ML20147D798
| ML20147D798 | |
| Person / Time | |
|---|---|
| Site: | Waterford  |
| Issue date: | 07/07/1987 |
| From: | LOUISIANA POWER & LIGHT CO. |
| To: | |
| Shared Package | |
| ML20147B261 | List: |
| References | |
| HP-1-230, NUDOCS 8803040168 | |
| Download: ML20147D798 (117) | |
Text
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SURVEILLANCE PROCEDURE l
OFFSITE DOSE CALCULATION MANUAL
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PORC Meeting No. bb[
Reviewed , d d f M / A _ / 7-2-fy PORC Chairsaa DATI <
l AFProved Plant Manager-Nuclear Ch ./ ) ~A. 8 )
DATE ' {
I Effective Dats !
I G803040168 800226 2 PDR ADOCK 050 l R
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) AgytW CT: HP-1-230 - Offsite Dose Calculation Manual (Rev. 6)
MRC RIvtp l The Peac has reviewed this itse sad dotarstand that a safety eeslaation was peeieseed (as app 11saisle), saaa sa Essowiewed saieey gesettea does set asist (as applicante), that a staage to the Teenetsal Speti41sattaea is set ,
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required, and that anslaar safety)#1was set adversely affected. 1 i
I cagga RSC01Ht.YDED CF PCaC 53E833 PORC NEMBE2 Foa uthoVAL OA!I RE7TW , FINN T13 No antatassase f.
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\ Pene ne.tu. u. 9 7- 26 tue u. asu, his itse is ressemoeded for approve 17 T13 10 0 This itas requirse sac /NSC review prior ta taptemesutieaf C 113 NC 1f yes, eseurs documentation supportia, review is attached, nas ttee requirse Q'A review prior ts ??!=W approval? C T13 NO I i
Pt#7 ".MfAct2.WCLLAR OttcVAL (R.tIIA to 5.4.12.1)
Comments:
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i Approved by II/.F gage M Plaat nasager-nuciaar l
WT. I .00 6 Revtsson 7 Attachment 6.1 (1 of 1) l 18 I - -
h WATERFORD 3 SES I l
PLANT OPERATING MANUAL Check Block Below [
j I CIANGE/RIVISION/DEUTION REQUEST $lPON l[lPORCS/C l Procedare No. H8- l - 21c Title or#se rs s. u e,. m o, % a www i i
Effective Data (if differest free approval date) l Ceeslote 4. 3. tad C l i
A. Change No. M/4 l[lPermanent l[lDeviaties Empiraties Data i
- 3. Revisies No. (4 !
C. Deletion l[lT13 ([lNC
, l I DESC3LIFFICW 0F CIANGE OR RIVISION l k n-u0 a LT. ,,,L A/O 5 OlL'O k tha, aAA>d L&uil. L SC
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t 1%iT U SIGNATURE 3 ORIGINATOR /7////d DATE 6/s/d 7 ( :
SAFETT/CotRtITMENT REVIIW !
Does this change, revision, or deletion -
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- 1. Change the design, description, function and/or j operation of r. system structure or composest described l in.the TSAR 7 YES No N l
- 2. Change the procedures as described in the TSAR? TES NO X
- 3. C asust tests /esperinsata act described in the TSAR 1 YES NO X
- 4. Require a change to the Technical Specifications? T13 NO X
- 5. Alter the implementation of any commitments? YES NO K If the ansvar to any of the aoove is Yes, complete and attach a 10CTR50.59 Saf,ety Evaluation.
SATITT/ Cot 91ITMENT RE,V,J /# /77&I's - DATE 6 //// ?
TECINICAL RIVII
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DATE 4 ////1 GROUP MEAD REVIIW Nf d?M i . t4 4d DATE E//8 ?
TL%RARY APPROVAL * (SRO) C ,,DATI TIMPORARY APPROVAL
- DATE
- Temporary approval sust be followed by Plant Manager /APM-N - Nuclear a,pproval within 14 days.
UNT-1-003 Revision 10 Attachment 6.7 (1 of 1) 30
.m .
j/ Survsillanca Prcezdura RP-1-230 Offsita Dosa Celculctica Manual '
R vision 6 TABLE OF CONTENTS 1.0 PURPOSE
2.0 REFERENCES
3.0 PREREQUISITES .
4.0 PRECAUTIONS AND LIMITATIONS 5.0 INITIAL CONDITIONS 6.0 MATERIAL AND TEST EQUIPMENT 7.0 ACCEPTANCE CRITERIA .
4 8.0 PROCEDURE 8.1 Site Characteristics
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' 8.2 Radiolo'gical Environmental Monitoring Program 8.3 Radiological Environmental Monitoring Interlaboratory Comparison Program 8.4 Liquid and Gaseous Radwaste Block Flow Diagram 8.5 Liquid and Gaseous Waste Sampling and Analysis 8.6 Dose Calculations Due to Liquid Effluents 8.7 Determination of Alarm / Trip Setpoints for Liquid Monitors i 8.8 Representative Sampling of Liquids 8.9 Projecting Dose for Radioactive Liquid Effluents 8.10 Dose Rate Due to Gaseous Effluents
- 8.11 Air Dose Calculations Due to Noble Gases 8.12 Dose Calculations Due to Radioiodines and Radioactive Materials in Particulate Form 8.13 Determination of Alarm / Trip Setpoints for Gaseous Monitors 8.14 Projecting Dose for Radioactive Gaseous Effluents 8.15 40CFR190 Dose Evaluation
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Survaillanca Procsdura HP-1-230 I 1
Offsits Dasa Calcalation M:nual Revision 6 ;
l 9.0 SETPOINTS 10.0 ATTACHMENTS 10.1 Annual Average Dispersion and Deposition Parameters for Areas at or Beyond the Unrestricted Area Boundary (Table 1) (1 page) 1047 Radiological Environmental Monitoring Program (Table 2)
(2 pages) 10.3 Sample Location Table (Table 3) (7 pages) 10.4 Sector and Zone Designators for Radiological Sampling and Monitoring Points (Table 4) (1 page) 10.5 REMP Sample Locations Within 2 Miles of Waterford 3 (Figure 1) (1 page) 10.6 REMP_ Sample Locations Within 10 Miles of Waterford 3 (Figure 2) (1 page) 10.7 REMP Sample Locations Within 50 Miles of Waterford 3 (Figure 3) (1 page) 10.8 Liquid Waste Management System Effluent Sources and' Release Pathways and Points (Figure 4) (2 pages)
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10.9 Gaseous Effluent Sources, Gaseous Waste Management Systems Effluent Sources, and Exhaust Release Points (Figure 5)
(1 page) 10.10 Open Terrain Correction Factor (Figure 6) (1 page) 10.11 Site-Related Liquid Dose Factor (Table 5) (1 page) 10.12 Bioaccumulation Factor for Freshwater Fish and Invertebrate and Ingestion Dose Factors for Adults (Table 6) (5 pages) 10.13 Dose Factors for Exposure to a Semi-Infinite Cloud of Noble l
Gases (Table 7) (1 page) 10.14 Inhalation Dose Factors for Child (Table 8) (3 pages) 10.15 Values of L-Theta-V (Table 9) (5 pages) l 10.16 Pathway Dose Factors Due to Radionuclides Other Than Noble Gases, R (Table 10) (19 pages) 10.17 Relative Deposition for Ground-Level Releases (All Atmospheric Stability Classes) (Figure 7) (1 page) 2 l l
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dury:111enca Proccdura HP-1-230 Offsite Dose Calculation Manual Revision 6
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10.18 Annual Average Dispersion Parameters at or Beyond the Unrestricted Area Boundary (Table 11) (2 pages) 10.19 Annual Average Deposition Parameters for Areas at or Beyond the Unrestricted Area Boundary (Table 12) (2 pages) 10.20 ODCM Technical Specifications Cross-Reference (Table 13)
(1 page)
LIST OF EFFECTIVE PAGES Title Revision 6 1-103 Revision 6 G M (
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Survaillanca Procsdura HP-1-230 Offsits Dsse Calculction Mr.nual Rsvisica 6
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1.0 PURPOSE 1.1 This document provides: (1) the general characteristics of the Waterford 3 site; (2) the detailed Radiological Environmental Moni-toring Program (REMP); (3) the description of the Radiological Environmental Monitoring Interlaboratory Comparison Program; (4) the liquid and gaseous radwaste block flow diagram; (5) the Radioactive Liquid and Gaseous Waste Sampling and Analysis Programs; (6) the general methodology to be used to calculate dose to individuals due to releases of radioactive gaseous and liquid effluents from the Waterford 3 site; (7) the general methodology to be used to calculate effluent monitor setpoints and allowable release rates to ensure compliance with the Waterford 3 STS, 10CFR20, and 10CFR50 criteria; (8) the methodology to be used to ensure representative sampling of
. liquids; and (9) the methodology to be used to comply with 40CFR190 criteria.
1.2 The Offsite Dose Calculation Manual (ODCM) follows the general models
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suggestid'by NUREG 0133 (Nov., 1978) and Regulatory Guide 1.109 (Mar., 1976). However, alternate calculation methods from those presented may be used provided the overall methodology is acceptable and consistent with regulation or provided the alternate methodology is conservative. In addition, the most up-to-date dose conversion factors and bicaccumulation factors may be substituted in lieu of ,
Regulatory Guide 1.109 values.
1.3 Actual step-by-step dose calculations will be performed by in plant ;
procedures which are consistent with the methodology presented in this document.
2.0 REFERENCES
2.1 Waterford SES Unit 3 STS (Standard Technical Specifications), Chapter 16 of Waterford 3 FSAR 1
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SurvIlllinea Prce;durr HP-1-230 Offsita Dosa Calculation Mnnuel R;visica 6 2.1.1 Technical Specification Section 3/4 11.1 2.1.2 Technical Specification Section 3/4.11.2 2.1.3 Technical Specification Section 3/4.11.4 2.1.4 Technical Specification Section 3/4.12.1 2.1.5 Technical Specification Section 3/4.12.3 2.1.6 Technical Specification Section 6.14.1 2.1.7 Technical Specification Section 6.14.2 2.1.8 HP-1-215, NRC Radiological Reporting Requirements 2.2 USNRC Regulatory Guide 1.111, Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases of Gaseous-Effluents from Light-Water-Cooled Reactors, July 1977 -~
2.3 USNRC Regulatory Guide 1.113, Estimating Aquatic Dispersion of Ef-fluents from Accidental and Routine Reactor Releases for the Purpose of Implementing Appendix I, April 1977 2.4 USNRC Regulatory Guide 1.109, Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR Part 50, Appendix I. Revision 1, October, 1977 2.5 USNRC NUREG 0133, Preparation of Radiological Effluent Technical Specifications for Nuclear Power Plants, October 1978 2.6 Title 10, Code of Federal Regulations, Parts 20, 50 and 100, Latest Edition 5
Surv illcncs Preendure HP-1-230 Offsita Dosa Csiculation Menuni Revision 6 2.7 Title 40, Code of Federal Regulations, Part 190, Latest Edition 3.0 PREREQUISITES NONE 4.'0 PRECAUTIONS AND LIMITATIONS References 2.1.6 and 2.1.7 should be satisfied at all times 5.0 INITIAL CONDITIONS Reference 2.1.6 should be satisfied prior to implementation.
6.0 MATERIAL AND TEST EQUIPMENT NONE
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7.7 ACCEPTANCE CRITERIA NONE 8.0 PROCEDURE 8.1 SITE CHARACTERISTICS Waterford 3 SES is located on the west (right descending) bank of the Mississippi River at River Mile 129.6 between Baton Rouge, Louisiana, and New Orleans, Louisiana. The site is in the north-western section of St. Charles Parish, Louisiana, near the towns of Killona and Taft.
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Survsillence Proccdurs HP-1-230 Offsite Dosa Calculation Msnunl- Rsvision 6 t
The geographic coordinates for the Waterford 3 reactor are Latitude 29' 59'142" North, and Longitude 90' 28' 16" West. Based on the UTM (Universal Transverse Mercator) Zone 15, the UTM coordinates are Northing 3,320,743 meters and Easting 743,962 meters.
The Mississippi River is'the closest prominent natural feature to Waterford 3, while other important natural features include Lac des Allemands, about 5.5 miles southwest of the site, and Lake Pontchar-train, about 7-miles northeast of the site. The land slopes gently from its high points near the Mississippi (10-15 ft. above mean sea ,
level) to extensive wetlands located 1.5 to 2.5 miles inland from the river.
Most of the man-made features are located on the narrow strip of dry land between the Mississippi River and the wetlands. Near the Waterford 3 site are several large industrial facilities, including Waterford 1 and 2 (0.4 miles northwest of the site), Little Gypsy Steam Electric Station (0.8 miles northeast of the site, across the river froa Waterford 3), Beker Industries, a fertilizer manufacturer ~~'
(0.6 miles east-southeast), Occidental Chemical Company (0.8 miles east-southeast), and Union Carbide, a chemical manufacturer (1.2 1 miles east-southeast). Louisiana Power & Light Company (LP&L) owns !
l and operates the above-mentioned steam electric stations.
s A map of the UNRESTRICTED AREA and SITE BOUNDARY for radioactive ef-fluents (Figure 5.1-3) is provided in the STS. LP&L will have full control of all activities conducted within the exclusion area boundary of the Waterford 3 site. All of the property within the designated exclusion area is owned by LP&L with the exception of the bottom lands below mean low water of the Mississippi River.
LP&L owns, in title, all surface rights within the exclusion area boundary of the plant. There is presently no intention to allow ex-pioration for subsurface minerals from points on the surface of the exclusion area.
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, Survaillenca Procidura HP-1-230 l
l Offsita Doss Celculation Mtnual Rsvision 6 l
The Mississippi River, Louisiana Highway 18, the Missouri Pacific i Railroad right-of-way, and the west (right descending) bank' levee of the Mississippi River constitute traversals of the site exclusion area as allowed by 10CFR100.3 (a). Refer to the Waterford 3 Emergency Plan Implementing Document for the arrangements which have been made to give LP&L author ~ty and control over these traversals. (Note that Louisiana Highway 3127 does traverse the SITE BOUNDARY but not the exclusion area. However, LP&L does have the authority to control this traversal in accordance with the Waterford 3 Emergency Plan Implementing Document.)
In addition to Waterford 3, there are two fossil-fueled units, Waterford SES Units 1 and 2, which are owned by LP&L and which are within the site exclusion area. The plant staff for these two units consists of about 60 people. Since this includes workers assigned to shifts, it ia a conservative estimate of the maximum number of fossil plant personnel that would be within the exclusion area at any given time. Evacuation procedures for Waterford SES Units 1 and 2 are described in the Waterford 3 Emergency Plan Implementing ~
Document.
A portion of the land within the SITE BOUNDARY is utilized for agricultural activities. Farmers presently work the land but can lie expected to actually be in the field less than 10 percent of l the time.
Fishing in the Mississippi River from the batture is a rare practice in the Waterford area. An estimated maximum of 2 people may be ex-pected to be engaged in this activity for a period less than 10 percent of the time within the exclusion area. j l
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Surveillenca Proczdura HP-1-230 Offsito Doss Calculation Manuni R vision 6 Texaco maintains a gas valve station east-southeast of the Waterford 3 SES island structure just within the radius of the exclusion area.
This valve station is automated and requires only periodic monthly maintenance involving, typically, two persons. Evacuation procedures for these maintenance workers are described in the Waterford 3 Emergency Plan Implementing Document.
The Waterford property is shown in Figure 5.1-3 of the STS and includes 3,561.3 acres. The plant area is about 48 acres and is defined as including the fenced area immediately adjacent to Waterford 3. The site area is shown in Figure 5.1-3 of the STS along with principal station structures and nearby features. The site includes only station structures and does not include any residential, recreational, or other industrial structures. There is a visitor center approximately 1.0 mile SSW of the plant.
The SITE BOUNDARIES for establishing effluent release limits along with radioactive effluent release points are given in Figure 5.1-3 of the STS: The nearest distances to the boundary line are shown in ~ ~ '
Table 1 of this procedure. The release point elevations for gaseous ;
effluents are provided in Figure 5.1-3 of the STS.
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The restricted area, defined for the purpose of controlling ingress into and egress from the site, coine' ides with the plant area which is enclosed by the plant perimeter fence.
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Survsillance Procsdura -
HP-1-230 Offsite D:sa Calculttion Minual Rsvision 6 For the purpose of establishing effluent release limits in accordance with 10CFR20 and Appendix I to 10CFR50, the concept of the restricted area, as defined above for the purpose of ingress and egress control, is not applicable. The effluent release limits are established in order to ensure that: (1) the concentrations of the radionuclides in gaseous effluents discharged from the plant stack and exhaust systems do not result in exceeding the limits outside the site boundary set forth in Table II, Column 1 of Appendix B to 10CFR20; (2) the concen-tration of radionuclides in liquid effluent at the unrestricted area boundary does not exceed the limits set forth in Tchle II, Column 2 of Appendix B to 10CFR20; and (3) the cumulative liquid and gaseous radionuclide releases do not result in exposures to individuals outside the UNRESTRICTED AREA or SITE BOUNDARY in excess of the limits set forth in Appendix I to 10CFR50, 1980 population by annular secto'rs within 5 miles of Waterford 3 can be found in the Environmental Report. Population was estimated for 1977 and projected for 1980. The methodology for estimating and projecting population is described in detail in section 6.1.4.2 of q the Environmental Report. The closest town to Waterford 3 is j Killona, 0.9 miles west-northwest. Other towns near the plant include Norco 2.5 miles east; Hahnville, 3.7 miles east-southeast; j and Laplace, 4.7 miles north. There are also smaller settlements j and homes along both banks of the river, the nearest such place to Waterford 3 being Montz, 1.0 mile northeast. !
i 8.2 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 1
This section satisfies Surveillance Requirement 4.12.1 of the Waterford 3 STS.
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l Survsillence Procadura HP-1-230 I Offsite Dosa Calculation Manus 1 Rivision 6 l Table I shows the average annual dispersion parameters for areas at I or beyond the exclusion area boundary. This table will be subject to change based on the annual land-use census results. Tables 2, 3 and 4 are the detailed Radiological Environmental Monitoring Program, the Sample Location Table, and the sector and zone designations for the sample locations, respectively. Figures 1, 2 and 3 show the sample locations for samples within 2, 10 and 50 miles of'Waterford 3, respectively.
Deviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment and other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, every effort shall be made to complete corrective action prior to the end of the next sampling period. All deviations from the sampling schedule shall be docu-mented in the Annual Radiological Environmental Operating Report. It is recognized that, at times, it may not be possible or practical to continue to obtain samples of the media of choice at the most desired ~~~
location or time. In these instances, suitable alternative media and t locations may be chosen for the particular pathway in question and :
appropriate substitutions made within 30 days in the Radiological l Environmental Monitoring Program. )
8.3 RADIOLOGICAL ENVIRONMENTAL MONITORING INTERLABORATORY COMPARISON PROGRAM l
This section satisfies Surveillance Requirement 4 12.3 of the Waterford 3 STS.
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Surveillenca Praccdura HP-1-230 Offsita Dosa Calculation M nual Rsvision 6 Quality assurance in radiological environmental sampling will be maintained through participation in the Environmental Protection Agency's Radiological Laboratory Quality Assurance Program. The summary of results will be presented in tabular form and will detail the type of analysis, the preparation (collection) date, the date the results are returned, the mean of the analyses (usually tripli-cate), the standard deviation, the date the values are released for :
information, the known value, the three standard deviation limit, and a two standard deviation /three standard deviation warning / action flag. If the sample analysis indicates results outside the three standard deviation range, then the corrective actions taken to prevent a recurrence will be documented and submitted along with all results when the Annual Radiological Environmental Operating Report is submitted.
8.4 LIQUID AND GASEOUS RADWASTE BLOCK FLOW DIAGRAM This section of the document presents the block flow diagrams for the radwaste systems. Any modifications to the radwaste systems -~
should be documented in the ODCM. In order to obtain a more detailed description of the various components, see the appropriate sections of the FSAR. Figures 4 and 5 show the existing radwaste systems.
8.5 LIQUID AND GASEOUS WASTE SAMPLING AND ANALYSIS 8.5.1 Liquids 8.5.1.1 At Waterford 3 there are four liquid holdup systems ,
that should always contain detectable activity.
These liquid radiological effluent batch release I systems include: l l
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Surveillence Prac; dura HP-1-230 Offsita D:s2 Calculation Mrnusl R;visica 6 A. Boric Acid Condensate (BAC) - four tanks B. Waste Condensate (WC) - two tanks C. Laundry Waste (LW) - two tanks D. Waste Tanks (WT) - three tanks 8.5.1.2 In addition to the tanks above, there are other holdup tanks and sumps that may contain detectable activity. These tanks and sumps include the following:
A. Regenerative Waste Tank (RWT) - one tank B. Filter Flush Tank (FFT) - one tank C. Turbine Building Industrial Waste Sump (TBIWS) -
two sumps D. Dry Cooling Tower Sumps (DCTS) - two sumps NOTE If flo'w to the sump is isolated and volume of release is known, sump discharge may be treated as a batch release rather than a continuous release.
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t Survaillenca Prce: dura HP-1-230 l
Offsite Doss Calculction Manual Ravision 6 l
8.5.1.3 If the contents of the RWI or FFT contain detectable radioactivity, no discharges from these tanks shall be made to the UNRESTRICTED AREA and the contents of these tanks should be directed to the liquid radwaste treatment system. The TBIWS shall be required to be sampled and analyzed if any of the following condi-tions exists: (1) primary to secondary leakage is occurring or (2) activity is present in the secondary system, as indicated by either the steam generator blowdown monitor or secondary sampling and analysis; or (3) activity was present in the TBIWS during the previous four weeks. If none of these situations exists, then the sampling and analysis of this stream need not be performed. Sampling and analysis of the DCTS will be required only when detectable activity exists in the Component Cooling Water System.
4.511.4 There are three additional' liquid radiological effluent "
continuous releases at Waterford 3. These include:
A. Circulating Water Discharge
- 1. Steam Generator Blowdown
- 2. Steam Generator Blowdown Heat Exchanger B. Auxilliary Component Cooling Tower (Water) pumps l (ACTP) 8.5.1.5 The Steam Generator Blowdown will be analyzed weekly via an in-line continuous composite sampler when blowdown is discharged to the waste ponds or )
cirenlating water discharge.
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Survaillanca Prcerdura HP-1-230 Offsito D:sa Calculation M:nual Rsvision 6 8.5.1.5.1 Steam generator blowdown may be routed to the waste ponds only if no detectable radioactivity is precent.
8.5.1.6 Sampling and analysis of the steam generator blowdown heat exchanger will be required only when detectable activity exists in the secondary system.
8.5.1 7 Sampling and analysis of the ACTP discharge will be required only when detectable activity exists in the Component Cooling Water System.
8.5.2 Gases 8.5.2.1 Waterford 3 gaseous radiolog'ical effluent batch releases include: i A. Waste Gas Holdup Tanks (WGHT) - three tanks
- - _ _J within the Gaseous Waste Management System (GWMS)
B. Containment Purge (CP) 8.5.2.2 Gaseous radiological effluent continuous releases should include: ,
A. The Fuel Handling Building (FHB) ventilation exhaust B. The Containment Purge (CP)
C. The Plant Stack (PS) l D. The Main Condenser Evacuation and Turbine Gland Sealing System (MCE & TGSS) i l
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Surv.illcnce Prsesdura HP-1-230 Offsito Dosa Cniculation M:nual RIvisica 6 8.5.2.3 For the MCE & TGSS, if no primary to secondary leakage exists, then only the RETS Table 4.11-2 gross beta or gamma analysis need be performed. If a primary to secondary leak exists and the release from the MCE & TGSS has not been released via the PS, then the sampling and analysis found in Table 4.11-2 must be performed. A continuous permit should be issued if detectable activity is released through the MCE and TGSS.
8.6 DOSE CALCULATIONS DUE TO LIQUID EFFLUENTS This section presents the calculated methods used for calculating liquid effluent doses in accordance with Surveillance Requirements 4.11.1.1.1, 4.11.1.2 and 4.11.1.3.1 of the Watsrford 3 Standard Technical Specifications (STS).
- . . -c NOTE The Waterford 3 Radiological Effluent Technical Specifications (RETS) are a subset of the Waterford 3 STS. For purposes of this document, RETS and STS are interchangeable.
m 8.6.1 The dose contributions foc the total time period g1I At g
should be determined by calculation at least once every 31 days and a cumulative summation of these total body and any organ doses should be maintained for each calendar quarter. l These dose contributions should be calculated for all radio-nuclides identified in liquid effluents released to the UNRESTRICTED AREA using the following expression:
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Survaillanca Preccdure HP-1-230 Offsita D:sa Calculation Mtnual Rsvision 6 n
Dgg = aty Ffgjg Ait Ctg (1) m Dt
- Ab 1Dgg (2) where:
D d
= the cumulative dose commitment to the total body or any organ (t) from the liquid effluents for each liquid release in mrem during time period (2)
Dg = the curtulative dose commitment to the total body or any organ (t) from the liquid effluents for all (1)
, time periods a
yg Atgin aren 6t g = ,the length of the 1*h time period over which the
_ , , release is made, in hours -
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=
Cg the concentration of radionuclide (i) in undiluted l liquid effluent during time period Atgfrom any liquid release, in pCi/al A
it
= the site-related ingestion dose commitment factor to the total body or any organ (t) for each identified j nuclide (i) listed in Table 4.11-1 of the Waterford 3 I STS in mrem-ml per br-pCi (Table 5) i Fg = the near field average dilution factor for Cg during l
any liquid effluent release. Defined as the ratio of the undiluted liquid waste flow during release to the average flow from the site discharge structure to site boundary receiving waters.
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Survsillenca Procsdura HP-1-230 Offsita Dosa Celculation Manusl Rsvision 6 l
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Fg = liquid radioactive waste flow discharge structure exit flow l l
The liquid radioactive waste flow is the maximum flow from the ;
effluent release, The discharge structure exit flow is the l
flow during disposal from the discharge structure release l point into the receiving water body. For radionuclides not l determined in each batch or weekly composite, the doae contri-bution to the current calendar quarter cumulative summation may be approximated by using a ratio of concentrations based on the previous monthly or quarterly composite analyses. When the current quarterly composite is analyzed, these contribu-tions will be updated as appropriate, ,
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8.6.2 Equation (2) above for calculating the dose contributions j requires the use of a dose factor, A gg, for each nuclide (i) j which embodies the dose factors and dilution factors for the points of pathway origin. The adult total body dose factor
- .and,the adult organ dose factor for each radionuclide will be -s used from Table E-11 of Regulatory Guide 1.109; thus the list contains critical organ dose factors for various organs. The dose factor is written:
A it o( w/D, + U gBFg ) DGgg (3) where:
Uy = 730 kg/yr. adult water consumption Dw = Dilution factor from near field area to potable water intake = 220 220 = avr Mississippi flow maximum discharge flow ,
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Surv2illcnca Prscedura HP-1-230 l 1
Offsite Dosa Calculction M:nual RIvision 6 ;
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A = Composite dose parameter for the total body or critical it organ (t) of an adult for nuclide (i) for all appro-priate pathways (ares /hr per pCi/ml) :
K, = Units conversion factor,1.14E5 = lospCi/pci -x 10 3 al/l + 8760hr/yr Ug = 21 kg/yr, adult fish consumption BFg = Bioaccumulation factor for nuclide (i) in fish (pCi/kg per pCi/1) from Table A-1 of Regulatory Guide 1.109 (Table 6)
DCFgg = Dose conversion factor for nuclide (i) and organ (t) for adults (ares /pci). Values are from Table E-11 of Regulatory Guide 1.109 (Table 6)
Inserting the usage factors of Regulatory Guide 1.109 as
~~~
appropriate into equation (3)~gives':
Agg = [(3.78E + 5) + (2.39E + 6)BF g] DCFgg (4)
NOTE For other liquid pathways, the appropriate dose factors will be utilized. t l
\
l l
i 1
I I
19 I
Surv2illenca Procedura HP-1-230 Offsite Dosa Calculaticn M:nusi Rsvisien 6 8.7 DETERMINATION OF ALARM / TRIP SETPOINTS FOR LIQUID MONITORS Waterford 3 STS 3.3.3.10 and 3.11.1.1 require that the liquid ef-fluent monitoring instrumentation alarm / trip setpoints be set so that the concentration of radioactive material released from the site is limited to 10CFR20, Appendix B, Table II, Column 2 for radionuclides other than dissolved or entrained noble gases. (For dissolved or entrained noble gases, the concentration shall be limited to 2E-4 pCi/ml total activity.) This section presents ne method to be used for determining setpoints in accordance with Surveillance Requirements of 4.11.1.1.2 of the Waterford 3 STS.
8.7.1 Determination of Liquid Monitor Setpoints 8.7.1.1 The calculated setpoints for the liquid effluent monitors satisfy the following equation:
n (SF) (RF) (F + f)g[1 C i (5) e= ~~
TMPC (f) where; n
IC t = the undiluted effluent gamma concentration in pCi/ml i=1 for all radionuclides (1). The value will be derived from radioanalysis of liquid effluent to be released.
This ralue will be supplied for each liquid release, i
20 i
Surv2illanca Precsdura HP-1-230 Offsita Dosa Calculetion M:nual Rsvisica 6 c= the setpoint, in pCi/ml, of the liquid effluent ,
monitor measuring the ra'dioactivity concentration in the effluent line prior to dilution and subsequent release. This setpoint represents a value which, if exceeded would result in concentrations exceeding the limits of 10CFR20, Appendix B, Table II. Column 2, to an UNRESTRICTED AREA. '
f= the liquid effluents flow as measured at the liquid effluent monitor location in gpm.
F= the dilution water flow as determined via pump curves or other apropriate measures that determine currect plant operating configuration in gpa.
l l
NOTE
~ .
F is large compared to f; .'. F + f E F. .;
SF = Safety factor to ensure that the effluent limit is not exceeded. Actual value is set by procedure (in the range 0.5 - 0.9).
RF = Release fraction allocated to this release (to be used only in situations of simultaneous or concur-rent release).
n C m C C = gjlMPC
- J E1 MP g
C J =
MC the undiluted nongamma MPC) fraction for all J nongamma radionuclides (j) 21
Survaillcnca Praccdure HP-1-230 Offsita Dosa Calculation Manual R; vision 6 C
i = undiluted gamma MPC g fraction for all ganuna C
i radionuclides (i)
MPC = Maximum Permissible Concentration for the applica-3 ble nongamma-emitting isotope (j) from 10CFR20, Appendix B, table II, column 2.
MPC g = Maximum Permissible Concentration for the applica-ble ganna-emitting isotope (i) from 10CFR20, Appendix B, table II, Column 2.
8.7.1.2 The values of Cfand C will be measured for each 3
release and the parameters for f and F will be supplied based on current plant operating configura-tions. The setpoint will be calculated in terms of
- pCi/al and the liquid effluent monitor will be adjusted as necessary to ensure that liquid releases
, are secured prior to exceeding limits specified in 10CFR20, Appendix B,-Table'II, Column 2 to an UNRESTRICTED AREA.
f Example:
Assume Cg = 3E-4 pCi/al ]
C) = 3E-4 pCi/mi i
f = 50 pm F = 750,000 gpm i
I
+
MPCg = 2E-5 pCi/ml MPC) = 3E-7 pCi/ml 22 l
l l
Surv2illenca Prccadura HP-1-230 Offsito Dosa Calculatica Minual R;visien 6 e = (f)TMPC 'TMPC = 2E-5 + 3E-7 = 1E+3 3E-4 pCi/al)(750,000 gpa) c _- ((50 gpa) (1E+3) c = 4.51E-3 pCi/al Then the SF and RF values can be applied; e.g., SF =
0.8 and RF = 1 because normally concurrent releases will not occur.
c = 3.61E-3 pCi/ml 8.8 REPRESENTATIVE SAMPLING OF LIQUIDS i
8.8.1 Prior to grab sampling liquid waste tanks, methods should be :
used to guarantee representative sampling. Large volumes of liquid waste should be mixed in as short a time as possible l
_ .and, uniformly distributed prior to sampling. To determine the -
minimum mixing time for tanks from which releases are made, '
the following tests were performed prior to initial tu e for release purposes. .
- 8.8.1.1 The tank was filled to a known volume. '
8.8.1.2 A specific quantity of a selected chemical and/or sediments was added to the tank.
8.8.1.3 Recirculation was initiated through the normal path.
8.8.1.4 Periodic santples was taken until equilibrium is reached.
23
Surv illanca Pracadura HP-1-230 Offsita Dosa Colculatica M:nual R vision 6 8.8.1.5 The time observed to completely mix the tank is used as a minimum recirculation time prior to effluent sampling. Records of the test will be maintained.
8.9 PROJECTING DOSE FOR RADIOACTIVE LIQUID EFFLUENTS Technical Specification 3.11.1.3 requires that appropriate subsystems of the liquid radwaste treatment system be used to reduce releases of radioactivity when the projected doses due to the liquid ' effluent from each reactor unit to UNRESTRICTED AREAS would exceed 0.06 mrem total body or 0.2'arem to any organ in a 31-day period. The following l calculational method is provided for performing this dose projection.
At least once every 31 days, the total dose from all liquid releases for the quarter-to-date will be divided by the number of days into the quarter and multiplied by 31. If this projected dose exceeds 0.06 area total body or 0.2 arem any organ, and the Liquid Waste Management System.has not been operating, it shall be operated, if operation would reduce the monthly projected doses below 0.06 mres -7 total body or 0.2 mrem any organ. (This is performed in accordance ;
with Surveillance Requirements 4.11.1.3.1 and 4.11.1.3.2.) i 8.10 DOSE RATE DUE TO GASEOUS EFFLUENTS i This section presents the calculational methods used for calculating
- gaseous effluent doses in accordance with Surveillance Requirements 4.11.2.1.1 and 4.11.2.1.3 of the Waterford 3 STS.
l l
24
..m_
Survaillenca Precidura HP-1-230 Offsito Dose Celculction M:nual Rsvision 6 8.10.1 Real Time Meteorological Input The instantaneous dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE BOUNDARY shall be limited to the following values:
8.10.1.1 Release rate limit for noble' gases:
n l Deb =K(X/Q)gy({1 Kg (Q)(y (6) n Des = K'(X/Q)gy g{g (Lt + 1.lMg ) (Q)(y (7) +
8.10.1.2 Relekse rate limit for Iodine-131, Iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days:
, n DOI *(XIO)&v1El Pgg (Q)gy (8) where:
D eb = the instantaneous dose rate to the total body (b) due I
- to noble gases in sector 8 for the release in mres/yr; not to exceed 500 ares /yr Des = the instantaneous dose rate to the skin (s) due to 3 noble gases in sector 0 for the release in mrem /yr; not to exceed 3000 mres/yr 4
f I
1 25
Survaillenca Precadura HP-1-230 l Offsita Dosa Celculatien Manual Rsvisien 6 i
)
DOI = the instantaneous dose rate to the child thyroid (I) for Iodine-131, Iodine-133, tritium, and radionuclides in particulate form with half-lives greater than l 8 days in sector 0 for the release in units of ares /yr; not to exceed 1500 ares /yr. l l
K' = a constant of unit conversion, IE6pci/pci. l
- K g= the total body dose factor due to gamma emissions for ;
each identified radionuclide (i) in units of ares /yr per pCi/m 3 (Table 7).
1 Lg= the skin dose factor due to beta emissions for each j identified radionuclide (i) in units of arad/yr per l pCi/m 3 (Table 7). I I
Ng= the air dose factor due to gamma emissions for each i identified radionuclide (i) in units of arad/yr per pCi/m 3 (Table 7). The constant 1.1 converts air H dose to skin dose. l j Pgg = the thyroid dose parameter for Iodine-131, Iodine-133, l tritium, and radionuclides in particulate fom with half-lives greater than 8 days (i) for the inhalation i I
pathway only, in eres/yr per pCi/m3 (Same as Ri values listed in Table 10, Page 2). The dose factor
- is based on the most restrictive group (child) and
]
most restrictive organ at the SITE BOUNDARY.
1 Pgg = (child breathing rate of 3700 m 3/yr)(DFAg) (K') where DFA g is the inhalation dose factor for each radio-nuclide from Table 8. l 1
j 26
Surv illenca Pr:ctdura HP-1-230 Offsite Dosa Celculation Manual Ravisica 6 a
1 11= summation for all identified radionuclides .
(Q)(y = the average release rate of noble gas or of Iodine-131, Iodine-133, tritium, and radionuclides in the parti-culate form with half-lives greater than 8 days (i) during the time of release from all vent releases '
(v). Value is averaged over one hour and is in units "
of pCi/sec.
(X/Q)gy = the average atmosphere dispersion factor at the SITE BOUNDARY for the time of the release in sector 6 in sec/m8 for all vent releases (v). When release time is greater than I hour, the average shall be based on obsebvations of windspeed and atmospheric stability taken at least every hour during the release.
__ . - c=
(X/Q)gy = Lgy/u where:
i
= the average wind speed determined at least hourly, '
i during time of the release, in sector 0 , as 10 '
meters above grade, in m/sec and, Lev = 2.032/r0 zj' l 2.032 = (2/n)b divided by the width in radians of a 22.S*
sector, r
0= the distance from the release to the receptor for each sector (0) in a, and provided in Table 9.
l 27 l
l
Surveillenca Preczdura HP-1-230' Offsite Doso Celculation Manual RIvisica 6 I,) = the vertical (z) standard oeviation of the materials
- in the plume, for stability class j, with a corree-tion for additional dispersion within the building wake cavity, restricted by the condition that
\
I,3 =(ol3+0.5Dj/n) 1 43 o,3 f i
furthermore, I zj
- 4 "zj I
when i
\
2 (o,2 + 0.5D /n) >Ji o,)
1 and i
D, a the maximum adjacent building height (z) either up or downwind from the release point. !
1 l 0,3 = the vertical (L) standard deviation of the material in the plume at the downwind distance for stability class J.
I .
- 28 l a
Surv;illcnca Prte: dure KP-1-230 Offalto Dosa Calculatica Manual R;visies 6 The (X/Q) values to be calculated using the above model will be adjusted to reflect the results of analysis of the straight line trajectory model (Reference 2.2, R.G. 1.111, Sections C.1.c and C.2.c). This adjustment is accomplished by multiply-ing the (X/Q) values by the correction factors, found in Figure 6, which applies to areas with terrain features similar to those at the Waterford 3 site.
I NOTE The Radioactive Effluent Release Report, to be sub-mitted within 60 days after January 1, of each year, shall include an annual summary of meteorological data collected over the previous year in the required format by Tech Spec. 6.9.1.8. The meteorological conditions concurrent with the time of release of radioactive materisis in gaseous effluents, as deter-mined by sampling frequency and measurements, shall be used for determining the gaseous pathway doses.
8.10.2 No Real Time Meteorological Input (Used in Place of Real Time) l 1
l The dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE ,
(
BOUNDARY shall be limited to the following values and expressions:
8.10.2.1 Release rate limit for noble gases:
n .
K' (X/Q)y ({g KgQgys 500eres/yr. total body (9)
D .
K' (X/Q)y g{g(L g + 1.1Mg ) Qgy5 3000erem/yr, skin (10) 29
Surveillance Pr:ctdura HP-1-230 Offsita Dose Calculctics Manual R;visies 6 8.10.2.2 Release rate limit for Iodine-131, Iodine-133, tritium and for all radionuclides in particulate form with half-lives greater than 8 days:
n .
(X/Q), ({g P it 91vi 1500 ares /yr any organ (11)
Where:
Q,=
g the average release rate of radionuclides (i) in gaseous effluent from all vent releases (v) in ici/sec (X/Q), = .1E-5 sec/m3 in the ESE sector at 0.6 mile for a 1 vent releases (v) (the highest calculated annual ave. '-e dispersion factor at the SITE BOUNDARY based on historzm ' data).
-- . - ~ ~ -
NOTE
! All radioiodines are assumed to be released in elemental form.
.I 8.11 AIR DOSE CALCULATIONS DUE TO NOBLE GASES This sectioa presents the calculational methods used for calculating 7 noble gas effluent dose to air in accordance with Surveillance Requirement 4.11.2.2 of the Waterford 3 STS.
8.11.1 Real Time Meteorological Input The air dose due to noble gases released in gaseous effluents to areas at and beycnd the SITE BOUNDARY will be determined by the following erpressions:
L I
30 e t
Surveillanc] Pr:c: dure HP-1-230 Offsito Dosa Calculttien Manual Revisi n 6 8.11.1.1 During any calendar quarter, for gamma radiation:
a m D
0y
- U'I' 2)iEl (d i) jEl (Otj ) (*/9)jev (9)ijv (12)
During any calendar quarter, for beta radiation:
n m D
gg=(1.14E2)g{g(N)){3(4t))(X/Q)jgy(Q)1)y g (13) 8.11.1.2 During any calendar year, for gamma radiation:
n m Dg
= (1.14E2) ({g (H g ) ){g (6t)) (X/Q) j0v(9)ijv (l')
During any calendar year, for beta radiation:
n m D (15) gg=(1.14E2)g{3(N)){g(At))(X/Q)jgy(Q)f)y g
where all terms are as previously defined; and Dg = the total gamma (y) air dose in sector 0 from
~~
gaseous effluents for the total time period (e.g.,
quarter or year) m jEl 0"j and not to exceed 5 mrad quarterly or 10 mrad yearly D
OS =
the total beta (S) air dose in sector 0 from gaseous effluents for the total time period (e.g., quarter or year) m jEl at) and not to exceed 10 mrad quarterly or 20 mrad yearly yr.
1.1% ' = (1E6pCi)-(8760hr.}
Ci 11
Surveillalco Prscedura HP-1-230 Offsite Dosa Calculatica Manual Revisica 6 l
(Q)g),= the average release rate of radionuclides (i) during the time of release At) for vent releases (v) ,
, At) = the length of the j' time period over which (X/Q)0v
.and Qg) , are accumulated for all gaseous releases (hours).
Mg and Ng= the ganusa and beta air dose factors (respectively) for a uniform semi-infinite cloud of radionuclide (1) (arad/yr per pCi/a )8 (Table 7)
(X/Q)jgy = the average atmospheric dispersion factor at the site boundarf for the time of the release (j), in sector (8), in sec/m8, for all vent releases (v).
i When release time is greater than one hour, the average shall be based on observations of windspeed and atmospheric stability taken at least every hour ,
during the release.
8.11.2 No Real Time Meteorological Input (Used in Place of Real Time) ,
The air dose due to noble gases released in gaseous effluents -
to areas at or beyond the SITE BOUNDARY will be determined by the following erpressions when the real time meteorological inputs are not applicable:
8.11.2.1 During any calendar quarter, for gamma radiation:
n a D (16)
= (1.14E2) (X/Q), g{i (M g ) j{g (Atj ) (Q)gy r
During any calendar quarter, for beta radiation:
n .
j Dp =.(1.14E2) (x/Q)y g{g(N)){g(At))(Q)g),
g (17)
- 32 l
- Surveillanco Pr:cedura HP-1-230 0ffsita Dos 2 Calculatits Manual Revision 6 ;
8.11.2.2 During any calendar year, for gamma radiation n a D 6 = (1.14E2) M ygjg (M g) j{g (4t )y (Q)g) , (18)- 1 During any calendar year, for beta radiation; a m
, D=(1.14E2)(x/0),g{3(N)jg(At))(Q)fjy g j (19)
! where all values are as defined previously; and D = the total. gamma (y) air dose from gaseous effluents for the total time period and not to exceed 5 stad quarterly and 10 mrad yearly.
D, a the total beta (S) air dose from gaseous effluents for the j total time period and not to exceed 10 mrad quarterly and 20 mrad yearly, t
_ Qgjy = the average release rate of radionuclides (i) in gaseous .j effluent from all vent releases (v) in pCi/sec during the ;
time period 4t). ;
(X/Q),= 1.1E-5 sec/a8 in the ESE sector at 0.6 mile for all vent l
- releases (v).
i
- 8.12 DOSE CALCULATIONS DUE TO RADIOIODINES AND RADIOACTIVE MATERIALS IN 1 PARTICULATE FORM l
This section presents the calculational methods used for calculating doses due to Iodine-131, Iodine-133, tritium, and radionuclides in a
particulate form in accordance with Surveillance Requirement 4:11.2.3 ,
of the Waterford 3 STS.
i a
i 33 I
Surveill=ce Pr:ceduro HP-1-230 Offsita Dosa Celculctirn Manual Revisica 6 8.12.1 Real Time Meteorological Input The dose to a MEMBER OF THE PUBLIC from Iodine-131, Iodine-133, tritius, and all radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents released to areas at and beyond the SITE BOUNGARY will be determined by the following expressions: ,
8.12.1.1 During any calendar quarter for age group a:
n a D
ata =(1.14E-4)gjg(Rgg,) ){3 (At)) ((W)0jv (9)ijv] (20) 8.12.1.2 During any calendar year for age group a:
n a D
0ta =(1.14E-4)g{g(Rgg,)3];(At))[(W)0jv(S)ijv] (21) where all terms are as previously defined; and
_ ,D 6ta = the cumulative dose due to Iodine-131, Iodine-133, --
tritius, and radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents, to an organ (t), of an individual (a), in sector 6, l for the total time period:
4 a !
I I at i j=1 d l not to exceed 7.5 mrem in any calendar quarter or 15 l area in any calendar year. j 4
j 1.14E-4 =.87 r.
4 i
)
i i
34 i l
l
Surveillance Pr:cadure HP-1-230 Offsite Dosa Calculaticn Manual R; vision 6 Rgg, = the dose factor from each identified radionuclide (i), for each applicable organ (t), and age group (a), in mrem /yr per pCi/m3 for the inhalation pathway and in mrem /yr per pCi/m2 -see for the food and ground plane pathway from Table 10. For sectors with real pathways within 5 miles of the plant, the values of Rg are used based on these real pathways; for sectors with no real pathways within 5 miles from the plant, Rg is used assuming that the cow grass-milk pathway exists at the 5-mile distance. (R g's were calculated using the methodology found in Reference 2.5, pages 31-36.)
W Ojv = dispersion parameter for time period (j) and release pt (v) for calculation of food pathway dose W
Ojv = (X/Q)gyj for the inhalation pathway
~ ~~
-Wjv=
O (D/Q)gy) for the food and ground plane pathway where (X/Q) q is as defined previously; and, (D/Q)gy = relative deposition for the time period (atj ), in sector (6), for release pt (v), in square meters.
When at) is greater than one hour, relative deposi-tion shall be based on observation of atmospheric stability taken at least every hour during at),
fd 0 gy (UI930vj *(0.3927)(rg )
35
Surveillance Procedura HP-1-230 offsito Dosa Calculatica Matual Revisien 6 where:
(0.3927)r0= are length of the 22.5* sector at distance r 0 I" meters.
fg= wind direction factor; equals 1 if wind in hour t is into sector 0; equals zero if wind is not into sector 6.
dev = relative deposition rate for ground-level vent release (v) at distance (re ) in sector (0) for all stability classes of interest, (seters ~1) taken from Figure 7.
i 8.12.2 No Real Time Meteorological Input (Used in Place of Real Time)
The dose to an individual from Iodine-131, Iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents released to areas at and ~~'
beyond the SITE BOUNDARY will be determined by the following ;
i expressions:
i 8.12.2.1 During any calendar quarter:
n D
ita = 1.14E-4 At I Rgg, Wy Qgy. (22) i=1 1
8.12.2.2 During any calendar year:
n Dgg, = 1.14E-4 at I Rgg,V,Qgy (23) i=1 where all terms are as previously defined; and at = the time required for the release in hours for all release's >
per quarter or per year 36 r
Surveilla:ce Prscedurs HP-1-230 Offsite Dosa C 1culatica Manual Revisien 6 I
Dgg, = the cumulative dose to an organ (t), age group (a), due to
- radionuclides (i) in gaseoas effluents; not to exceed 7.5 ares !
quarterly or 15 ares yearly H
V, a the dispersion parameter for estimating the dose to an indi-vidual at the controlling location for long tera vent releases (v) l W, = (t/Q), for the inhala' tion pathway from vent releases l (v) in sec/a 8, from Table 11 or Table 1, for the
- critical receptor.
i l
l V, = (57Q),forthefoodandgroundplanepathwaysfrom j vr.ut releases (v) in a 2, from Table 12 or Table 1, ,
i for the critical receptor.
8.13 DETERMINATION OF ALARM / TRIP SETPOINTS FOR GASEOUS MONITORS Waterford 3 STS 3.3.3.11 states that the radioactive gaseous ef-
) fluent monitoring instrumentation alara/ trip setpoint be set to l l ensure that the limits of Waterford 3 STS 3.11.2.1 are not ex- l
) ceeded. i i !
1 h
i
- 1 1 ,
I i
1
- 1 37 i l
l
Surveillance Prtendura HP-1-230 .
Offsito Dosa Calculctica Manual Revisies 6 ,
i 8.13.1 Setpoint Calculations for Gaseous Monitors The calculated high level alarm and flow termination trip setpoints will be regarded as the limiting conditions for the ,
actual setpoint adjustments. The gaseous effluent radiation r monitor setpoints are usually expressed in pCi/cc. For conservatism, an administrative safety factor SF (% of dose rate limit) will be introduced into setpoint calculation. To ;
allow for multiple sources of release from different or ccamon l release points, the allowable operating setpoints will be ,
controlled administratively by allocating a percentage of the total allowable release to each release source (RF).
8.13.2 General Gaseous Setpoint Bases Gaseous setpoints will be based on noble gas dose rate (less ,
than or equal to 500 ares /yr total body, and less than or equal to 3000 ares /yr skin). Specifically, gaseous setpoints will be based on the most limiting of the following equations: '-"
l 8.13.2.1 Total Body ;
500 aree/yr.)(RF)(SF) !
9 tb , ((X/Q),(1E6pci/pci) n l I Ei Siv i=1 n
I Q i=1 IV l
l 4
i Then, based on maximum flow rate, the monitor setpoint SN in uCi/cc can be calculated:
i l
f Q
Lb SN a F
- max 1
38 i l
Surveillance Prac dure HP-1-230
' Offsits D:s2 Calculati:n Manual Revisies 6 I
l where:
l F,,, a maximum effluent flow rate (cc/sec).
n I = summation of all nuclides considered.
i=1 I Qtb = maximum release rate all wed to give limiting total body (tb) dose of 500 mres/yr (pCi/sec). 1 Kg= the total body dose factor due to gamma emissions for each identified radionuclide (i) in units of ares /yr per pCi/m3 (Table 7).
Qgy = average release rate of isotope (i) from the release point (v) in pCi/sec.
RF = pelgase fraction allotted to release point in consideration. --
U
- (X/Q),= 1.1E-5 sec/a8 (in the ESE sector at 0.6 mile). The sector 1 with highest value of annual average atmospheric dispersion factor at the site boundary for the release point (v) in question.
i j
SF = administrative safety factor to account for uncontrollable 4 variables (sampling, monitoring errors, etc.). Usually, the SF takes on a value between 0.5-0.8.
3' I
5
Surveillanca Procedur2 MP-1-230 l' Offsite Doso Csiculatica Manual R.visica 6
, 8.13.2.2 For skin i
l (3000 aree/yr.)(RF)(SF)' (25)
S skin *
! (M),(IE6pci/pci)n, ,
i I (Lg + 1.1 M g)Qgy i=1 n
l iV
- i=1 -
i
) SN = S skin
} Faam where all terms are as defined above except:
l- Q skin = maximum release rate allowed to give limiting skin dose of f'
. 3000 ares /yr (pci/sec).
Lg= .skig dose factor due to beta emissions for each identified - -;
j radionuclide (i) in units of ares /yr per pCi/a8 (Table 7). l l
q 1.1 = conversion factor to convert from air to skin dose. f i
Mg= air dose factor due to samma emissions for identified noble ;
j sas isotope (i) in units of arad/yr per pCi/s 8 from Table 7. l i
4 i j 8.13.3 Gaseous Setpoint Calculations Based on Kr-88.
1 i i
Since the noble gas dose rate is more limiting than the !
radiciodine dose rate, the initial monitor setpoints can be l based on a conservative count rate using Kr-88 until operating j experience is accumulated. Total body dose will be more l limiting than skin dose; therefore,-the release limit would i be:
t :
1 i
! l l !
40 '
l i'
Surveillance Pr:cxdura HP-1-230 Offsita Dosa C21culati n Manual Revisica 6 (500 mrem /yr.)(RF)(SF) (24a)
(X/Q)y(le6pCi/pC1)(h-88)
Then, based on maximum flow rate, the monitor setpoint SN in pCi/cc can be calculated:
SN =
r-88 (26)
F,,,
where:
F,,,= maximum effluent flow rate (cc/sec)
NOTE l To determine whether total body or skin dose is more limiting for Kr-88, equations (24) and (25) are solved _
8I"**
- 1 **# 9 for Qgr-
' 88' Kr-88 is required t reach the total body limit of 500 mrem /yr, the total body dose is more limiting.
f S.14 FROJECTING DOSE FOR RADIOACTIVE GASEOUS EFFLUENTS Technical Specification 3.11.2.4 requires that appropriate subsystems of the Gaseous Radwaste Treatment System be used to reduce releases of radioactivity when the projected doses due to the gaseous effluent to areas at and beyond the SITE BOUNDARY would exceed, in a 31-day period, either:
0.2 mrad to air from gaerna radiation; or 0.4 mrad to air from beta radiation; or 0.3 mrem to any organ of a MEMBER OF THE PUBLIC.
41
Surveillanco Pr:c; dura HP-1-230 Offsite Dosa Calculttica Mazual Revisica 6 The following calculational method is provided for performing this dose projection.
At least once every 31 days the gamma air dose, beta air dose and the maximum organ dose for the month-to-quarter will be divided by the nunber of days into the quarter and multiplied by 31. If these projected doses exceed any of the values listed above and the Gaseous Waste Management System has not been operating, it shall be operated to reduce radioactivity levels prior to release. (This is performed in accordance with Surveillance Requirements 4.11.2.4.1 and 4.11.2.4.2.)
8.15 40CTR190 DOSE EVALUATION This section demonstrates compliance with Surveillance Requirements 4.11.4.1 and 4.11.4.2 of the Waterford 3 STS. Specifically, the dose or dose commitment to any MEMBER OF THE PUBLIC due to releases of radioactivity and radiation from uranium fuel cycle sources shall be limited to less than or equal to 25 arem to the total body or any organ (except the thyroid, which shall be limited to less than or
]
equal to 75 mrem) over 12 consecutive months.
Dose evaluations to demonstrate compliance with the above dose limits need be performed only if the quarterly doses calculated in sections 8.6, 8.10, 8.11 and 8.12 exceed twice the dose limits of STS 3.11.1.2.a. 3.11.1.2.b, 3.11.2.2.a, 3.11.2.2.b, 3.11.2.3.a or 3.11.2.3.b, respectively; i.e., quarterly doses exceeding 3 mrem to I the total body (liquid releases), 10 mrem to any organ (liquid I releases), 10 mrad gamma air dose, 20 mrad beta air dose, or 15 mrem to the thyroid or any organ from radioiodines and particulates ;
(gaseous releases). Otherwise, r.o evaluations are required. I 1
42 t
Surveillance Prac:durs HP-1-230 Offsite Dosa Calculatio2 Manual Revisita 6 For the evaluation of doses to real individuals from liquid releases, the same calculational methods as employed in section 8.6 will be used. However, more encompassing and realistic assumptions will be made concerning the dilution and ingestion of radionuclides by individuals who live and fish in the Waterford 3 area. The results of the Radiological Environmental Monitoring Program will be used in determining the realistic dose based on actual measured radio-nuclide concentrations. For the evaluation of-doses to real indivi-duals from gaseous releases, the same calculational methods as employed in sections 8.10, 8.11 and 8.12 will be used. In sections 8.10 and 8.11, the total body dose factor should be substituted for the gamma air dose factor (M g ) to determine the total body dose.
Otherwise, the same calculational sequence applies. More realistic assumptions will be made concerning the actual location of real individuals, the meteorological conditions, and the consumption of food. Data obtained from the latest land use census should be used to' determine locations for evaluating doses. The results of the Radiological Environmental Monitoring Program will be included in determining more realistic doses based on actual measured radio- ~~~
nuclide concentrations.
Cumulative dose contributions from direct radiation, from the reactor
- unit, and from Radwaste Storage Tanks shall be determined utilizing the results of routine plant perimeter surveys, TLD data, or a
] combination of both when necessary, r
! 9.0 SETPOINTS NONE I i 10.0 ATTACHMENTS !
1 10.1 Annual Average Dispersion and Deposition Parameters For Areas At or Beyond the Unrestricted Area Boundary (Table 1) 43 -
l l
Surveillance Pr:c;durs HP-1-230 Offsito Dose Cciculatica Manual Revisita 6 10.2 Radiological Environmental Monitoring Program (Table 2) 10.3 Sample Location Table (Table 3) 10.4 Sector and Zone Designators for Radiological Sampling and Monitoring Points (Table 4) 10.5 REMP Sample Locations Within 2 Miles of Waterford 3 (Figure 1) 10.6 REMP Sample Locations Within 10 Miles of Waterford 3 (Figure 2) 10.7 REMP Sample Locations Within 50 Miles of Waterford 3 (Figare 3) 10.8 Liquid Waste Management System Effluent Sources and Release pathways and Points (Figure 4) 10.9 Gaseous Effluent Sources, Gaseous Waste Management Systems Effluent Sources, and Exhaust Release Points (Figure 5) 10.10 Opea Terrain Correction Factor (Figure 6) 10.11 Site-Related Liquid Dose Factor (Table 5) 10.12 Bioaccumulation Factor for Freshwater Fish and Invertebrate and l Ingestion Dose Factors for Adults (Table 6) i i
10.13 Dose Factors for Exposure to a Semi-Infinite Cloud of Noble Gases (Table 7) 10.14 Inhalation Dose Factors for Child (Table 8) l 10.15 Values of L-Theta-V (Table 9) l 1
44 l
i s';rveillanca Prsecdura i HP-1-230 Offsite Dosa Calculctics Mainal Revisica 6 b
4 i 10.16 Pathway Dose Factors Due to Radionuclides Other Than Noble Gases, R (Table 10) !
- 10.17 Relative Deposition for Ground-Level Releases (All Atmospheric ,
Stability Classes) (Figure 7) 10.18 Annual Average Dispersion Parameters at or Beyond the Unrestricted Area Boundary (Table 11) 10.19 Annual Average Deposition Parameters for Areas at or Beyond the [
Unrestricted Area Boundary (Table 12)
, 10.20 ODCM Technical Specifications Cross-Reference (Table 13) {
t j i
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a 6
5 i
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ANNUAL AVERAGE DISPERS80N AND DEPOSITION PARAMETERS FOR AREAS AT OR BETOND THE UNRESTRICTED AREA BOUNDARY (TABLE 1) l LPR QTDFORD $1TE, U$1NG JAN - EC 1984 ET DATA - RUN 1/29/87 at0VO LEWL RELEA!!, 0 M C0ettRTED U$1NG STI.4 4RD OPO TDRAIN FACTCR$ '
SPECd1CPolMT5OFINTEREST l ELEA$t TTFE Or I!KCT!DN DISTANCE I/9 F 1/0 t/0 l ID LOCATION FROM$1TE (MILIS) (MTER$) (EC/ CUB.MtTD) (SEC/CU .ETD) (Et/ CUB.ETB) (PD $0.ETR) gg 2 g gi CAT 8. g ECAT I MILK COWS W 1.10 1770. 1.d44 1.6 44 1.4 44 4.M49 E MILK C0WS W 4.40 7081. 1.M-07 f.7L 44 7.5t48 2.5E 10 6 MILK 00AT E 3 30 5311. 4.4-07 4.347 34t47 5.7E-L0 g WETABLE SMtDEN N 1 10 1770. 5. 4 -04 5.3 44 4.7E44 1.X-9s 6 Vt ETAaLE 6ARMN NME 1.30 2092. 3.5E-04 3.2 44 3.W44 4.M49 8 WETAILI 6MtMM E 1.00 IMt. 5.7E44 5.7f 46 5.K44 1.4(48
- G WETABLE SMtMN ENE 0.90 1448. 7.M44 7.3 44 4.M44 1.M-08 6 WOETABLE 6MtMN E 3.20 5149, 4.g47 4.347 3.M47 6.2t-10 6 VEETABLE SWtMN ESE 2.30 3701. 7.K-07 7.3E -07 4.1E47 1.0E-09 8 WIETAILI 84RMN ss 2.30 3701. 4. 5 -07 4.3-07 5 2E47 , 9.2E-10 8 VEET 6MtKW $ 0.90 1444. 5.4E44 5.4 44 4.E44 2.M48 8 WET GAAMN $$W 0.90 1448. 4.9t-04 4.9 44 4.5 44' 2.0E44 AEI SARMN 0.90 4.7:44 4.7'-04 4. 44 49 6 SW 1444.
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EllREE3 Elf .0 . .i . 4.N 6 SE 3.90 4276. 2.5F-07 2.4 47 19t47 2.M-10 1 8 E31ENCES W 1.30 20t2. f.7t47 f.7 -07 E.X47 3.E49 6 ESIENCES M . 6.90 1448. 1.M44 1744 1.5-44 4.M49 ~~
$ E31ENCES W 0.90 1448. 2.E44 2.3 44 2.X46 1.1E46 8 ESIENCES M 2.00 3219. 7.E-07 7.7 -07 4.4E-07 2.K49
, 8 $171 30U O Mtf N 0.80 1287. 1.1E-05 11 45 1.M-05 3.1E-00 4 Slit IGJOMtf leIE 0.M TH. 1.K45 1.0 45 1.M-05 4.1E48 6 41 touGARY E 0.60 *H. 1.E-05 1 6 -05 1. 45 4. 2 -08 8 81 IRISMtf EE 0.M tu. .7t-05 1 7 -05 1. 45 3.9t-08 N U M
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- 9. -44 bN 22148 4.d44 h R : : Y $$E 0.00 1297. 4. -44 3. 44 2.!!48 l '
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- I 317t IDLISARY Wsw 1.50 2414 1 X44 1.3;-04 1.1E46 5.?E49 6 IITE 30ueHti W 1.00 1Mt. 1.M44 1.7 44 1.5-04 4.7E49 4 $1TE 80uGARY M 0.90 1287. 2.2t44 22 44 2.M44 8.9(49 s B IITE 80l#$4RT W 0.00 1287. 3 4-04 3.4L -04 3.M44 1.5-08 I I IITI 30L8 M tf leN 0.to 1444. 4.4E46 4.4 44 3.M4e 1448 VUT MS BUIL)!NI PWtAMETit$1 WN EIINT (ETEltSi 0.00 EP. VIO EIDIT (ETERS) 10 0
- il4ETD (ETDS) 0.00 IUILDIE E!ONT (ETRS) 41.0 EIITYELOCITT (ETDS) 0.00 IL36.RIN.CIS.EC.4p(A (ID.ETtt$) 2464.0
- EAT DIS $10N Raft (CAL /IEC) 0.0 i ALL Inoue LIwt EttAsEs.
I HP-1-230 Revision 6 Attachment 10,1 (1 of 1) i 46 i
l
Table 2
! RADIOLOGICAL ENVIROISENTAL MONITORING PCOGRAM P
Sample Type Location l Analysis Frequency Volume TLD A-2, B-1, C-1, D-2, E-1, TIE
- Quarterly N/A F-2, G-2, M-2, J-2, K-1, L-1, M-1, N-1, P-1, Q-1, R-1, A-5, B-4, D-5, E-5, F-4, G-4, M-6, P-6, Q-5, i R-6, F-9, G-9, E-15, J-15, , i E-30 i Radiciodine and APP-1, APQ-1, APG-1, Gross beta, I-131 Weekly 285m3 /wk Particulates APC-1, APE-30 isotopic Quarterly composite 3700 m 8 /qtr I
. Ground Water GWJ-1 y isotopic, M-3 Quarterly 4 liters Drinking Water
- DWG-2, DWE-5 , DWP-7 N-3 Quarterly composite Nomogeneous Gross beta, y isotopic Monthly composite 4 liters I-131 8 Semi-monthly composite Surface Water # SWG-2, SWE-5 , SWP-7 M-3 Quarterly composite Monogeneous y isotopic Monthly composite 4 liters Shoreline Sedieei.t SHWE-3, SHWJ-1 y isotopic Semi-annually 2 kilograms Milk MKE-4, MKQ-5, MQ-45, MQ-1 y isotopic, I-131 Semi-monthly / monthly 4 liters Fish FN-1, FM-2 y isotopic In season or g '500 grams i semi-annually Food Products FPP-1 y isotopic At harvest time l 500 grams Broad Leaf BIA)-1, BLB-1, BLK-15 y isotopic, I-131 Monthly 500 grams When milk sacples not collected l
HP-1-230 Revision 6 Attachment 10.2 (1 of 2) 47 I _. _ _ - , _ _ _ . . _ _ . _ _ _ _ .
. _ _ - - - . . _ _ - - - . - . - - - - . . ~ . . ~ . - _ - - - . . - - - . - - - . - . _ . - - . - _ - - - ---
Tchte 2 (Contimmed) '
- a. ;
4 ,
a.
One or more instruments, such as a pressurized ion chamber, for measuring and recording dose rate continuously i
may be used in place of, or in addition to, integrating dosimeters. A TLD is considered one phosphor, two or more phosphors in a packet are considered Itwo or more dosimeters. Geographical limitations affect siting of dosimeters.
b.
Airborne particulate sample filters shall be analyzed for gross beta radioactivity 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> or more af ter i
saspling to allow for rados and thoroa daughter decay. If gross beta activity in air particulate samples is greater individual than samples.ten times the yearly mean of control samples, gamma isotopes analysis shall be performed on the ,
Gamma isotopic analysis means the identification and quantification of gamma emitting radionuclides that may be attributable to the effluents from the facility.
\ c.
Drinking Water and Surface Water samples are* identical samples.
i d.
4 l The downstream sample is beyond the mixing zone.
c j e. t A composite sample will contain aliquots of sample taken proportional to the quantity of flowing liquid that '
results in a specimes representative of the liquid flow.
t
- f. ;
Ground water samples shall be taken when this source is tapped for drinking or irrigation purposes la areas '
where the hydraulic gradicat or recharge properties are suitable for contamination.
g.
This analysis will Le performed when the dose calculated for the consumption of water is greater than 1 arce s per year as calculated for maximum organ and age group as per the 00CN (see section 8.6). '
I h.
Milk will be collected semimonthly when animals are on pasture, monthly otherwise. If milk sampling is not performed, broad leafy vegetation will be sampled.
i i.
Striped mullet, gizzard shad, freshwater drum, and catfish will be collected. If they are not available, substitute species will be collected and identified in reporting.
- l j.
One sample of each principal class of food products will be sampled in an area irrigated by water in which plant wastes have been inadvertently discharged (see section 8.5 of this procedure). If harvest occurs more .
than once a year, sampling shall Le performed during each discrete harvest. If harvesting occurs continuous-ly, sampling shall be monthly. Tuberous and root products will be sangled when available. ;
l 4
NP-1-230 Revision 6 Attachment 10.2 (2 of 2)
! t
__ _- . . - - - ----------e" ' ' ' ' ' " ' * * " ~ ~ ' ~
THE 3 SAMPLE LOCATION TABLE ;
LOCATION LOCATION MILES FROM SECTOR i NUMBER DESCRIPTION PLANT DIRECTION j DIRECT RADIATION (TLD)
A-2 (Eastbank) On fence enclosure surrounding 1.1 N water tower west of Little Gypsy opposite Etinenne St. Access from River Road (LA 628). The TLD's are located on the (S) fence opposite the entrance gate to the water tower.
B-1 (Eastbank) On fence enclosing the 0.8 NNE transmission tower 0.3 miles west (up-river) from Little Gypsy. Access from River Road (LA 628). TLD's are located at SW corner j of fence enclosure.
C-1 (Eastbank) On fence enclosing the Little 0.8 NE l Gypsy Cooling Water Intake. Access is i
from River Road (LA 628) across from Little Gypsy Powsr Station entrance.
l i TLD's are on the south side (inside) of '
the Cooling Water Intake fence enclosure, directly opposite the entrance gate.
l D (Eastiank-) Located at USGS Witness Post "
1.1 ENE Survey Marker approximately 0.3 miles east of Little Gypsy Power Station.
Access from River Road (LA 628) near the west end of the Bonne Carre Spillway.
1 TLD's are on the back of the Survey i Marker Sign (located on levee).
E-1 (Westbank) Located on utility pole 0.2 E along River Road (LA 18) approximately !
0.3 miles east of Waterford 3 plant I entrance. Access from LA 18. TLD's are !
on the third utility pole east of the construction entrance road.
F-2 (Westbank) Located on fence enclosure 1.1 ESE surrounding the LP&L substation on LA 3142. Access from LA 3142 approximately
- 0.2 miles south of LA 18. TLD's are on 4 the southeast corner of the fence {
- y. enclosure.
l 1
l KP-1-230 Revision 6 Attachment 10.3 (1 of 7) 49
TABLE 3 (Continued)
LOCATION LOCATION MILES FROM SECTOR NUMBF3 DESCRIPTION PLANT DIRECTION G-2 (Westbank) Located on utility pole on 1.2 SE East side of LA 3142 near Witco entrance gate (Next to Union Carbide Star Plant Gate 3). Access from LA 3142 approximately 0.2 miles north of railroad overpass.
H-2 (Westbank) Located on fence enclosure 1.2 SSE to shell road off of LA 3142. Access from LA 3142 south of railroad overpass on east side of LA 3142. TLD's are on the south side of the gate for shell road. (Just south of Texaco pipeline station).
J-2 (Westbank) Located on northeast corner of 1.3 S fence enclosing Texaco valve station south of LA 3127. Access from LA 3127, approximately 0.6 miles west of LA 3127/3142 intersection.
K-1 (Westbank) Located behind "Private Road" ,
1.0 SSW sign at Gate 8 entrance off of LA 3127.
Access frem LA 3127, approximately 1.3 miles west of LA 3127/3142 intersection.
(Gate 8 is the acess to the Waterford 3 switchyard statior).
L-1 (Westbank) located behind "Private Road" 1.0 SW sign at LP&L Gate 9 entrance off of LA 3127, approximately 1.6 milt west of LA 3127/3142 intersection. (Gate 9 is an access road for Waterford 3).
M-1 (Westbank) Located on south gate into 0.7 WSW the Waterford 1 and 2 fuel oil storage tank enclosure. Access is either thru LP&L Gate 8, Gate 9 off of LA 3127, the shell access road from LA 18 between Waterford 3, or thru the Waterford 1 and 2 access road.
N-1 (Westbank) Located behind the "No 0.9 W Trespassing" sign off on Short Street, in Killona, just south of the Killona Elementrary School.
KP-1-230 Revision 6 Attachment 10.3 (2 of 7) 50
TABLE 3 (Continued)
LOCATION LOCATION MILES TROM SECTOR NUMBER DESCRIPTION PLANT DIRECTION l
P-1 (Westbank) Located on Short Street TLD 0.8 WNW j is on fence at air sample station APP-1. ;
Q-1 (Westbank) Located on fence enclosing air 0.8 NW ;
sample station approximately 0.5 miles vest of Waterford 1 and 2 on River Road (LA 18).
- R-1 (Westbank) Located on fence enclosure for 0.5 NNW ,
Waterford 1 and 2 Cooling Water Intake i Structure. Access is from River Road (LA 18) opposite Waterford 1 and 2. TLD's are on the southwest corner of fence.
A-5 (Eastbank) Located on utility pole just 4.5 N I east of the Shady Nook Trailer Park on Hwy 61 in Laplace. TLD's are on second utility pole east of trailer park on ,
! north side of Hwy 61 (eastern end of '
Laplace).
B-4 (Eastbank) Located on utility pole just 3.8 NNE i 4 east of shell access road to South Central r
~
Bell transmission tower on south side of !
- ~
Hwy 61. Transmission tower is just east
, of Weigh Station at St. John /St. Charles
- Parish line. TLD's are on first utility pole east of access road. r 2
i D-5 (Eastbank) Located on fence gate on shell 4.2 ENE :
access road to Big 3 Chemical Plant. [
, Shell access road is approximately 0.1 miles west of Hwy 61/48 intersection (at black and yellow gate). TLD's are on
- fence gate 0.1 miles north on shell l l access road from Hvy 61. l
]
, E-5 (Easebank) Located on the Norco Substation 4.2 E fence enclosure. Access from River Road (LA 48) onto Wesco St. (adjacent to Norco j Shell Chemical Plant), take Wesco St. to '
- the dead end. TLD's are located on sixth fence post south of the north I substation gate.
i HP-1-230 Revision 6 Attachment 10.3 (3 of 7) 51 l
TABLE 3 (Continued) '
t LOCATION LOCATION MILES FROM SECTOR I NUMBER DESCRIPTION PLA)ff DIRECTION F-4 (Westbank) Located on utility pole benind 3.5 ESE blonde brick house on Aquarius St. in Hahnville. Access from River Road (LA 18) ,
and turn onto Oak St. Follow Oak St. to t Hickory St., turn right on Hickory St. ,
and follow to Aquarius St. and turn left.
Blonde brick house is second house on right 4
(west) side of Aquarius St. heading south.
I G-4 (Westbank) Located on railroad sign 3.2 SE i 1
northwest side of LA 3160/ railroad track t
intersection. Access from either LA 3127 or River Road (LA 18) onto LA 3160.
H-6 (Westbank) Located on a construction 5.7 SSE sign on the southwet side of the second canal bridge east of LA 3160 along LA 3127.
P-6 (Westbank) Located on utility pole at 5.5 WNW southwest corner of LA 640/ railroad j track intersection. Utility pole is j just west of LA 640 and east of radio i transmission tower. i l
~
] Q (Westbank-) Located on fence post 5.0 NW
- surrounding (green) river marker '
j on levee just east of Edgard. Fence i post is located along River Road (LA
- 18) across from the Webre's house, j R-6 (Eastbank) Located on fence enclosing 5.3 NNW j 1 LP&L Laydown Yard on LA 3223 in La Place. ;
- Access from Hwy 61 onto Elm St. (LA 3223), !
take Elm St. to the northeast corner of I l LA 3223/ railroad intersection. TLD's l 4
are located on the southeast corner of
! fence enclosure.
F-9 (Eastbank) Located on entrance gate 8.2 ESE !
to Destrehan Substation. Access from I i River Road (LA 48), approximate 0.3 miles east of Luling-Destrehan Ferry, I onto Destrehan Road (west of Bunge l Corp. Grain Elevator), and proceed i to substation gate, l I
- HP-1-230 Revision 6 Attachment 10.3 (4 of 7) 52 1 l l
l
TABLE 3 (Continued) i LOCATION LOCATION MILES TROM SECTOR f i NUMBER DESCRIPTION PLANT DIRECTION i
G-9 (Westbank) Located on back fence of 8.1 SE i LPE District Office in Luling. Access j via Ellington St. from either River Road (LA 18); or Second or Third St. '
from Paul Mallard Rd. (LA 52) to Ellington St.
E-15 (Eastbank) Located on Kenner Substation 11.8 E
< fence enclosure. Access from either
] River Road (LA 48) or Hwy 61, turn onto Alliance Ave. TLD's are located on the north side of the fence enclosure,
.near a light pole. ,
1 J-15 (Westbank) Located on fence enclosure 12.0 S *
- surrounding LPE switchprd at M
- 631/ Hwy 90 intersection iu Des Allemands.
TLD's are on the northwest corner of
) fence. Access from LA 631 via shell j
road.
E-30* (Westbank) Located on fence at LPE 27.0 E General Office on Delaronde St. in
, Algiers. TLD's are og the fence, facing the Mississippi River, in the ~~
passageway to the transformer shop.
l Airborne ;
i APP-1 (Westbank) Located in soybean field 0.8 WNW
.i at northwest corner of Short St. in ,
Killona. -
l APQ-1 (Westbank) Located at northwest corner 0.8 NW '
j of soybean field on east side of Killona.
i Access from River Road (M 18) approxia-
] ately 0.6 miles east of LA 18/3141 ;
l intersection. 1 I l i APG-1 (Westbank) Located at the north side 0.5 SE I of the Secondary Metrology Tower.
] APC-1 (Eastbank) Located inside the Little Gypsy 0.8 NE Cooling Water Intake Structure fence enclosure.
HP-1-230 Revision 6 Attachment 10.3 (5 of 7)
. 53 1
TABLE 3 (Continued)
LOCATION LOCATION MILES FROM SECTOR NUMBER DESCRIPTION PLANT DIRECTION APE-30* (Westbank) Located on the roof of the 27.0 E LPE General Office building on Delaronde St. in Algiers.
l l
l Food Products FPP-1 (Westbank) Located in soybean field on 0.8 WNW
- eastern edge of Killona; between air sample stations APP-1 and APQ-1.
Bread Leaf BLQ-1 (Westbank) Located between LA 18 and 0.8 NW soybean field on eastern edge Killona, ~
near air sample station APQ-1.
BLB-1 (Eastbank) Located at wooded area at the 0.8 NNE southwestern corner of the LPE Little Gypsy plant along River Road.
BLK-15* (Westbank) Located 3.5 miles SSW of 15.0 SSW Des Allemands on Hwy. 90.
~ . . -
Iraestion Milk MKE-4 (Westbank) Located .8 miles west of the 4.0 E Time Saver in Hahnville off of River Road.
NKQ-5 (Westbank) Located at the Webre's house, 5.0 NW just across LA 18 from river marker, at j the eastern and of Edgard.
MKQ-45* (Eastbank) Located off ot I-12 in Denhas 52 NW ,
Springs. Take LA 3002 south of LA 1034 i then right to LA 1032. Turn left and go l
to fara 1 mile on the right. ;
I NKQ-1 (Westbank) 1.0 miles west of Waterford 3 1.0 NW i at the corner of River Road and Post Street j in Killona. ;
I
. l l
I MP-1-230 Revision 6 Attachment 10.3 (6 of 7) !
54 j
i l
TABLE 3 (Continued) i LOCATION LOCATION MILES FROM SECTOR :
NLMBER DESCRIPTION PLANT DIRECTION Fish FH-1* Upstream of the plant intake structure.
FH-2 Downstress of the plant intake structure. >
i 1 l D erborne GWJ-1 (Westbank) Located at 40 Arpent Canal 0.3 8 i south of the plant. Access from LA :
j 3127 through LP&L Gate 8. The canal is
! northwest of the shell access road / railroad i
! track intersection. I DWG-2 (Westbank) Located at the Union Carbide 2.0 ESE SWG-2 drinking water canal. Access from LA 3142 j through Gate 28.
SHWE-3 (Westbank) Located at the Foot Ferry 3.0 E Landing off of LA 18 in Taft.
i SHWJ-1 (Westbank) Located at 40 arpent canal 1.0 S '
south of plant. Access thru LP&L gate 8 l 1
off of LA 3127). ;
- Dht-5 (Eastbank) Located at the St. Charles 4.5 E Sht Parish Waterworks off of River Road ~ ~i j (LA 48) near New Sarpy.
l DWP-7* (Westbank) Located at the St. John Parish 6.5 NW i 4
SVP-7 Waterworks off of LA 18 in Edgard. '
i )
Q DEN 011S CONTROL LOCATIONS '
i J
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i 1
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l NP-1-230 Revision 6 Attachment 10.3 (7 of 7) 1 55 4
Table 4 SECTOR Alm 20K DESIGNATORS FOR RADIOEDGICAL SAMPLING Aim NONITORIIIG POINTS SECTOR NOKNCLATINtE , ZONE NOKIICIAftME CENTENLIN OF SECTOR IN DEGREES TRUE NORTH 22 \* NILES FRON fle0N FACILITY SECTOR FACILITT 20K 0 & 360 *A N 0-1 1 22% B INIE 1-2 2 45 C E 2-3 3 67% D ENE
- 3-4 4 90 E E 4-5 5 112h F ESE 5-6 6 135 C SE 6-7 7 157k N or SSE 7-8 8 ISO J S S-9 9 2024 E SSW 9-10 10 225 L SW 10-15 15 247% N WSW 15-20 20 270 N W 20-25 25 2925 P 141W 25-30 30 315 Q NW 30-35 35 3375 R NNW 35-40 40 40-45 45 45-50 50 AREA SEGElfT - An area is identified by a Sector and Zone designator. Thess, area N-1 is that area which lies between 348 3/4 and lik degrees true morth from the facility out to a radiens of I mile. Area G-4 woestd be that area between 123 3/4 to 146 k degrees and the 3- and 4-mile arca free the facility. For Airborne, Ingestfee (ellk), and Food Prodiacts pathways, the sector designator will be preceded by acronyms AP, K , med FP, respectively.
- The letters I and O have been omitted from these sector designators so as to eliminate possible confusion between letters and numbers.
NP-I-230 Nevision 6 Attachment 10.4 (1 of 1) 56 L
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FICURE .4 (CONT.)
LIQUID WASTE MANAGEMENT- SYSTEM EFFLUENT SOURCES '
AND RELEASE, PATHWAYS AND PolNTS 5
SOURCES KLEASE PATHWAYS AND POINI$
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IIP-1-230 Revision 6 Attachment 10.8 (2 of 2) i
_ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ __ __ _se
FIGURE 5 f
. GASEOUS EFFLUENT SOURCES G4SEGB WASTE MAAMGEA&ENT SYSTEAGS EFFUENT SOtMCES AAD EXNAUST RELEASE PONTS I
4 ST&h RELEASE NBalts J
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ilP-1-230 Revision 6 Attachment 10.9 (1 of 1)
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s o l W01oV4 NQl103W00 63 HP-1-230 Revision 6 Attachment 10.10 (1 of 1)
TABLE 5 SITE RELATED LIQUID DOSE FACTORS .
A;, = ( 3. 78E+ 05 + 2.39E+068Ff )DCF/ r (ares /hr per uCi/ali UJ DCF(eres/pCif f At GI LLI LIVER G! LLI LIVER Cc-51 2.0E+02 6.69E-07 --
3.20E+02 --
Mn-54 4.0E+02 1.40E_05 4.57E-06 1.34E+04 4.37E+03 Mn-56 4.0E+02 3.67E_06 1.15E-07 3.51E+03 1.20E+02 Fe-55 1.0E+02 1.09E-06 1.90E-06 2.61E+02 4.55E+02 Fe-59 1.0E+02 3.40E-05 1.02E-05 8.14E+03 2.44E+03 Co-58 5.0E+01 1.51E-05 7.45E-07 1.81E+03 8.93E+01 Co-60 5.0E+01 4.02E-05 2.14E-06 4.82E+03 2.57E+02 Hi-63 1.0E+02 1.88E-06 9.01E-06 4.50E+02 2.16E+03 Hi-65 1.0E+02 1.74E-06 6.86E-08 4.17E+02 1.64E+01 Cu-64 5.0E+01 7.10E-06 8.33E-08 8.51E+02 9.99E 00 2n-65 2.0E+03 9.70E-06 1.54E-05 4.64E+04 7.36E+04 Sr-89 3.0E+01 4.94E-05 --
3.56E+03 --
Sr-90 3.0E+01 2.19E-04 --
1.58E+04 -- I l
Y-90 2.5E+01 1.02E-04 --
6.13E+03 --
2r-95 3.3E 00' 3.09E-05 9.75E-09 2.55E+02 8,06E-02 ~~9 2r-97 3.3E 00 1.05E-04 3.39E-10 8.32E+03 2.80E-03 Hb-95 3.0E+04 2.10E-05 3.46E-09 1.51E+06 2.48E+03 I-131 1.5E+01 1.57E-06 5.95E-06 5.69E+01 2.16E+02 Cs-134 2.0E+03 2.59E-86 1.48E-04. 1.24E+04 7.07E+05 Cs-137 2.0E+03 2.1tE-06 1.09E-04 1.01E+04 5.21E+05
- 1. Extracted from Table A-1 of Regulatory Guide 1.109, Revision 1,1977,
- 2. Extracted from Table E-11 of Regulatory Guide 1.109, Revision 1,1977.
HP-1-230 Revision 6 Attachment 10.11 (1 of 1) 64 l
l l
l
~.
e TABLE 6 BIOACC N TION FACTOR FOR FRESHWATER FISH AND INVERTE3RATEl (pci/Kg per pC1/ liter)
FRESHWATER ELEMENT FISH INVERTEBRATE E 9.0E-01 9.0E-01 C 4.6E 03 9.1E 03 Na 1.0E 02 2.0E 02 P 1.0E 05 2.0E 04 Cr 2.0E 02 2.0E 03 Mn 4.0E 02 9.0E 04 Fe 1.0E 02 3.2E 03 Co 5.0E 01 2.0E 02 Ni 1.0E 02 1.0E 02 Cu 5.0E 01 4.0E 02 "
Zn 2.0E 03 1.0E 04 Br 4.2E 02 3.3E 02 Rb 2.0E 03 1.0E 03 Sr 3.0E 01 1.0E 02 Y 2.5E 01 1.0E 03 Zr 3.3E 00 6.7E 00 1
- 1. Extracted from Table A-1 of Regulatory Guide 1.109, Revision 1,1977.
RP-1-230 Revision 6 Attachment 10.12 (1 of 5) l
TABLE 6 BICACCL'MULATION FACTOR FOR FRESHWATER FISH AND INVERTE3 RATE 1 (pCi/Kg per pCi/ liter)'
FRESHWATER ELEMENT FISH INVERTE3 RATE Nb 3.0E 04 1.0E 02 l Mo 1.0E 01 1.0E 01 Tc 1.5E 01 5.0E 00 Ru 1.0E 01 3.0E 02 Rh 1.0E 01 3.0E 02 Te 4.0E 02 6.1E 03 I 1.5E 01 5.0E 00
-- . . Cs 2.0E 03 1.0E 03 -'i Ba 4.0E 00 2.0E 02 La 2.5E 01 1.0E 03 !
Ca 1.0E 00 1.0E 03 Pr 2.5E 01 1.0E 03 Nd 2.5E 01 1.0E 03 W 1.2E 03 1.0E 01 Np 1.0E 01 4.0E 02 1
HP-1-230 Revision 6 66 -
-- - - _z ------.----
-- m l
l I .
TABLE 6
!=CE5 f 104 Oust FaC ron'$ rom acut f 5
. ("4EM pea eCl INCEifEDI reuCL IL E SOME LivEt f.ACCY TMysOt0 E!ONEY LuNO
.H
.. ~ ...
I 40 DATA t.3SE-01 1.03 E-0 7
.........-.. - ........--..-.GI-LLI ...-
1.05s~07 1.05E.07 1.0SE-07 1.0SE-07 C 14 2.84E.06 S.68E-07 S. 48 E-0 7 S.68E-07 S.686-07 S.68f=07 S.68E.07 44 24 1.708 06 1.70f.06 1. 70 E-0 6 1.70E-06 1.708-06
=_==-_ ... .... .. .. t. FOE-06 . .
1.708 06 ,
... . ~ ...
p 32 1.93E.04 1.20f=0S 7. 448 -0 e 40 UATA NC 04fA NO 04r4 2.17E-05 CR 51 40 DATA NO oaf 4 2. 6e t -0 9 1.$9E-09 S.864 10 3.$1E-09 )
mm $4 40 UATA 6.69E.07
= _- :
4.575-06 8. 72 E-0 7 40 QAfA 1.J6E-06 NO DATA 1.408-05 mg $4
_ - - . . - __. {
40 DATA 1 152-07 2.04E-04 40 OATA t.46E-07 40 OAfA ft SS 2.758-06 1.90F-04 3.675-06 4.43C-47 40 04f4 NO DATA 1.06t=06 1.09E-06 Pt 19 4.340 06 1.028 0S 3.91E.06 90 OATA 40 04TA 2.85E-06 3.40E-45 CO 58 MC DATA 7. 4 hi=07 1. 6 7E-0 4 90 04f4 CO 60 40 OATA 40 04f4 40 DATA 1.318 05 2 147-04 4. 72C-0 4 NO 04 f4 40 04 f 4 NO DATA 4.02E-41 MI 63 1.308-04 9.0LE-04 4.J68 06 40 DATA 90 04TA
=
_ = = - _ - - _ ..-
NO DATA 1.88A.06
- __-_..- _- =- _
NI et S.28E-47 4.868-04 3 138-0 8 . 40 D A T A 40 DATA 40 oaf 4 t.74E.06 CW 64 40 O&fa 8.33E-04 3. 91 E-0 8 40 oaf 4 2 108 07 No DATA 2M 6S 4.848-06 1.344-0S e. 9et-4 6 go DATA 7.10E-04 1 03E.0$ 40 DATA 9.70f 06 24 69 1.018-04 1.17E-PO 1.37f-09 40 04T4 1.20E.08 NO DATA 84 83 10 OATA 40 0474 4.028-08 NQ Ca*A 2.94E-09 88_84 40 04f4 40 04TA S.79E-08 40 OATA . MO 44 f 4 , S.215-08 40 DATA 40 DATA 40 OATA 4.09E.13
__==... =-- _- _= _..- _.-_ .=-- __-
8A 85 MO CATA 40 DATA 2.148-09 MO Daft NO DATA 48 86 NO 0474 2.11E-09 40 04tA LT E-24 9.838-06 40 OATA 40 DATA 90 OATA 4.168-06 48 88 40 0474 6.03E.08 1.21E-08 20 DA TA 40 DA TA 40 O&fA
= -- = -- -_.=_
8.368-89 at 89 NO DA TA 4. 01 E-0 8 - 2. 82 C-4 4 90 O A TA SA"89 NO DATA 40 O&TA 2.33E-21 3.088-04 40 OATA 4.848-04 10 OATA 40 OATA 20 DAT4 4.94E-05 sa 90 7.34E-03 40 047A t . A6E-0 3 90 04f4 40 DATA 20 Data 2.19E.44 54 91 S.678-06 MO 0474 2.298 17 90 OATA 40 04f4 SR 92 2.135-06 10 04fA 90 04f4 2.70E-05 Y to 9 308 08 Mr1 04f4 NO DAT4 40 O&fA 4.268 45 9.62E.09 40 OAT 4 2.$80 10 90 DafA 90 04fA 40 0474 1.025 04 l
Y 9tm 9.09E-11 40 DATA 3.52E-12 40 QAf4 NO DATA MC DATA 2.67E-10 Y 91 1.4t8 07 40 0474 3.77E-09 MC DATA NO CA TA 40 04f4 7.76E-OS Y 92 8.4SE-10 NO DATA 2.47E-t1 40 QATA 90 QAf4 l
MO QAYA 1.48E-05 l 1
KP-1-230 Revision 6 Attachment 10.12 (3 of 5) 67
-~ -- . - --,--..... _ .. -
l l
TABLE 6 (concinued) 14C85f104 005E F4Cf0*S 70* 40Vtf5 (MetM Pkt PCI 19CE5ff01 NUCL108 8041 L!vfR f . 400Y TMv9080 E!DNEY LUNG Cl-tt!
Y 93 2.684-C1- NO CATA 7.40t-11 NC OATA NO DATA 40 CATA 8.500-05 ZR 9) 3.048-08 1.758-09 6. 60 E-0 9 NO DATA 1.S18 00 NO DATA 3. c 98 -O S ZA 97 L.48E-09 3.398-10 1. $ 5 8- 10 NO DafA S.128-10 NO DATA 1.058-04 94 95 6.228-09 3.444-09 1.868-09 NO DATA 3.428-49 40 QATA 2.10E-OS MO 99 343 DafA 4.318-06 8.208-07 40 QATA 9.766-06 4C DATA 9.99f-06 i FC 99m 2.475-10 6.98t-10 8. 89 t -0 9 NO DATA 1.068-04 3.428-10 4 135-07 l
- ==- _ _ . . - _ - - _ _ - - - l FC101 2.S44-10 3 468-10 3.598-49 90 O&fa 6.594-09 1 87 tate 1.108-21 autel 1.858-07 NO DATA 7.978-08 40 OATA 7.066-07 MO DATA 2 1s6-05 l Rut 03 1.544-08 40 04,fa 6 088-09 40 DATA 1.996-07 20 OATA 9.425-44 i
\
__-_=__
. = . _ _
9U106 2.7bt-04 90 DATA 3.488-07 40 CATA S.114-04 40 OATA 1 788-04 AG110m 1.406-07 1 488-07 8.79t-Ot 90 CATA 2.9tt-07 40 QATA 6.04t=0S I ftt25m 2.49E-04 ,9.7tt-07 3 51C-4 7 8.068*07 1.G94-05 40 DATA 1.078-04 l 7t127= 6.77E-06 2.42C-06 8. 2 5 t =0 7 1.718-06 2.758-49 WO DATA 2.279-0S ,
ftt27 1.108-OF 3.91 7. 3 8 t =0 8 8.158-08 4.488-07 20 04fA 8.48t-06 i ft129m 1.15E-05 4.2,8-08s.04 1. A28-0 6 3.958-04 4.808-05 40 DATA S.79t=0S l
== .-
18129 3.14t=08 1.18t=08 7.438-09 2.418-48 1.328-07 40 DATA 2.371-08 ~ ~' l ftt3tm 1 73t-04' 8.'4 6 C -0 7 7.0$t =0 ? 1. J 44 -04 8.578-04 40 DafA 8.408-05 f8131 1.978-08 9.23t+09 6.221-09 1.428-08 8.434-04 40 QATA 2.79t-09
=- ... --
ftt32 2.52E-04 1.415-04 1. 5 J 8-0 6 1.808-06 1.578-05 40 QATA 7.71E-01 t 130 7.566-07 2.218-46 6.408-07 1 891-04 3.488-04 20 OATA 1.928-04 1 131 4.164-06 S.958-04 3.618-06 1.95t=43 1.028-65 40 SATA 1.575-04 1 112 2.018-07 S.43P-07 1. 90t-4 7 1.908-45 8. 4 S k-07 20 OAT A 1.021-07 I 113 1.421-04 2.4ff=06 7.538-47 3.638-04 4.31E-06 20 DATA 2.228-06 I 134 1.064-07 2.888-07 1 018-07 4.998-04 4.584-07 40 QATA 2.518-10 t 135 4.438-07 1.1Ed=04 4.288 07 7.458-05 1.465-06 NO DATA 1 118-04 C3134 6.228-45 L.488-04 1.218-04 NO DATA 4.798-05 1.596-05 2.$98-06 C5116 6.513-06 2.571-05 1. 8 5 E -0 9 40 DATA 1.415-05 1.968-06 2.928-06
.= -
=- -- =.. =_=_ _
CS137 7.97E-OS 1.098-04 7.148-05 40 CATA 3.704-0S 1.238-05 2 118-04 C5138 S.521-08 1.C9t=07 5.406-04 NO DATA 8.018-0A 7.918-09 4.45t-13 84139 9.701-08 6.912-11 2 844-09 90. DATA ' 6.468-11 1 92t=11 1.728-07 i
i I
_ l I
HP-1-230 Revision 6 Attachment 10.12 (4 of 5) 68
TABLE 6 (continued) -
144817104 001t P4C7041 702 40 ULT 1
("#EM PLR PCI 140817803 wuCLIUE SOME LivfA f . A007 TMTEOlO RIONEY LUNC GI-LLI 84140 2.03C-OS 2.5 5t =08 1 338-04 40 Dafa 8.6ft=09 1.468-08 4.tst-05 Ratel 4.FIE-08 1.54C-11 1. 5 9 E-0 9 90 DATA 3.318-11 2.028-11 2.221-17 94142 2.138-ce 2.198-11 1. 3 4t-0 5 SO Data 1.353-11 1.24E-11 1.003-26 Lat44 2.300-09 1.262-09 J.3JC-to Mc DAT& NO O&ra 40 SATA 9.2SE-45 LA142 1.284-10 S.82!-11 1 458-L1 40 04?& HC O&fa 40 DATA 4.2$8-47
- E14L 9.344-09 4. LAC-09 f.14C-LO 40 04f4 2.944-09 ko DAf4 2.428-45
__ _= _
Ct143 1.458-49 1.22P-04 1.35E-LO 90 OA74 S.378-10 20 OATA 4.$4t-45 C8144 4.ASE-47 2. G 4 8-0 7- 2.628-08 40 oaf 4 1.218-47 40 04fA 1.4 9 E-06 88141 9.2 0E-09 3.492*09 4 348-10 90 04f4 2.138-09 90 04f4 4.03E-05 pel44 3.018-11 1.255-11 1. Sit-L2 90 DATA 7.098-12 to 0474 4.338-L8 mot 47 6.29E-09 7.J7t=09 4. 3tt-L e 90.OAfa 4.218-49 90 04f4 3.49t-05 m 157 1.035-07 8.415-08 3.018-18 90 04f4 40 047A 26 0474 2.828-01 km239 1.19E-09 1.17C-10 6.45E-11 90 04f4 3.458-10 40Okt *2.408-05 I
f I
l l
l HP-1-230 Revision 6 Attachment 10.12 (5 of 5) 69
=.
.-~_ _ _ _
'TABI.E 7 005t rectees 70s (IPClunt to A stx1.turtw!Tt CL0uo or 10ttr casts mue114e s.a t e*( Nt ) s Stia *
- f _;Q )
.. Ale * ( hb ) -l e 4 y f Kt tr 83m 2.88t 04 ** .-- 1.93t.05 7.58t.04 tr.45e 1.97t 03 1.46t.03 1.23t 03 1.17t.03 Er 85 1.95E.03 1.348 03 1.72t.05 1. 61 t 05
' ~
tr 87 1.03E.02 9.738 03 6.17t.03 5.92C.03 tr.88 2.93t 03 2.37t.03 1.52t.02 1.47t 02 Er.49 1.04t 02 1.01t 02 1.738 02 1.66E.02 tr.90
- 7.838 03 7.29t.03 1.83t 02 1.58t 02 to-131e 1.118 03 4.76t.04 1.54t 04 9.15t.05 I e.13 3's 1.48t.03 9.94t.04 3.27E.04 2.51 C 04 Ie.133 1. 05 t.03 3.08t.04 3.53t 04 2.94t.04 2e.135e 7.39t.04 7.118 04 3.36C 03 3.12t.03 Ie-135 2.46E 03 1.868 03 1.92t.03 1.81t.03 - - -
Ie-137 1. 2 7 t.02 1.22t 02 1.512 03 1.42E.03 Ie-(38 4.75t.03 4.13t.03 9.21t 03 8.83t.03 Ar.41 3.28t.03 2.89t 03 9.30t.03 8.84t.03 1
'er.4. 3 pct.pr -
eres.e 3 DG1=pr 2.88C.04 e 2.88 a 10*4 a
RP-1-230 Revision 6 Attachment 10.13 (1 of 1) 70 .
\
TABLS 8 INMakafl04 0C18 84C7025 Pot CHILO (DFA1) 184Em PEA #CI 1* MALE 03 4WC1808 8098 Livfa f. AODF Thvadl0 a10NEY LUNG -
GI-LLI H J 40 Data 3.c4E-07 3.04s-4f * . 04d*C7 1.04C-01 2.042-07 1.04E-07 C 14 9.70E-04 1.42E-06 1.92E-06 1.E2E-06 1.42E-06 1.87E-06 1.828-04 44 24 4 3SE-06 4.35**e6 4.3st-04 4.3%E-on 4.3SE-e6 4.15E-04 4.3SE-06 7 32 7. 04 E-04 1.09E-03 2.4 f t-0 5 NO OATA NO CafA %d 04fA 1 146-05 CA St NO CATA NO 0474 4 17 E-0 8 2.J1r-es 4.176-19 6.99E-06 2.93E-07 mm S4 40 04fA 1.14!-OS 2.577-06 40 3ATA 2. 71 E -0 6 4.26E-04 6.19 F-04
__ _ . -_ ---_ _=--- _=- _ = - -
- M S4 40 04fA 4.448-10 8.43E-11 40 DATA 4 92E-10 3.SSE-06 1.33E-45 TE SS 1 288-05 6.80E-06 2. 8 0 E-0 4 40 0=ia 40 DATA 3.00E=0S 7.75E-47 PE $9 S.39C-04 9.G4E-06 4. S I C-0 6 90 QATA NO DATA 3.43C-04 1.91E-OS CD SO 90 DATA 4.299-07 8. S S E-0 7 20 04f% 4C 04fA 2. 99E-44 9 29E-44 CO 60 40 DATA 3.59E-04 4.12E-04 %n O&fe 40 04f4 1.918-03 2.40E-49 il 6A 2 22E-04 1.257-01 7.568-06 40 DATA 40 DATA 7.438-01 1 71E-06 tot 63 0.04E-10 7.91E-11 4.44E-11 4n DAfA MC 04f4 2. 21 E-04 2.2 7 t=0S Cu 64 90 04f4 1.J9E-lo 2. 90 C-10 bc OATA 1.43E-09 2.59E-44 9.92E-46 2M 63 1 158-09 3.068-05 1.90E-OS' 90 DafA 1.91E 01 2.69E-o* e.41E-44 24 41 1.81E-11 2.61E-11 2.41L-12 40 QATA 1.54E-t1 3.446-07 2.75R-04 pt 83 40 CATA 40 utfA 1. 2 E E -0 7 90 0474 NO DAf4 NO DATA dA 44 20 DATA LT E-24 90 04TA 1. 4 s t-17 40 0474 40 Daf4 4C OATA LT E-24
.- _-- = - - _ = .~. _==:=--
59-85 20 04f4 - 40 '04 f 4 6.44E-49 40 DATA 40 oaf 4 40 DATA LT E-24
- ,4 40 46 20 Defe S,J6C-05 1.04E-05 90 CATA 40 CATA >0 Data at 44 40 OATA 2.16E-04 i.52E-Of 9.90C-08 20 DATA 40 0474 NO CAfa 4.448-49
- - =- - = _=
- 40 89 40 DATA 9.31E-00 7.848-04 40 DATA 4C OAfa SR 49 1.62 E-44 90 CafA 40 04f4 S.118-10 4.648-04 40 CATA 40 QATA S.31C-04 4. 3 2 8 -e5 54 90 2.73E-02 40 DATA --
. = = _=- _ = = _ - _ = . -
SR 91 3 2EE-04 90 CATA 1 248-09 40 QAf4 90 DATA 1.44E-05 SR 92 4.708-45
- 3. 34 E-09 NO 04f4 1.*2E-10 40 OATA 40 DATA 6.49C-44 6.SSE-01 Y 90
.=
1 11E-06 40 0474 2 94f=44 40 0474 40 04 f A 7.07E-05 7.2 4E-O S I
= -
=== __.
Y . 91
- 1.17E-10 40 QATA s 4.94E-il 90 QAf4 40 CATA 7.60F-07 4.648-47 Y 91 2.478-04 90 04f4 4.19 E -0 4 40 DATA 40 CAf4 7.10E-64 4.9fE-45 I
7 92 S.S0E-09 N0 DafA 1.5 f t-10 90 04f4 90 04fA 6.44E-C6 6.44E-05 l
l l
HP-1-230 Revision 6 Attachment 10.14 (1 of 3) 71
r TABLE 8 (Continued) 13 MAL 4fl0N QLS N P &C roa5 rca CHILO (DFAg)
(*Ets 8t4 8CI INMALE01 1UCLlot guwt L!Ega f . 40 07 THfm010 E!OMET LU 4G GI-LL!
T 91 S.04E-08 40 04f4 1. I t t -0 9 40 Daft 40 O&f4 2.011-09 1.0SE-04 22 95 S.lJf-OS 1.13E=oS 1.00E-OS 40 DATA 1.41a-OS 6.03f-04 1.69t=0S 22 97 S.07C-06 7.J45-07 4 128-09 *O 0474 1 0SE-08 1.068-0$ 9.49t-05 h4 95 6.3St-06 2.488-06 1.77E-06 Nn 04f4 2.33E-06 1.66f-04 1.00E-05
=0 99 40 DATA 4.44E-04 1.13 E -0 4 40 Daft 1. c 6 E -0 7 1.64E-05 1.428-05 fC 998 4.stE-13 9.41C-1J 1.56E-11 40 QATA 1.3ft-tt 7.S7f-07 1.30E-06 TClet 2.19t=14 2.30f-l* 2.115st3 NG DafA 3.175-13 1.3Al-07 4.417-09 Rut 03 7.55E-07 40 04f4 2.90f-07 40 DATA 1.104-06 1.79E<04 1.215-CS AW105 4.134-10 *U 047A 1.308-10 mn OATA 3.638-10 4.30E-04 2.69E-05 4U104 3.64E-05 40 04fA 4. 5 7f-06 40 047A 4.97f-49 3.87E-03 1 16E-04
- 4G110m 4.36E-06 3. cat-06 2. 4 f f =0 4 kn DATA S.74L-06 1.44f-03 2.711-05 781259 1.J28-06 6.29f-07 2.478 07 S.201-07 NC OATA 1 294-04 9 13E-04
=- ...
TE127m 6. 72 E -06 2.318-04 8. l et-0 7 1.44E-04 1.72E-05 4.00C-04 1.93E-09 IE127 7.49E-10 2 575-10 1. 61 E -10 S.30E-10 1.911-09 2.717-06 1.528-05 181278 S.19E-04 1 4SE-04 8 22E-0 7 1 718-04 1.144-09 4.74E-04 4.918-05 TE129 2. 64 E- k 1 9.45E-12 4.44C-12 1.93E-11 6.94L-11 7.9tE-07 6.498-06 . m.
rt13tp 1.438 1.60E-08 1.37t-04 2.64E-08 1.088-07 S.S6E-01 8.32E-OS fE131 S.47C-12 2.JEE-12 1.78C-12 4.S9t-12 1.99C-11 S.SSE-07 3.644-47 ,
ffl32 1.10E-07 7.34E-08 7 12E-08 0.34E-08 4.796-07 1.028-04 3.721-05 1 130 2.21E-06 4.4J!-04 2 285-06 4.99E-04 6.41k-04 *n DATA 1.385-04 1 131 1 30E-09 1.30E-OS 7 378-04 4.39E-03 2.134-05 40 DATA 7.64f-07
= -
I 132 S.72t-07 1.10E-04 $ . 018 -0 7 S.2SE-OS 1.69E-06 40 DATA 3.45t-07 1 133 4.44C-04 S.49C-06 2.088-06 1.04t-43 9 138-06 nc 047A 1.444-04 I 134 3 178-07 5.441-07 2 61E-0 7 1 378-05 8.92E-47 no Data 2. Set-07
=
1.135 1.13E-06 2.166-06 1.12E-04 2.14C-04 3.425-04 40 QATA 1.20E-06 CS134 1.745- 04 2.74E-04 4.0 f E =0 S 40 cafA s.93E-09 3.275-49 1.04E-06 C3116 1.764-01 4.428-05 '3.14E-05 *n Gefa 2. Sat-OS 3.93E-06 1.138-04
_= ._ - :== .=_ -- -
C3137 2.4SE-04 2.23f=04 1. 4 f E-0 5 40 04f4 7.618-05 2.8tE-OS 9.74t-07 C3138 1.7tt=07 2.27E-07 1.SCE-0 7 40 DafA 1. 6 8 E -0 7 1 44E-04 7.29E-08 84139 4.988-10 2.66F-13 1.45E-ti NC 0474 2.33t-13 1.56E-04 1. 5 6E-0 5
.. ==- =.--- --
HP-1-230 Revision 6 Attachment 10.14 (2 of 3) 72
TABLE. 8 (continued)
IhMALAfl04 OCSE peCTotS PC2 CHILC (DFA1 )
(FREN,P!4 PCI INM AL f oi NUCLICE SUNE LlVER f.30CY THYeOlc ElchtY LuMG ". ! -L L I 0A140 2.00E-OS 1.FSE-08 1. t FE-0 6 40 QA7A S.711-09 4.7tE=04 2.75E-05 Sat 41 S.29t-Lt 2.1SE-14 1.727-t2 NO DATA 2.56E-t* 7. 8 9 E-0 7 T.44E-08 84142 1 35E-11 1.73C-IS 7. 3*C -1 3 40 CATA F.37 tats 4.44E.07 F.4LP-10
~ . -.~.-- ... . ....-.... ...
Lat40 1.F48-0F 6 08E-04 2 04 E-0 5 NO DATA 10 OATA 4.94E-09 6.let-OS
. LA442 3.50E-10 1.14E-10 3.49E-11 90 QATA NO CATA 2.3Sf=06 2.0SE-05 cit 44 1.048-OS S.28E-06 T. 8 3 E-01 40 CATA 2.3tt-06 1.47E-04 1.51E-OS
=--
CE143 9.89E-08 S.37E-08 7.77E-49 40 QATA 2.264-04 1.12E-05 1.44E-05
- CI!44 1.83E-03 S.72C-04 9.77E-OS 90 DATA 3.17E-04 1 23E-03 1.0SE-14 P4163 4.998-06 1.20E-06 2.47E-0T 40 DATA 8.113-07 1.47E-04 2.63E-OS
_. _=-- - _ - _
Pet 44 1. ALE =11 4.99d-12 8. TOE-13 40 QA7A 2.444-12 4.23E-47 5.32E-at M0147 2.92W-06 2.36E-06 1. 8 4 f-0 7 40 DAT4 1 10E-06 4.87k-05 2 22P-05 w 187 4.4tE-09 2 418-09 1.117-09 40 CATA NC CAfA 1.LLf=0S 2.44E-05 1... - .. . . .. _ . .... _. ... _
97239 1.2 4E-0 7 9.048-09 6. 3 9 E -19 NO Cafa 2.63E-e8 1.57E-05 1.73E=0S u
I i
l HP-1-230 Revision 6 Attachment 10.14 (3 of 3) 73
I TABLE 9 '
Values of L-Theta-V (Inverse Meters-Seted)
Calculated Usins Open-Terrain Factors Pathwav MILX COWS Sector Distance Paseuill Cateserv (Miles) (Meters) A B C D E F 6 W !.1 1770 3 3E-M 1.6K45 3.1tE-05 7.01E-05 1.0K-04 1.58E-04 2.4N-04 W 4.4 7081 3.44E-07 3.7K-07 f.48E-07 3.16E-M 5.1K-M 8.5N-M 1.40E-05 L
HP-1-230 Revision 6 74 Attachment .10.15 (1 of 5)
_ _ _ _ _ 1
~
7 .
.I TABLE 9 I
l 4
l Values of L-Theta-V (Inverse Meters-Sevared)
Calculated Usins Open-Terrain Factors Pathwav) MILK GOAT Sector Distance PSeuill Catetotv 1
(Miles) (Meters) A B C I E F 6 1
E 33 5311 5 23E-07 7.70E-07 1.87E-M 5 67E-M f.01E-M 1.46E-05 2.35E 45 t
. . n 1
l l
HP-1-230 Revision 6 75 Attachment 10.15 (2 of 5) i
\
TABLE 9 I
i Values of L-Theta-V (Inverse Meters-Sevared)
Calculated Usins Oren-Terrain Factors Pathwav! VEGETABLE GARDEN Sector Distance Paseuill Cateserv (Miles) (Meters) A B C D E F G N 1.1 1770 3.28E46 1.60E45 3.!M-05 7.01E-05 10X44 1.58E44 2.42E44 i WE 13 2092 2.4K-06 9.85E46 2.02-05 4 64E45 6.85E-05 104E44 16X44 !
E 1.0 1609 3.91E46 2.1345 415E-05 8.91E-05 1.30E44 2.00E44 3 06E44 ENE 0.9 1448 . 4.8X44 2.90E45 5.5X-05 1 1M44 1.71E44 2.61E44 3.99E44 E 3.2 5150 5.48E-07 8.35E-07 2 01E-04 6 04E-04 9.5X-04 154E45 2.4M-05 ESE 2.3 3701 9.17E47 2.00E-06 4.55E46 12X-05 1.89E-05 2.9M45 4.74E45 SE 2.3 3701 9.1N47 2.00E-06 4.5X46 12X45 1.89E45 2.99E-05 4.74E-05 S 0.9 1448 4.83E46 2.9'445 5.57E45 1 17E-04 171E44 2.61E44 3.98E44 .
SSW 0.9 1448 4.8X-04 2.90E-05 5 57E45 1 17E44 1.71E44 2.61E44 3.99E44 "
SW '0.9 1448 4.8X46 2.90E-05 5.5X45 1 1N44 1.71E44 2.61E44 3.98E-04 WSW 09 1448 4.83E-06 2.90E45 5.5X45 11444 171E44 2.41E-04 3.99E-04 W 11 1770 3.28E-06 1.60E-05 3.1M-05 7.01E45 1.0X-04 1.58E44 2.4N44 WW 0.9 1448 4 8X44 2.90E-05 5.5X45 114-04 1.71E-04 2 61E44 3 99E44 W 0.9 1448 4.8X-04 2.90E45 5.57E45 1 17E-04 1.71E44 2.61E44 3.99E44 NNW 2.9 4667 4.36E-07 1.08E46 2.54E46 7.44E-04 1 1M-05 1.8445 3.00E-05 e
HP-1-230 Revision 6 76 Attachment 10.15 (3 of 5)
m; ~ - ..
TABLE 9 I
l Values of L-Theta-Y (Inverse Meters-Seuated)
Calculated Usins Onn-Terrain Factors Pathwav: RESIDENCES Sector Distance Paseuill Cateserv (Miles) (Meters) A B C D E F 8 M 0.8 '1287 7.7M-06 4.1E-05 7.7K-05 1.59E44 2 32E44 3.54E44 5.4M44 letE 0.8 1297 7.7M-06 4.13E45 7.7M45 1.59E44 2.32E44 3.54E44 5.4M44 IE 0.9 1448 4.8X4s 2.9M-05 5.5M-05 1 1M44 171E44 2.61E44 3.99E44 ENE 0.9 1448 4.8E-04 2 90E-05 5.5M-05 1 1M44 171E-04 2.61E44 3.99E44 E 2.4 4184 7 54E-07 144E-06 3 35E-06 9.41E-06 146E-05 2.3K-05 3.71E45 ESE 3.4 5472 5.0M-07 7.1X-07 1.74E-04 5.3X46 8.49E46 1.3E-05 2.2X-05 SE 3.9 6276 4 09E47 5.02E-07 1.26E-06 4.02E46 6 5M44 106E45 1.74E-05 2.4X46 9.85E46 2.02E-05 4.64E-05 6.85E-05 1.04E44 16X44 :
il -
13 2092 M - 0.9 1448 4.8E-06 2.9M-05 5.5M-05 1.1M44 1.71E44 2.41E44 3.99E44 .,
W 0.9 1448 4.8X-06 2 90E-05 5.5M45 1 1M-04 1.71E-04 2.61E44 3.99E44 M 2.0 3219 1.15E46 2.93E46 6 5M-06 1.49E-05 2.54E-05 4.02E-05 6 32E-05 l
l l
l 1
l l
HP-1-230 Revision 6 Attac) ment 10.15 (4 of 5) 77 I
r- _
TABLE 9 1
l 1
Values of L-Theta-V !
(Inverse Meters-Sevared)
Calculated Usins Open-Terrain Factors Pathwavi SI7E $0UNMRT Sector Pastance Paseuill Catsserv (Miles) (Meters) A B C D E F 8 N 0.8 1287 7.7446 41R-05 7.78E45 1.59E44 2.3X44 3.5444 5.434
) TIE 0.6 966 2.01E-05 7.94E-05 1.4244 2.74E-04 4.01E44 6.21E44 9.61E44
)E 0.4 966 2.01E-05 7.94E-05 1.4X44 2.74E44 4.01E44 6.21E44 9.61E44 DE 0.6 944 2.01E-05 7.94E45 14144 2.7444 4.01E44 6 21E44 9.61E44 E 08 1287 7.7446 4.1X-05 7.78E-05 1.59E-04 2 3144 3.54E44 5.40E-04 ,
ESE 0.6 966 2.01E-05 7.9M45 1.42E44 2.74E44 4.01E-04 6.21E44 9.61E44 SE 0.6 964 2.01E-05 7.94E-05 14N44 2.74E44 4.01E44 6.21E44 9.61E44 SSE 0.8 1287 7.7N-N 4.1X-05 7.7K45 1.59E44 2.3144 3.54E44 5.40E44 S _1. 6 2575 1.6K-M 5.46E-M 1.16E45 2.82E-05 4.21E45 6 54E-05 102E44 -
SSW 31 4989 5.'75E-67 9.0N-07 2.1K-04 6.46E46 10N45 1.44E45 2.4K-05 SW 3.4 5472 5 00E-07 71X-07 1.74E-M 5.3X-M 8 49E-M 1.3K-05 2.2K-05 I WSW 1.5 2414 1.8X-M 6 55E 06 1.38E45 3.29E-05 4.89E45 7.5?t-05 1.1K44 W 10 1609 3 91E-M 2.1X-05 41K-05 0.91E45 1.30E44 2 00E44 3.0E44 M 0.6 147 7.7N44 4.13E-05 7.78E-05 1.59E44 2.3344 3.5444 5.40E44 ,
W 0.8 1287 7.74-4 41X45 7.78E-05 1.59E44 2.3144 3.5M44 5 4K44 NW 0.9 1448 4.83E-M 2.90E45 5 5N-05 1.1N44 1.71E44 2.61E44 3.90E44 1 1
i l
HP-1-230 Revision 6 Attachment 10.15 (5 of 5) 78 i l
l TABLE 10 PAIllWAY DOSE FACTORS DUE TO RADIONUCLIDES OTHER t THAN NOBLE GASES, R .
1 EHVIRONMENTAL PATHWAY-DOSE COHVERSIGH FACTORS R(I) FOR CASEOUS DISCHARGES PATHWAY: IHHALATION AGE GROUP: INFAMT (1 0F 4) i HUCLIDE ORCAN D0SE FACTORS (HREH/YR.PER UCI/CU.NETER) j TOTAL BODY 80HE LIVER THYROID KIDHEY LUNC GI-LLI 2 H----3 .647E+03 .400E+00 .647E+03 .647E+03 .647E+03 .647E+03 647Et03
.400E+00 .575E+02 CR--Si .992E+02 .000E+00 .t32E+02 .l28E+65 .357Ee03 MH--54 .498E+04 .et0E+00 .253E+05 .400E+04 .490E+04 .184E+07 .766E*44 FE--59 .948E+04 .836E+05 .235E+05 .406E+44 .000E+00 .102E+47 .244E+45 C0--58 .382E+04 .000E+00 .122E+04 .000E+04 .000E+00 .777E+06 .lllE+05 CO--60 .ll8E+05 .000E+00 .802E+04 .000E+04 .000E+00 .45tE+07 .319E+45 2N--65 .3tlE+05 .193E+05 .626E+05 .000E+00 .325E+05 .647E+06 .514E+05 SR--89 .ll4E+05 .398E+06 .000E+08 .000E+00 .006E+00 .283E+07 .612E.uS SR--90 .259E+07 .409E+88 .000E+00 .000E+44 .480E+00 .ll2E+08 . 3 3 t E
- 0/.
2R--95 .203E+05 .Il5E+06 .279E+05 .000E+00 .3tlE+05 .175E+07 .217E+05 I--131 .196E+05 .379E+05 7444E+05 .148E+08 .518E+05 .006E+04 .106E+04 ,
I--133 .560E+04 .132E+05 .192E+05 .356E+07 .224E+05 .006E+48 .216E*u4 CS-134 .745E+05 .396E+06 .703E+06 .4eeE+04 .190E+06 .834E+05 .133E+04 CS-136 .529E+05 .483E+05 .135E+06 .400E+08 .564E+05 .ll8E+05 .143E 04 i CS-137 .455E+05 .549E+06 .682E+46 .008E+44 .172E+06 .713E+05 .133E+04 BA-140 .290E+04 .560E+05 .56eE+02 .000E+44 .334E+02 .164E+07 .384E+05 CE-141 .199E+04 .277E+05 .167E+05 .000E+46 .525E+04 .517E+06 .216E*05 BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF l FOR N/0,
, DEPLETED X/O AND RELATIVE DEPOSITION llP-1-230 Revision 6 Attachment 10.16 (1 of 19)
I i
l . TABLE 10 (CONT.J . ,
3
- PAllWAY DOSE FACTORS DUE TO RADIONUCLIDES OTHER i .
THAN NOBLE GASES, R 1
~
i
] ENVIRONMENTAL PATHUAY-DOGE CONVERSION FACTORS A(I) FOR GASEOUS DISCHARGES I
l PATHUAY: INHALATION -
ACE GROUP: CHILD (2 0F 4 )
i t .
NUCLIDE ORCAN OO8E FACT 0RS (MREM /YR PER UCI/CU. METER) 1 TOTAL BODY BONE LIVER THYROID KIDHEY LUNG GI-LLI !
- _______ _____m__ ________ ________ ________ ________
________ ________ i l N----3 .182E+04 .000E+0e .112E+04 .Il2E+44 .ll2E+04 .ll2E+04 .ll2E+04 i CR--58 .354E+43 .000E+44 .484E+44 .855E+02 .243E*02 .174E+05 .009E+44 4
MH--54 .951E+44 .486E+44 .429E+45 .460E+44 .866E+45 .158E+47 .229E+65 i FE--59 .367E+45 .247E+65 .334E+05 .400E+0e .486E+44 .327E+47 .747E+65 C0--58 .386E+44 .600E+44 .177E+44 .446E+44 .000E+44 .lllE+47 .344E+05 CO--60 .226E+05 .446E+44 . .831E+05 .460E+80 .486E+44 .707E+47 .962E+45
~
j 2N--65 .783E+45 .426E+65 .ll3E+46 .440E+0e .714E+05 .995E+46 .863E+45 t SR--89 .372E+05 .599E+66 .444E+04 .666E+44 .464E+0e .216E+47 .167E+46 i SR--Se .644E+47 . tete +49 . 6 8 6E+ 4 4 .664E+60 .400E+0e ,.lltE+48 .343E+66 l 2R--95 .37eE+05 .19sE+66 .4tSE+45 .40eE+44 .596E+45 .223E+47 .618E+05 I--138 .273E+65 .48tE+65 .48tE+45 .162E+49 .788E+05 .000E+44 .284E+44 I--833 .77eE+44 .166E+45 .283E+05 .385E+47 .338E+45 *
.040E+0e .548E+04 CS-134 .225E+G6 .651E+46 .letE+07 .468E+44 .330E+06 .12tE+46 .385E+44
! CS-136 .tl6E+46 .651E+65 .17tE+46 .40eE+44 .955E+45 .145E+45 .41GE+44 l CS-137 .128E+46 .967E+66 .825E+46 .444E+44 .282E+46 .te4E+46 .362E+44 SA-144 .433E*04 .746E+05 .648E+02 . tete +0e .2tlE+02 .174E+07 .te2E+46 '
. CE-141 .290E+44 .392E+G5 .195E+05 .448E+04 .455E+44 .544E+46 .566E+45 4
- BASED ON 1 UCI/SEC RELEASE RATE OF EACH ISOTOPE 3 AND A VALUE OF 1 FOR X/0, i
DEPLETED X/G AND RELATIVE DEPOSITION l
IIP-1-230 Revision 6 80
TABLE 10 (CON'T) '
5 PATHWAYDOSEFACTORSDfETORADIONUCLIDESOTHER THAN NOBLE GASES, R i
ENVIRONMENTAL PATHWAY-DOSE COHVERSIGH FACTORS R( I) FOR GASE058 DISCHARGES l PATHUAY: INHALATION ACE GROUP: TEEH ( 3 0F 4 )
HUCLIDE ORGAH OOSE FACT 0RS (MREM /YR PER UCI/CU. HETER)
TOTAL BODY B0HE LIVER THYROID KIDHEY LUNG CI-LLI H----3 .127E+44 .000E+4e .127E+44 .827E+04 .t27E+44 .127E+44 .127E+04 CR -58 .135E+03 ,000E+00 .400E+08 .750E+02 .307E+02 .21eE+05 .300E+04 MN--34 .840E+04 .000E*00 .SilE*03 .000E+06 .t27E+05 .198E+07 .668E+05 '
FE--59 .343E+05 .359E+05 .370E+05 .000E+06 .400E+00 .153E+07 .l?8E+06 CO--58 .278E+04 .400E+04 .207E+04 .000E+08 .000E+00 .134E+07 .952E+05 CO--60 .198E+05 .000E+44 .15tE+05 .000E+04 .006E+00 .872E+07 .259E+06 ZH -65 .624E+05 .386E+45 .334E+06 .000E+44 .864E+05 .t24E+07 .466E+05 SR--89 .325E+05 .434E+06 .484E+00 .400E+08 .000E+00 .242E+0? .37tE+06 SR--98 .668E+07 .198E+49 .464E+49 .000E+4e .000E+00 .165E+08 .765E+06 ZR--95 .385E+05 .346E+86 .458E+45 .480E+84 .674E+05 .269E+07 .149E+06 I--831 .264E+05 .354E*05 .49tE+05 .146E+48 .840E+05- .000E+00 .649E+04 ,
I--833 .622E+04 .122E+05 .203E+45 .292E+47 .359E+05 .000E+00 .103E+05 "
CS-134 .549E+06 .502E+06 .It3E+47 .446E+88 .375E+06 .t46E+46 .976E+04 CS-136 .337E+06 .515E+05 .194E+06 .484E+88 .ll4E+46 .t?8E+45 .109E+65 CS-137 .38tE+06 .670E+06 .848E+06 .400E+44 .344E+46 .t2tE+06 .848E+04 BA-140 .352E+04 .547E+05 ,670E+02 .000E+00 .228E+02 .283E+07 .229E+06 CE-141 .217E+04 .284E+05 .190E+05 .040E+44 .888E+44 .684E+06 .t26E+06 BASED OH 3 UCI/SEC RELEASE RATE OF EACH I'SOTOPE I AHO A VALUE OF 1 FOR X/O, DEPLETED X/O AND RELATIVE DEPOSITION IIP-1-230 Revision 6 Attachment.10.16 (3 of 19) 81 l-
TABLE 10 (CON' ) ,
1 l
PATHWAY DOSE FACTORS DUE TO RADIONUCLIDES OTHER THANNOBLEGASES,R l -
1
, ENVIRONMENTAL PATHWAY-DOSE COHVERSION FACTORS R( I ) FCR. GASEOUS DISCHARGES 1
PATHWAY: IHHALATION ACE GROUP: 400LT ( 4 OF 4 )
HUCLIDE DRGAH D08E F A C'T O R S (NREN/YR PER UCI/CU.NETER)
TOTAL BODY BONE LIVER THYROID KIDHEY LUNG GI-LLI H----3 .126E+04 .000E+00 .126E+04 .126E+44 .526E+04 .l26E+04 .126E+04 CR--Si .300E+03 .000E+44 .000E+04 .595E+42 .220E+02 .344E+05 .332E+04 MH--54 .630E+04 .000E+0e .396E+05 .000E+48 .984E+84 .544E+87 .774E+05
, FE--59 .30AE+05 .Il8E+45 .278E+05 .840E+00 .400E+00 .102E+87 .188E+06 .
CO--58 .207E+04 .000E 30 .158E+04 .000E+0e .044E+00 .926E+96 .106E+06 !
CO--66 .340E+4S .000E+00 .ll5E+05 .000E+0S .086E+00 .597E+07 .265E+06 2H--65 .466E.05 .324E+05 .803E+06 .800E+04 .690E+05 .864E+46 .534E+05 SR--89 .8 PE+04 .304E+06 .000E+44 .000E+48 .400E+64 .344E+07 .350E+06 !
SR--90 .649E+07 .992E+08 .060E+08 .000E+88 .486E+08 .964E+07 .722E+06 j 2R--95 .233E+05 .307E+06 .344E+05 .000E+44 .542E+05 .177E+07 .154E+06 I--131 .20SE+05 .252E+05 .358E+05 .ll9E+08 .613E+05 .000E+08 .628E+04 I--133 .452E+04 .864E+04 .348E+45 .285E+07 .258E+05 .000E*04 .886E+04 CS-134 .728E+06 .373E+06 .848E+46 .000E+48 .287E+06 .976E+G5 .304E+05 1 CS-136 .ll0E+06 .390E+05 .146E+06 .000E+0e .856E+05 .124E+05 .ll?E+05 CS-137 .428E+06 .478E+06 .62tE+06 .000E+44 .222E+06 .752E+45 .164E+05 .
S A-14 0 .257E+04 .390E+05 .490E+02 .000E+60 .367E+02 .827E+07 .288E+06 CE-148 .153E+04 .199E+05 .335E+05 .406E+48 .626E+04 .362E+06 .120E+06 BASED ON I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AHO A VALUE OF l FOR X/Q, DEPLETED X/O AND RELPTIVE DEPOSITION llP-1-230 Revision 6 Attachment 10.16 (4 of 19) 82 i
e
i TABLE 19 (CONT.). _
i PATHWAY DOSE FACTORS DUE TO RADIONUCLIDES OTHER THANN0BLNGASES,R 1
ENVIRONMENTAL PATHWAY-DOSE CONVERSIGH FACTORS R( I) FOR CASE 058 DISCHARCES PATHWAY: GROUND-PLAHE DEPOSITION ACE GRour: ALL (1 0F 1 )
f HUCLIDE ORCAN D0SE FACT 0RS _ (SG. HETER-HREH/YR PER UCI/SEC )
H----3 .000E+00 g
- CR--Si .463E+07 HH--54 .138E+10
FE--59 .27tE+09 00--58 .376E+09 CD--60 .215E+11 {
i 2H--65 .74tE+09 SR--89 .2tSE+65 SR--90 .600E+40 ZR--95 .243E+49 I--131 .172E+08 I--133 .245E+07 CS-134 .477E+fe' CS-136 .tS6E*69 ^
CS-137 .803E+18
{
.204E+08 SA-140 CE-141 .336E+48 BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR X/G, DEPLETED X/Q AHD RELATIVE DEPOSITION Attachment 10.16 (5 of 19) j IIP-1-230 Revision 6 83
l TABLE 13 (CONT.)
PATlWAY DOSE FACTORS DUE TO RADIONUCLIDES OTHER
- THAN NOBLE GASES, R i
i .
ENVIROHnENTAL PATHWAY-DOSE CONVERSION FACTORS R( I) FOR CASEOWS DISCHARSES i
! PATHWAY: COWS MILK (CONTAMINATED FORAGE) AGE GROUP: INFANT (1 0F 4 )
1 l '
! HUCLIDE ORCAN D0SE FACT 0RS (SG. METER-MREM /YR PER UCI/SEC)
TOTAL BODY BONE LIVER THYROID KIDHEY LUNC CI-LLI I H----3 .23GE+44 .464E+ee .238E+e4 .238E+44 .238E+e4 .238E+44 .238E+44
- CR--51 .844E+86 .466E+44 .484E+0e .525E+46 .ll5E+46 .192E+47 .234E+88 ,
! MN--54 .442E+48 .446E+44
.195E+49 .44GE+44 .432E+48 .446E+44 .716E+49
, FE--59 .77eE+49 .ll2E+10 .196E+14 .ee8E+88 .486E+4e .578E+49 .934E+49
. CD--58 .300E+49 .444E+64 .12tE+49 .400E+64 .666E+44 .486E+44 .362E+49 I CO--64 .144E+18 .400E+44 .44tE+49 .446E+4e .446E+44 .944E+44 .le5E+10
- ZH--65 .439E+13 .277E+18 .95tE+38 .eGGE+4e .468E+ll .846E+0e .Se3E+l1 i SR--89 .184E+10 .628E+11 .486E+44 .444E+4e .486E+44 .444E+44 .129E+14 SR--98 .355E+12 .648E+12 .eeGE+44 .444E+44 .44GE+04 .446E+4e .759E+ie j 2R--95 .587E+44 .348E+45 .828E+44 .488E+44 .692E+04 .eetE+et .412E+07
, I--131 .341E+10 . .27tE+10 .320E+1e .'l65E+l3 .373E+10 .440E+44 .ll4E+49 I--133 .355E+48 .363E+08 .529E+48 .962E+10' .764E+08 .466E+48 .895E+07 i sS-834 .34eE+13 .l81E+l2 .337E+12 .444E+44 .867E+11 .356E+11 .985E+89
, CS-136 .le8E+11 .982E+10 .289E+18 .444E+0e .ll5E+11 .235E+14 .439E+49 i CS-137 .283E+ll .257E+l2 .34tE+12 .446E+44 .848E+ll .327E+11 .94tE+49 i
BA-14e .689E+00 .824E+le .324E+47 .000E+04 .285E+46 .738E+86 .295E+49 l CE-141 .855E+45 .216E+46 .132E+46 .484E+04 .447E+45 .444E+44 .682E+08 J
i . ,
) BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR X/0, 1 DEPLETED X/G AND RELATIVE DEPOSITION }
I IIP-1-230 Revision 6 !
g Attachment 10.16 (6 of 19) )
t
---.___w I
a TABLE IS (CoH'T) .
PATHWAY DOSE FACTORS DUE TO RADIONUCLIDES OTHER
- t
. THAN NOBLE GASES, R i
l .
ENVIRONMENTAL PATHWAY-DOSE CONVERSIGH FACTORS R(I) FOR CASE 058 DISCHARGES PATHWAYS COWS HILK (CONTientHATED FORACE) ACE GROUP: CHILD ( 2 OF 4 ) f l
HUCLIDE oRCAN D0SE FA C'T 0 R S ( SG. METER-MREN/YR PER UCI/SEC )
TOTAL, BODY BONE LIVER THYROID KIDHEY LUHG GI-LLI
! H----3 .157E+44 .400E+04 .357E+44 .357E+44 .857E*e4 .157E+44 .157E+04 l CR--51 .548E+46 . tete +ee .464E+44 .292E+46 .774E+45 .515E+46 .269E+49 i
, HH--54 .??9E+48 .eSeE+04 .865E+49 .884E+86 .294E+88 .44GE+44 .879E+68 FE--59 .483E+e9 .666E+49 .974E+49 .440E+64 .406E+44 .2SSE+49 .ledE+14 CO--58 .385E+69 .400E+44 .605E+68 .66eE+44 . 4 e E+ 4 4 . 4 e E+ 4 4 .353E+49 00--64 .636E+s9 .400E+44 .216E+49 .466E+88 . 44 E+ 6 e .466E+44 .124E+18 2N--65 .342E+1I .28?E+81 .556E+1I .804E+44 .347E+1I .et4E+04 .966E+84 SR--89 .943E+09 .334E+11 .446E+44 .48eE+44 . 44 K+ 0 e .406E+00 .l28E+;6 SR--98 .342E+l2 .558E+12 .446E+44 .444E+44 .400E+44 .600E+44 .752E+18 2R--95 .374E+64 .19fE+65 .42tE+44 .440E+00 .662E+44 .600E+60 .439E+47 I--131 .743E+49 .l34E+10 .83tE+44 .432E+12 .215E+10 .444E+0e .ll6E+49 I--133 .645E+47 .872E+49 .213E+49 .395E+14 .354E+49 .484E+44 .457E+87 CS-134 .J8SE+ll .ll2E+12 .384E+12 .44eE+44 .570E+11 .245E+11 .992E+49 CS-136 .994E+10 .503E+10 .338E+ll .000E+44 .736E+14 .lleE+lo .466E+49 CS-137 .224E+ll .16tE+12 .854E+12 .444E+44 .563E+ll .191E+89 .966E+49 BA-140 .34fE+68 .584E+49 .58tE+66 .444E+46 .367E+46 .385E+46 .296E+49 CE-141 .900E+64 .le9E+66 .544E+45 .000E+0e .239E+05 .GetE+ee .679E+49 4
BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AHO A VALUE OF 1 FOR X/0, DEPLETED X/G AND RELATIVE DEPOSITION l
1 HP-I-230 Revision 6 Attachment. 10.16 (7 of 19) [
j 85
(
t
_ _ _ _ _ - _ _ _ - _ _ _- _- - - __ . - - ._ L . ~ . - A
~
TABLE 10 (c0el'TI PATlWAY DOSE FACTORS DUE TO RADIONUCLIDES OTIER IllAll llDBLE ' GASES, R g ENVIRONMENTAL PATHWAY-DOSE CONVERSIGH FACTORS R( I ) FOR CASEOUS DISCHARGES PATHWAY: COWS MILK (CONTAMINATED FORACE)
ACE GROUP TEEH (3 UF 4)
NUCLIDE ORCAH D0SE FACT 0RS ( SO.NETER-NREM/YR PER UCL"SEC )
TOTAL BODY BONE LIVER THYROID KIDHEY LUNC GI-L LI H----3 .994E+43 .GetE+es .994E+03 .994E+03 .994E+03 .994E+03 .994E+43 CR--58 .249E+06 .464E+04 .400E+0e .139E+46 .546E+05 .355E+46 .418E+0S MM--54 .139E+48 .666E+ee .700E+$8 .000E+44 .209E+0S .400E+0e .544E+49 FE--59 .233E+s9 .259E+49 .684E+49 .eetE+44 .000E+04 .194E+49 .943E+14 C0--58 .993E+48 - .460E*04 .396E+68 .400E*00 .400E+44 .408E+44 .546E+49 CO--68 .313E+49 .466E+64 .139E+49 .000E+04 .400E+4e .e46E+04 .38tE+10 2H--65 .I7GE+01 .I45E+11 .365E+1I .88SE+44 .234E+11 .SS4E+44 .155E+11 i
SR--89 .392E+09 .133E+1l .46SE+ee .46SE+00 .SeOE+0e .4eSE+68 .159E+14 SR--90 .886E+ll .330E+12 .40eE+4e .844E+44 .488Et48 .484E+44 .926E+le t i ZR--95 .179E+e4 .824E+44 .26eE+44 .SetE+04 .392E+44 .440E+48 .600E+s7 I--831 .443E+09 .536E+49 .754E+49 .219E+12 .129E+10 .400E+44 .148E+09
- I--133 .366E+47 .768E+07 .l20E+44 .86SE+10 ~.2tlE+49 . tete +ee .908E+47
! CS-134 .531E+11 .486E+11 .Il4E+12 .400E+44 .364E+11 .l39E+11 .142E+14 CS-136 .599E+10 .223E+14 .877Eele .400E+'40 .477E+14 .752E+49 .745E+49 CS-137 .388E+11 .669E+ll .894E+ll .480E+46 .383E+11 .llSE+18 .127E+10 i BA-144 .356E+88 .242E+09 .296E+44 .444E+88 .194E+46 .199E+46 .373E+49 CE-141 .344E+44 .443E445 .296E*05 .400E+44 .339E+05 .600E+00 .846E+49 i
. BASED OH 1 UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR X/0, DEPLETED X/G AND RELATIVE DEPOSITION l
j HP-1-230 Hevision 6 Attachment 10.16 (8 of 19)
! 86 1 .
E _-- _ _ _________ _ _ _ _ _ _ _ _ - _. .. t . __.-. ._ ._ _ _ _ . . ._-. ._. _
TABLE 13 (Coel*T) .
1 PATHWAY DOSE FACTORS DUE 10 RADIONUCLIDES DIlER TilAll100BLE IGASES, R g i
i-ENVIRONMENTAL PATHWAY-DOSE CONVERSI0H FACTORS R(I) FOR GASEOUS OfSCHARCES PATHWAY: COWS MILK (CONTAMINATED FORAGE) - AGE GROUP: AOULT ( 4 0F 4 )
I HUCLIDE ORCAN D0SE FACT 0RS ( 80. HETER-NREN/YR PER UCI/SEC )
TOTAL BODY BONE LIVER THYROID KIDHEY LUNG GI-LLI
-_------ _------- ---_-__- )
l H----3 .763E+43 .400E+44 .763E+03 .763E+03 .763E+43 .763E+43 .763E*43 i CR--51 .343E+46 .444E+0e .400E+4e .852E+05 .384E+45 .389E+66 .359E+49 MH--54 .902E+47 .400E+88 .420E+48 .600E+44 .12SE+0S .80eE+04 .129E+49 ~
.133E+49 .I48E+49 .340E+89 .Ge4E+44 .SeeE*80 .973E+88 .Il6E+le i FE--59 C0--58 .528E+48 .444E+06 .225F+48 .666E+46 .486E+44 .444E+44 .477E+49 C0--66 .lGIE+49 .Ge4E+44 .820E+48 .446E+46 .444E+44 .eetE+88 .154E+16 2H--65 .996E+10 .695E+le .28SE+11 .StGE+44 .I46E+11 .444E+04 .937E+11 SR--89 .266E+69 .724E+14 .440E+44 .666E+86 .684E+0e .400E+44 .Il6E+16 '
SR--90 .574E+11 .234E+12 .464E+00 .464E+44 .464E+44 .GetE+4e .676E+le 2R--95 .le2E+44 .47tE+44 .15tE+44 .SetE+64 .237E+44 .88eE+44 .479E+07 I--131 .242E+89 .295E+49 .423E+89 .138E+12 .724E+49 .486E+86 .lllE+49 I--133 .245E+47 .36eE+07 .674E+87. .99tE+49 .ll8E+48 .400E+88 .686E+47 CS-134 .545E+ll .
268E+18 .666E+13 .804E+44 .216E+11 .786E+10 .ll?E+18 i CS-136 .372E+10 .131E+10 .587E+le .484E+48 .287E+10 .394E+49 .587E+49 CS-137 .331E+l1 .369E+11 .565E+11 .SetE+48 .17tE+11 .569E+10 .977E+49 ~
BA-140 .079E+07 .534E+49 .16SE+06 .400E+44 .572E+05 .964E+85 .276E+49 CE-141 .165E+44 .242E+45 .163E+45 .684E+48 .759E+44 .000E+48 .625E+48 1
BASED OH I UCI/SEC RELEnSE RATE OF EACH ISOTOPE I' AND A VALUE OF 1 FOR X/0,
! DEPLETED M/0 AND RELATIVE DEPOSITION i
) IIP-I-230 Revision 6 l 87 16 (9 of 19) 1 l
{ i o_ _ _ _ _ . _ _ _ _ __ _ _ _ _ . t____ _ __ ._ ._. _ _ _ _ _ _
1 TABLE 10 (CON'T) l PAllWAY DOSE FACTORS DUE TO RADIONUCLIDES DIllER TilAN NOBLE' GASES, R, L
ENVIRONMENTAL PATHWAY-DOSE CONVERS!0H FACTORS R(I) FOR CASEOUS DISCHARGES PATHWAY: MEAT (CONTAMIHATED FORAGE) AGE CROUP: CHILD (1 OF 3)
HUCLIDE ORGAN D08E FACTORS (SQ. METER-MREM /YR PER UCI/SEC )
TOTAL BODY BONE LIVER THYROID KIDHEY LUNC CI-LLI H----3 .234E+03 .000E+00 .234E+03 .234E+03 .234E+03 .234E+03 .234E+03 CR--51 .875E+04 .000E+00 .000E+00 .486E+44 .133E+04 .887E+44 .464E+46 MH--54 .213E+07 .000E+00 .800E*07 .000E+44 .224E+07 .000E+06 .672E+07 FE--59 .382E+09 .3/5E+09 .606E+89 .000E+00 .840E*00 .l?6E+09 .631E+49 :
C0--58 .501E+08 .000E+00 .164E+08 .000E+88 .000E+00 .000E+08 .955E+08 !
CO--60 .204E+89 .000E+00 .693E+08 .000E+00 .400E+00 .006E+08 .384E+09 ZH--65 .62tE+09 .375E+09 .999E+s9 .400E+04 .629E+89 .086E+00 .l?5E+49 SR--89 .137E+08 .480E+09 .400E+08 .460E+00 .446E+44 .000E+08 .886E+08 SR--98 .264E+10 , .104E+11 .000E+00 .000E+08 .400E+48 .000E+88 .140E+09 ZR--95 .520E*06 .266E+07 .584E+06 .000E+4e .836E+06 .000E+40 .609E+49 p I--131 .94tE+07 .165E+08 .166E+08 .547E+le .272E+08 .000E+88 .147E+07 -
I--133 .269E+00 .574E+00 .780E+00 .332E+03 .ll8E+01 .000E+84 .286E+00 CS-134 .384E+09 .907E+09 .349E+18 .400E+08 .461E+89 .165E+49 .802E*07 CS-136 .294E+08 .160E+08 .439E+48 .000E+00 .234E+08 .349E+07 .154E+07.
CS-137 .38CE+09 .133E+10 .328E+18 .880E+44 .486E+49 .156E+49 .799E+07 BA-140 .254E+07 .435E+08 .388E+45 .400E+80 .324E+05 .227E+85 .220E+48 CE-141 .164E+04 .221E+05 .lleE+05 .406E+08 .484E+04 .084E+08 .330E+08 BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR X/Q, DEPLETED X/O AND RELATIVE DEPOSITION l W-1-230 RedsUn 6 88 Attaclunent 10.16 (10 of 19)
i 4
TABLE IG (CON'T) ,
1 PATlWAY DOSE FACTORS DUE TO RADIONUCLIDES OTIER
~
thall NOBLE '6ASES, R g ENVIRONMENTAL PATHUAY-DOSE CONVERSIGH FACTORS R(I) FOR CASEOUS DISCHARGES l
. AGE GROUP: TEEN ( 2 0F 3 ) l PATHUAY: HEAT (CONTAHINATED FORAGE)
I ORGAH D0SE FACT 0RS (SO. HETER-HREM/YR PER UCI/SEC )
HUCLIDE TOTAL BODY BONE LIVER THYROID KIbHEY LUNG GI-LLI i -------- -------- --------
H----J .994E+03 .400E+44 .194E+03 ,.194E+43 .194E+03 .194E+03 .194E+43
.561E+04 .400E+44 .000E+44 .312E+44 .123E+44 .848E+44 .943E+46 CR--58 HH--54 .339E+07 .404E+0e .788E+47 . 40 6E+ 4 4 . .249E+47 .600E*00 .143E+48
-FE--59 .194E+s9 .28tE+09 .493E+89 .844E+4e .000E+44 .156E+49 .ll?E+14
.323E+48 .400E+0e .140E+68 .SetE+4e .484E+44 .044E+44 .193E+49 CO--58 .400E+80 .76eE+49 CO--64 .33tE+49 .400E+04 .583E+48 .400E+04 .GetE+4e ZH--65 .445E+49 .25eE+49 .868E+49 .648E+88 .555E+89 .404E+6e .367E+49 SR -89 .726E+47 .253E+49 .844E+4e .440E+44 .664E+04 .484E+44 .342E+48 E SR--94 ,199E+18 .845E+10 .404E+44 .404E+68 .444E+4e .eGGE+44 .226E+49 2R--95 .325E+06 .l54E+07 .472E+46 .644E+44 .693E+86 .844E+04 .l89E+10 1--831 ,667E+07 .887E+47 .124E*48 .363E+le .214E+88 .084E+44 .246E+47 I--133 .164E+03 .389E+44 .524E+04 .732E+02 . .920E+44 .004E+44 .397E+44
'CS-134 ,562E+89 .514E+49 .12tE+10 .486E+0e .385E+89 .547E+49 .15tE+48 CS-136 .245E+48 .926E+47 .365E+48 .084E+44 .198E+49 .383E+07 .293E+87 CS-137 .335E+09 .724E+09 .963E+89 .084E+0e .328E+49 .127E+49 .137E+49 BA-140 .452E+07 .236E+48 .289E+05 .48eE+4e .98eE+04 .194E+45 .364E+88 CE-141 .941E+03 .Il7E+05 .784E+44 .440E+88 .369E+44 .GetE+0e .224E+88 SASED OH l UCI/SEC RELEASE RATE OF EACH ISOTOPE I AHO A VALUE OF 1 FOR X/0,
- DEPLETED X/O AND RELATIVE DEPOSITION HP-I-230 Revision 6 Attachment 10.16 (11 of 19)
- 89 6
r--_----_________---x...___._-_ ._
. ] . _ ., , ,_
TABLE 19 (CON'Tl ,
i !
PATitfAY DOSE FAC10RS DUE 10 RADiolluCLIDES OTIER I s S IllAll fl0BLE GASES, R i i !.
(
i ENVIRONMENTAL PATHWAY-DOSE CONVERSIGH FACTORS R(I) FOR GASEOWS DISCHiWISES f PATHWAY: MEAT <CONTANINATED FORAGE >
AGE GROUP ADULT < 3 0F 3 ) !
I HUCLIDE ORCAN D0SE FACT 0RS (SG. METER-NREN/YR PER UCI/SEC)
TOTAL 80DY GONE LIVER THYROID KIDHEY ' LUNG GI-LLI i
.325E+03 .SeeE+4e .325E+03 .325E+03 .325E+03 .325E+03 .325E+43 i H----3 CR--58 .742E+44 .setE+44 .406E+0e .489E+44 .155E+44 .93tE+44 .176E+C7 MN--54 .175E+47 .000E+44 .917E+47 .444E+44 .273E+47 .000E+44 .~28 t E+ 49 FE--59 .238E+49 .264E+49 .628E+89 .44eE+44 .GetE+44 .174E+49 .247E+1e C0--58 .468E+49 .460E+64 .182E+48 .466E+0e .440E+00 .400E+44 .368E+69 CO--60 .166E+49 .68eE+48 .752E+49 .446E+44 .844E+48 .646E+et .14tE+16 2H--65 .SilE+49 .355E+49 .il3E+1e .400E+4e .756E*e9 .400E+44 .792E+49 SR--89 .862E+07- .340E+49 .eetE+44 .600E+4e .eetE+44 .400E+00 .482E+49 ,
SR--90 .345E+1e .124E+11 .444E+6e .600E+44 .GetE+44 .448E+44 .359E+49 l 2R--95 .486E+e6 .887E+47 .599E+44 .880E+0e .944E+46 .GetE+44 .194E+14
.875E+67 .167E+49 .153E+48. .541E+10 .262E+48 .444E+44 .463E+07 I--131
.578E+44 4
I--133 .896E+88 .374E+64 .643E+88 .945E+02 .tl2E+48 .446E+80 C5-134 .326E+10 .647E+49 .154E+14 .460E+te .496E+49 .865E+49 .269E+49 CS-136 .338E+49 .l19E+48 .469E+49 .444E+64 .26tE+48 .358E+07 .533E+67 ,
CS-137 .781E+69 .872E+49 .319E+10 .446E+44 .485E+49 .135E+49 .23tE+48 SA-14e .18?E+47 .285E+49 .35SE+05 .000E+4s .922E+45 .205E+45 .587E+49 CE-141 .te7E+44 .140E+05 .946E+44 .444E+44 .446E+44 .404E+et .362E+08 i
i SASED OH 1 UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR X/0, DEPLETED X/O AND RELATIVE DEPOSITION O
HP-3-230 Revision 6 Attachment 10.16 (12 of 19) 2 90 e
h- . . _ . . - __ _ _ , . . . __ _ _ _ _ , _ , _ _ __
TABLE 19 (CON'T) - ,
l !
l PAlltfAY DOSE FACTORS DUE TO RADIONKLIDES OTER THAN NOBLE' GASES, R g -
4 ENVIRONMENTAL PATHWAY-DOSE CONVERSION FACTORS R(I) FOR CASEGUS SteeMbAGES ACE GROUP: CHILO (I OF 3)
PATHUAYi LEAFY VEGETABLES ,
gsg.ngIgg-nRgg/yg ggg ucI/sEc>
augligg ______ , _ _ _ ___ggsg ggceg _ _ _ ___ggg _ _ _I g g s BONE LIVER THYROID KIDHEY LUNG CI-LLI TOTAL 900Y -------- -------- -------- --------
.44eE+04 .000E*00 .400E+44 .400E+04 .444E+44 .49eE+44 .4stE+44~ ,
H----3 .617E+07 CR--51 .ll6E+46 .SetE+44 .400E+44 .645E+05 .176E+45 .llSE+46 MH--54 .377E+s9 .SeeE+44 .664E+e9 .SetE+88 .386E+89 .400E+44 .557E+49 FE--59 .338E+09 .395E+49 .639E+09 .eGeE+0e .884E+86 .lS5E+09 .665E+49
.196E+89 .400E+44 .64tE+48 .400E+44 .446E+04 .SetE+et .374E+89 C0--58 .218E+14 CO--60 .ll2E+le .80eE+ee .378E+49 .440E+44 .400E+48 .400E+48 2N--65 ,834E+10 .88tE+89 .216E+18 .setE+48 .336E+14 .SetE+80 .384E+49
.le2E+14 .000E+44 .400E+44 .000E+48 .400E+04 .138E+10 i SR--89 .357E+ll
.480E+49 .367E+11 SR--94 .395E+12 .124E+l3 .SetE+48 .SetE+44 .eetE+0e
.752E+44 .384E+47 .644E+86 .440E+44 .12tE+07 .40eE+44 .SSIE+69 2R--95 I I--838
.885E+48 .343E+49 .l43E+e9 .474E+11 .235E+49 .400E+44 .328E+48 I--833 .l65E+47 .354E+47 .43?E+47 .Sl2E+49 .729E+47 .600E+44 .l?6E+37 CS-334 .530E+18 .355E+11 .255E+11 .SetE+46 .79eE+14 .284E+10 .l38E+89 CS-136 .144E+49 . Gile +49 .223E+49 .000E+88 .Il9E+49 .l?7E+48 .783E*07 ;
CS-l37 .33SE+le .239E+ll .229E+ll .400E+44 .746E+18 .268E+84 .343E+49 i 84-14e .16eE+48 .275E+49 .24tE+46 .SetE+0e .783E+05 .143E+86 .139E+49 ~
CE-14l .483E+05 .652E+46 .325E+46 .446E+86 .943E+46 .400E+ee .446E+89 SASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF l FOR M/0, j DEPLETED M/G AND RELATIVE DEPOSITI0H l
HP-I--230 Revision 6 h Attachment 10.16 (13 of 19) 4 91 i
___j _ _ _ _ __ _ _ __
TABLE ID (con'. .
i '
PAllWAY DOSE FACIORS DUE TO RADIONUCLIDES OTHER .
~
. THAN NDBLEfGASES, R g ENVIRONMENTAL PATHWAY-DOSE CONVERSION FACTORS R(I) FOR CASE 008 DISCHAftCES .
PATHWAYS LEAFY VEGETABLES AGE GROUP: TEEN ( 2 0F 3 )
1 i HUCLIDE ORCAN D0SE FACT 0RS ( 80. HETER-HREN/YR PER UCI/SEC) 4 TOTAL BODY SOME LIVER THYROID KIDHEY LUNC CI-LLI
_______ ________ ________ ________ ________ ________ ________ ________ i
- H----3 .259E+44 .SetE+44 .259E+44 .259E+44 .259E+44 .259E+44 .259E+04 JR--SI .613E+05 .600E+44 .064E+4e .340E+45 .834E+65 .075E+45 .le3E+48 MH--54 .946E+48 .444E+44 .454E+49 .400E+44 .135E+09 .406F+0e .93tE+49 FE--59 .16tE+89 .17eE+49 .416E+49 .600E+6e .686E+44 .13tE+49 .983E+49 CO--58 .984E+49 .400E+44 .434E+68 .40eE+44 . 446E+ 44 .440E+44 .599E+49 SG--64 .564E+49 .400E+88 .249E+49 .400E+64 .466E+44 .446E+44 .324E+14 2H--65 .665E+49 .423E+49 .847E+14. .484E+44 .946E+49 .400E+44 .622E+49
- SR--89 .43tE+89 .154E+11 .600E+44 .446E+04 .446E+08 .440E+44 .l?9E+14 J i SR--94 .665E+12 .75tE+12 .484E+44 .000E+44 .466E+44 .SetE+44 .281E+11
, 2R--95 .372E+46 .l?tE+47 .541E+46 .400E+44 .795E+66 .440E+0S .125E+18 i__iai .577E.4. .767E+4. .ie7E+.9 .ai2E+ii . 5E+49 .8.eE.4. .2i2E...
I I--833 .teeE+47 .194E+47 .329E+47 .459E+49 .577E+47 .000E+88 .249E+07 CS-134 .752E+14 .669E+te .162E+11 .040E+48 .StSE+14 .197E+14 .202E+49 CS-136 .it4E+09 .43tE+4G .976E+49 .400E+44 .924E+48 .146E+44 .137E+66 CS-337 .469E+10 . tete +11 .135E+11 .440E+44 .459E+10 .178E+14 .192E+49
! SA-144 .884E+07 .137E+89 .169E+66 .444E+49 .576E+45 .fl3E+46 .282E+49 CE-141 .216E+05 .28tE+46 .198E+46 .40eE+44 .894E+45 .40eE+44 .537E+49 j
l l BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AHO A VALUE OF 1 FOR X/Q, DEPLETED X/O AND RELATIVE DEPOSITION i HP-1-230 Revision 6 Attaciument 10.16 (14 of 19) 92 i
1 g s
TABLE 19 (CON'T, .
~
PAllWAY DOSE FACIORS DUE TO RAD 101100LIDES OTlER
. TilAll 1108tE MSES, R g ENVIRONMENTAL PATHUAY-DOSE CONVERSION FACTORS R(I) FOR CASE,0US DISCHARGES AGE GROUP: A00LT ( 30F 3 )
PATHUAY: LEAFY VECETABLES ,
HUCLIDE ORGAH D08E FACT 0RS (Se. HETER-HREN/YR PER UCI/5EC)
BONE LIVER THYROID KIDHEY LUNC GI-LLI TOTAL BODY -------- -------- -------- --------
.226E+04 .600E+44 .226E+44 .226E+44 .226E+44 .226E+44 .226E+44 H----3 .613E+45 CR--58 .462E+45 .400E+44 .466E+00 .276E+05 .162E+05 .ll6E+46
.597E+0S .000E+0e .313E+09 .400E+4e .930E+48 .000E+44 .958E+49 NH--54 .823E+48 .982E+89 FE--59 .ll3E+89 ,125E+49 .295S+49 .Ge6E+44 .000E+44 C0--50 .686E+68 .488E+00 . 3 ME+ 48 .000E+44 .404E+44 .400E+44 .62fE+49
.369E+09 .664E+4e .16?E449 .440E+49 .400E+44 .404E+44 .314E+18 CO--64 .684E+44 .635E+49 2H--65 .456E+49 .317E+49 .86tE+16 .GeeE+44 .674E+49 i
.294E+49 .99GE+10 ,60GE+86 .etGE+49 .eeOE+00 .etGE+44 .159E+14 SR--69 SR--98 .340E+12 .605E+l2 ,SetE+44 .eGGE+08 .446E+0e .444E+00 .l?5E+ll 2R--95 .254E+66 .ll7E+87 .375E+46 .440E+44 .599E+46 .440E+44 .119E+14 I--131 .66tE+68 .846E+68 .ll5E+49 .379E+ll .198E+49 .000E+44 .344E+49 I--133 .lllE+07 .269E+47 .363E+47 .534E+49 .634E+47 .846E+48 - .326E+67 C5-134 .982E+14 .453E+10 .leGE+11 .eetE+44 .349E+le .l 6E+14 .lS9E+49
.128E+49 .422E+49 .867E+49 .400E+04 .927E+0S .l27E+68 .lS9E+08 C5-136 CS-137 .578E+10 .636E+10 .87eE+14 .48eE+44 .295E+10 .98tE+49 .166E*49 BA-14e .837E+47 .12SE+49 .16tE+86 .480E+0e .546E+05 .999E+05 .263E+49 CE-141 .154E+45 .196E+46 . 133E+06 .000E+44 .616E+45 .600E+84 .587E+s9 SASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR M/0, ^
DEPLETED X/O AND RELATIVE DEPOSITION HP-1-230 Revision 6 Attaciument 10.16 (15 of 19) 93
' 5 . . .
_____}
t TABLE 13 (c0N'T, l
t .
PATlWAY DOSE FACTORS DUE TO RAD 100100LIDES OTIER
, thall 110BLE IGASES, R g ENVIRONMENTAL PATHWAY-DOSE CONVERSION FACTORS RCI) FOR GASEOUS DISCHARGES
, PATHWAY: COATS MILK (CONTANINATED FORAGE) . AGE GROUP: INFANT ( 1 0F 4 )
i t
- HUCLIDE ORGAN D0SE FACT 0RS (SG.NETER-NREM/YR PER UCI/SEC) i ------- _--_---------__------------_--------__-----------------------------_--- .
TOTAL'SODY BONE LIVER THYROID KIDHEY LUNG CI-LLI b
! H----3 .445E+05 .000E+44 .405E+45 .445E+45 .405E+45 .405E+45 .445E+45
! CR--51 .966E+05 .444E+04 .464E+04 .630E+05 .13SE+45 .123E+44 .2SIE+47 l NN--54 .530E+07 .setE+4e .234E+48 .000E+04 .5lSE+07 .400E+98 .859E+47 FE--59 .le6E+48 .846E+0S .254E+48 .44eE+68 .40eE+44 .75tE+47 .32tE+48 C0--58 .364E+48 .440E+04 .845E+68 .444E+44 .444E+44 .464E+44 .362E+49
! CO--60 .325E+49 . tete +4e .529E+49 .444E+00 .444E+44 .eetE+44 .326E+49 I
2H--65 .527E+1e .333E+88 .II4E+11 .StGE+40 .554E+10 .StGE+44 .964E+10 SR--89 .378E+10 .132E+12 .484E+44 .440E+4e .400E+0e .400E+44 .27tE+14 SR--94 .325E+12 .82SE+13 .GetE+44 .444E+44 .444E+44 .444E+44 .859E+ll 2R--95 .745E+03 .40SE+44 .994E+43 .884E+44 .le7E+04 .484E+44 .495E+06 I--131 .169E+10 .326E+14 .384E+18 .326E+13 .44SEtte .440E+44 .337E+49
, I--133 .tS6E+48 .436E+ee .635E+48 .115E+11 .844E+48 .888E+44 .le7E+0S l CS-134 .I82E+12 .542E+12 . tete +13 .840E+04 .26eE+12 .I67E+12 .275E+14 CS-136 .324E+11 .295E+11 .867E+11 .44GE+44 .345E+1i .746E+10 .132E+te CS-137 .640E+11 .772E+12 .943E+12 .444E+44 .242E+12 .982E+18 .282E+1e SA-t44 .743E+87 .844E+49 .844E+44 .SetE+44 .342E+05 .SS5E+05 .354E+88 CE-141 .lS6E+44 .260E*e5 .85SE+45 .440E+49 .4SSE+44 .400E+44 .SISE+07
, BASED GN i UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF 1 FOR X/S, j DEPLETED X/S AND RELATIVE DEPOSITION l .
j
}lP-1-230 Revision 6 Attachment. 10.16 (16 of 19)
- 94
- i. ,
. - __ . _ .t _ _ _ . .. . . -.
i.
TABLE 13 (CON'i,
) C' PATINAY DOSE FACIORS DUE 10 RADI0lluCLIDES DIIER
~
. t. TilAll 100BLE IGASES, R g -
.; /
3 ENVIRONMENTAL PATHWAY-DOSE COHVERSION FACTORS R(I) FOR GASEOSS DISCHAftGES
) PATHWAYr GOATS HILK (CONTAHINATED FORACE) . ACE GROUP: CHILD ( 2 OF 4 ) -
1 l .
14UCL IDE ORGAN D0SE FACTORS ( SG . METER
_______ _ _ _ _ __ _ _ __ __ _ _ _ _ _ _ __ __ __ __ __ __ _ _ _ _ _ _ __ __ _ _ __ __ __ __ _ _ _ _ __ _- MR E M / YR TOTAL 80DY BONE LIVER THYROID KIDHEY LUNG CI-LLI 4
- H----3 .267E+05 .888E+4e .267E+05 .267E+05 .267E+45 .267E+45 .267E+85 -
. CR--58 .649E+05 .400E+04 .400E+44 .330E+45 .924E+04 .6tSE+45 .323E+07 i MH--54 .335E+47 .se6E+44 .326E+48 .468E'+60 .353E+47 .GetE+44 .le6E+44
- FE--59 .629E+07 .784E+87 .326E+88 . tete +44 .480E+44 .366E+47 .135E+88 j CO--58 .222E+48 .464E+44 .727E+47 .SetE+84 .000E+44 .440E+44 .424E+48 CO--64 .764E+88 .884E+44 .259E+0S .400E+49 .444E+44 .SetE+44 . .343E+49' ZH--65 .4tlE+18 .248E+16 .664E+18 .SetE+44 .416E+10 .SetE+44 .ll6E+10 SR--89 .198E+10 .694E+11' .400E+44 .480E+44 .000E+44 .400E+44 .268E+14 SR--98 .297E+12 .ll7E+13 .48eE+44 .setE+04 .400E+44 .800E+ee .358E+11 2R--95 .449E+43 .236E+44 .565E+43 .48eE+0e .722E+03 .SetE+4e .527E+46 1 I--131 .892E+49 .l56E+14 .357E+14 .519E+12 .258E+10 .400E+0e .348E+49 I--133 .966E+07 .246E+44 .255E+0S .474E+10 .425E+0S .400E+44 .le3E+88 C5-134 .ll6E+12 .337E+12 .552E+12 .884E+0e .878E+12 .614E+18 .296E+le CS-136 .268E+11 .l5tE+11 .415E+11 .000E+44 .221E+11 .329E+le .146E+18 I CS-137 .683E+18 .484E+l2 .463E+12 .440E+44 .151E+12 .543E+11 .296E+18 BA-146 .489E+07 .781E+0S
.694E+45 . tete +44 .200E+45 .366E+45 .355E+49 CE-141 .976E+03 .33tE+85 .453E+44 .te6E+44 .286E+44 .eetE*04 .885E+47
{
BASED OH I UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF l FOR X/0, l DEPLETED M/S AND RELATIVE DEPOSITION HP-1-230 Revision 6 Attacte nt 10.16 (17 of 19) 95 l )
TABIf IS (C0tl*Ts .
PATWAY DOSE FACTORS DUE 10 RADIONUCLIDES OTHER
,. THAN manse GASES, R g .
ENVIRONMENTAL PATHUAY-DOSE CONVERSIGH FACTORS R(I) FOR GASEGUS DISCHARGES PATHWAY: GOATS MILK (CONTAMINATED FORAGE) . AGE GROUP: TEEN (3 0F 4) l i NUCLIDE ORGAH D0SE FACT 0RS (SG.NETER-NREN/YR PER UCI/SEC)
TOTAL 80DY B'ONE LIVER THYROID KIDHEY LUNC GI-LLI i ------- -------- -------- -------- -------, -------- -------- --------
! H----3 .169E+05 .400E+44 .869E+05 .869E+05 .169E+05 .169E+45 .669E+45 i
CR--51 .299E+05 .048E+44 .486E+44 .566E+65 .655E+04 .427E+05 .542E+47 MH--54 .167E+47 .006E+44 .44tE+47 .686E+0e .25tE+47 .000E+44 .172E+49
' FE--59 .343E+07 .336E+47 .785E+47 .400E+04 .400E+44 .247E+47 .186E+49 ,
CO--58 .194E+48 .000E+00 .476E+47 .400E+44 .e40E+44 .480E+44 .656E+48 CO--64 .376E+s3 .46eE+44 .867E+44 .000E+44 .SetE+44 .440E+00 .2t?E+49 2H--65 .265E+10 .t26E+18 .439E+14 .440E+48 .2SIE+90 .SetE+0e .196E+18 SR--89 .842E+49 .284E+11 .000E+44 .688E+44 .486E+64 .440E+64 .334E+10 SR--90 .l?tE+12' .694E+92 .SetE+44 .000E+04 .000E+44 .GetE+00 .195E+11 '
2R--95 .214E+03 .98SE+43 .392E+43 .eGGE+88 .45SE+43 .SetE+44 .720E+44 ,
! I--838 .484E+49 .643E+49 .901E+49 .263E+12 .855E+14
~
.486E+44 .178E+49 i
I--133 .44eE+47 .858E+07 .844E+49 .200E+10 .253E+88 .400E+00 .199E+48 CS-134 .159E+12 .346E+12 .343E+12 .800E+44 .le9E+12 .417E+18 .427E+18 '
I CS-136 .177E+18 .669E+00 .263E+11 .000E+44 .143E+11 .226E+10 .292E+14
- CS-137 .930E+tl .200E+I2 .267E+12 .400E+48 .949E+11 .353E+01 .38eE+18 i SA-140 .lS7E+s7 .290E+88 .356E+05 .setE+44 .12tE+45 .239E+45 .44GE+88
~
CE-141 .448E+43 .532E+44 .355E+44 .484E+44 .167E+44 .400E+44 .le2E+49 l .
i l
BASED ON 1 UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF i FOR X/0, DEPLETED M/G AND RELATIVE DEPOSITION
, i l HP-1-230 Revision 6 -
Attachment 10.16 (18 of 19) 96
- l~
I
f TABLE 19 (CON' .s ~
PATHWAY DOSE FACIORS DUE TO RADIONUCLIDES OTHER THAN NOBLE GASES, R g ENVIRONMENTAL PATHWAY-DOSE CONVERSION FACTORS R(I) FOR CASEOUS DfSCHARCES ;
AGE group: ADDLT (4 0F 4 )
PATHWAY: GOATS MILK (CONTAMINATED FORAGE) .
f ORGAN O O S .E FACT 0RS ( SG. METER-HREN/YR PER UCI/SEC )
HUCLIDE LIVER THYROID KIDHEY LUNG CI-LLI TOTAL BODY BONE
.484E+49 .138E+45 .834E+85 .638E+05 .130E+05 .336E+45 $
H----3 .838E+85 .377E+84 .227E+45 .434E+47 CR--51 .871E+85 .400E+88 .40$E+08 .182E+45
.585E+47 .400E+04 .158E+47 .006E+0e .155E+48 MM--54 .963E+66 .446E+44 .127E+47 .851E+68
.193E+07 .453E+87 .486E+49 .486E+44 FE--39 .374E+87 .etBE+49 .573E+48 C0--58 .633E+07 .000E+80 .282E+47 .466E+44 . 40 6E+ 4 6 ,
.984E+07 .44GE+66 .444E+04 .444E+44 .585E+49 CO--66 .217E+49 .440E+44 .446E+44 .165E+14
.IISE+18 .823E+49 .262E+10 .404E+00 .l?5E+18 i ZH--65 .486E+48 .404E+44 .244E+14' SR--89 .436E+69 .352E+11 .468E+44 .664E+44
.49tE+12 .484E+44 .400E+08 .446E+44 .444E+84 .l42E+11 SR--98 .321E+12 .SetE+84 .284E+03 .446E+49 .575E+06 .
ZR--95 .123E+03 .565E+03 .381E+03
.507E+49 .166E+12 .869E+89 .446E+68 .334E+49 I--131 .298E+09 .355E+49 .000E+44 .727E+47
.465E+07 .849E+07 .il9E+14 .l4tE+48 I--133 .247E+07 .647E+11 .285E+10 .354E+14 CS-134 .363E+12 .840E+11 .284E+12 .486E+44
,155E+11 .446E+49 .863E+10 .I18E+14 .176E+10 CS-136 .I82E+1i .393E+14 .571E+11 .293E+10
.lllE+12 .15tE+32 .446E+44 .514E+11 CS-137 .992E+18 .687E+44 .116E+65 .331E+48 BA-840 .105E+87 .36fE+68 .242E+05 .886E+44 i
.444E+48 .98tE+03 . G e 6E+ 0 8 .756E+47 CE-141 .223E+03 .296E+04 .l96E+44 BASED OH l UCI/SEC RELEASE RATE OF EACH ISOTOPE I AND A VALUE OF l FOR X/0, DEPLETED X/0 AND RELATIVE DEPOSITION 1
IIP-1-230 Revision 6 Attachment 10.16 (19 of 19) 97 k
I FIGURE 7 )
1 Relative Deposition for Ground-Level Releases (All Atmospheric Stability Classee) 10-3 -
l l l .
i .
I l
i 104 \ '
.-. N ;;;;
e i w ie :
h X i I N e N u I h
- A i
< s% .
E
$ 10-6 \
C
$8
,;. , , \, , ,
. . . i . .. i w 2 e i ie is e X
$ ~ '
l l' F ll 1 'AI l y l ll ll l l l l \ - I w
8 N l
10-6 ;
. , , .. i, , ,
, .. . , i,,,,
A l
, , . .. e.. . i e i . i ,,ii, i i i e t i ,
6e i t iiie i ii6 ei!ei :
I I I I I il I i i IIii i I I I IIltil l l l l l ' ll I
l l l l ll l l l l llllil i '
ll l l l l 10-7 0.1 1.0 10.0 100.0 200.0 f
PLUME TRAVEL DISTANCE (KILOMETERS) 1 i
Obtained from Regulatory Guide 1.111 (March,1976) l
~
HP-1-230 Revision 6 Attachment 10.17 (1 of 1)
- 98 i
j.
1
ANNUAL AVERAGE DISPERSION PARAMETERS AT OR BEYOND THE UNRESTRICTED AREA BOUNDARY (TABLE 11)
L71L MTERFORD SITE: USING JM - MC !?86 MET DATA - RUN 1/29/87 8ROUND ISEL RFLDSE 0 M G KCATo UNDDtETD CO N CT D USIN6 STAG ARD OPEN TERRAIN FACTORS ANNUAL M RASE CHI /9 (SEC/E TER CU KD) DISTANCE Im !LES FROM TE SITE KCTOR 0 250 0.500 0 750 1 000 1.500 2 000 2.500 3.000 3 500 4.000 4.500
$ 5.340E451629E45 8.454E46 4.249E-061.704E44 f.35tE47 4.064E-47 4.305E-07 3.250E-07 2.544E-07 2 091E@
$$W 4.44M4513ttE45 7 552E46 3.85N-061559E-04 8.52M-07 5.44M47 3.847E47 2.883E47 2.26M471832E47 SW 4.283E-051.34X-05 7.218E46 3.468E46147M44 8.057E-07 5.160E-07 3 62K-07 2 71M-07 2.12tt-071.725E-07 WSW 3.81N-051.178E-05 6.247E46 3181E46129X46 7 07?E-07 4.53E-07 3191E47 2 3tM471873E471.518E-07 W 2.056E45 4 33M44 3.40tE-041747E-06 7.14M47 3.91K47 2.511471769E471.32E471040E-07 8.432E-08 M 1.528E45 4.735E46 2.57X46131K44 5.344E-07 2.93K-071843E-071324E-07 f.f2N44 7 775E40 6.301E45 W 2.34E45 7.315E46 3.92E46 2.01346 8.221E-07 4.504E-07 2.84E-07 2.02K471.51E-071.189E-07 9.634E-08 M 4.37M451323E45 6.841E46 3.472E44141E44 7 820E47 5 06X47 3.591E-07 2.70tE47 2134E-071.740E-07 N 8.80N45 2.61M-051.323E-05 6 686E44 2.733E441.52M-04 9.920E47 7.0fR-07 5.381E-07 4.263E-07 3.488E-07 M 8.40M-05 2.501E45126M45 6.33M44 2.57N46142fE46 f.34K-07 4 6tM@ 5.000E-07 4.02tE47 3 279E-07 4 E 7 42X45 2.22E-051.134E45 5.72E44 2.330E441291E-06 8.409E47 5 79M47 4.540E-07 3 591E47 2 935E-07 EME 7.775E-05 2.32X-051.176E45 5.934E46 2.42N46134K44 8 771E-07 6.259E-07 4.744E-07 3.754E47 3.071E47 E 6.34K-051.91E-05 9.81E44 4.98M-06 2 034441 12tE46 7.334E47 5.218E-07 3.945E47 3.116(47 2.543E47 EK 5.661E451.6tK-05 8.639E46 4.351E441765E'-04 f.77tE47 6.381E-07 4.554-07 3.45R47 2.734E47 2.236E-07 SE 4.954E451.483E-05 7.558E46 3.790E461.525E44 0.437E47 5 51X-07 3.938E-07 2.tB9E-07 2.34tE471.939EW SSE 4 87X-051482E45 7.66tE46 3.852E44154244 8 498E47 5.51tE47 3 725E-07 2.968E-07 2 344E471913E47 ANNUAL AVDA6E CHI /9 (SEC/ETO CUED) DISTANCE Im!LES FROM TE $!TE SECTOR 5.000 7.500 -10.000 15.000 20 000 25 000 30.000 35.000 40.000 45.000 50.000 8 1.749E47 9.341E44 6 214E46 3.6tK44 2.54M481.93M-041.534-041.264E461.07M-04 9.237E49 8.102E49 SSW 1.525E47 7.785C-04 5.238E46 3.051E-08 2.00E-08155E-041225E40100N-04 8.42E49 7.232E49 6 311E-09 SW 1.435E-07 7.50tE46 4.t2X48 2.867E46196M40144N-08115N48 f.42X49 7.t22E49 6.001E-09 5.936E49 WSW 1.24E-07 6.61K44 4 342E46 2.531E-08173X-0812fM-041.01M-04 8 33E-09 7.011E49 6.021E49 5.256E-09 W 7.018E-04 3.67K-00 2.413E461.40E46 f.414-09 7.17M49 5.447E49 4.41K49 3.8tX49 3.331E-09 2.f06E-09 M 5.24N-00 2.742E401.??7E40104248 7.135E49 5.31E49 4.184E49 3.419E49 2.87X-Of 2.444E49 2.149E-09 W 8.01K40 4.189E-00 2.744E461.575E481.08tE-08 8.114E49 4.385E49 5.21K49 4.38K49 3.759E-09 3.27EE49 i M 1.455E47 7.74K-04 5.14X-00 3.04240 2.10E461.584E481254-061.034-04 8 73K49 7 534E49 6 600E-09 N 2.t2M-071.58M@ 1.050E47 6.339E-08 4.41K40 3.34K-04 2.64X46 2.201E-081.86E461.41K401.417E-09 M 2.771E-071.501E471.00M-07 6.052-08 4 22tE46 3.20E-00 2.55?t-04 2.11E4617?E461.554E-081366E-09 NE 2.440E471.323E-07 8.83tE46 5.290E-08 3.673E-00 2.77E-00 2.21M-041.824E441.545E-081.335E-C81 172E-08 )
EE 2.575E47138K47 9.283E46 5.554E-04 3.868E-00 2.t25E44 2 330E-041724E-061630E461.40fE481.23SE-02 l l
E 2.12?E471.140E-07 7.589E40 4.512E-04 3.12500 2.358E461.874-041544E461.30E-08112?E-08 9.87tE-0*
ESE 1.87E-071.011E-07 6.769E44 4.05X40 2.823E46 2.13E-001.70X40140E-081.191E-001.03M40 9.047E-09 SE 142M47 8.79M48 5 8tfE-06 3.54244 2.47X-081.8744014tSE46123E46104ft-06 9.07K49 7.979E-09 SE 160X47 8 584E46 5.72K-06 3.41M-00 2.34K-001.78IE46142X-081 174E40 9 93K-09 8.585E49 7.534E-09
, VO T AND SUILDING PARAMET DS!
RELDSE EIGHT (METERS) 0.00 REP. WIO EIGHT (ETDS) 10 0 DIAETR (ETUS) 0.00 8UILDING EIGHT (ETDS) 41 0 DIT VELOCITT (ETERS) 0.00 8LDS. MIN.CRS.SEC. AREA (SQ.ETERS) 2468.0 4
EAT DIS $10N RATE (CAL /SEC) 0.0 ALL BROUM LEVEL RELD SES.
HP-1-230 Revision 6 99 Attachment 10.18 (1 of 2) l
ANNUAL AVERAGE DISPERSION PARAMETERS AT OR BEYOND THE UNRESTRICTED AREA BOUNDARY (TABLE 11)
LPtL WATERFORD $!TE: USING JAN - MC 1986 MET DATA - RW 1/29/87 st0 W 8 LIVEL RELEASte 0 M ,
O KCAT: USEPLETO CH!/9 (EC/ETER CUED) FOR EACM SEGMDff E6 EXT lt0VNDARIES IN MILES FROM TW $!TE D!KCTION .5-1 1-2 2-3 3-4 45 5-10 10-20 20-30 30-40 40-50 FROM SITE S 8.324 44 1.t2K44 6 23tE-07 3.2tM47 2104E47 f.761E-04 3.74fE-00 1.94X-00 126M48 9.250E49 SSW 7.330E46 1 755E-06 5 635E-07 2.921E-07 1845E47 8.37M48 3.100E44 1.565E44 1005E48 7.245E-09 8W 7.020E46 1.666E44 5 32M-07 2 753E-07 1 734-07 7 800E-06 2.921E46 1.471E-06 f.449E49 4 313E-09 WSW 4114E46 1 453E-06 4 676E-07 2 422 -07 1 52M-07 6 944E-00 2.578E-06 1.300E-04 8.340E-09 6.031E47 W 3 321E44 8.004E-07 2 59M-07 1.344E47 8 491E-06 3 858E-00 1432E46 7.21N49 4.433 49 3.33H4' M 2.495E44 4.022E47 1 941E-07 100$E47 4 34M-00 2.878E44 1 065E-06 5.340E-09 3 43M49 2.46BE @
NW 3.82K-06 9 21X-07 2 974E-07 1 53tE-07 f.70N48 4.3fM-06 1.62E-06 816X49 5 23X-09 3.764E-09 M 4.762E46 1.591E44 5 20tE-07 2.74X47 1.753-07 8.101E-04 3.094E-06 1.593-08 103M40 7.545E4?
N 1 32M-05 3.073 44 1 02M-04 5 444E 47 3.51M-07 1647E47 6.428E-04 3 359E-08 2 20E -00 1.415E 08 M 125M45 2 900E44 9.60M47 5139E47 3.320E-07 1.564E-07 4 134-06 3.22M-06 2.121E46 1.556E-08 E 112M45 2.62X44 8 64E47 4.594E-07 2.f54E47 1.381E47 5.35M-04 2.799E-06 1 828E-00 1.337E43 06: 1.172E45 2.724E-06 9 01E47 4.800E47 3 0tM47 1 44 4-07 5.63X40 2 93fE48 1.t28E48 1411E4!
E f.737E44 2.28M46 7.543-07 3.993E-07 2.56M-07 1 1tM-07 4.581E-06 2.37K-06 154M-06 1 12SE48 ESE 8.58M-04 1.990E46 4 554E47 3.494E-07 2 250E-07 1053E47 4.11M-00 2.144E-06 140ft-08 1.032E-08 E 7.4fE46 1724E46 5 663 -07 3.024E-07 1951E47 f.16fE40 3.591E-08 1 882E-06 1.239E-08 9.090E-09 i
$$E 7.56X46 1.749E46 5 676E47 3.004E47 192E47 8.944E46 3 461E-06 1 794-00 1 17E49 8.59't-07 I
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l HP-1-230 Revision 6 10 0 Attachment 10.18 (2 of 2)
n- - - - ~ - - _ . . . .-.--... -e ---- -- '
ANNUA 1. AVERAGE DEPOSITION PARAMETERS FOR AREAS AT OR BEYOND THE UNRE3TRICTED AREA BOUNDARY (TABLE 12) '
LPtL t"TERFORI $1TE: USING JAN - KC 1986 MET NTA - RW 1/29/87 GRO W D LEVEL RELEASE: 0 M C!RRECTD USIN6 STANDED OPEN TERRA!N FACTORS RELATM DEPOSITION PER WIT AREA (M**-2) AT FIED POINTS SY DOWWINI SECTORS ********************
DIRECTION DISTANCES IN MILES -
FROM SITE 0 25 0.50 0.75 1 00 1.50 2.00 2.50 3.00 3 50 4 00 4 50 S
1.863E47 6.30M-08 3 235E-041538M8 5 52449 2.740E491.61X491.05E-09 7.433-10 5.500E-10 4.2G-10 SSW 1.851E47 4.26M-08 3 214E-M 152ttM9 5.4tM49 2.722E491.60X-091.HM49 7.384-10 5.47X-10 4.21M-10 0 1.89K-47 4.41M-08 3 295-00156E-05 5 62E-09 2.790E-091.64M-091.07E49 7.569E-10 3.61M-10 4.32X-10 WBW 2.004-07 6.778E-00 3 48K-001.65M-08 5.f4X49 2.94M-091.732491.13E49 7.ffE-10 5.72E-10 4.56E-10 W 8.14fE-00 2.75E-M 1415E-00 4.72M49 2.41E-091.190E49 7.05E-10 4.620E-10 3.251E-10 2.40ft-101.85M-10 WW 6.04E-04 2.044E-08105M-08 4.ffM49179X49 8.89M-10 5.234-10 3 42M-10 2.413-10178X-101.37M-10 0 1.0E-07 3.524E40181K40 8.60X-09 3.090E-091.533-09 f.024E-10 5.90M-10 4.158E-10 3 001E-10 2.374E-10 NNW
!.588E47 5.36M-08 2 757E481311E46 4.700E-09 2.33M-091375E49 f.M1E-10 6.334E-10 4 694-10 3.41M-10 N
2.08M-07 7 05M-04 3 42X48172X-08 6.18M49 3.068E-09180M49118X-09 8.324-10 6.16fE-10 4.754E-10 M 1.63M-07 5 511E-06 2 83M-081.345E48 4.83M49 2 3?M491411E-09 f.24M-10 6.5E-10 4.81K-10 3 71X-10 E 16fft-07 5 74448 2 94ff-081.402E-06 5.03M49 2.498E-091471E-09 f.431E-10 6.777E-10 5.022E-10 3.87M-10 EE 1.55fE-07 5.271E-06 2 70E441.28M-08 4.621E-09 2.272E491.349E-09 8.83E-10 6.21M-10 4 60K-10 3.551E-10 E 126fM! 4.2E48 2188E-001.04M-M 3.734-091.85X491.091E-09 71M-10 5.028E-10 3.72E-10 2.871E-10 ESE f.6%-08 3.27?E-081684E-04 8.004E49 2.875E49142E-09 8.3fE-10 5 417E-10 3 84K-10 2.86M-10 2.20ff-10 SE I.7bE-06 2.f E -00 1 521E-00 7.230E-09 2 597E-09 1.298E 4 9 7 58X -10 4.f M -10 3.494E-10 2.50 M -10 1.ff5E-10 SSE 1.41E47 4.784-00 2.W-041.168E-04 4195E49 2.000E491225-99 8.021E-10 5.644-10 410K-10 3.22X-10 DIRECT!0N IISTANCES IN MILES FROM SITE 5.00 7 50 10.00 15.00 20.00 25.00 30 00 35.00 40.00 45.00 50.00 5
3.373-10 1.498E-10 f.074-11 4.544-11 2.77E-11 1 861E-11 1.334-11 1.001E-11 7.787E-12 6.22K-12 5.07M-12 SSW 3.35M-101.480E-10 9.01E-114.55X-112.758E-11184ff-11 1.325E-11 f.f5M-12 7.73E-12 6180E-12 5.044E-12 0 3.434-101.52E-10 f.2M-114.671E-112.82M-11 1.8?E-11 1.358E-11 1.020E-117.730E-12 6 335E-12 5.171E-12 WSW 3.62K-10141X-10 9.7E-114.734-112.tlE-112.00N-11 1435-11 1.077E-118.37M-12 6 691E-12 5.4E-12 I W 1.475E-10 6.553-113.96fE-112.00E-111214-118.141E-12 5.83X-12 4.380E-12 3.406E-12 2.721E-12 2.221E-12 -
WNW 1.094E-10 4.861E-112.f44-11 1.488E-11 f.000E-12 6.HM-12 4.328E-12 3.25M-12 2.52M-12 2.01K-121.644-12 0 1.88E-10 8.380E-115.07E-112.54E-11 1.553E-11 1.041E-117.46K-12 5.6M-12 4.356E-12 3.479E-12 2.84M-12 M 2.874-10127M-10 7.73X-113.90fE-112.36E-11 1.58E-11 1 13X-118.534-12 6.636E-12 5.301E-12 4.32E-12 N
3.77X-101678E-101.0!E-10 5.13M-113.10fE-112.08K-11 1.494-11 1 12X-118 721E-12 6.f6M-12 5 68E-12 M 2.750E-10131M-10 7.73K-114.012-112.42K-11 1.628E-11 1.167E-118.761E-12 4.813-12 5.441E-12 4.441E-12 E 3.07E-101.366E-10 8 274E-114.1M-112.531E-11 1694-111.21E 11 f.131E-12 7.10K-12 5.671E-12 4.62fE-12 i DE 2.821E-10125X-10 7.591E-113.83M-112 32X-11 155M-111.!!E-118.378E-12 4.514E-12 5.2E-12 4.247E-12 E
2.281E-1010!X-10 6.138E-11310X-111.878E-11125fE-11 f.02312 6.774E-12 5 267E 12 4 208E-12 3.434-12 ESE 1755E-10 7.7tE-114.72X-112.38X-111.445E-11 f.68M-12 6.941E-12 5.212E-12 4.05X-12 3.23M-12 2.6E-12 SE 1.585E-10 7.0 M -11 4.266E-11 2 15 K-11 1 305E-11 8.750E-12 6.27 K-12 4.700E-12 3 64M-12 2 72 4-12 2.38 M-12 SSE 2.54r-101 138E-10 6.891E-113.483E-112.100E-11 1 41X-11 1.01X-117.605E-12 5.flX-12 4.723E-12 3 855E-12 :
)
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KP-1-230 Revision 6 gj Attachment 10.19 (1 of 2)
ANNUAL AVERAGE DEPOSITION PARAMETERS FOR AREAS AT OR BEYOND THE UNRESTRICTED AREA BOUNDARY (TABLE 12) l LPtL t"TDFORS $1TE USIN8 JAN - KC 1986 ET DATA - RLSI 1/29/37 OROLMD LEVEL' RELEASE, 0 M
- ut**************** RELATIVE DEPOSITION PD UNIT AREA (M*t-2) If DOWWWIS SECTORS ************************ l SEGMGT DOLMDARIES IN MILES l DIRECTION .5-1 1-2 2-3 3-4 4-5 5-10 10-20 20-30 30-40 40-50 FROM $1TE l
$ 3.163-00 6.47N-09 1 691E-09 7.594E-10 4.29E-10 1.652-10 4.779E-11 1 89 4-11 1.013-11 6.261E-12 l SSW 3.14X-os 6 435E-09 1.680E-09 7.54E-10 4.268E-10 1.641E-10 4.748E-11 1.882E-11 1.005E-11 6 220E-12 SW 3.220E-00 6.59E-09 1 72N -09 7.734E-10 4.375E-10 1 682E-10 4.86N-11 1 929E-11 1 03M-11 6.37E-12 WSW 3 403 -00 6.968E-09 1 819E-09 8169E-10 4.621E-10 1 77N-10 5 141E-11 2.038E-11 1.000E-11 6 735E-12 W 1.38K-00 2.833E-09 7.395E-10 3.321E-10 1.879E-10 7.22E-11 2.090E-11 8 285E-12 4.424E-12 2.738E-12 WWW 1.02K-06 2 10K-09 5.484E-10 2.464E-10 1.394E-10 5 360E-11 1.551E-11 6 146E-12 3.28N-12 2.033-12 0 1 749E-06 3.62R-09 9.458E-10 4 24K -10 2.40K-10 9.241E-11 2.67X-11 1.060E-11 5.658E-12 3.503-12 NNW 2.495E-08 5 519E-09 1.441E-09 6.471E-10 3.661E-10 1.400E-10 4.07X-11 1.614E-11 8.62M-12 5 332-12 N 3.541E-06 7.254E-09 1.894E-09 8.505E-10 4.811E-10 1 85M-10 5.35K-11 2.123-11 1.13X-11 7 01 N-12 le8: 2.76E-08 5.64E 49 1.479E-09 6 64 K-10 3.758E-10 1 44 5 -10 4 181E-11 1 657E-11 8.848E-12 5.47N-12 E 2.88K-08 5.905E-09 1.54N-09 6.924E-10 3.91N-10 1 50E -10 4.35N-11 1.72N-11 9.22K-12 5.700E-12 EE 2.64E-00 5 41K-09 1 414-09 6.353-10 3.594-10 1 382E-10 3.998E-11 1 585E-11 8 462-12 5.23N-12 E 2.139E-04 4.381E-09 1.14 4 -09 5.137E-10 2.90E-10 1 11N-10 3.23K-11 1.281E-11 6.84X-12 4.235E-12 ESE 1.646E-08 3.371E-09 8.800E-10 3.95N-10 2.23E-10 8.590E-11 2.48M-11 9.85K-12 5 264E-12 3.258E-12 SE 1.46E-06 3.042-09 7.948E-10 3 57K-10 2.019E-10 7.764E-11 2 24N-11 8.904-12 4.755E-12 2.94X-12 SSE 2.401E-08 4.fiK-09 1.28 4 -09 5.766E-10 3.243-10 1.25 4 -10 3.629E-11 1 438E-11 7 481E-12 4.754E-12 YENT AO SUILDIN6 PARAETER$1 RELEASE EIGHT (ETDS) 0.00 REP. WIS EIGHT (ETDS) 10.0 DIAETD (ETDS) 0.00 IUIL31NB E IGHT (ETDS) 61.0 EXITVELOCITT (ETDS) 0.00 BLDB. MIN.CRS.SEC. AREA (SE.ETDS) 2468 0 E AT DISSION RATE (CAL /SEC) 0.0 1
ALL OROUO LEWLMS. - '
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HP-1-230 Revision 6 102 Attachment 10.19 (2 of 2 l
ODCM TECHNICAL SPECIFICATIONS CROSS-REFERENCE (TABLE 13)
Tech Spec ODCM Dose Calculation Section Section Methodology 3.3.3.10 8.7 Determination of Alarm / Trip 3.11.1.1 Setpoints for Liquid 4.11.1.1.2 Monitors 3.3.3.11 8.13 Determination of Alara/ Trip 3.11.2.1 Setpoints for Gaseous 3.11.2.4 Monitors 4.11.2.4.1 3.11.1.1 8.6 Liquid Effluents 4.11.1.1.1 3.11.1.2 -
4.11.1.2 3.11.1.3 4.11.1.3.1 3.11.2.1 8.10 Gaseous Effluents 4.11.2.1.3 (Dose rate due to Noble Gases, 4.11.2.4.1 Radiciodines, Particulates, and _ _ _
Radionuclides with half-lives greater than 8 days.)
3.11.2.1 8.11 Noble Gases 3.11.2.2 4.11.2.2 3.11.2.3 8.12 Radioiodines, Particulates, and 4.11.2.3 Radionuclides with half-lives greater than 8 days 3.11.4 8.15 Total Dose 4.11.4.1 (40CFR190) 4.11.4.1 3.12.1 8.2 Radiological Environmental 4.12.1 Monitoring 3.12.3 8.3 Interlaboratory Comparison Program 4.12.3 KP-1-230 Revision 6 Attachment 10.20 (1 of 1) 103
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ATTACHMENT 2
) CORRECTIONS TO THE SEMIANNUAL RADI0 ACTIVE f EFFLUENT RELEASE REPORT FOR THE PERIOD OF JANUARY l TO JUNF 30, 1987 i 1 j 1
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TABLE 1A (1 of 1)
REPORTCAi! DORY SDIAIN0AL kvHATION OF AU. RELDIES DY 00ARitt TYM 0F ACT!Vlif : ALL AIRt0 Rut EFFLUENii REPORf!N8 KRICS 00ARitR I 1 AND 00ARTER I 2, 1987 i UNIT 8004RitR1 10VARitt 2 stit. TOTAL *:
- : HOURS iH0VR$ i(RROR 1 TYPE OF (FFlupt i 80-2160 2161-4344 : :
A.FIS$1CNANDACT!VAi!0NPRODUCil
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ~ - . . .
- 1. TOTAL N LEAll :CUL!tl 3.4tE021 1.90t 03 : 1.50t01:
j ........................
- 2. AVD ME RELEAlt Raft FOR PERIOD UCl/SEC i 4.4tt01 2.42t02 1 : N/A N/A
- 3. M K OT OF APPLICAk t LIMIT I. RADIO!00!Ilt$
- 1. TOTAL 10 DINE 131 CUR!ES 6.75t-04: 4.4X 05 : 1.50t01 .
- 2. AVDAGE Kltn$t RATE FOR PERIOD UCl/SEC 1.60t4 5.64t- M i i 1 : N/A N/A
- 3. M K D1 0F APPLICA RE LIMIT W
C.PARf!CULAitt i
1.PARTICULAfts(HALF-t,lVil)ICAYli CURIES : 1.20E04: 2.94t 05 1.50t01 i 2. AVERA6C RELEASE RATE OR MR100 UC1/SEC i 1.54E05 3.74t-fi :
- 3. MKDT OF APPL! CAKE LIM!T i ! N/A : N/A
- 4. SROSS ALPHA RAD 10 ACTIVITY CUR!El 3.67t 07 9.70t M i f
D. TRIT!UM l.TOTALRELEASE : CURIES : 6.24E00: 4.66E 00 1.50E01:
I .... .... .... .. .. ...... .. .. ...
2.AVD40EELEAS(RATEFORPD100 UCl/SEC : 1.02t-01: 3.93t01:
- 3. MEDT OF APPLICAkt LIMIT : 1 : N/A i M/A i J
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ATTACHMENT 3 CORRECTIONS TO THE SEMIANNUAL RADIOACTIVE ,
EFFLUENT RELEASE REPORT FOR THE PERIOD OF JULY 1 TO DECEMBER 31, 1986 i
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TABLO 1A (1 of 1)
RIP;47CAffiRT SEM!Abtual SUMMAfl04 DF ALL RELEALES IV 004RTER itFE CF ACT!Vlif : ALL AIRD0 Ret EFFLUENTS REPORilb6 FERIOD GUAATER 6 3 AND BUARTER 04,1964 t
I V41T :DunRTER 3 :DUARTER 4 alli. TOTAL i 1 ikOURS skOURS ERROR 1 ;
TYPEOFEFFLUENT I I4345-6532 16553 1760 i i A. FIl$10N AND AcilVAT!0N PR000Cil 1.7074LRELEAll CURIES 3.14E 03 i 4.03E 03 1.50E01
- 2. AVERAGE RELEASE RATE FDR PERIOD IUC!/SEC i 3.tSE 02 5.07E02
- 3. FERCENT OF APPLICABLE LIMIT 1 N/A N/A i I. RADIO!CD! hts ;
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- 1. TOTAL 100!NE131 iCURIES 7.56E-04 1.09E 03 1.50E 01 i 1 2. AVERAGE kELEASE RATE FOR PERIOD IUCI/SEC 9.$2E-05i 1.37E 04
- t. ... .. .. ...... ........... ........... ............................ ..
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- 3. PERCENT OF APPLICABLE LIMIT i 1 i W/A N/A i C.PARTICULATES
- 1. PARilCULATES (HALF LIVil>I DAtl) iCURIES 3.62t 04 1.53E 04 1.50E01 i 1
- 2. AVERh6E RELEASE PATE OR PERIOD IUCl/IEC i 4.56E 07 e 1.93E 05 ;
- 3. PERCENT OF APPLICABLE LIMIT i 1 N/A N/A i l
- 4. SRDSS ALPHA RADIDACTIV!ff ICUR!ES 7.84E-46: 6.tBE 44 ?
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D. Trit!UM
........... ...... .... .............. .. .......... .... .. .... ..... I
- 1. T014L RELEASE CUR!El i 1.50E01 2.9?E01 1.50E01 l
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- 2. AVER 44E RELEAlt RATE FDR PER!00 IUCl/SEC 1.07E011 3.44E 60 : l i ....... ...... .. .. .......... .... ............ .. ..............
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- 3. PERCENT OF APPLICABLE LIM!i i 1 N/A N/A i ,
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ATTACHMENT 4 ;
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j CORRECTIONS TO THE SEMIANNUAL RADI0 ACTIVE !
1 EFFLUENT RELEASE REPORT FOR THE PERIOD OF ;
- JANUARY l TO JUNE 30, 1986 i.
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TABLE lA (1 o' 1) 7 AEPORTCAtt6CRf a SER!AmyAL tumATION OF ALL RELEAMI If DUARTER l TYPt Cf AttlVITY : ALL AlRt0 Rut EFFLUENTS :
REPCRT!kl PERICD BUARTER l 1 AND OUARTER l 2 Ith
... .. . .......................... .... ................ ~ ............. .. ....
I UNIT 100ARTER1 iOUARitt 2 itSt. TOTAL i 4 : IHOURS IHOURI :CAROR 1 :
TYPE OF EFFLUthi 10-2160 121614344 A.Flll!0NANDACT! VAT!0NPRDUCTS
. .... ........ .. ...... ~ ................ ~ ....................... ~ .......
1.T0tALRELEAlt iCUR!El i 3.52t 03 5.37E02 1.50t01
... .......... ..........-.. .. ....-.. ~ .. ~ .. .. ~ .... .................
- 2. AVERAE ktLIASE Raft FOR PERIOD IUCl/SEC 4.53t02 6.83t01:
3.PERClili0FAPPLICAlltLIMIT 1 i N/A N/A i
. .. .. ~ . ...... ...... .... .... .. .......... .. ...... ....
- 3. RAD 10100! Nil
- 1. TOTAL 100!WE131 iCURIES 3.83t04 2.ttt03: 1.50t 01 :
- 2. AVERAtt RELEAlt RATE FOR PERICD IUC1/SEC 4.93t-05 3.70E 04 :
3.PERCENTOFAPPLICAktLIMIT : 1 : N/A i N/A [
............. ... ~ .. .. ...... ........ .... .. .. .. .... ......
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! l C.FARTICULAftl
... .. ~ ..... .. ...... ............ .......... .......... ...... .. .... .
- 1. FARTICULAffl (HALF-LIVEDI DAf t) iCURitt : 0 Mt 001 0. Mt 00 1.50t01i 4
- .AVERA6CRELEAltRATEORPER100 IUC1/ Sit 0.00t 00 1 0.00t00: ,
L 3.PERCENTOFAPPLICABLELIMIT 1 : N/A N/A 4.GRCllALPH4RAi!0ACTIVlif CURitt i 2.32t M i 2.11t H :
D. TRIT!UM 1 1.TOTALRELEAlt iCURIES 5.18E 00 1.71t00 1.50t01
.. ~ .......... ...... .................... .. ...... .. . .. .. ...... .
- 2. ACRAM RELEASE RATE F04 PERIOD IUC1/SEC 6.ME-01: 2.ltt-01:
3.PERCENTOFAPPLICAktLIM!i : 1 i N/A : N/A :
... .. ..... .. ..-....~ ..-....~....~.....- ~.-....- -
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TABLE IB (1 of 1)
REPORTCAftiDRf : $!MIAhuuAL A!RD0tht CONT!WUOut ELEVATED W M 0cht LEVEL RittAlti. 10 fall FOR LACH huCLI M Ru t4SD.
TYPEOFAtilVITY : ALL A!Rt0Att EFFLUEIITS REPORilblPERIOD : 0044ttR I 1 Ale 6UARTER I 2, 19H ELEVAfflRELEAlti SADUhD Ritt45tl :
i Uuti 190ARTER 1 CUAAitR 2 004ATER 1 00ARTER2 4
- HOURS HOURI H0Utt H00Rt :
i 02160 2161 4344 0 2160 21614344 WUCLIM F!lllCW6Alti ........
KR45M cut!!I : 0.0 M 00 1 0.00t 00 1.11t01 1.92t 00 :
KA40 : Cutlti 0.006001 0.0M 00 1.51E 00 1.85E00:
It 133M Cut!El : 0.0 M 00 1 0.0 M 00 : 1.77E H : 0.0M 00 : ;
IF133 : CUR!ts : 0.0M 00 0.0M 00 1 3.21E03 4.24102:
j Il 135 : CUR!ll : 0.0M 00 0.0M 00 1.43t02 2.7 M 01 :
- CUR!!S : 0.0M 00 0.0M 00 3.37E03 4.56E 02 :
101ALFORPERIOD IC0thil 113) : Cutlti 0.0M M i 0.0M 00 3.83t44 2.91103:
!.133 : Cutlil : 0.0M 00 0.0M 00 4.11( 4 6 1.43( 4 4 :
TOTALFORPER100 : CUR!ti 0.0M 00 0.0M H : 3.00( 4 4 3.05( 4 3
........ ...... ...... ........ ................ . . .... .. .. .. ......... ... .. i i
l PARTICULAfts 1 H-3 : CURits : 0. HE 00 0.0M 00 5.lK H : 1.71t00:
TC 99M : Cut!E0 0.0M M 0.0M M 0.0M 00 4.5N47 8 ALPHA : CUR!El : 0.0M H : 0.0M H : 2.3N46 2.llt46 :
l .. .... . .. ...... .. .. .. .... . ................. .. .. ...... ........
I TOTALFCRFERIDO : CUR!ti 0.0M 00 : 0.0 M M i 5.1 M 00 : 1.71t00e i . .
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ATTACHMENT 5 l
CORRECTIONS TO THE SEMIANNUAL RADI0 ACTIVE '
EFFLUENT RELEASE REPORT FOR THE PERIOD OF JULY I TO DECEMBER 31, 1985 l
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! ATTACHMENT 6
- CORRECTIONS to THE SEMIANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT FOR THE PERIOD OF MARCH 4 TO JUNE 30, 1985 i
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l TABLE 1A (l of 1) l l
REPDATCATE60RY i SEMIANNUAL SUMMATION OF ALL RELEASES BY QUARTER j
TYPE OF ACTIVITY : ALL AIRBCRNE EFFLUENTS
- QUARTER I 3 AND QUARTER I 4, 1985 l REPDRf!N6 PERIOD l
- UNIT QUAATER 3 10VARTER 4 EST. TOTAL : l HOURS HOURS ERROR % :
14345-6552 e6553-8760 : :
TYPE DF EFFLUENT A. FIS$!0N AND ACTIVAi!DN PRODUCTS
- 1. TOTAL RELEASE : CURIES : 9.05E 02 6.0lt 03 : 1.50E 01 :
- 2. AVERA6E RELEASE RATE FDR PERIOD :UC!/SLC 1.14E 02 : 7.55E02:
- 3. PERCENT OF APPLICABLE LIMIT : : i W/A : N/A :
B. RAD 1010 DINES
- 1. TOTAL 10 DINE 131 CURIES : 2.83E 04 2.60E-03 : 1.50E 0! :
- 2. AVERA6E RELEASE RATE FOR PERIOD :UC1/SEC 3.54E-05: 3.27E04:
% i N/A : N/A
- 3. FERCENT OF APPLICABLE LIMli C. PARTICULATES
- 1. PARilCULATES (HALF-LIVES)8 DAYS) CURIES : 7.61E-7 r 0.00E 00 1.50E01 1
- 2. AVERA6E RELEASE RATE OR PERIOD UCI/SEC : 9.58E-08 : 0.00E 00 : ;
i N/A : N/A :
- 3. PERCENT OF APPLICABLE LIMIT %
CURIES : 9.81E-06: 2.44E-06: l
- 4. 6ROSS ALPHA RADIDACilVITY 1
....... .................. .... .. .. ............ .. .. ........ ...... 1 1
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- 0. TRIT!UM
- 1. TOTAL RELEASE CURIES : 0.00E 001 0.00E 00 : 1.50E01:
... .. .... .. ...................... ........ .... ...... ...... ... 1 i
UCl/SEC : 0.00E 40 0.00E 00 :
- 2. AVERA8E RELEAS( RATE FOR PERIOD l 1
1 i % i N/A : N/A :
- 3. PERCENT OF APPLICABLE LIMIT l
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TABLE lA (1 of 1)
REPORTCATE60RY : SEMIAlul0AL SUMMATION OF ALL RELEACC Si QUARTER TYPE OF ACTIVITY : ALL AIRBORNE EFFLUENTS QUARTER I 1 AND QUARTER t 2, 1985 REPORf!N6 PERIOD UNIT iGUARTER 1 iSUARTER 2 EST. TOTAL i ROURS HCURS : ERROR 1 :
82161-4344 : :
- 0 2160 TYPE OF EFFLUENT A.FIS$10NANDACTIVATIONPRODUCTS
- 1. TOTAL RELEASE CURIES : 1.46E-02: 1.29E 03 i 1.50E 01 :
................. .... .......................... .. .. ............ ..........~ .....
- 2. AVERA3E RELEASE RATE FOR PERIOD IUCl/SEC 1.88E-09: 1.64E 02 :
- 1 : N/A : N/A
- 3. PERCENT OF APPLICABLE LIMIT B. RAD 10100!NES .......... .......
CURIES : 0.00E00 5.94E 04 1.50E01:
- 1. TOTAL 100!NE 131 .... ...... .. ...
- 2. AVERAGE RELEASE RATE FOR PERICf IUCl/SEC : 0 N E 00 : 7.57E 05 :
- 1 : N/A N/A
- 3. PERCEXT OF APPLICABLE 1,lMIT C.PARTICULATES CURIES : 0.00E 00 : 7.65E-07 1.50E01:
- 1. PARTICULATES (HALF LIVES)9 DAYS)
- 2. AVERA6E RELEASE RATE OR PERIOD UCl/SEC 0.ME00: 9.99E 08 :
- 1 : N/A : N/A ,
- 3. PERCEMT OF APPLICABLE LIMIT )
............... ................................................................ i CURIES : 0.00E 00 : 3 !BE-06 i
- 4. 6ROSS ALPHA RADICACTIVITY )
............... ...... ........................................................ l j
D. TRIT!LM l 1,TOTALRELEASE CURIES : 0.00E 00 i 0.00E 00 : 1.50E 01 :
- 2. AVERAGE RELEAS(RATE FOR PERIOD
- UCl/SEC : 0.00E00: 0.00E 00 :
... .. ...... ...... .... ................................ ................ N/A
- 1 : N/A :
- 3. FERCENT OF APPLICABLE LIMIT
.