (cc/sec-CFM) t NOBLE GAS MONITOR TAG ID AND RANGE CT-RE-21B GT-RE-21B CT-RE-21B ACCIDENT TYPE r GT-R -10B or GT-RE-10B or GT-RE-10B LOW RANGE MID-RANGE HIGH RANGE FUEL HANDLING ACCIDENT-REACTOR BLDC. 4.91 E2 4.67 E2 4.69 E2 FUEL HANDLING ACCIDENT-FUEL BLDC.
4.91 E2 4.67 E2 4.69 E2 MAIN STREAM BREAK 5.70 E2 7.60 E2 7.73 E2 CVCS LETDOWN LINE RUPTURE 5.70 E2 7.60 E2
,7.73 E2 WASTE GAS DECAY TANK RUPTURE 7.20 E2 4.96 E2 5.16 E2 LIQUID RADWASTE TANK FAILURE 1.02 E3 2.89 E3 2.54 E3 ROD CLUSTER CONTROL ASSEMBLY 1.24 E3 3.05 E3 3.07 E3 LOCKED ROTOR ACCIDENT 1.24 E3 3.04 E3 3.06 E3 S/G TUBE RUPTURE =
5.70 E2 7.60 E2 7.73 E2 LOSS OF COOLANT ACCIDENT (LATER)
(LATER)
(LATER)
[f WHOLE BODY DOSE RATE FACTOR AND
\\.
CHILD THYRCID/WHOLE BODY RATIO TABLES a
I TABLE 3.2 WHOLE BODY TABLE 3.3 ACCIDENT TYPE DOSE RATE CHILD THYROID /
FACTOR WHOLE BODY (mrem-m3/uCi-hr)
RATIO i
FUEL HANDLING ACCIDENT INSIDE REACTOR BUILDING 3.24 E-2 3.1 El FUEL HANDLING ACCIDENT INSIDE FUEL HANDLING BLDC.
3.24 E-2 3.0 E0 MAIN STREAM BREAK CVCS LETDOWN LINE RUPTURE 3.94 E-1 9.3 E2 2.78 E-2 1.0 El
~
WASTE GAS DECAY TANK RUPTURE 4.57 E-1 1.8 E-1 LIQUID RADWASTE TANK FAILURE S/C TUBE RUPTURE 6.74 E-1 1.5 E-1 3.94 E-1 1.7 E-1 ROD CLUSTER CONTROL ASSEMBLY EJECTION LOCKED ROTOR ACCIDENT 5.45 E-1 3.1 E-1 LOSS OF COOLANT ACCIDENT 5.45 E-1 3.4 E-1 (LATER)
(LATER) fy."
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DOSE RATE PROJECTION BASED ON KNOWN EFFLUENT ISOTOPIC RELEASE RATE This attachment provides the methods for calculating projected Whole Body and Child Thyroid Dose Rates, when th=. effluent flow rate and the concentration of each radioactive isotope released is known.
a 1.0 nETERMINATION OF WHOLE BODY RELEASE RATE
.4 1.1 Record the EFFLUENT FLOW' RATE from Attachment 2, Determination of Rel, ease Pathway and Effluent Flow Rates -and record on FORM j
4A.
1.2 Record the known concentration of each noble gas isotope on FORM 4A.
1.3 Complete the calculation on FORM 4A.
2.0 DETERMINATION OF CHILD THYROID RELEASE RATE 2.1 Record the EFFLUENT FLOW RATE from Attachment 2, Determination of Release Pathway and Effluent Flow Rt.*.es FORM 4B.
3
' ; 2.2 Record the known concentration of each iodine isotope on FORM
.~'<
4B.
-)
~ 2.3 If the effluent sample was taken upstream of a ESF filter in the release pathway, assume a RELEASE FRACTION of 0.10 and record on FORM 4B.
Otherwise, the RELEASE FRACTION is 1.0.
2.4 Complete the calculation on FORM 4B.
3.0 DETERMINATION OF PROJECTED WHOLE BODY AND CHILD THYROID DOSE RATES Using the WHOLE BODY RELEASE DOSE RATE FACTOR, and the CHILD
- i-THYROID RELEASE DOSE MTE FACTOR, determine the PROJECTED WHOLE BODY DOSE RATE and the PROJECTED CHILD THYROID DOSE RATE for the selected distances of interest, using FORM 4A and 48.
i l
3.1 Record the METEOROLOGICAL DISPERSION FACTORS (X/Q) from Attach-ment 1, Determination of Meteorological Dispersicn Factors
.(X/Q) and Plume Dimensions, on FORM 4A and 4B.
3.2 Complete the calculations on' FORM 4A and 4B.
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v..a ESTIMATION OF DOSE RATE BASED ON FIEIB MONITCRING TEAM DATA This attachment provides the methods for estimating Whole Body and Child Thyroid Dose Rates at various locations, utilizing actual field measurements taken by the Field Monitoring Teams.
1.0" SURVEY LOCATION DATA 3 1 From the Field Monitoring Data determine the field r.:onitoring location which has the highest radiological survey readings,
.and record the data for that location on FORM 5A.
1.2 Record the METEOROLOGICAL DISPERSION FACTOR-(X/Q) for that location from Attachnent 1, Determination of Meteorological Dispersion Factor (s) (X/Q) and Plume Dimensions, on FORM SA.
4 NOTE Field Monitoring shall be performed in' accord-ance war.h EIP-ZZ-00223, Field Monitoring.
Data will be radioed by the Field Monitoring Tean(s) to the Field' Team Communicator, who shall log the dita and relay it to the ' Dose Assessment Coordinator.
r.~'; 2. 0 ESTIMATION OF WHOLE BODY AND CHILD THYROID DOSE RATES
, ' 3c
( f 2.1 Record the METEOROLOGICAL DISPERSION FACTOR (S)-(X/Q) for each SELECTED DISTANCE of interest from Attachnent 1, Determination of Meteorological Dispersion Factors (X/Q) and Plume Dimensions on FORM SA.
3.0 Determine the ESTIMATED WHOLE BODY DOSE RATE for each SELECTED DISTANCE of interest on FORM SA.
4.0 Determine tete DOSE EQUIVALENT ICDINE CORRECTION FACTOR from TABLE 5.1 and record on FORM SA.
5.0 Dietermine the ESTIMATED CHILD THYROID DOSE RATE for each SELECTED DISTANCE of interest on FORM SA.
r i
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' [;1 ESTIMATION OF DOSE RATES' BASED ON ISOTOPIC ANALYSIS OF ENVIRONMENTAL SAMPLES This attachment provides the methods for calculating Whole Body and Child Thyroid Dose Rates, utilizing the results of ISOTOPIC ANALYSIS of ENVIRONMENTAL SAMPLES taken by the field monitoring team (s).
It is probable that the Whole Body dose rate or the child Thyroid dose rate would be the limiting dose rate in the early stages of an accident.
As an accident progresses, dose
-rates to other body organs (skin, lung, bone, etc.) and age groups (infant, teen, adult) should.be calculated.
NOTE Samples collected by field moni-toring teams for use in accordance with this attachment have to be returned to the EOF Laboratory (or other designated facility with gamma spectrosco gamma analysis. py capability) for The time expended by Field Monitoring Teams in returning samples to the EOF should be taken intc consideration before instructing teams to col-g.
lect samples for use in accordance
'oN with this attachment.
N.,.!
(Specifically Ncble Gas samples).
1.0 ESTIMATION OF WHOLE BODY DOSE RATES 1.1 Record sample ID, location and time sample taken on FORM 6A.
1.2 Determine the MEASURED WHOLE BODY DOSE RATE, using the CONCEN-TRATION of each noble gas isotope and FORM 6A.
l 2.0 ESTIMATION OF CHILD THYROID DOSE RATES h
2.1 Record sample ID, location and time sample taken on FORM 6A.
,i 2.2 Determine the CHILD THYROID DOSE RATE, using the CONCENTRATION of each iodine isotope and FORM 6A.
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WHOLE BODY 00SE' RATE CALCULATION ORKSHEET '
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MEASURED i.
WHOLE BODY WHOLE BODY DOSE RATE CONCENTRATION x OOSE FACTOR
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SAMPLE 10 SAMPLE LOCATION TIME SAMPLE TAKEN i.
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CHILO THYR 010 DCSE RATE CALCUI.ATION WORKSHEET
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DOSE RATE PROJECTION BASED ON STEAM EFFLUENT MONITORS This attachment provides the method for projecting offsite
?
Whole Body and Child Thyroid Dose Rates,. utilizing data from the Effluent Steam Monitors in the Radiation Monitoring System, for releases via the Secondary Side Atmospheric Relief Valves and Auxiliary Feedwater Turbine Discharge.
l 1.0* DETERMINATION OF WHOLE BODY AND CHILD THYROID DOSE RATE 1.1 Record the Steam Effluent Monitor Reading from the RMS Cisplay
~
l in the Control Room on the Radiation Monitoring Panel on FORM 7A.
1.2 Record the METEOROLOGICAL DISPERSION FACTOR (S) (X/Q) from At-tachment 1,. Determination of Meteorological Dispersion Factor (s) (X/Q) and Plume Dimensions, on FORM 7A.
1.3 Determine the NOBLE GAS RELEASE RATE and record on FORM 7A.
1.4 Determine the PROJECTED WHOLE BODY DOSE RATE on FORM 7A.
1.5 Determine the PROJECTED CHILD THYROID DOSE RATE on FORM 7A.
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_12
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L flater)
PaitifcTto enf D TwyRoto litiR thTE CALCULAff5iI L
~
PtGJECTED 1810LE PROJECTED CHILD BOOT DOSE RATE I CHILD THYR 010/
fatem/Me)
THYRCID DOSE RATE
=
IEAS WNott 500Y RATIO (mrem /Mr) flater)
I flater) 2 flater) 3 flater) a 5
flater)
__ 5 flater) 6 flater) 7 flater) 8
- ' flater) 9 flater) a..
10 J '(1 ster) 12 flater)
._15 i
/:
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, DATE:
TIME:
. ~ PtaronMap sy:
FORM 7A ATTACHMDT 7 FACE 2 og 2 m
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l Prccad. No.
EIP-ZZ-02211 Rev.
o D
'f.;u; DOSE RATE PROJECTION BASED ON ISOTOPIC ANALYSIS OF CONTAINMENT AIR SAMPLES This attachment provides a method of projecting offsite Whole Body and Child Thyroid dose rates from unmonitored leakage from containment, utilizing isotopic analysis of containment air samples.
1.0 IDENTIFICATION OF SAMPLE, X/Q AND CONTAINMENT LEAKAGE RATE 1.1 Record sample ID on FORMS 8A and 8B.
1.2 Determine the METEOROLOGICAL DISPERSION FACTOR (S) (X/Q) for each selected distance of interest from Attachment 1, Determi-
~
nation of Meteorological Dispersion Factor (s) and Plume Dimen-sions and record on FORMS 8A,and 8B.
1.3 Determine the CONTAINMENT LEAKAGE RATE (-A13) and RECORD on FORM 8A and 8B.
NOTE If unknown, use 2.31 E-8/sec (or 0.2 percent of the containment volume / day).
-:_2.0 DETERMINATION OF PROJECTED.WHOLE BODY DOSE RATES
\\
,S M.1 Record the known CONCENTRATION of each noble gas isoptope in the containment atmosphere on FORM 8A.
^
2.2 Complete the calculations on FORM 8A.
2.3 Record PROJECTED WHOLE BODY DOSE RATES on Attachment 12.
3.0 DETERMINATION OF PROJECTED CHILD THYROID DOSE RATE 3.1 Record the known concentration of each iodine isotope in the containment atmosphere on. FORM 8B.
3.2 Complete the calculations on F'ORM 8B.
1 3.3 Record the PROJECTED -CF.ILD 13YROID DOSE RATES on Attachment 12.
61
, Page 1 of 3 l
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7.13E10 TOTAL WHOLE BO0f 00$E FACTOR C0aRECTED
/N RELEASE U ?)
(*..-apTE.).
m PR(LIECTED WHOLE B007 00$E RATE
. CALCIA.ATION WORESEET METEOROLOGICAL TOTAL WHOLE BOOT PROJECTED DISPER$108f Dost FACTut CORRECTED WHOLE B007 FACT 0q t
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- CHILD THYROID DOSE FACTOR CORRECTED RELEASE RATE CALCULATION WORKSHEET SAMPt.t ID t
3 CHILD TNYR0!D CHILO THYRoto DOSE FACTOR 10JINE CONTAINMENT 005Er^5'OR-RELEASE RgTE CotCENTRATION 1 LEAKAGE RATE I / mReis.M.ccg mRes.M
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(1/ set)
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a sec.hr I-131 1 31[14 I IIT t.56E12 I-III 1.11[13 I'l34 s.04!)1 II'!35 6.39[12 TOTAL CHILO TNTROID 00$! rACTOR CORRECTED 4ELEASE (ATE.
[
fmRevt.M* '
gleC*hr PROJECTED CMILD TMrR010 DCSE RATE
-CALCULATION WORK 5 MEET 0 :
~
TOTAL CHILD THYR 0!D DOSE FACTOR CORRECTED PROJECTED MET!OR0 LOGICAL RELEASER 4TE CHILD THfR0!D 015PER$10N (ACTOR I
(mRes.M*\\
(sec/M*)
005E RATE
=
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0 m,
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i
- DOSE PROJECTION / ASSESSMENT FOR PARTICULATE ACTIVITY This section provides the methods for projecting offsite'sur-
. face contamination levels utilizing data from the appropriate particulate effluent monitor or from isotopic analysis of an effluent particulate sample.
The method for dose assessment for the inhalation and ingestion pathways is also included.
-t This-attachment is generally to be used to deter-
?
i mine the long term affect of; the accident on the environment.
It may not be necessary to utilize this attachment for initial dose assessments.
Fnvironmental samples should be collected in ac-cordance with the Radiological Envir6nmental Moni ~
a i
toring Program (identified in QS-22).
Collection locations for sampling may be modified as deter-i mined by field surveys and/or dose projections and calculations performed in accordance with this procedure.
(This also includes section 1 of this attachment.)
1.0 DETERMINATION OF PROJECTED OFFSITE CONTAMINATION LEVELS
.1 Record.the PARTICULATE EFFLUENT-MONITOR TAG ID and EFFLUENT
' t./
PARTICULATE ACTIVITY CONCENTRATION (uci/cc) on FORM 9A.
1.2 Determine the PARTICULATE RELEASE RATE, using the EFFLUENT FLOW RATE (from Attachment 2, Determination of Release Pathway and Effluent Flow Rates) and record on FORM 9A.
1.3 Record the Meteorological Dispersion Factor (s) (X/Q) from At-tachment 1, for.each selected distance of interest.
1.4 Determine and record on FORM 9A the length of time (in hours) the release occurred.
1.5 Complete the calculations on FORM 9A snd record PROJECTED OFF-1 SITE CONTAMINATION LEVELS on Attachment 12, if actual data is not available.
t NOTE This section shall be used until such time as 1
actual field Monitoring Measurements and or analysis cf environmental sample is (are) performed.
s 2.0 DETERMINATION OF DOSE RATES FROM CONTAMINATED SURFACES 2.1 Determine the SURFACE CONTAMINATION LEVEL with isotopic i
{
analysis of. soil samples collected at field locations.
._1
.* Page 1 of 11
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EIP-ZZ-02211 1
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0 5
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o 2.2 Multiply the SURFACE CONTAMINATION LEVEL by the appropriate CONTAMINATION DOSE RATE CONVERSION FACTOR to obtain the DOSE
[
RATE FROM CONTAMINATED SURFACES and record on FORM 9B.
r.
I NOTE CONTAMINATION DOSE RATE CONVERSION FACTORS for isotopes that are not listed may be found in USNRC Regu-latory Guide 1.109.
These values must be multiplied by 1.0E12 PCi/Ci to correct for units.
2.3 Sum the DOSE RATE FROM. CONTAMINATED SUFJACES for each isotope and record the values obtained on At-tachment 12.
3.0 DETERMINATION OF INHALATION DOSE ASSESSMENT 3.1 Perform INHALATION DOSE ASSESSMENT for adults and children, utilizing the results of isotopic analysis of particulate air samples collected by Field Monitoring Teams.
These assessments are performed and recorded on FORM 9C and 9D.
NOTI This assessment should be performed after ini-O tial WHOLE BODY AND CHILD THYROID DOSE PROJEC-h]
TIONS are complete as inhalation dose equiva-J 1ents are comparatively small.
However, the m
significance of inhalation dose assessment may be increased if there is a significant holdup ~
of activity prior to release.
Inhalation dose assessment should be completed for the whole 4
body, the lung and for any organ whose inhala-tion dose factor is more restrictive (greater) than that of the lung.
3.2 Determine and record the CONCENTRATION of each iso-tope in the sample on FORM 9C and 9D.
3.3 Multiply the concentration of each isotope by the IN-HALATION DOSE FACTOR to obtain the INHALATION DOSE RATE for the whole body, lung, and restrictive organ (if any).
NOTE INHALATION DOSE FACTORS for isotopes that are not listed may be found in USNRC Regulatory Guide 1.109, Table E-7 (adult) and Table E-9 (child).
These values must be mul-tiplied by 6.55 Ell (child) or 1.42 E12 (adult) to incor-porate breathing rates and activity conversion factors i
.(6.33 E05 cc/hr for child, 1.36 E06 cc/ hour for adult, and 1.0 E06 pCi/uci).
~,
(7 'h
(
'.4 Sum these values and multiply by the Exposure Time to obtain the INHALATION DOSE COMMITMENTS.
.j Page 2 of 11
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v Procsd. No.
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0 (3-3.5 Determine the CRITICAL POPULATION SEGMENT AND THE CRITICAL OR-GAN-of the POPULATION for the ingestion pathwaf.
3.6 Record the INHALATION DOSE COMMITMENTS on Attachment 12, FORM 12A.
NOTE Not applicable to Forms 10A and i
10B 4.0
_ ASSESSMENT OF INGESTION DOSE COMMITMENTS 4.1 Ingestion dose assessment is performed and recorded on FORMS.9E, 9F, and 9G.
4.2 Record on FORM 9E, 9F an'd 9G SAMPLE TYPE, SAMPLE LOCATION, and SAMPLE ID.
4.3 Determine the appropriate DAILY INGESTION FACTOR from TABLE 9.1, Daily Ingestion Tactor and Record on FORM 9E and 9F.
NOTE FORM 9G has the DAILY INGESTION FACTOR incorporated within the IN-GESTION DOSE FACTOR.
[
NOTE INGESTION DOSE FACTORS are from
_f USNRC Regulatory Guide 1.109, Ta-ble E-11 for the Adult, Table E-13 for the. Child, and Table E-14 for the Infant, these are modified by a unit conversion factor of 1.0E5 pci/pci.
4.4 Record the ISOTOPIC CONCENTRATION of the sample on FORM 9E,~9F and 9G.
4.5 Perform the calculations on FORM 9E, 9F and 9G to obtain the isotopic INGEST:ON DOSE COMMITMENT.
4.6 Sum the ISOTOPIC DOSE COMMITMENT values to obtain the Whole Body, GI tract and critical ogran IN-GESTION DOSE COMMITMENTS for the food item.
4.7 Determine the CRITICAL POPULATION SEGMENT and CRITICAL ORGAN of the population for the ingestion pathway.
4.8 Record the INGESTION DOS-l COMMITMENTS on Attach-ment 12, FORM 12A.
rQ,. "
NOTE Not applicable to Forms 10A and 10B.
- Page 3 of 11
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0 r
..S TABLE 9.1 DAILY INGESTION FACTOR Infant Child Adult Milk (1/ day) 0.9
.9 0.85 Water.(1/ day) 0.9 1.4 2.0.
Meat / Poultry (kg/ day) 0
.11 0.3 Vegetables / Fruits (kg/ day) 0 1.44 1.6 Fish (kg/ day) 0 0.02 0.06
[%
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9 4'
(vCyg,g)
Pn0JECito 0Frsitt ContantnATION 90acsntti
=
Meteorological Projected Offstte Particulate Disperfion Release Conversion Contaninetion Aelease aate Fac. tor (I/Q)-a fine (access 4,
Distance (i.Ci/sec)
(sec/d)
(heurs)
Levels a 3.6 !.05 (Cf/m')
=
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~1 3.6 E-05 ree r
N4 3.6 f-05
.)
3.6 E-05 4
3.6 E-05 5
1.6 E-05 6
3.6 f-05 1
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. s.'.. ; -
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( ar e* * *' / hr
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/
9.40!03 (Skin)
Fe $9 8.00(03 (WS) 3.20C03 iskin)
Co 55 7.00CO3 (WS)
?.00!04 (Stin)
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Cs-134 t,ggga gvgg 4.90E03 (5 tin)
- Cs-137 4,70gD3 gvg}
2.40E03 (5 tin)04-140 2.10E03 (WR) 1.70f04 (Stin) to-140 1.50f04 (WR) 3.70f02 (5 tin)
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a 0088 FACTOs e
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1.55807 (Lunel I.
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DOSE FACTOR 150Tott fuC1/cel fmres.ee/uct mrt (WS)
(LUNO 80TMEnl taranthr et espesurel
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EXPOSURE TIME COMPl!TMENT fNeural Imreal wMOLE BOOT m
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!!JCESTION DOSE ASSESS.*.ENT WORMStfEET
- ADULT Meat /Peultry O risa d vesetani.sircuit O Sample Typer Milk Water Sample Location:
Sample IC I5OTOPIC l
DAILY l
INGESTION l
INGESTION CONCENTRATION X
INCESTION FACTOR x
DOSE FACTUR 4
DOSE COMtt!TMENT ISOtCPE (uci/ unit *l f
=
(unit /dav) imrom/uci) terem) '
t 4
8.84 (W8)
Sr-89 i
3.08E2 ftoN!!
(SOf:El 1.8623 (WB)
(W89
, 2.19E2 (GI) 10 1)
Sr-90 6
7.58E3 (SONE)
(BONEl 3.41 (WB)
(Wat 1.17 (CI)
(CT)
I-131 1.95E3 (THYROID)
(THYROID 1 7.53E-1 (Wal (W3 4
2.22 (CI)
(C:li t-133 3.63E2 (THYRCID)
(THvacIDI 1.21E2
_(W5)
(W51 2.59 (CT) fCT) es-134 1.48E2 flit TR)
(LIVEnt p;
g.
7.14 E1 tw3)
(W8t t[ 3 i1*
'M 2.11 (CI)
(CI)
Cs-137 4
1.09E2 (liver)
(LIVER) i'
- A unit equals 1 liter for milk and water and 1 <g for all others l
" aree/ day of exposure
- t s
Total Whole Sody Ingestion Dose Commitment mres Total Thyroid Ingestion Dose Comunisment mrom
)
Total CI Tract Ingestion Dose Connaitment stem Total tone Ingestion Dose Consnitsent meen Total Liver Ingestion Dose Commitment seem e
DATE:
TIME:
l,Cs' PERFORMED BY:
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roRM 9E ATTACHf!ENT 9 Page 9 of 11
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INTEGRATED DOSE ASSESSMENT This attachment provides the method to record Projected' and Measured Whole Body and Child Thyroid Dose Rates at one loca-tion for comparison and calculation of cumulative exposures.
1.0 IDENTIFICATION OF SAMPLE LOCATION 1.1 Identify thE location and record in FORM 10A.
NOTE Maintain a separate Attachment 10, Integrated Dose Assessment; for each location that Dose y
Assessment is performed.
2.0 DETERMINATION OF THE' CUMULATIVE WHOLE BODY DOSE AND CUMULA-TIVE CHILD THYROID DOSE i:
2.1 Determine the PROJECTED, ESTIMATED, or MEASURED WHOLE BODY DOSE RATES AND CHILD THYROID DOSE RATES at the location from J
one of the following attachments and record on FORM 10A.
~ - Dose Project. ion Based on Noble Gas Effluent Monitors N3 - Dose Projection Dased on Effluent Isotopic Ar.alysis
' ~/ - Estimation of Dese Rate Based on Field Monitoring Data - Estimation of Dose Rate Based on Isotopic.
Analysis of Environmental Samples - Dose Rate Projection Based on Steam Effluent Monitors - Dose Rate Projection Based on Isotopic Analysis of Containment Air Samples a
2.2 Determine the ELAPSED TIME from the start of the release to the first calculation.
The ELAPSED TIME, thereafter, is the time between subsequent calculations.
Record the ELAPSED TIME on FORM 10A.
2.3 Determine the T.STIMATED WHOLE BODY DOSE and ESTIMATED CHILD THYROID DOSE for each period of ELAPSED TIME.
2.4 Determine the total CUMULATIVE WHOLE BODY DOSE and CUMULATIVE CHILD THYROID. DOSE by adding all of the ESTIMATED WHOLE BODY DOSES and ESTIMATED CHILD THYROID DOSES for all of the elapsed time periods during the release.
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3.0 DETERMINATION OF TOTAL WHOLE BODY POPULATION' DOSE AND TOTAL CHILD THYROID POPULATION DCSE 3.1 Determine the highest CUMULATIVE WHOLE BODY DOSE in each af-facted sector in the 2-mile, 5.-mile and 10-mile zones and record on FORM 108.
1 3.2 Determine the highest CUMULATIVE CHILD THYROID DOSE in each LFFECTED SECTOR inside the 2-mile, 5-mile and 10-mile zones and record on FORM 10B.
3.3 Determine the POPULATION DENSITY of each AFFECTED SECTOR in the 2-mile, 5-mile and 10-mile zones using Figure 10-1, 10-Mile EMERGENCY PLANNING ZONE POPULATION DENSITY and record on FORM 10B.
3.3.1 Population centers are identified on TABLE 10.1, POPULATION CENTERS, with the population and distance from the plant, for j
use in determining dose to a-specific population center.
3.4 Using FORM 110B, determine the TOTAL WHOLE BODY POPULATION DOSE ~and TOTAL CHILD THYROID POPULATION DOSE in each AF'TECTED SECTOR in the 2-mile, 5-mile and 10-mile zones.
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- TABLE 10.1 POPULATION CENTERS POPULATION POPULATION DISTANCE FROM PLANT CENTERS (MI.LES )
Chamois 615 6
Fulton 12,248 Hams Praire (TBD) 10 l
7 Mokane 398 8
Morrison-234 10 Portland (TBD) 5 Readsville (TBD) 4 Rhineland 172 15 Starkenburg (TBD) 13 Steedman (TBD) 1
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CONTINGENCY CALCULATIONS F
This attachment provides a method to project offsite whole body and child thyroid doses, utilizing conservative accident assumptions, in the event that no data is available from the Radiation Monitoring System.
As it is unlikely that actual accident conditions would be similar to those postulated, this attachment should only be used until other data is available.
1.0 NOBLE GAS AND IODINE ACTIVITY RELEASED DETERMINATION 1.l*
Determine the Noble Gas Activity Released and the Iodine ac-
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tivity Released for each isotope using one of the following tables.
Table 11.1 - Loss of Coolant Accident Contingency Calculation Table 11.2 - Steam Generator Tube Rupture Contingency-Calculation Table 11.3 - Fuel Handling Accident Inside Reactor Building Contingency calculation Table 11.4 - Fuel Handling Accident Inside Fuel Handling Building Contingency Calculation 8..
Table 11.5 - Main Steam Break Contingency Calculation
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Table 11.6
~CVCS Letdown Line Rupture Outside Reactor Building Contingency Calculation Table 11.7 - Rod Cluster Control Assembly Ejection Contingency Calculation Table 11.8 - Locked Rotor Accident Contingency Calculation Table 11.9 - Waste Gas Decay Tank Rupture Contingency Calcula-tion Table 11.10- Liquid Radwaste Tank Failure Contingency Calcula-tion 1.2*
(LATER - REMAINDER OF ATTACHMENT TO BE DEVELOPEU UPON COMPLETION OF ABOVE TABLES) 5 i
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