ML18017A265

Semiannual Effluent & Waste Disposal Rept for Susquehanna Steam Electric Station 920101-920630. W/920826 Ltr

ML18017A265
Person / Time
Site:	Susquehanna
Issue date:	06/30/1992
From:	Barclay R, Carson B, Keiser H PENNSYLVANIA POWER & LIGHT CO.
To:	Martin T NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION I)
References
PLA-3840, NUDOCS 9209010275
Download: ML18017A265 (207)

Text

,~,ccEr.ER~TED ~TRrhvTror DEMo~R~Trox REOVLA~Y INFORMATION DISTRIBUTION SYSTEM IRIDB) sYSTEM DOCKET FACIL: 50-387 Susquehanna Steam Electric Stationi Unit 1I Pennsglva 05000387 50-388 Susquehanna Steam Electric Stationi Unit 2I Pennsglva 05000388 AUTH. NANE AUTHOR AFFILIATION CARSONI B. H. Pennsylvania Poeer 8c Light Co.

BARCLAYIR. K. Pennsylvania Poeer 5 Light Co.

KEISERI H. N. Pennsglvan.ia PouJel Zc Light Co.

RECIP. MANE RECXPXENT AFFXLIATIQN NARTINi T. T. Region 1 (Post 820201)

SUBJECT:

"Semiannual EfFluent u~ Waste D R usguehanna Steam Electric Station 9201 -920630. L4/920826 tr.

DISTRXBUTXON CODE:

TITLE: 50. 3&a XEOSD COPIES RECEIVED: LTR (a ) (2) Semiannual ENCL Ef f luent Release Reports Sl ZE: '

NOTES: LPDR 1 cg Transcripts. > NAXMELLIG 05000387 LPDR 1 cg Transcripts. 'AXMELL G 05000388 A REC lP IENT COP IES REC IP lENT COPIES ID CODE/NANE LTTR ENCL ID CODE/NANE LTTR ENCI PD1-2 LA 3 3 PD1-.2 PD 1 RALE I GH i J.

INTERNAL ACRS 1 1 NRR/DREP/PRPBll 01 1 , RGNl DRSS/RPB LE 02 1 1 EXTERNAL: BNL TICHLERI J03 1 1 I EGK.G S NPSQNI F NRC PDR 1 1 NOTES:

NOTE TO ALL "RIDS" RECIPIENTS:

PLEASF HELP US TO REDUCE WASTE! CONTACT THE DOCUMENT CONTROL DESK.

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Pennsylvania Power 8 Light Company Two North Ninth. Street o Allentown, PA 18101-1179 ~ 215/774-5151 Harold W. Kaiser Senior Vice President-Nuclear 215/7744194 AUG 7.6'fggZ Mr. Thomas T. Martin Regional Administrator, Region I U.S. Nuclear Regulatory Commission 475 Allendale Road King of Prussia, PA 19406 SUSQUEHANNA STEAM ELECTRIC STATION SEMI-ANNUALRADIOACTIVEEFFLUENT RELEASE REPORT Docket No. 50-387 PLA-3840 FILE R41-2A and 50-388

Dear Mr. Martin:

N f

s In accordance with 10CFR50.36a(a)(2) and the Susquehanna SES Unit 1 and 2'Technical Specifications, attached is the Semi-Annual Radioactive Effluent Release Report for SSES Units 1 and 2 covering the period January 1 through June 30, 1992.,

Very truly yours, H. W. Ke ser Attachment cc: t NRC-Document Control33estc (ortginnli NRC Region I Mr. G. S. Barber - NRC Resident Inspector Mr. J. J. Raleigh - NRR Project Manager ACAAgt-9209010275 920630 PDR ADOCK 05000387 i'DR

S I 1 S: h 4 Il 1 H

I I+ E 1 h

R k I l'

SUSQUEHANNA STEAM ELECTRIC STATION SEMIANNUAL EFFLUENT AND WASTE DISPOSAL REPORT REPORT PERIOD: 1/1/92 - 6/30/92 Prepared by:

B. . Carson R. . arc ay Health Physicist Health Physicist Reviewed by:

.San Supervisor Environmental Services - Nuclear Approved by:

oty Supervisor - Operations Technology 9209010275 I

Pennsylvania Power L Light Company Two North Ninth Street

. Allentown, Pennsylvania 18101

L O O

~SEC I~0

1. Introduction and Supplemental Information . . . . . . 1

2. Effluent and Waste Disposal Data . . . . . . . . . . 12

3. Changes to the Offsite Dose Calculation manual . 31 and the Solid Waste Process Control Program

4. Reports of Exception to the SSES Effluent...... 35 Honitoring Program

5. Changes to Radiological Environmental Monitoring. . . 37 Locations as Identified in the Offsite Dose Calculation Hanual (ODCN)

Table 1: Technical Specification Limits . . . . . . . . . . . 9 Table 2: Airborne Effluents-Summation of All Releases... .14 Table 3: Airborne Effluents . . . . . . .' . . . . . . . . .15 Table 4: Waterborne Effluents- Summation of All Releases... .17 Table 5: Waterborne Effluents............... .18 Table 6: Solid Waste and Irradiated Fuel Shipments. . . . . .19 Table 7: Solid Radioactive Waste Class A. . . . . . . . . .22 Principal Radionuclides and Percent Composition Liquid Radwaste Filter Hedia - HIC (Dewatered)

Table 8: Solid Radioactive Waste - Class A. . . . . . . . . .23 Principal Radionuclides and Percent Composition Condensate Demineralizer/Radwaste Demineralizer

- HIC (Dewatered)

Table 9: Solid Radioactive Waste - Class A. . . . . . . . . .24 Principal Radionuclides and Percent Composition Condensate Demineralizer/Radwaste Demineralizer-Carbon Steel Liner (Dewatered)

Table 10: Solid Radioactive Waste - Class A. . . . . . . . . .25 Principal Radionuclides and Percent Composition Ultrasonic Resin Cleaning Waste - HIC (Dewatered)

~

Table 11: Solid Radioactive Waste Class A. . . . . . . . . .26 Principal Radionuclides and Percent Composition Processed DAW - Strong Tight Container Table 12: Solid Radioactive Waste - Class A. . . . . . . . . .27 Principal Radionuclides and Percent Composition Non-Processed DAW - Strong Tight Container Table 13: Solid Radioactive Waste - Class A. . . . . . . . . .28 Principal Radionuclides and Percent Composition Cartridge Filters - HIC Table 14: Estimated Total Errors Associated with . . . .29 Effluent measurements .

Table 15: Data Not Reported in Previous. . . . . . . . .30 Semiannual Report

LIST OF FIGURES Figure 1: SSES Airborne Effluent Release Points......... 4 Figure 2: SSES Waterborne Effluent Release. Pathway....... 5

SECTION 1 INTRODUCTION AND SUPPLEMENTAL INFOKILATION

HTRODU T 0 The Susquehanna Steam Electric Station (SSES) is located in Salem Township, Luzerne County, Pennsylvania. It is on the west bank of the Susquehanna River, 8 km northeast of Berwick. The Station consists of two boiling water reactor generating units, each with 1,050 MW net electrical capacity. The reactor and generating units were supplied by General Electric, while the Bechtel Corporation served as architect-engineer and constructor.

Construction of the Station began in the early 1970s. Fuel load began in Unit 1 in July of 1982. Initial criticality,was achieved in the Unit 1 reactor on September 10, 1982. The reactor reached 100X power for the first time on February 4, 1983. Commercial operation of Unit 1 was declared on June 8, 1983. Initial criticality of Unit 2 occurred on Hay 8, 1984. Unit 2 was declared commercial on February 12, 1985.

Airborne effluents are released from the Susquehanna Station via five rooftop vents on the reactor building (see Figure 1). Each vent is continuously monitored, and a program of periodic sampling and analysis is conducted as specified in the plant Technical Specifications. All waterborne effluents are released in batch mode and are sampled and analyzed prior to release. Waterborne effluents from the site are released into the cooling tower blowdown line for dilution prior to release to the Susquehanna River (see Figure 2). Blowdown line flow rates are at least 5,000 gpm during periods of liquid radwaste release. The diluted effluent is introduced to the river by way of a perforated diffuser pipe placed on the river bed. The diffuser serves to rapidly and uniformly mix the station discharge with the main flow of the river.

This report presents a summary of the quantities of radioactive materials which were released from the Susquehanna Steam Electric Station during the period from January 1, 1992 to June 30, 1992. In addition, this report serves as a medium for notifying the US Nuclear Regulatory Commission staff of changes to PPKL's Offsite Dose Calculation Manual (ODCH) and Solid Waste Process Control Program (PCP) and documentation of any exceptions to the SSES effluent monitoring program which must be reported per Technical Specifications 3.3.7.10 and 3.3.7.11.

Airborne and waterborne radioactive effluent releases to the environment during the report period were sampled and analyzed in accordance with the

.requirements of the Technical Specifications. All radioactive effluent releases were within the concentration and release limits specified in the Radiological Effluent Technical Specifications (RETS). Calculations and terms utilized in this report are those outlined in the SSES Offsite Dose

. Calculation Manual (ODCN).

Section 1 contains supplemental information pertaining to effluents from the Susquehanna plant. Included are regulatory limits (Table 1), sampling and analysis methods, and characterization of the .

number and duration of batch and abnormal releases, if any.

Section 2 contains effluent and waste disposal data for the report period.

Table 2 contains a summation of all airborne releases, grouped into the radionuclide categories of gases, particulates, iodines, -and tritium.

Average release rates are presented and compared to the applicable lim Table 3 presents the totals of specific radionuclides in airborne effluerfts.

Waterborne effluents are summarized in Table 4. Average diluted concentrations are presented and compared .to the applicable limits. Table 5 presents the release quantities of specific radionuclides in waterborne effluents over the report period.

Tables 6 through 13 present a characterization of the solid radioactive waste shipped off site during the report period. included are the volumes and curie contents associated with each type of solid waste. An estimate of major nuclide composition is presented for each waste type, as well as the number of waste shipments from the site, how they were transported, and their final destination.

Table 14 contains estimates of the errors associated with the measurements involved in quantifying effluents. Sampling errors, counting errors, and .

errors associated with determining effluent flow rates and volumes all contribute to the total error of effluent measurements. Error estimates are presented for each category of radionuclide detected in airborne and waterborne effluents and solid wastes during the report period.

Table 15 presents effluent data from previous report periods which was not available at preparation time for the associated semiannual report.'ection 3 of this report is reserved for documentation of changes to t Offsite Dose Calculation Manual and the Solid Waste Process Control Program.

Section 4 presents a listing of cases in which airborne ot waterborne effluent monitoring instrumentation was declared inoperable and was not restored to operability within the time period specified in Technical Specification Table 3.3.7. 10-1 or 3.3.7.11-1 Action Statements.

Section 5 contains changes to radiological environmental monitoring locations identified in the ODCN pursuant to Technical Specification 3.12.1 and 3.12.2. Revised figures showing the locations of these changes are included in this report.

FIGURE I SSES AIRBORNE EFFLUENT RELEASE POINTS I oui~

WQ I Z Z 'g Zflog e

Iy ~

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WOI ZZ$ ~ T ZCB Zw W

W zoRa Z zV~ Xzw+

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+

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Dgg g I + ~ ~

j

~ p WIBC+ Ry N I

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FIGURE 2 SSES MATERBORNE EFFLUENT RELEASE PATHWAY SUSQuE~m RvER ~

INTA(t S$ , I2 I CPM CL RAINJALL I@75%~ fl.OW WAICR Iay OPM (Iy)

OitOOOPM tADIDACTIVL RADwADTC AC%A llIDATMCNT WAX%% V%$

c"8 4AO CPM OAW WATCQ TNEATNlIIT CEIL AL VWSTC PLANT PLANT TRKATIALHT USCO EVAPORATION Of&NCIIAUZERHNSTLS RAINFALL QCHCRA EVAPORATION I4,i5O CPM 14>'550 GPIA CII CHICA(

8 WAST%

TRCAT4%&t 478 000 0PM RAW WAR TRES~ WA5TES SO CPM FM TKR ONCCN5gl CL

~CAT EVAPORATION 0

CIC IIAHCKAS OP/

POND 45GPM MAKC U EMCQCtNCT thCAOCICY, L

~ I HCAl'

~AIClWHCCR5 Mq I ~+e4ERSJ)

SPRAY I relCAaICT1 I I l POND io SPNI 1 l I I

lkCAAAHCV InWa I I

INI$ T DOWN IO,OOO CPM QA)

SUPPLENENTAL INFORNTION

1. Re ulator Limits Technical Specifications 3/4.11. 1 and 3/4.11.2 outline requirements for release of radioactive liquid and gaseous effluents, respectively. Concentration of radioactive material liquid effluents and dose or dose commitment resultant thereof are limited in unrestricted areas. Dose and dose rate due to radioactive materials released in gaseous effluents are limited in areas at or beyond the site boundary. Technical Specification limits are listed in Table 1.

2. aximum Permissible Concentrations in Waterborne Effluents The concentrations of radioactive materials in waterborne effluents are limited to the concentrations specified in 10 CFR Peart 20 Appendix B Table II, Column 2, for radionuclides other than dissolved or entrained noble gases.

For dissolved or entrained noble gases, the concentrations are limited to the following values, as stated in the applicable Technical Specification:

Nuclide PC uCi ml Kr 2.0E-04

'Kr 5.0E-04 "Kr 4.0E-05 9.0E-05 Ar 7.0E-05 133mx 5.0E-04 133X 6.0E-04 135mx 2.0E-04

'"Xe 2.0E-04 These values are calculated using Equation 20 of ICRP Publication 2 (1959), adjusted for infinite cloud submersion in water.

3. ~E effluents was The average gamma energy for gaseous radioactive 3.00E-2 MeV. The average beta energy for gaseous radioactive effluents was 1.46E-1 MeV.

4. Measurements and A roximations of Total Radioactivit Analyses of specific radionuclides in effluent samples are used to evaluate the radioactive composition and concentration of effluents.

6

ethods of uanti in f en s

a. Fission and Activation Gases: Gas samples are routinely collected monthly and analyzed with a Ge(Li) detector system which incorporates a data reduction program to determine radionuclide composition in terms of specific activity. Data tapes from the continuous vent monitors are used to determine the average concentration of noble gases. The Ge(Li) isotopic scan is used to convert the continuous vent monitor activity to actual activity based on the determined nuclide mixture. The vent and sample flow rates are continuously monitored, and the average flow rates for each vent are used to calculate the total activity released in a given time period. When the continuous monitors are out of service, manual grab samples are taken from each vent once each eight hours (once each four hours .for the standby gas treatment vent).

b. Iodines: Iodine is continuously collected via an isokinetic sampling assembly in each vent. Filters are normally exchanged once per week and analyzed on a Ge(Li) system. The daily average flow rates for the vents and sample pumps are averaged for the duration of the sampling period, and a ratio of vent flow rate to sample flow rate is determined. The ratio is used to determine the total activity of each isotope released during the time period in question. When the continuous monitors are out of service, iodine is continuously collected on charcoal cartridges attached to air samplers which draw directly from affected rooftop vent(s) or from alternate sampling ports available on the sample lines.

C. Particulates: Particulates are continuously collected via an isokinetic sampling assembly in each vent. Filters are normally exchanged once per week and analyzed on a Ge(Li) system. Flow rate corrections are performed as for iodines. When the continuous vent monitors are out of service, particulates are continuously sampled directly from the affected rooftop vent(s) or from alternate sampling ports available on the sample lines.

d. Waterborne Effluents: Each tank of liquid radwaste is sampled and analyzed for principal gamma emitters prior to release.

Each sample tank is recirculated for a sufficient amount of time prior to sampling to ensure that a representative sample is obtained. Samples are analyzed on a Ge(Li) system and release permits are generated based on the values obtained from the isotopic analysis and the most recent values for tritium, gross alpha, iron-55, and strontium-89 and -90. An aliquot based on release volume is saved and added to monthly and quarterly composite containers. The monthly tritium analysis is done in-house. The quarterly composite is sent to a vendor laboratory for iron-55, strontium-89 and -90, and gross alpha analyses.

The concentration of each radionuclide in each batch is decay corrected from the time of counting to the midpoint of the release period, and is then multiplied by the volume of the

'7

batch to determine the total quantity of each nuclide released in each batch. The isotopic totals for each are summed to determine the total source term for the report period.

1

TABLE 1 A. RUOBL I R:

l. ~ 500 mrem - TOTAL BODY S 3000 mrem - SKIN annual site total "instantaneous" limits (Tech Spec. 3.11.2.1)

2. g 5 mrad - AIR GANJA g 10 mrad - AIR BETA

- quarterly air dose limits per reactor unit (Tech Spec. 3.11.2.2)

3. g 10 mrad - AIR GAMN g 20 mrad - AIR BETA

- annual air dose limits per reactor unit (Tech Spec. 3.11.2.2)

B. - 3 U T CU A 0

BORN

l. g 1500 mrem ORGAN (inhalation pathways only) annual site total "instantaneous" limits (Tech Spec. 3.11.2.1)

2. g 7.5 mrem - ORGAN

- quarterly dose limits per reactor unit (Tech Spec. 3. 11.2.3)

3. g 15 mrem - ORGAN

- annual dose limits per reactor unit (Tech Spec. 3. 11.2.3)

I. LIIUID I UEUIU:

1. Concentration S 10CFR20 Appendix B, Table II, Column 2

- site total "instantaneous" limits (Tech Spec. 3.11.1.1) 9

2. g 1.5 mrem - TOTAL BODY 5 5 mrem ORGAN

-- quarterly dose limits per reactor unit (Tech Spec. 3.11.1.2)

3. g 3 mrem TOTAL BODY 6 10 mrem - ORGAN

- annual dose limits per reactor unit (Tech. Spec. 3.11.1.2)

RBORNE FF U N AS S 0 PERC N F T CHN CAL SP C CAT ON Fission and Activation Gases A derived release rate limit based on the Technical Specification limit of 500 mrem/yr was calculated from the expected mix of noble gas radionuclides presented in Table 4.4 of the SSES Final Environmen'tal Statement (NUREG-0564). The limit is 8.51E+05 uCi/min (1.42E+04 uCi/sec).

Iodine-131 A derived release rate limit based on the Technical Specification limit of 1500 mrem/yr from I-131, tritium and particulates with half-lives greater than 8 days was calculated from the annual release quantity of I-131 provided in Table 4.4 of the SSES Final Environmental Statement (NUREG-0564). The limit is 1.41E+02 uCi/min (2.35Ee00 uCi/sec).

Particulates A derived release rate limit based on the Technical Specification limit of 1500 mrem/yr from I-131, tritium and particulates with half-lives greater than 8 days was calculated based on the expected mix of particulate radionuclides presented in Table 4.4 of the SSES Final Environmental Statement (NUREG-0564). The limit is 7.72E+02 uCi/min (1.29E+01 uCi/sec).

Tritium A derived release rate was calculated based on the 10 CFR 20 Appendix B, Table II, Column 1, Maximum Permissible Concentration for tritium (2.0E-07 uCi/cc) to unrgstricted areas. A relative concentration of 4.1E-05 sec/m was assumed. The limit is 2.93E+05 uCi/min (4.88E+03 uCi/sec).

10.

E. BORN F U N 'S S Fission and Activation Products Dose calculations are performed on quarterly activity totals from waterborne effluents using the LADTAP II dose program. The calculated doses are'hen compared to Technical Specification 3.11.1.2 quarterly dose limits for liquid effluents (TOTAL BODY LIMIT: 1.5 mrem per reactor unit, ORGAN LIMIT: 5 mrem per reactor unit).

Tritium

. Liquid effluent quarterly tritium concentrations are

'compared to the 10 CFR 20 Appendix B, Table II, Column 2, Maximum Permissible Concentration limit of 3.0E-03 uCi/ml to un'restricted areas.

Dissolved and Entrained Gases Liquid effluent quarterly concentration totals for dissolved and entrained gases are compared to the most restrictive Maximum Permissible Concentration for a noble gas 4.0E-05 uCi/ml (Kr-87) from the SSES Technical Specification Table 3.11.1.1-1.

.0 11

SECTION 2 EFFLUENT AND WASTE DISPOSAL DATA 12

rb e 1 ents Summaries of the radionuclide total curie activities, average release rates are included in Tables 2 and 3.

First Second guarter ggarter

1. Number of Batch Releases: 0 0

2. Total Time Period for Batch Release: NA NA

3. Maximum Time Period for a Batch Release: NA NA

4. Average Time Period for a Batch Release: NA NA

5. Minimum Time Period for a Batch Release: NA NA bnormal Releases

1. Number of Releases 0 0

2. Total Activity Released NA NA If a radionuclide was not detected, zero activity was used for that isotope in dose calculations. A zero activity indicates that no activity was positively detected in any sample when samples were analyzed with techniques which achieved the required Lower Limits of Detection (LLD) as specified in the SSES Technical Specification Table 4.11.2.1.2-1, Radioactive Gaseous Maste Sampling and Analysis Program. In all cases, these LLDs were less than the levels required by Technical Specifications. The following are typical LLDs.

Radionuclide LLD uCi cc Kr-87 4.6 E-08 Kr-88 5.3 E-08 Xe-133 5.4 E-08 Xe-133m 1.3 E-07 Xe-135 1.5 E-08 Xe-138 1.2 E-07 Hn-54 2.9 E-14 Fe-59 2.8 E-14 Co-58 1.8 E-14 Co-60 3.8 E-14 Zn-65 4.4 E-14 Mo-99 3.3 E-13 Cs-134 2.4 E-14 Cs-137 2.1 E-14 Ce-141 1.5 E-14 Ce-144 7.0 E-14 I-131 4.4 E-14 I-133 2.8 E-13 Sr-89 2.0 E-15 Sr-90 3.0 E-16 H-3 2.6 E-08 Gross Alpha 5.0 E-16 13

TABLE 2 SBlIANNUAL EFFLUENT AND WASTE DISPOSAL REPORT (1992)

AIRBORNE EFFLUENTS - SUNSLTION OF ALL RELEASES First Second A. Fission and Activation Gases Unit Ouar ter Ouarter Total Release Ci 1.01E+01 3.04E+01 Average Release Rate for Period uCi/sec 1.2BE~OO 3.87E+00 Percent of Technical Specification Limit 9.06E.03 2.73E.02 B. l odines Total 1-131 Ci O,DOE+00 O.DOE+00 Average Release Rate for Period uCi/sec O.DOE+00 O.DOE+00 Percent of Technical Specification Limit O.DOE+00 O.DOE+00 C. Particulates Particulates ulth Half-Lives i 8 Da 2.22E.03 4.29E.04*

Average Release Rate for Period E-OS Percent of Technical Specification Limit 2.19E-03 4.23E-04 Gross Alpha Radioactivity 4.16E-07 4.17E.07 D. Tr i t iud Total Release Ci 6.46E+00 1 45E+01 Average Release Rate for Period uCi/sec 8.22E.01 1.84E+00 Percent of Technical Specification Limit 1.68E-02 3.78E-02

<<Sr-89, Sr-90 and gross alpha values are estimated based on first quarter 1992 sample analyses and second quarter 1992 ventilation exhaust rates.

TABLE 3 SENIANNUAL EFFLUENT AND MASTE DISPOSAL REPORT (1992)

AIRBORNE EFFLUENTS Continuous Node Continuous Hode Nucli des Released Unit First Quarter Second Quarter A. Fission and Activation Gases Xe-133 1.01E+01 3.04E+01 Total for Period 1.01E+01 3.04E+01

8. lodines 1-131 Ci O.OOE+00 O.OOE+00 I-133 Ci O.OOE+00 O.OOE+00 1-135 Ci O.OOE+00 O.OOE+00 Total for Per i od Ci O.OOE+00 O.OOE+00 C. Particulates Cr.51 Ci O.OOE+00 O.OOE+00 Hn-54 Ci 9.05E.04 4.11E.04 Fe-59 Ci 1.56E-04 4.85E.06 Co-58 Ci 1.17E-04 O.OOE+00 Co-60 Ci 3.32E.04 1.30E 05 Zn-65 7.09E.04 O.OOE+00 Sr-89 Ci O.OOE+00 O.OOE+00*

Sr-90 Ci O.OOE+00 O.OOE+00i Cs-137 Ci O.OOE+00 O.OOE+00 Ce.141 Ci O.OOE+00 O.OOE+00 Ce-144 Ci O.OOE+00 O.OOE+00 Total for Period Ci 2.22E.03 4.29E-04

• Reported values are estimated based on first quarter 1992 sample analyses and second quarter 1992 ventilation exhaust rates.

Mate orne ff ue ts Summaries of the radionuclide total curie activities, average diluted concentrations, and percent of applicable Technical Specification limits are included in Tables 4 and 5.

First Sec ILtt R 1 guarter guarte

1. Number of Batch Releases: 7.20E+01 1. 01E+02

2. Total Time Period for Batch Releases: 1.20E+04 1.65E+04

3. Haximum Time Period for a Batch Release: 2.85E+02 2.75E+02

4. Average Time Period for a Batch Release:.. 1.67E+02 1.64E+02

5. Hinimum Time Period for a Batch Release: 8.00E+00 1.00E+00

6. Average Stream Flow During Period of Release of Effluent into a Flowing Stream: >6.89E+03 >6.40E+03 (Cooling Tower

• Units of time and flow are expressed in Blowdown Flow Rate) minutes and gallons per minute (gpm),

respectively.

7.39E+06 8.42E+06 (Susquehanna River Flow Rate) bnor al ea e

1. Number of Releases: 0 0

2. Volume Released: NA NA

3. Total Activity Released: NA NA If a radionuclide was not detected, zero activity was used for that isotope in dose calculations. A zero activity indicates that no activity was positively detected in any sample when samples were analyz'ed with techniques which achieved the required Lower Limits of Detection (LLD) as specified in the SSES Technical Specification Table 4.11. 1. 1.1-1, Radioactive Liquid Waste Sampling and Analysis Program. In all cases, these LLDs were less than the levels required by Technical Specifications. The following are typical LLDs.

Radionuclide LLD UC Hn-54 4.5 E-08 Fe-59 5.0 E-08 Co-58 2.4 E-08 Co-60 5.4 E-08 Zn-65 4.9 E-08 Ho-99 1.7 E-07 I-131's-134 2.0 E-08 2.2 E-08 Cs-137 2.6 E-08 Ce-141 3.2 E-08 Ce-144 1.3 E-07 Sr-89 4.0 E-08 Sr-90 4.0 E-09 Fe-55 1.0 E-06 H-3 4.6 E-06 Gross Alpha 3.0 E-08 16 e

TABLE 4 SENIANNUAL EFFLUENT AND MASTE DISPOSAL REPORT (1992)

MATERBORNE EFFLUENTS - SUMNTION OF ALL RELEASES First Second A. Fission and Activation Products Unit Quarter Owrter

1. Total Release (Kot including TritiLss, Gases Al a) 6.05E 03 1.25E.02>>

2. Average Diluted Concentration During Period uC3/al 1.88E-OS 3.08E-08

3. Percent of Applicable Lia3t 7.27E-04 2.16E.03

8. TritiLss 1 ~ TotaL Release Ci 1.99E+01 2.32E+01

2. Average Diluted Concentration During Period uCi/al 6.20E-05 5.71E.OS

3. Percent of licable Limit 2.07E+00 1.90E+00 C. Dissolved and Entrained Gases

1. Total Release Ci 4.44E.04 6.32E.04

2. Average Diluted Concentration uC3/al 1.38E-09 1.56E.09 Duri Period

3. Percent of Appl3cable Liait 3.46E-03 3.89E 03 D. Gross Alpha Radioactivity

1. Total Release Ci O.DOE+00 O.DOE+00>>

E. Voluse of Masts ReLeased (Prior to Dilution) Gallons 9A3E+05 1.2SE+06 Liters 3.57E+06 4.84E+06 F. Voltage of Dilution Mater Used During Period of Release Gallons 8.39E+07 1.06E>>08 Liters 3.1SE+08 4.01E+08 G. Vol~ of Dilution Mater Liaed Over Entire Per3od Gallons 9.03E+08 8.39E+OS Liters 3.42E+09 3.17E+09

>>Reported values are estimated. 33onthly and quarterly snsple analyaea uere not available at the time of report preparation.

17

SENlNONlL EFFLlKÃf NO lNSTE DlSPOSAL RERRT EFFLMPS 41992'ATERBQtlK Batch Node Batch Node Nuclides Released Unit First Quarter Second Quarter A. Fission and Activation Products Na 24 Ci O.DOE+00 O.DOE+00 Cr-51 Ci O.OOE-M 1.63E.04 Nn-54 Ci 4.42E 04 2.68E-03 Fe-55 Ci 4.9'.03 6.77E-03*

Fe-59 Ci 1 42E-05 4.78E.04 Co-58 Ci 3.28E-06 5.95E-05 Co-60 Ci 5.60E-04 2.14E-03 Zn-65 Ci 2.50E 05 2.10E-04 Sr-89 O.DOE+M 0.00E+OP'.OOE+00 Sr-90 Ci O.DOE+00 Zr-95 Ci O.OOE+00 1.76E 06 Zr-97 Ci 0.DOE+00 5.03E-07 Tc-99m Ci O.OOE+00 O.DOE+00 Ag-110a Ci 2.39E-07 O.DOE+00 1-131 Ci O.OOE+00 O.DOE+00 Cs-134 Ci 7.87E.07 O.DOE+00 Cj-137 Ci 1.29E 05 7.80E 07 Ce-141 Ci O.OOE+00 O.DOE+00 Ce-144 Ci O.OOE+00 0.00E+00 Total for Period Ci 6.05E.03 1.25E 02 B. Tritiua Ci 1.99E+01 2.32E+01 Total'for Period Ci 1.99E+01 2.32E+01 C. Dissolved and Entrained Gases Ar-41 Ci O.DOE+00 O.DOE+00 Kr-85e Ci O.DOE+00 O.OOE+00 Kr-85 Ci O.DOE+00 O.DOE+00 Kr-87 Ci O.DOE+00 O.DOE+00 Kr-88 Ci O.DOE+00 O.ME+00 Xe-133e Ci O.DOE+00 O.DOE+00 Xe-133 Ci 2.10E.04 3.21E-04 Xe-135a Ci O.OOE+00 O.OOE+00 Xe-135 Ci 2.34E-04 3.11E-04 Total for Period Ci 4.44E.04 6.32E.04 Report va ues are est>mat s on rst quarter soap e ana yses sec quarter 1 discharge volumes.

18

TABLE 6 SEMIANNUAL EFFLUENT AND WASTE DISPOSAL REPORT SOLID WASTE AND IRRADIATED FUEL SHIPMENTS DATA PERIOD: JANUARY 1, 1992 - JUNE 30, 1992 A. SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL umbe o Shi ments Mode o ran ta es to 33 Truck Barnwe11, SC B. IRRADIATED FUEL SHIPMENTS Number of Shi ments Mode of rans or at o estinat o NONE NOT APPLICABLE NOT APPLICABLE 19

SUSQUKDNNA STEAM ELECTRIC STATION RADIOACTIVE WASTE REPORT SEMI-ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT SOLID RADIOACTIVE WASTE DATA PERIOD: Ja u 7/rale~

PREPARED BY: P. LEWI - H PHYSICIST - RADWASTE 731 94 APPROVED BY D. L HAGAN EF ENTS MANAG SUPV.

20

P 0

1. All Activi'ties Reported in millicuries (mCi) unless otherwise noted.

2. Reported Activities, as indicated with the (<) sign, are comprised in whole or part of MDL Values.

3. No Class B or Class C waste disposed of during this report period.

4. No waste disposed of in the following Waste Streams during this report period:

Condensate Demineralize/Radwaste Demineralizer Solidified using Portland Cement Evaporator Concentrates Solidified using Portland Cement Sump Sludge Solidified using Portland Cement Absorbed Oil Liquid Oily Waste (Petroleum Based Material)

Dewatered RWCU Filter Media Liquid Radwaste Filter Media Solidified using Portland Cement

5. Processed DAW is that which has been volume-reduced by means of compaction, supercompaction, incineration or other means prior to disposal. Non-processed DAW is that which has been disposed of without benefit of volume reduction (usually metals).

21

TABLE 7 CLASS A SOURCE OF WASTE: LIQUID RADWASTE FILTER MEDIA TYPE OF CONTAINER HIC METHOD OF PROCESS: - DEWATERED ISOTOPES ACTIVITY (mCi) 4 OF TOTAL Ag-110m Am-241 9 '64E+01 0 OOOE+00 0 '24 0.004 Am-243 0 ~ OOOE+00 0 ~ 004 C-1'4 4 '98E+00 0 F 004 Ce-144 5 '08E+01 0 F 014 Cm-242 4 '03E-03 0 F 004' Cm-244 2 '31E-03 F 004 Co-58 Co-60 3.618E+03 1.471E+04 0 '64 3 '84 Cr-51 3.281E+04 7.774 Cs-134 0 ~ OOOE+00 0 F 004 Cs-137 O.OOOE+00 0 F 004 Fe-55 Fe-59 2.894E+05 1 701E+04 68 4

'34

'34 H-3 5 '68E+01 0 ~ 014 Hf-181 I-129 2 '78E+02 3 '82E-01 0 '54 O.ooa I-131 0 ~ OOOE+00 0 F 00\

Mn-54 5.554E+04 13 ~ 154 Nb-94 0 OOOE+00 0 F 004 Nh-95 4.585E+01 0.014 Ni-59 0 ~ OOOE+00 0 F 00\

Ni-63 4 '18E+02 0 lot

~

Np-237 0 ~ OOOE+00 0 00\

F Pu-238 0 ~ OOOE+00 0 004 Pu-239 0 ~ OOOE+00 0 F 004 Pu-241 O.OOOE+00 0 ~ 004 Pu-242 0 ~ OOOE+00 0 F 00%

Sh-124 3 166E+02 0 ~ 074 Sb-125 O.OOOE+00 0 F 004 Sr-89 5 '46E+01 ,0 ~ 014 Sr-90 0 ~ OOOE+00 0 F 004 Tc-99 < 2 167E-01 0 F 00%

Zn-65 8 '03E+03 1 904 TOTAL ACTIVITY (Ci 422 '09810 100 F 004 CONTAINER VOLUME 536 '00 f43 15 '98 1A3 22

TABLE 8 CLASS A SOURCE OF WASTE: CONDENSATE DEMINERALIZER/

RADWASTE DEMINERALIZER TYPE OF CONTAINER: HIC METHOD OF PROCESS: DEWATERED ISOTOPES ACTIVITY (mCi) OF TOTAL Ag-llom 1 '23E+02 G. 194 Am-241 1 '19E-01 0. 004 Am-243 O.OOOE+00 0.004 C-14 7.421E+02 0.744 Ce-144 O.OOOE+00 0.004 Cm-242 O.OOOE+00 0.004 Cm-244 1 '44E-01, 0.00%

Co-58 5.883E+03 5.89%

Co-60 2 '62E+04 23.664 Cr-51 1.200E+02 0.124 Cs-134 4.776E+01 0.05%

Cs-137 1 '27E+02 0 ~ 124 Fe-55 3 '18E+04 37.264 Fe-59 4.590E+02 0.464 H-3 4 '06E+02 0.404 Hf-181 O.OOOE+00 0.00%

I-129 4 1 '18E+01 0.014 I-131 1.010E+02 0 104 Mn-54 1.524E+04 15.274 Nb-94 O.OOOE+00 0.004 Nb-95 O.OOOE+00 0 004 F

Ni-59 O.OOOE+00 0.004 Ni-63 3.857E+02 0.394 Np-237 O.OOOE+00 0 004 Pu-238 4.096E-01 0 004 Pu-239 2.395E-01 0 004 Pu-241 O.OOOE+00 0.00%

Pu-242 O.OOOE+00 0.004 Sb-124 2.395E+00 0.004 Sb-125 O.OOOE+00 0.004 Sr-89 3 '87E+01 0.04%

Sr-90 4 '74E+00 0.004 Tc-99 < 9 '23E+00 0 F 01\

Zn-65 1.524E+04 15.27%

LA-140 5.2231E+00 O.OOX Xe-131M 5.4230E&l 0. OOX I-133 3.3730E&1 O.OOX Sr-92 3.9951E+00 O.OOX Tc-99M 7.1449E&1 O.OOX TOTAL ACTIVITY (Ci) 99.854198 100.00X CONTAINER VOLUME 4099.200 'ft:3 116.079 m3 23

TABLE 9 CLASS A.

SOURCE OF WASTE CONDENSATE DEMINERALIZER/

RADWASTE DEMINERALIZER TYPE OF CONTAINER'ARBON STEEL LINER METHOD OF PROCESS. DEWATERED ISOTOPES ACTIVITY (mCi) 4 OF TOTAL Ag-llom 1 '4&E+00 0.17\

Am-241 9 '30E-04 0 ~ 004 Am-243 0 F 004 C-14 Ce-144 0 ~ OOOE+00 5 982E+00 0 OOOE+00 0 '9\

0.004 Cm-242 0 ~ OOOE+00 0.004 Cm-244 7 '19E 04 0.004 Co-58 Co-60 6.365E+00 1.886E+02 0

18

'24

'54 Cr-51, 6 ~ 620E+01 6 '84 Cs-134 6 '42E-01 0 074 Cs-137 3 '66E+00 0 31\

Fe-55 3 '92E+02 36 124 Fe-59 2 '89E+01 2. 344 H-3 7.326E+01 7. 17%

Hf 181 0 ~ OOOE+00 0 00\

'44 F

I-129 C 3 '41E-01 0 I-13 1 O.OOOE+00 0.00\

Mn-54 2 '50E+02 '24 '44 Nb-94 O.OOOE+00 0 004 F

Nb-95 O.OOOE+00 0 F 004 Ni-59 0 ~ OOOE+00 0 F 004 Ni-63 Np-237 3 '16E+00 O.OOOE+00 0 '04 0 F 004 Pu 238 2 '41E-03 0 F 004 Pu-239 1.429E-03 0 F 00\

Pu-241 0 ~ OOOE+00 0 F 004 Pu-242 0 ~ OOOE+00 0 F 004 Sb-124 O.OOOE+00 0 ~ 000 Sb-125 0 OOOE+00 0 F 000 Sr-89 3 '70E+00 0.344 Sr-90 Tc-99

&~ 496E-02

< 2 ~ 724E-01 0

0

'14

'34 Zn-65 TOTAL ACTIVITY (Ci) 2 '84E+01 1 '22149 2 '44 100 F 004 CONTAINER VOLUME 513.600 ft3 14.544 m3

TABLE 10.

CLASS A SOURCE OP WASTE: ULTRASONIC RESIN CLEANING WASTE TYPE OF CONTAINER HIC METHOD OF PROCESS DEWATERED ISOTOPES ACTIVITY (mCi) 4 OF TOTAL Ag-110m 4 '64E+01 0 F 014 Am-241 7.287E-02 0 F 004 0 F 00\

Am-243 C 14 Ce-144 0 ~ OOOE+00 2 '09K+02 O.OOOE+00 0 '6\

0 F 004 Cm-242 1.047E-02 0 00\

Cm-244 9.285E 04 0 F 004 Co-58 3.074E+02 0 ~ 084 Co-60 2.028E+04 5 '74

'14 Cr-51 7.777E+02 0 Cs 134 6.423E+01 0 '24 Cs-137 1 230E+02

'51E+05 0 '34 88 '94 Fe-55 3 Fe-59 7 '15E+02 0 19%

H-3 2.887E+01 0 ~ 014 Hf-181 0 OOOE+00 0 F 004 I-129 < 5. 688E-01 0 F 004 I-131 0 Oot' Mn-54 Nb-94 0 ~ OOOE+00 1.754E+04 O.OOOE+00

'5\

0 ~ Oot Nb-95 0 ~ OOOE+00 0 F 004 Ni-59 0 ~ OOOE+00 0 F 004 Ni-63 5.359E+02 0 '44, 0.004 Np-237 O.OOOE+00 PQ-238 3 '22E-06 0 004 Pu-239 ~ 4.380E-02 0 F 00%

PQ-241 0 ~ OOOE+00 0 004 Pu-242 0 ~ OOOE+00 0 F 004 Sb-124 2 '54E+01 0 F 01\

Sb-125 0 ~ OOOE+00 O.ooa Sr-89 6 '70E+00 0 F 004 Sr-90 3 '44E-01 0 F 000 Tc-99 g 9 '88E-01 0 F 004 Zn-65 1 '36E+03 0 ~ 434 TOTAL ACTIVITY (Ci) 377 '05060 100 F 004 CONTAINER VOLUME 331iooo l!t3 9.373 m3 25

TABLE 11 CLASS A SOURCE OF WASTE: ERASED DAW TYPE OF CONTAINER: STRONG TIGHT CONTAINER METHOD OF O'ROCESS: N /A ISOTOPES .ACTIVITY (mCi) OF TOTAL Ag-110m O.OOOE+00 0.00\

Am-241 7.841E-01 0. 024 Am-243 , O.OOOE+00 0. 004 C-14 1 045E-01 0. 004 Ce-144 O.OOOE+00 0 004 Cm-242 7 899E-03 0.004 Cm-244 4 013E-03 0 F 004 Co-58 Co-60 6.312E+00 2.275E+02 0

7

'04

'94 Cr-51 7 250E-01 0. 02%

Cs-134 O.OOOE+00 0.00%

Cs-137 O.OOOE+00 0.004 Fe-55 . 2 693E+03 83 944 Fe-59 1.722E+01 0.544 H-3 1 160E-01 0 004 F

Hf-181 O.OOOE+00 0.004 I-129 C 1.046E-01 0 F 004 I-131 O.OOOE+00 0 F 004 Mn-54 Nh-94 2.234E+02 0 ~ OOOE+00 6 '64 0 F 004 Nh-95 O.OOOE+00 0 F 004 NI-59 0 OOOE+00 0 F 00\

Ni-63 8 516E+00 0.274 Np-237 O.OOOE+00 O.boa Pu-238 1 '26E-02 O.ooa Pu-239 4+635E-03 0 F 004 Pu-241 Pu<<242 8 '41E-01 0 OOOE+00 0 '3\

0 F 00\

Sb-124 0 ~ OOOE+00 0.004 Sb-125 O.OOOE+00 0 F 004 Sr-89 O.OOOE+00 0 F 00\

Sr-90 0 ~ OOOE+00 0~004 Tc-99 < 1.413E-01 0 F 004 Zn-65 TOTAL ACTIVITY (Ci) 2 '40E+01 3 '07676 0 '24 100.000 CONTAINER VOLUME 921 '00 ft3 26 '92 m3 26

TABLE 12 CLASS A SOURCE OF WASTE: NON-HtOCESZR DAW TYPE OF CONTAINER: STRONG TIGHT CONTAINER METHOD OF PROCESS: N/A ISOTOPES ACTIVITY (mCi) OF TOTAL'.004 Ag-110m O.OOOE+00 Am-241 9 '61E-03 0 F 00%

Am-243 O.OOOE+00 O.OO4 C-14 2 '82E-01 'O. OOi Ce-144 O.OOOE+00 0.00%

Cm-242 1.461E-02 0.004 Cm-244 5.979E-03 0.004 Co-58 3.812E+02 0.77%

Co-60 3 '39E+03 7 ~ 18%

Cr-51 3 '78E+03 7.674 Cs-134 0 ~ OOOE+00 0.00$

Cs-137 O.OOOE+00 O.ooi Fe-55 3 '23E+04 71.504 Fe-59 6.227E+02 1.264 H-3 3 '83E-01 0 004 Hf-181 0 ~ OOOE+00 0 004 I-129 1 856E-01 0 F 004 I-13 1 O.OOOE+00 O.oot Mn-54 5 '02E+03 10 '54 0.004 Nb-94 0 ~ OOOE+00 Nb-95 0 ~ OOOE+00 0 F 004 Ni-59 0 ~ OOOE+00 0 F 004 Ni-63 9 '17E+01 0 194 Np-237 0 ~ OOOE+00 0 F 00\

Pu-238 lo979E 02 0 F 604 Pu-239 8o151E 03 0 F 004 Pu-241 1+597E+00 0.004 Pu-242 0 ~ OOOE+00 0 F 00%

Sb-124 0 ~ OOOE+00 0 F 004 Sb-125 0 ~ OOOE+00 0 F 004 Sr-89 0.074 Sr-90 Tc-99 3 ~ 411E+01 2 '39E 02 2 ~ 189E-01 0 '0t 0 F00%

Zn-65 5 '61E+02 1" TOTAL ACTIVITY (Ci) 49 '66420 19'00.004 CONTAINER VOLUME 315.000 et3 8.920 m3 27

TABLE 13 CLASS A SOURCE OF WASTE: CARTRIDGE FILTERS TYPE OF CONTAINER' HIC METHOD OF PR OCE SS: N/A ISOTOPES ACTIVITY (mCi) 4 OF TOTAL Ag-110m 0 OOOE+00 '0.004 Am-241 6.465E-03 0.00t Am-243 O.OOOE+00 0 004 C-14 1.657E-01 0 004 Ce-144 O.OOOE+00 0 F 004 Cm-242 8 '19E-03 0 F 004 Cm 244 3 '44E-03 0 F 004 Co-58 5 ~ 460E+01 0 324 Co-60 1 ~ 328E+03 7 684 Cr-51 2.929E+02 1 ~ 694 Cs<<134 0 OOOE+00 0 F 004 Cs-137 0 ~ OOOE+00 0 F 00\

Fe-55 1.368E+04 79 ~ 124 Fe-59 H-3 1 ~ 078E+02 1 ~ 554E-01 0 '24 0 F 004 Hf-181 0 OOOE+00 0 F 004 I-129 1 ~ 481E-01 0 F 00\

I-131 0 ~ OOOE+00 0 004 Mn-54 Nb-94 1 ~ 652E+03 0 ~ OOOE+00 9 '64 0 F 00\

Nb 95 0 OOOE+00 0 F 004 Ni-59 0 ~ OOOE+00 .0 004 Ni-63 4 '23E+01 ~

0 ~ 244-Np-237 0 ~ OOOE+00 0 ~ 004 Pu-238 1;306&02 0 ~ 004 Pu-239 5 '01E-03 0 ~ 004 Pu-241 Pu-242 1 '32E+00 0 ~ OOOE+00 0 '14 0 o'00$

Sb-124 0 ~ OOOE+00 0 000 Sb-125 0 ~ OOOE+00 0 004..

Sr-89 2.903E+00 . 0 024' Sr-90 2 '70E-03 '

,0 ~ 004 Tc-99 ~ 678E 01 0 00t Zn-65 1 276E+02 0 744 TOTAL ACTIVITY 17 '86441 100 F 06'.

CONTAINER VOLUME 271 '00 it3 7.691 m3 28

TABLE 14 ESTIMATED TOTAL ERROR ASSOCIATED WITH EFFLUENT AND RADWASTE NEASURBIENTS DATA PERIOD: JANUARY 1, 1992 TO JUNE 30, 1992 casu erne t IILttt Estimated

1. Airborne Effluents

'a ~ Fission and Activation Gases 15.9X

b. I-131 13.3X C. Particulates 15.8X

d. Tritium 5.7X

2. Waterborne Effluents

a. Fission and Activation Products 5.0X

b. Tritium 3.3X

c. Dissolved and Entrained Gases 8.4X

d. Gross Alpha Activity 4.0X

e. Volume of Waste Released 5.0X (Prior to Dilution)

f. Volume of Dilution Water used 15.0X During Period-s

3. Source of Waste and Processing Employed (Waste Stream)

a. Liquid Radwaste Filter Media 15.1X (Dewatered - HIC)

b. Condensate Deminer alizer/ 15.1X Radwaste Demineralizer (Dewatered HIC) c ~ Condensate Demineralizer/ 15.1X Radwaste Demineralizer (Dewatered Carbon Steel Liner)

d. Ultrasonic Resin Cleaning Waste 15.1X (Dewatered - HIC)

e. Cartrid'ge Filters (HIC) 15.1X Compacted DAW 25.0X (Strong Tight Container) g Non-Compacted DAW 25.0X (Strong Tight Container) 29

TABLE 15 SEMIANNUAL EFFLUENT AND WASTE DISPOSAL REPORT

.DATA NOT REPORTED IN PREVIOUS SEMIANNUAL REPORT NUCLIDE CATEGORY UNIT FOURTH QUARTER 1991 A. Airborne Effluents

1. Sr-89 Ci 0.00E+00

2. Sr-90 O.OOE+00

3. Gross Alpha Ci 1.88E-06 B. Waterborne Effluents

1. Sr-89 Ci O.OOE+00

2. Sr-90 Ci O.OOE+00

3. Fe-55 Ci 3. 13E-03

3. Gross Al ha Ci 0.00E+00 30

SECTION 3 CFMlVGES TO THE OFFSITE DOSE CALCULATIONMANUAL AND THE SOLID NASTEPROCESS CONTROL PROGRAM 31

CHANGES 0 E OFFSITE DOSE CALCUL TION ANU L Three revisions to the SSES Offsite Dose Calculation Hanual (ODCH) occur red during the period, approved on 2/21/92, 3/6/92 and 6/25/92.

The revision of 2/21/92 was substantial, with credit taken for the entire document review. Section 8.2, which pertains to operability requirements for ventilation exhaust treatment systems, was revised to make level of detail and commitment in place more appropriate. Section 10.3 had title change from "Criteria for Potential Unmonitored Release Pathways"- to "Evaluation and Honitoring Criteria for Effluent Pathways." The text was changed to clarify evaluation procedures for potential unmonitored releases. Section 11.0, "ODCH Revision and Control," was changed to require review of the ODCH by SSES PORC before approval by Hanager-Nuclear Technology, for all subsequent revisions. Appendix E, "Hethods Used to Generate Dose Rate Calculation Morksheets," was deleted because these methods are incorporated into more appropriate station procedures. The Dilution Factor for LADTAP releases has been specified to the number used by the LADTAP program. "Dilution Factors and Transit Times as a Function of River Level" was changed to tabular form (Table D-1) to facilitate reading the desired dilution factors and transit times. Figures 5 and 6 have been replaced with new diagrams which show better symbolic detail, and .more accurate placement of sampling stations with reference to the SSES site. These figures are computer generated, and will be much simpl to modify in response to future sampling point changes. Table 4 was expanded to include dose calculation factors specific to 40 isotopes.

Elements of Table 6 (maximum values for pathways) were consolidated into Table 4 so that Table 6 could be eliminated. Dose factors for all Reg.

Guide 1. 109 pathways, age groups and receiver organs have been included.

The second paragraph in section 10.8, regarding use of the shortest averaging period for vent monitor history data, was removed because it was ambiguous. Several detail and typographic corrections were also made.

Because the ODCH received a complete review pursuant to section 11.0 of the document, an entire copy of the revision is included under this heading.

T he revision of 3/6/92 addresses section 10.6 definition of "Appropriate Treatment" for liquid wastes. This revision provides for the use of the atmospheric demineralizer, prior to the startup and use of this system.

The atmospheric demineralizer is considered appropriate treatment for the liquid radwaste chemical processing subsystem, which is specifically intended for organically-contaminated or other high-conductivity liquid waste. For batches containing no identified gamma activity above T.S.

Table 4.11.1.1.1-1 LLD level, release without treatment is considered appropriate. Figure 1, "Liquid Radwaste System Flow'iagram" was changed to include the atmospheric demineralizer 'system. CST berm water was added as an influent source to the chemical waste system. A copy of pages changed for this revision is included under this heading.

32

The revision of 6/25/92 provides for the addition of a farm, location 12F7, in Figure 6 (" Environmental Monitoring Locations Greater than One Mile from the SSES"). This farm is located 8.3 miles WSW from the plant.

The addition of this sampling point is made pursuant to Tech. Spec.

Table 3.12.1-1(4c). The farm was identified in the 1991 Land Use Census as a location irrigating with Susquehanna River water downstream of SSES discharge. Table 6 was also changed to include this farm. A copy of pages changed for 'this revision is included under this heading.

All the requirements of SSES Technical Specifications are being met following the changes discussed above.

33

PENNSYLVANIA POMER & LIGHT COMPANY SUSQUEHANNA STEAM ElECTRIC STATION OFFSITE OOSE CALCULATION MANUAL Prepared By Date Reviewed By Date S pervisor- nvironmental Services

,Nuclear Reviewed By QA -021 Date t g or Approved By Date ~ +i Manager -Nuclear T chnology DATE (1 of 124)

SUMNRY OF ODCN CHANGES Changes other than those of a minor, editorial nature are summarized below.

l. Section 8.2 "Gaseous Waste Treatment" pertaining to the operabiljty requirements for ventilation exhaust treatment <stems was revised to make the level of detail and commitment in place more appropriate (p. 31).

2. Section 10.3, previously entitled, "Criteria for Potential Unmonitored Release Pathways," was changed to "Evaluation and Monitoring Criteria for Effluents Pathways." The text was revised to clarify evaluation procedures for potential unmonitored releases (p. 49), in resolution to SOOR 1-90-392.

3. Section 11.0, "ODCM Review and Revision Control," was revised to require review of the ODCM by PORC before approval can be authorized by the Manager Nuclear Technology for all new revisions.

4, Appendix E, "Methods Used to Generate Dose Rate Calculation Morksheets,"

was deleted due to being incorporated into more appropriate station procedures.

5. The Dilution Factor for liquid releases (page 22) has been specified to the number used by the LADTAP program. "Dilution Factors and Transit Times as a Function of River Level," was changed to tabular form (Table D-1, p. D-3) to-facilitate reading the desired dilution factors and transit times.

6. Figures 5 and 6 have been replaced with new diagrams which show better symbolic detail and more accurate placement of sampling stations with reference to the SSES site. These figures are computer-generated and will in the future be much simpler to modify in reflection to sampling station changes.

7. Table 4 has been expanded to include dose calculation factors specific to forty isotopes. Elements from Table 6 (maximum values for pathways) have been consolidated into these pages so that Table 6 could be eliminated.

Each page now has a matrix listing for pathway, age group and receptor organ.

8. Several detail and typographic corrections have been made. These include those for liquid effluent setpoint calculation (p. 6), waterborne effluent factor descriptions (p; 14), equations 10 (p. 21) and ll (p. 22), for new limits (pp.51-D/g location documentation (p. 42), and for projected dose 2).

9. The second paragraph in section 10.8 (p. 53), regarding use of the shortest averaging period for vent monitor history data, was removed because it is ambiguous. The following paragraph properly qualifies what is meant by the shortest averaging period.

(2 of 124)

10.~ This document has been received a total review per requirements in Section and changes herein will not reduce the accuracy-or reliability of

~ ~

11.0,

~

dose calculations or setpoint determinations in accordance with Technical

~ ~ ~

Specification 6.14.2.a.2.

~ ~ ~ ~

(3 of 124)

TABLE OF CONTENTS Revis)on

~~e

1.0 INTRODUCTION

.................................. 1 12/11/89 2 2/21/92 3 12/11/89 2.0 SETPOINTS.....................................~ 4 2/21/92 2.1 WATERBORNE EFFLUENT MONITORS...-.......... 2/21/92 12/11/89 2/21/92 12/11/89 12/11/89

2. 2 AIRBORNE EFFLUENT MONITORS... - .. - -........ 9 2/21/92 10 12/11/89 11 12/11/89 12 12/11/89 3.0 WATERBORNE EFFLUENT CONCENTRATION MEASUREMENTS 13 2/21/92 14 2/21/92 4.0 AIRBORNE EFFLUENT DOSE RATES .............. 15 2/21/92

4. 1 NOBLE GASES............................ 15 2/21/92 4.2 RADIONUCLIDES OTHER THAN NOBLE GASES... 16 2/21/92 17 2/21/92 18 2/21/92 19 12/11/89 20 2/21/92 5.0 INDIVIDUAL DOSE DUE TO WATERBORNE EFFLUENT.... 21 2/21/92 22 2/21/92 23 12/11/89 24 12/11/89 6.0 INDIVIDUAL DOSE DUE TO AIRBORNE EFFLUENT... 25 2/21/92

6. 1 NOBLE GASES............................ 25 2/21/92 6.2 RADIONUCLIDES OTHER THAN NOBLE GASES..- 26 2/21/92 27 2/21/92 7.0 TOTAL DOSE.................................... 28 2/21/92 29 2/21/92 8.0 OPERABILITY OF WASTE TREATMENT SYSTEMS..... 30 2/21/92 8.1 LI(UID WASTE TREATMENT................. 30 2/21/92 8.2 GASEOUS WASTE TREATMENT................ 30 2/21/92 31 2/21/92 32 2/21/92 8.3 SOLID WASTE TREATMENT .................... 32 2/21/92 2/21/92 33 (4 of )2f)

LIST OF FIGURES Revision Ram 4

Figure 1 Liquid Radwaste System Flow Diagram..."...... 34 2/21/92 Figure 2 Offgas and Recombiner System Flow Diagram... 35 2/21/92 Figure 3 Solid Waste Management System Flow Diagram.. 36 2/21/92 Figure 4 SSES Dry Contaminated Waste Processing...... 37 2/21/92 Figure 5 Environmental Monitoring Locations Within One Nile of SSES............................ 42 2/21/92 Figure 6 Environmental Monitoring Locations Greater than One Nile from SSES..................... 43 2/21/92 (5 of 124) fI

Revision

~ae 9.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM. 38 2/21/92 9.1 DEFINITIONS............................... 38 2/21/92 9.2 MONITORING PROGRAM............".......... 38 2/21/92 9.3 CENSUS PROGRAM............................ 39 2/21/92 9.4 INTERLABORATORY COMPARISON PROGRAM........ 40 2/21/92 41 2/21/92 10.0 DOSE ASSESSMENT POLICY STATEMENTS............ 49 2/21/92 10.1 SELECTION OF ANALYSIS RESULTS FOR 49 2/21/92 DOSE CALCULATIONS 10.2 ASSIGNMENT OF RELEASES TO THE REACTOR 49 2/21/92 UNITS 10.3 EVALUATION AND MONITORING CRITERIA FOR 49 2/21/92 EFFLUENT PATHWAYS 10.4 FLOW FROM THE SGTS VENT WHEN THE SYSTEM 50 2/21/92 IS NOT IN USE 10.5 ODCM SETPOINTS ARE UPPER LIMIT VALUES 51 2/21/92 10.6 DEFINITION OF "APPROPRIATE TREATMENT" 51 2/21/92 FOR LIQUID WASTES 10.7 MONITOR LINE-LOSS CORRECTIONS 52 2/21/92 10.8 SELECTION OF DATA FOR DETERMINATION OF 53 2/21/92 DOSE RATE COMPLIANCE 10.9 LOW-LEVEL RADIOACTIVITY IN THE SEWAGE 54 2/21/92 TREATMENT PLANT 11.0 ODCM REVIEW AND REVISION CONTROL............. 2/21/92 APPENDIX A SAMPLE CALCULATIONS OF ODCM PARAMETERS........................... A-1 2/21/92 A-2 2/21/92 A-3 12/11/89 A-4 2/21/92 A-5 2/21/92 A-6 2/21/92 A-7 2/21/92 A-8 2/21/92 A-9 2/21/92 A-10 2/21/92 A-11 12/11/89 A-12 12/11/89 A-13 12/11/89 APPENDIX 8 REPORTING REQUIREMENTS............... B-1 12/11/89 B-2 12/11/89 B-3 12/11/89 B-4 12/11/89 (6 of 124)

Revision

~ae ~ate APPENDIX C - SITE SPECIFIC INFORNTION USED BY GASPAR CODE.................. C-1 12/11/89 APPENDIX D - SITE SPECIFIC INFORNTION USED BY LADTAP CODE.................. D-1 2/21/92 D-2 2/21/92 0-3 2/21/92 (7 of 124)

LIST OF TABLES Revi sion Qge Table 1 Radiological Effluent Objectives and Standards.. 3 12/11/89 Table 2 Dose Factors for Noble Gases ................... 18 2/21/92 Table 3 Sample Annual Average Relative Concentrations and Deposition Rates............................ 19 12/11/89 Table 4 Dose Factors for Inhalation, Ingestion and Ground Exposure Pathways: Radionuclides Other T han Noble Gases................................ 20 2/21/92 Table 5 Waterborne Effluent Dose Parameters for Adults.. 24 '12/11/89 Table 6 Operational Radiological Environmental Monitoring Program.............................. 44 2/21/92 45 2/21/92 46 2/21/92 Table 7 Detection Capabilities for Environmental Sample Analysis................................. 47 2/21/92 48 2/21/92 Table B-1 Radiological Environmental Monitoring Program Annual Summary.................................. B-3 12/11/89 Table B-2 Reporting Levels for Nonroutine Operating R eportso ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ o B 4 12/11/89 Table D-1 Dilution Factors and Transit Times for SSES Effluents to Danville, PA....;.................. D-3 2/21/92 iv (8 of 124)

1.0 INTRopuCTION The purpose of this manual is to provide the parameters and methodolo be used in calculating offsfte doses and effluent monitor setpoints fo the Susquehanna Steam Electric Station, Units 1 and 2. Included are methods for determining maximum individual, whole-body, and organ doses due to waterborne and airborne effluents to ensure compliance with the dose limitations in the Technical Specfffcatfons. Methods are included for performing dose calculations to ensure co%plfance with the waterborne and airborne treatment system operabilfty sections of the Technical Specifications. This,manual includes the methods used for determining quarterly individual doses for inclusion fn Effluent and Waste Disposal Semiannual Reports.

The dose models consider two release modes: airborne and waterborne. All airborne effluents are treated as ground-level releases. Dose to each of the seven organs listed in Regulatory Guide 1.109 (bone, liver, total body, thyroid, kidney, lung, and GI-LLI) are computed based on the individual nuclide composition of the effluent. The largest of the doses are compared to 10 CFR 50, Appendix I design objectives.

Liquid effluents discharged into a river undergo mixing prior to consumption as either potable water or through the fish pathway. For releases to the Susquehanna River, river model dilution factors are used.

Doses to the seven critical organs are determined from individual nuclide contributions and are compared to the 10 CFR 50 Appendix I desfgn objectives. Complfance with the 10 CFR 20 maximum permissfble concentrations is done on a batch-by-batch basfs prior to discharge.

This manual discusses the methodology to be used fn determining effluent monitor alarm/trip- setpofnts to be used to ensure compliance with the instantaneous release rate limits in the Technical Specifications. Methods are descrfbed for determfnfng the annual cumulative dose to a real individual from liquid effluents, gaseous effluents, and direct radfatfon for critical organs to ensure compliance wfth 40 CFR 190 limits. The OEC 21588 (9 af 12))

exposure of an individual through any of the appropriate pathways.

The Radiological Environmental Honitoring Program is described in Section 9.0 of the manual, which includes the annual land use census survey and interlaboratory comparison program.

It is the responsibility of the SuperintendenZ of Plant-Susquehanna to ensure that this manual is used in performance of the surveillance requirements and for compliance with the limiting conditions of operations stated in the Technical Specifications. It is the responsibility of the Manager-Nuclear Technology to ensure adequacy and correctness of calculational approaches.

DAT (10 of 124)

/

TABLE RADIOLOGICAL EFFLUENT OBJECTIVES 5 STANDARDS 10 CFR 50 40 CFR 190* 10 CFR 20 APPENDIX I STANDARDS STANDARDS**

DESIGN OBJECTIVES (BOTH REACTOR (BOTH REACTOR (PER REACTOR UNIT) UNITS COMBINED) UNITS CQHB INED)

'WATERBORNE EFFLUENTS Dose to Total Body From all Pathways- 3 mrem/year Oose to any Organ From all Pathways 10 mrem/year AIRBORNE NOBLE GAS EFFLUENTS Dose Rate to Total Body - - - - --

-- 500 mrem/year Oose Rate to Skin - - - - - - - 3000 mrem/year Gama Dose in Air-Beta Dose in Air - - - - -- - - - - - -

10 mrad/year 20 mrad/year Dose to Total Body of an Individual 5 mrem/year Dose to Skin of an Individual - -- 15 mrem/year AIRBORNE RADIOIODINES AND PARTICULATES

=

Dose Rate to any Organ- 1500 mrem/year Oose to any Organ From all Pathways- 15 mrem/year TOTAL URANIlN FUEL CYCLE Dose to Whole Body From all Fuel Cycle Operations - - --- -- 25 mrem/year

! Dose, to Thyroid From all Fuel Cycle Operations 75 mrem/year Dose to any Other Organ From all Fuel Cycle Operations - - - - - -- - - - 25 mrem/year TOTAL QUANTITIES RELEASED Krypton-85 Released per Gigawatt-Year - - -- -- 50,000 curies Iodine-129 Released per Gigawatt-Year - - - - 5 millicuries Combined Plutonic-239 and Other Alpha-Emitting Radionuclides Mith Half Lives Greater Than One Year Released per Gigawatt-Year .5 mi llicuries

• As currently reflected in Technical Specification 3. 11.4.

~*Technical Specification limits set to ensure compliance with 10 CFR 20 limits

2.1 SP C - THE RADIOACTIVE LI(UID EFFLUENT MONITORING INSTRUMENTATION SHOWN. IN TABLE 3.3.7.10-1 SHALL BE OPERABLE WITH THEIR ALARM/TRIP SETPOINTS SET TO ENSURE THAT THE LIMITS OF SPECIFICATION 3.11.1.1 ARE NOT EXCEEDED. ~THE ALARM/TRIP SETPOINTS OF THESE CHANNELS SHALL BE DETERMINED IN ACCORDANCE WITH THE METHODOLOGY AND PARAMETERS DESCRIBED IN THE OFFSITE DOSE CALCULATION MANUAL (ODCM).

A gross radioactivity monitor providing automatic termination of liquid effluent releases is present on the liquid radwaste effluent line. Flow rate measurement devices are also present on the liquid radwaste effluent line and the discharge line (cooling tower blowdown). Precautions, limitations, and setpoints applicable to the operation of the Susquehanna Steam Electric Station liquid effluent C

monitors are provided in the applicable plant procedures. Setpoint values are to be calculated to ensure that alarm and trip actions occur upon approaching the MPC limits of 10 CFR 20, Appendix B, Table II, Column 2 at the release point to the unrestricted area. The calculated alarm and trip action setpoints for the. liquid effluent monitor and each flow measurement device must satisfy the following equation:

~cF+f gC (Eq 1) where:

C the liquid effluent concentration limit implementing 10 CFR 20 for unrestricted areas (uCi/ml).

c the setpoint (uCi/ml) of the radioactive liquid effluent monitor measuring the radioactivity concentration in the effluent line prior to dilution and subsequent release.

(12 of $ 24)

the radwaste d1scharge flow setpoint, in volume per unit time, fn the same units as F.

F the dilution (cooling tower blowdown) water flow setpoint as measured prior to injection of the radwaste, in volume per unit t1me.

Radioact1ve 11quid effluents from the SSES are only discharged as batch releases. and are discharged through. the liquid radwaste effluent line. The radioactive liquid waste stream is diluted in the plant discharge (cooling tower blowdown) line prior to entering the Susquehanna River. The limiting batch release concentration (c) corresponding to the liquid radwaste effluent line monitor setpoint is calculated from the above expression, The MPC value used for the liquid effluent concentration limit (C) in the above expression for the liquid radwaste effluent line monitor setpoint is I x 10 uC1/ml or the actual MPC for identified mixtures. Therefore, the expression for determining the setpoint on the liquid radwaste effluent line monitor becomes:

c < (1 x 10 ) f, (UCf/m1) (Eq. 2)

In order to prevent spurious isolations by the LRM effluent radiation monitor, the setpoint concentration, (c) can be defined as:

c i X(A) where (A) is the actual tank concentration and X P 1 The setpoint dilut1on factor must then be some factor, Y (where Y P X), times the minimum dilution factor.

(13 of 124)

f Im NPC where ~+~ I the minimum dilution factor f Im L+U - Qhl f HPC where ~+~ the setpoint,dilution factor f

The requirements of Equation (2) are then met as follows:

Y(A) HPC ~+~

f Since, by definition, Y > X and Y(A) > X(A), then:

c -X(A) gHPC f+~

f The setpoint concentration (c) can be converted to a setpoint count rate by use of the monitor calibration factor.

(Eq. 3)

Setpoint (cpm) + Background (cpm)

Cal. Factor (uCi/ml per cpm)

The setpoint for the dilution water flow (cooling tower blowdown) is 5000 gpm from both cooling tower basins. The setpoint for the LRM discharge flow can then be determined from:

L+U - MU (Eq 4) f HPC Sample calculations for determining the release concentration limits and setpoints are given in Section A.l.l of Appendix A.

The Service Mater System provides screened water from the cooling tower basin for, cooling plant systems and equipment. The Residual Heat Removal (RHR) Service Mater System provides water from the (14 of 124)

Engineered Safeguard Service Mater (ESSW) spray pond to the RHR heat exchangers. In post-accident conditions, RHR Service Water can supply water for vessel and containment flooding. The Service Water and RHR Service Water Systems are not normal pathways for'liquid effluents. Radiation monitors are in place on these systems to provide indication of leaks across heat exchangers into the service water. The high radiation setpoints for these monitors are set at 2E-5 uCi/cc cesium-137 equivalent. Considering the radionuclides predominant in SSES liquid effluents, e.g., Co-58, Co-60, Fe-59, Mn-54 and Cr-51, use of a setpoint based on the Cs-137 MPC is conservative based on the following parameters:

1) photon abundance (85K)

2) magnitude of applicable MPC (2E-5 uCi/cc)

Because Service Mater 5 RHR Servi.ce Mater are not normal release pathways for liquid effluents, no credit should be taken for possible dilution scenarios. A11 service water should be maintained below 2E-5 uCi/cc Cs-137 equivalent.

In order to minimize the chance of a change in the background of a monitor masking a significant trend in monitored activity, the alarm setpofnts for the Service Mater and RHR Service Mater monitors are determined as follows:

OF-C tte (15 of 124)

a. When monitor background~ (2E-5)/Cal. Factor:

KI RAD Setpoint 0.5 Background + (2E-5)/Cal. Factor DOWNSCALE or LOW RAD Setpoint 0.5 Background 4

b. When monitor background >(2E-5)/Cal. Factor:

HI RAD Setpoint Background + 0.5 (2E-5)/Cal. Factor DOWNSCALE or LOW RAD Setpoint Background - 0.5 (2E-5)/Cal. Factor Where:

Setpoint ~ Alarm threshold value to be entered into monitor~

.(cps for Service Mater, cpm for RHR Service Water).

Background Monitor background at most recent background determination (cps for Service Water, cpm for RHR Service Mater).

(2E-5) Cs-137 Maximum Permi ssibl e Concentration (uCi/ml ) .

Cal. Factor Monitor response factor per unit Cs-137 concentration determined during most recent (16 'of 124)

calibration (uCi/ml per cps for Service Mater, uCi/ml per cpm for RHR Service Mater).

The ALERT RAD setpoints for the RHR Service Mater monitors are maintained at 80X of the applicable HI RAD.petpoint (cpm).

2.2 0 N S S C C T 0 3 . THE RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION CHANNELS SHOMN IN TABLE 3.3.7.11-1 SHALL BE OPERABLE MITH THEIR ALARH/TRIP SETPOINTS SET TO ENSURE THAT THE LIMITS OF SPECIFICATION 3.11.2.1 ARE NOT EXCEEDED. THE ALARM/TRIP SETPOINTS OF THESE CHANNELS SHALL BE DETERMINED IN ACCORDANCE MITH.THE METHODOLOGY AND PARAMETERS IN THE ODCH.

Noble gas activity monitors, iodine samplers and monitors, and particulate samplers and monitors are present on the reactor building ventilation system (Units 1 and 2), the turbine building ventilation system (Units 1 and 2), and the standby gas treatment system exhaust vents. Effluent system flow rate and sampler flow rate are measured on all of the systems allowing the vent monitor microprocessor to calculate release rates based on measured flow rates. Precautions, limitations, and setpoints applicable to the operation of the SSES airborne effluent monitors are provided in the L*

applicable plant procedures. Setpoints are conservatively established for each effluent monitor so that the instantaneous dose rates corresponding to annual dose limits in 10 CFR 20.105 for unrestricted areas will not be exceeded.

The'eneral methodology for establishing plant ventilation airborne effluent monitor setpoints is based upon vent release rates derived from site-specific meteorological dispersion conditions, vent flow F

(17 of 124)

rates, and measured or expected radionuclfde mixtures in the gaseous effluents. The vent release 'rate can then be conve~ted to vent concentrations for input as setpoints for the applicable detectors.

It Since the vent monitors are prograamed to calculate concentrations of fodine-131 and particulate being released based on the rate of accumulation of activity on the filters, setpoints can be V.

established for the iodine and particulate channels.

The following method is used for calculating vent monitor hfgh radiation alarm setpoints:

l. An isotopic mixture is selected for the detector in question, if applicable. Noble gas and particulate detector setpo1nts are based on actual isotopic mixtures obtained from vent sample analysis or the FSARlFES expected release mixtures if actual samples do not contain sufficient detectable actfvfty to accurately estfmate the mixtures. The assumed isotopic mixtures are periodically reviewed to verffy that they remain representatfve of plant effluents.

2. The sel'ected noble gas or particulate mfxture fs used 1n the GASPAR program run to calculate the associated doses. The total source term (total curfes used for the calculation) does not matter as long as the proper nuclides are present 1n the relative proportions fndfcated fn sample analysis data or FSAR(FES tables.

For the iodine-131 setpofnt, any release total for. I-131 can be entered. The highest calculated annual average relatfve I

10 (18 of 124)

concentrations (X/Qs) at the site boundary are used for these GASPAR calculations.

3. The following ratio concept is used to calculate a release rate limit for the assumed mixture (or I-131).:

Calculated Dose mrem Dose Rate Limit mrem/ r ota GA ource erm m t ng e ease ate yr The limiting release rate of the assumed mixture (or I-131) can therefore be calculated:

Limiting Release (Ci/yr)

(Eq 5)

Total GASPAR Source Term Ci Dose Rate Limit mrem/ r a cu ate ose, mrem For the noble gas setpofnt, the calculated whole body and skin dose rates via the plume pathway are subject to the 10 CFR 20-derived limits of 500 and 3000 mrem/yr, respectively. The whole-body dose rate limit is usually most restrictive. For particulates and for iodine-131, the maximum calculated organ dose rate via the inhalation pathway is subject to the limft of 1500 mrem/yr.

4. The limiting release rates are converted to limiting vent concentrations using high limit vent flow rates.

(19 of 124)

Limiting Vent Concentration, uCi/cc Limitin Release Rate, Ci/ rj 1E6uCi/Ci (Eq 6)

(5.26E5 min/yr) (Vent Flow Rate, cc/min)

Sample calculations. of waterborne and airborne effluent monitor r<

setpoints are presented in Section A.1.2 of Appendix'A.

Vent flow rates and sample flow rates are monitored and recorded for each of the five SSES release points. The measured flow rates are used to calculate vent concentrations and release rates. Flow channel setpoints are set at approximately 10% and 90% of the calibrated sensor ranges to provide indication of possibly abnormal flow rates.

The main condenser offgas pre-treatment monitor provides indication of offgas activity prior to input to the holdup system. Alarm setpoints are based on two times and three times the steady state full power offgas activity readings.

SPECIFICATION 3.11.2.6 - THE CONCENTRATION OF HYOROGEN OR OXYGEN IN GAS TREATMENT SYSTEM SHALL BE LIMITED TO LESS THAN OR EQUAL TO 4% BY VOLUME.

Hydrogen recombiners are'sed at SSES to maintain the relative concentration of components of potentially explosive gas mixtures outside the explosive envelope. The main condenser offgas treatment system explosive gas monitoring system (offgas hydrogen analyzers) have setpoints to alarm at 1% and 2% hydrogen.

12 (20 of 124)

S - THE CONCENTRATION OF RADIOACTIVE MATERIAL RELEASED IN LIQUID EFFLUENTS TO UNRESTRICTED AREAS (SEE FIGURE 5.1.3-1)

SHALL BE LIMITED TO THE CONCENTRATIONS SPECIFIED IN 10 CFR PART 20, APPENDIX B, TABLE II, COLUMN 2 FOR RADIONUCLIDES OTHER THAN DISSOLVED OR ENTRAINED NOBLE GASES. FOR DISSOLVED OR ENTRAlNED NOBLE GASES, THE CONCENTRATION SHALL BE LIMITED TO THE CONCENTRATIONS SPECIFIED IN TABLE 3.11.1.1-1.

Liquid batch releases are controlled individually and each batch release is authorized based upon sample analysis and the existing dilution flow in the discharge line. The methods for sampling and analysis of each batch prior to release are given in the applicable plant procedures. A release rate limit is calculated for each batch based upon analysis, dilution flow and all procedural conditions being met before it is authorized for release.

Table 3.11.1-1 mentioned in Specification 3.11.1.1 contains the following "Maximum Permissible Concentrations of Dissolved or Entr'ained Noble Gases Released From the Site to Unrestricted Areas in Liquid Waste":

~uc ide C uCi Kr-85m 2E-4 Kr-85 SE-4 Kr-87 4E-5 Kr-88 9E-5 Ar-41 7E-5 Xe-131m 7E-4 Xe-133m 5E-4 Xe-133 6E-4 Xe-135m 2E-4 Xe-135 2E-4 These values were computed using Equation 20 of ICRP2 (1959), adjusted for infinite cloud submersion in water, with R equal to 0.01 rem/week, 13 (21 of 124)

the density of water equal to 1.0 gm/cm, and Pw/Pt equal to 1.0, where Pw/Pt is stopping power of water relative to tissue, and R is the dose rate limit for total body exposure. The HPC value for other liquid effluents is the actual HPC for identified mixtures, or lE-7 uCi/ml for unidentified mixtures.

The liquid radwaste effluent stream entering the discharge line is monitored and.,will automatically be terminated if the pre-selected monitor setpoint is exceeded as described in Section 2.1.

Additional monthly and quarterly analyses shall be performed in accordance with Table 4.11-1 of the SSES Technical Specifications.

DAT 14 (22 of 124)

4.0 R ORN 0 T S S . THE DOSE RATE DUE TO RADIOACTIVE FROM THE SITE (SEE FIGURE 5.1.3-1)

MATERIALS'ELEASED IN GASEOUS EFFLUENTS SHALL BE LIMITED TO THE FOLLOMING:

a. FOR NOBLE GASES: LESS THAN OR EQUAL TO 500. HREH/YR TO THE TOTAL BODY AND LESS THAN OR EQUAL TO 3000 NREH/YR TO THE SKIN, AND

b. FOR IODINE-131, FOR TRITIUM, AND FOR ALL RADIONUCLIDES IN PARTICULATE FORM MITH HALF-LIVES GREATER THAN 8 DAYS: LESS THAN OR EQUAL TO 1500 NREM/YR TO ANY ORGAN (INHALATION PATHWAY ONLY).

4.1 80DGR Noble gas activity monitor setpoints are established at release rates which permit some margin for corrective action to be taken before exceeding offsite dose rates corresponding to the 10 CFR 20 annual dose limits as described in Section 2.2. The methods for sampling and analysis of continuous ventilation releases are given in the applicable plant procedures. The dose rate in unrestricted areas due to radioactive materials released in airborne effluents may be determined by the following equat'ion for whole body dose:

( i)( /Q)v (Q iv) (Eq 7) and by the following equation for skin dose:

D g (Li + 1.1 Ni) (X/Q) (Q'iv (Eq 8) 15 (23 of 124)

where:

Ki the whole-body dose factor due to gamaa emissions for each ldenPf led noble gas radlonncllde (l) (mremiyr per uCi/m ) from Table 2.

v the rel ease r ate of radi onucl ide ( i ) from vent (v)

(uCi/sec).

(X/9)V ee the highest calculated annual average relative concentration for any area at or beyond the site boundary in an u]restricted area from vent release point (v) (sec/m ) such as from Table 3.

'wb the annual whole-body dose (mrem/yr).

Li the skin dose factor due to the beta emissions for each iden)ified noble gas radionuclide (i) (mrem/yr per uCi/m ) from Table 2.

the air dose factor due to gaaea emissions for each ident)fied noble gas radionuclide (i) (mrad/yr per uCi/m ) from Table 2 (conversion constant of 1.1 converts air dose-mrad to skin dose-mrem).

D s

the annual skin dose (mrem/yr).

Sample calculations for determining whole body and skin doses from noble gas radionuclides released from'he SSES are given in Section A.2.1 of Appendix A.

4.2 DIONUC ES 0 AN 08 E G S The methods for sampling and analysis of continuous ventilation releases for radioiodines and radioactive particulates are given in the applicable plant procedures. Additional monthly and quarterly analyses shall be performed in accordance with Table 4.11.2.1.2-1 of the SSES Technical Specifications. The dose rate in unrestricted areas due to inhalation of radioactive materials released in 16 (24,of 124)

airborne effluents may be determined by the following equation for any organ:

D E (Ri) (W) (Q ,v) (Eq g) where:

Ri the dose rate parameter based on inhalation pathway for radionuclides other than noble ga]es for the inhalation pathway (mrem/yr per uCi/m ) from Table 4.

the highest annual average dispersion parameter for estimating the dose to the3critical receptor; relative concentration (X/g) (sec/m ) for the inhalation pathway, such as from Table 3.

the release rate of radionuclide (i) from vent(v)

(uCi/sec),.

D c

the annual organ dose (mrem/yr).

Sample calculations for determining doses to critical organs from radionuclides other than noble gases released from the SSES are given in Section A.2.2 of Appendix A.

17 (25 of 124)

TABLE 2 DOSE FACTORS FOR NOBLE GASES' Whole Body Gamma Air Beta Air Dose Factor Skin Dose Factor Dose Factor Dose Factor K Li M on cl de C m* me r e d e Kr-83m 7.56E-02 1.93E+01 2.88E+02 Kr-85m 1.17E+03 1.46E+03 1.23E+03 1.97E~03 Kr-85 ~

1.61E+01 1.34E+03 1.72E+01 1.95E+03 Kr-87 5.920.03 9.73E+03 6.17E+03 1.03E+04 Kr-88 1.47E+04 2.37E+03 1.52E+04 2.93E+03 Kr-89 1.66E<04 1.01E+04 1.73Ew04 1.06E+04 Kr-90 1.56E+04 , 7.29E+03 1.63E+04 7.83003 Xe-131m 9.15E+Ol 4.76E+02 1.56E+02 1.11Ew03 Xe-133m 2.51E+02 9.94E+02 3.27E+02 1.48E+03 Xe-133 2.94B02 3.06E+02 3.53E+02 1.05E+03 co Xe-135m 3.12E+03 7.11E+02 3.36E+03 7.39E+02 Xe-135 1.81E+03 1.86E+03 1.92E+03 2.46E+03 Xe-137 1.42E+03 1.22E+04 1.51E+03 1.27E+04 Xe-138 8.83E+03 4.13E+03 9.21E+03 4.75E+03 Ar-41 8.84Et03 2.69E+03 9.30E+03 3.28E+03 The listed dose factors are for radionuclides that may be detected in airborne effluents and derived from Table B-1 in Reg. Guide 1. 109.

7.56E-02 7.56 x 10

TABLE 3 SAMPLE ANNUAL AVERAGE RELATIVE CONCENTRATIONS AND DEPOSITION RATES Site Relative Concentrations Relative Deposition Downwind Boundar (X/Q) 3 Rates 2

Sector Miles sec/m DQ m NNE .82 8.5E-6 2.2E-&

NE 1.1 2.6E-6 7.3E-9 ENE .86 4. 1E-6 1.4E-S E .80 3.6E-6 1.'7E-8 ESE .50 5.7E-6 2.9E-8 SE .34 6.7E-6 '3.7E-8 SSE .34 5.5E-6 3.5E-8 S .34 1.0E-5 3.4E-8 SSM .39 &.9E-6 2.5E<<8 SW .77 1. 7E>>5 3.4E-8 MSW 1.2 l. &E-5 2.3E-8 M 1.0 2.6E<<5 2.9E-S MNM .64 1.0E-5 1.2E-8 NW .64 7.0E-6 1.0E-8 NNM .61 7.5E-6 1.7E-8 N .61 7.9E-6 2.1E-S I

From 1980 Meteorology Sutimry for SSES Data Period: Ol/Ol/80 - 12/31/80 Site Boundary distances are approximate, and current as of 11/88.

19 (27 of 124)

TABLE 4 DOSE FACTORS FOR INHALATION, INGESTION AND GROUND EXPOSURE PATHMAYS: RADIONUCLIDES OTHER THAN NOBLE GASES(1)

(1)Reference letter R. K. Sarclay to File R9-5: Technical Documentation of Lotus 1-2-3 ODCHTAB and TGTMSTR files: Gaseous Dose Factor Calculation using NUREG-0133/Reg. Guide 1.109 Methodology, PLI 69605, 11/8/91.

20 (28 of 124)

A t'AT

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: H-3 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOEi00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00940 0.00E+00 0.00E+00 0.00E+00 CHILD 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT O.OOE+00 1.38E+03 1.38E+03 1.38E+03 1.38E+03 1.38E+03 1.38E+03 N/A MILK TEEN O.OOE+00 1.80E+03 1.80E+03 1.80E+03 1.80E+03 1.80E+03 1.80E+03 . N/A CHILD O.OOE+00 2.84E+03 2.84E+03 2.84E+03 2.84E+03 2.84E+03 2.84E+03 N/A INFANT O.OOE+00 4.31E+03 4.31E+03 4.31E+03 4.31E+03 4.31E+03 4.31E+03 N/A COW ADULT O.OOE+00 6.77E+02 6.77E+02 6.77E+02 6.77E+02 6.77E+02 6.77E+02 N/A MILK TEEN , O.OOE+00 8.82E+02 8.82E+02 8.82E+02 8.82E+02 8.82E+02 8.82E+02 N/A CHILD 0.00E+00 1.39E+03 1.39E+03 1.39E+03 1.39E+03 1.39E+03 1.39E+03 N/A INFANT O.OOE+00 2.11E+03 2. 11E+03 2.11E+03 2.11E+03 2.11E+03 2.11E+03 N/A MEAT ADULT O.OOE+00 2.89E+02 2.89E+02 2.89E+02 2.89E+02 2.89E+02 2.89E+02 N/A TEEN O.OOE+00 1.72E+02 1.72E+02 1.72E+02 1.72E+02 1.72E+02 1.72E+02 N/A CHILD O.OOE+00 2.08E+02 2.08E+02 2.08E+02 2.08E+02 2.08E+02 2.08E+02 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 2.11E+10 2.11E+10 2.11E+10 2.11E+10 2.11E+10 2.11E+10 2.11E+10 N/A TEEN 1.39E+10 1.39E+10 1.39E+10 1.39E+10 1.39E+10 1.39E+10 1.39E+10 N/A CHILD 8.58E+09 8.58E+09 8.58E+09 8.58E+09 8.58E+09 8.58E+09 8.58E+09 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.11E+10 2.11E+10 2.11E+10 2.11E+10 2.11E+10 2.11E+10 2.11E+10 N/A INGEST. TEEN '.39E+10 1.39E+10 1.39E+10 1.39E+10,1.39E+10 1.39E+10 1.39EtlO N/A CHILD 8.58E+09 8.58E+09 8.58E+09 8.58E+09 8.58E+09 8.58E+09 8.58E+09 N/A INFANT 0.00E+00 6.43E+03 6.43E+03 6.43E+03 6.43E+03 6.43Et03 6.43E+03 N/A INHAL. ADULT 0:OOE+00 1.26E+03 1.26E+03 1.26E+03 1.26E+03 1.26E+03 1.26E+03 N/A TEEN O.OOE+00 1.27E+03 1.27E+03 1.27E+03 1.27E+03 1.27E+03 1.27E+03 N/A CHILD O.OOE+00 1.12E+03 1.12E+03 1.12E+03 1.12E+03 1.12E+03 1.12E+03 N/A INFANT O.OOE+00 6.47E+02 6.47E+02 6.47E+02 6.47E+02 6.47E+02 6.47E+02 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• ""MAXIMUMVALUES FOR PATHWAYS***

~

GROUND'ROUND: GOAT COW TOTAL T: B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 4.31E+03.2.11E+03 2.89E+02 2.11E+10 2.11E+10 1.27E003 PAGE: 4-1 ae v (29 of 124)

DAY

O.D.C.N. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: C-14 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND'DULT Q.QQE+00 O.QQE+00 O.QOE+00 Q.OQE+00 O.OOE+00 O.QQE+00 O.QQE+00 O.OOE+00 TEEN 0'.OQE+00 O.OOE+00 O.OOE+00 O.OQE+00 0':-iOE+00 O.OQE+00 O.'.OQE+00 0'.QQE+00 CHILD O.OOE+00 O.OOE+00 O.OQE+00 O.OOE+00 O.OQE+00 O.QOE+00 Q.QQE+00 O.OOE+00 INFANT O.OOE+00 O.OQE+00 O.QOE+00 O.OOE+00 O.OOE+00 O.OQE+00 O.OQE+00 O.OOE+00 GOAT ADULT 1.69E+08 3.39E+07 3.39E+Q7 3.39E+07 3.39E+07 3.39E+07 3.39E+07. N/A MILK TEEN 3. 12E+08 6.24E+07 6.24E+07 6.24E+Q7 6.24E+07 6.24E+07 6.24E+07 N/A CHILD 7.68E+08 1.54E+08 1.54E+08 1.54E+08 1.54E+08 1.54E+08 1,54E+08 N/A INFANT 1.50E+09 3.21E+08 3.21E+08 3.21E+Q8 3.21E+08 3.21E+08 3. 21E+08 N/A COW ADULT 1.35E+08 2.71E+07 2.71E+07 2.71E+07 2.71E+OT 2.71E+OT 2.71E+07 N/A MILK TEEN 2.50E+08 4.99E+07 4.99E+07 4.99E+07. 4.99E+07 4.99E+07 4.99E+07 N/A CHILD 6. 14E+08 1.23E+08 1.23E+08 1.23E+08 1.23E+08 1.23E+Q8 1;23E+08 N/A INFANT 1.20E+09 2.57E+08 2.57E+08 2.57E+08 2.57E+08 2.57E+08 2.57E+08 N/A MEAT ADULT 1.36E+08 2.72E+07 2.72E+07 2.72E+07 2.72E+07 2.72E+07 2.72E+07 N/A TEEN 1. 15E+08 2.30E+07 2.30E+07 2.30E+07 2.30E+07 2.30E+07 2.30E+07 N/A CHILD 2.16E+08 4.33E+07 4.33E+07 4.33E+07 4.33E+07 4.33E+07 4.33E+07 N/A INFANT O.OOE+00 O.OQE+00 Q.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 2.06E+08 4.13E+07 4.13E+07 4.13E+07 4.13E+07 4.13E+07 4.13E+07 N/A TEEN 3.49E+08 6.98E+07 6.98E+07 6.98E+07 6.98E+07 6.98E+07 6.98E+07 N/A CHILD 8.53E+08 1.71E+08 1.71E+08 1.71E+08 1.71E+08 1.71E+08 1.71E+08 N/A INFANT O.QOE+00 O.OOE+00 O.OOE+00 O.OQE+00 O.OOE+00 O.QOE+00 O.QOE+00 N/A TOTAL ADULT 6.47E+08 1.29E+08 1.29E+08 1.29E+08 1.29E+08 1.29E+08 1.29E+08 N/A INGEST. TEEN 1.03E+09 2.05E+08 2.05E+08 2.05E+08 2.05E+08 2.05E+08 2.05E+08 N/A CHILD 2.45E+09 4.90E+08 4.90E+08 4.90E+08 4.90E+08 4.90E+08 4.90E+08 N/A INFANT 2.71E+09 5.78E+08 5.78E+08 5.78E+08 5.78E+08 5.78E+Q8 5.78E+08 N/A INHAL, ADULT 1.82E+04 3.41E+03 3.41E+03 3.41E+03 3.41E+03 3.41E+03 3.41E+03 N/A TEEN 2.60E+04 4.87E+03 4.87E+03 4.87E+03 4.87E+03 4.87E+03 4.87E+Q3 N/A CHILD 3.59E+04 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 N/A INFANT 2.65E+04 5.31E+03 5.31E+03 5.31E+03 5.31E+03 5.31E+03 5.31E+03 N/A BONE LI ER T.BQOY THYROID KIDNEY LUNG G. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS*""

GROUND: GROUND: GOAT COW TOTAL T.B../QRG. SKIN MILK: MILK: NEAT: VEGTBLE: INGEST'NHAL.

O.QQE+00 O.QOE+OQ 1.50E+09 1.20E+09 2.16E+08 8.53E+08 2.71E+09 3.59E+04 PAGE: 4-2 (30 of 124)

OAT

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: P-32 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 0;OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 0.09&40 O.OOE+00 O.OOE+00 O.OOE+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 9.28E+09 5.77E+08 3.59E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.04E+09 N/A MILK TEEN 1.71E+10 1.06E+09 6.64E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.44E+09 . N/A CHILD 4.22E+10 1.98E+09 1.63E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.17E+09 N/A INfANT 7.25E+10 5.12E+09 3.37E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.18E+09 N/A COW ADULT 4.36E+09 2.71E+08 1.69E+08 O.OOE+00 O.OOE+00 O.OOE+00 4.91E+08 N/A MILK TEEN 8.0SE+09 4.99E+08 3.12E+08 O.OOE+00 O.OOE+00 O.OOE+00 6.77E+08 N/A CHILD 1.99E+10 9.29E+08 7.65E+08 O.OOE+00 O.OOE+00 O.OOE+00 5.49E+08 N/A INFANT 4.09E+10 2.41E+09 1.59E+09 O.OOE+00 O.OOE+00 O.OOE+00 5.54E+08 N/A MEAT ADULT 1.55E+09 9.63E+07 5.99E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.74B08 N/A TEEN 1.31E+09 8. 11E+07 5.07E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.10E+08 N/A CHILD 2.47E+09 1. 15E+08 9.51E+07 O.OOE+00 O.OOE+00 O.OOE+00 6.82E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 7.09E+08 4.41E+07 2.74E+07 O.OOE+00'O.OOE+00 O.OOE+00 7.98E+07 N/A TEEN 9.57E+08 5.93E+07 3.71E+07 O.OOE+00 O.OOE+00 O.OOE+00 8.05E+07 N/A CHILD 2.16E+09 1.01E+08 8.34E+07 O.OOE+00 O.OOE+00 O.OOE+00 5.98E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.59E+10 9.89E+08 6.15E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.79E+09 N/A INGEST. TEEN 2.74E+10 1.70E+09 1.06E+09 O.OOE+00 O.OOE+00 O.OOE+00 2.31E+09 N/A CHILD 6.67E+10 3.12E+09 2.57E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.84E+09 N/A INFANT 1. 13E+ll 7.53E+09 4.96E+09 0.00E+00 0.00E+00 0.00E+00 1.73E+09 N/A INHAL. ADULT 1.32E+06 7.71E+04 5.01E+04 O.OOE+00 O.OOE+00 O.OOE+00 8.64E+04 N/A TEEN 1.89E+06 1. 10E+05 7. 16E+04 O.OOE+00 O.OOE+00 O.OOE+00 9.28E+04 N/A CHILD 2.60E+06 1. 14E+05 9.88E+04 O.OOE+00 O.OOE+00 O.OOE+00 4.22E+04 N/A INFANT 2.03E+06 1. 12E+05 7.74E+04 O.OOE+00 O.OOE+00 O.OOE+00 1.61E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN "Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

"*"MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 7.25E+10 4.09E+10 2.47E+09 2.16E+09 1.13Ef1 I 2.60E+06 PAGE: 4-3 (31 of 124)

DAT

O.D.C.H. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Cr-51 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND .

ADULT 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+05 4.61E+06 4.6IE+06 5.45E+06 TEEN 4. 61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 5.45E+06 CHILD 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 5.45E+06 INFANT 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 5.45E+06 GOAT ADULT 0.00E+00 O.OOE+00 1.61E+03 9.64E+02 3.55E+02 2.14E+03 4.06E+05 N/A MILK TEEN 0.00E+00 O.OOE+00 2.82E+03 1.56E+03 6.17E+02 4.02E+03 4.73E+05 N/A CHILD 0.00E+00 O.OOE+00 5.74E+03 3.19E+03 8.71E+02 5.82E+03 3.05E+05 N/A INFANT 0.00E+00 0.00E+00 9. 10E+03 5.94E+03 1.30E+03 1. 16E+04 2.65E+05 N/A COW ADULT O.OOE+00 O.OOE+00 7.99E+03 4.77E+03 1.76E+03 1.06E+04 2.01E+06 N/A MILK TEEN O.OOE+00 O.OOE+00 1.39E+04 7.75Et03 3.06E+03 1.99E+04 2.34E+06 N/A CHILD O.OOE+00 O.OOE+00 2.84E+04 1.58E+04 4.32E+03 2.88E+04 1.51E+06 N/A INFANT O.OOE+00 O.OOE+00 4.51E+04'.94E+04 6.43E+03 5.72E+04 1.31E+06 N/A MEAT ADULT O.OOE+00 O.OOE+00 2.50E+03 1.49E+03 5.50E+02 3.31E+03 6.28E+05 N/A TEEN 0.00E+00 0.00E+00 2.00E+03 1.11E+03 4.38E+02 2.85E+03 3.36E+05 N/A CHILD O.OOE+00 O.OOE+00 3.11E+03 1.73E+03 4.72E+02 3.16E+03 1.65E+05 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT O.OOE+00 O.OOE+00 3.35E+04 2.01E+04 7.39E+03 4.45E+04 8.44Et06 N/A TEEN 0.00f+00 O.OOE+00 5.02E+04 2.79E+04 1.10E+04 7. 17E+04 8.44E+06 N/A CHILD O.OOE+00 O.OOE+00 9.96E+04 5.53E+04 1.51E+04 1.01E+05 5.28E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 O.OOE+00 4.56E+04 2.73E+04 1.01Ee04 6.06E+04 1.15E+07 N/A INGEST. TEEN O.OOE+00 O.OOE+00 6.90E+04 3.83E+04 1.51E+04 9.85E+04 1.16E+07 N/A CHILD O.OOE+00 O.OOE+00 1.37E+05 7.60E+04 2.08E+04 1.39E+05 7.26E+06 N/A INFANT O.OOE+00 O.OOE+00 5.42E+04 3.53E+04 7.72E+03 6.88E+04 1.58E+06 N/A INHAL. ADULT O.OOE+00 O.OOE+00 1.00E+02 5.95E+01 2.28E+Ol 1.44E+04 3.32E+03 N/A TEEN O.OOE+00 O.OOE+00 1.35E+02 7.50E+Ol 3.07E+Ol 2.10E+04 3.00E+03 N/A CHILD O.OOE+00 O.OOE+00 1.54E+02 8.55E+01 2.43E+Ol 1.70E+04 1.08E+03 N/A INFANT O.OOE+00 O.OOE+00 8.95E+01 5.75E+01 1.32E+Ol 1.28E+04 3.57E+02 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

4.61E+06 5.45E+06 4.73E+05 2.34E+06 6.28E+05 8.44E+06 1.16E+07 2.10E+04 PAGE: 4-4 OAV (32 of. 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Mn-54 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN GROUND ADULT 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.61E+09

~ TEEN '.37E+09 1.37E+09 1;37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.61E+09 CHILD 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.61E+09 INFANT 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.37E+09 1.61E+09 GOAT ADULT O.OOE+00 6.14E+05 1.17E+05 O.OOE+00 1.83E+05 O.OOE+00 1.88E+06 N/A MILK TEEN O.OOE+00 1.02E+06 2.03E+05 O.OOE+00 3.05E+05 O.OOE+00 2.10E+06 N/A CHILD O.OOE+00 1.53E+06 4.07E+05 O.OOE+00 4.29E+05 O.OOE+00 1.28E+06 .

N/A INFANT O.OOE+00 2.84E+06 6.45E+05 O.OOE+00 6.30E+05 O.OOE+00 1.04E+06 N/A COW ADULT O.OOE+00 3.92E+06 7.49E+05 O.OOE+00 1. 17E+06 O.OOE+00 1.20E+07 N/A MILK TEEN 0.00E+00 6.54E+06 1.30E+06 0.00E+00 1.95E+06 0.00E+00 1.34E+07 N/A CHILD O.OOE+00 9.78E+06 2.61E+06 O.OOE+00 2.74E+06 O.OOE+00 8.21E+06 N/A INFANT O.OOE+00 1.82E+07 4. 12E+06 O.OOE+00 4.03E+06 O.OOE+00 6.68E+06 N/A MEAT ADULT O.OOE+00 4.79E+06 9. 14E+05 O.OOE+00 1.43E+06 O.OOE+00 1.47E+07 N/A TEEN O.OOE+00 3.65E+06 7.25E+05 O.OOE+00 1.09E+06 O.OOE+00 7.49E+06 N/A CHILD O.OOE+00 4.18E+06 1. 11E+06 O.OOE+00 1. 17E+06 O.OOE+00 3.51E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT O.OOE+00 2.80E+08 5.35E+07 O.OOE+00 8.34E+07 O.OOE+00 8.58E+08 N/A TEEN O.OOE+00 4.27E+08 8.46E+07 O.OOE+00 1.27E+08 O.OOE+00 8.75E+08 N/A CHILD O.OOE+00 6.34E+08 1.69E+08 O.OOE+00 1.78E+08 O.OOE+00 5.32E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 2.90E+08 5.53E+07 O.OOE+00 8.62E+07 O.OOE+00 8.87E+08 N/A INGEST. TEEN O.OOE+00 4.38E+08 8.69E+07 O.OOE+00 1.31E+08 O.OOE+00 8.98E+08 N/A CHILD O.OOE+00 6.49E+08 1.73E+08 O.OOE+00 1.82E+08 O.OOE+00 5.45E+08 N/A INFANT O.OOE+00 2.10E+07 4.77E+06 O.OOE+00 4.66E+06 O.OOE+00 7.73E+06 N/A INHAL. ADULT 0.00E+00 3.96E+04 6.30E+03 0.00E+00 9.84E+03 1.40E+06 7.74E+04 N/A TEEN O.OOE+00 5. 11E+04 8.40E+03 O.OOE+00 1.27E+04 1.98E+06 6.68E+04 N/A CHILD O.OOE+00 4.29Ei04 9.51E+03 O.OOE+00 1.'OOE+04 1.58E+06 2.29E+04 N/A INFANT O.OOE+00 2.53E+04 4.98E+03 O.OOE+00 4.98E+03 1.00E+06 7.06E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND'ROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

1.37E+09 1.61E+09 2.84E+06 1.82E+07 1.47E+07 8.75E+08 8.98E+08 1.98E+06 PAGE: 4-5 DAT (33 of 124)

O.D.C.N. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Fe-55 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.OCEANO 0.00E+00 0.00E+00 0.00E+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 2.06E+05 1.42E+05 3.32E+04 O.OOE+00 O.OOE+00 7.94E+04 8.16E+04 N/A MILK TEEN 3.65E+05 2.59E+05 6.04E+04 O.OOE+00 O.OOE+00 1.64E+05 1.12E+05 N/A CHILD 9. 17E+05 4.86E+05 1.51E+05 O.OOE+00 O.OOE+00 2.75E+05 9.01E+04 N/A INFANT 8.52E+07 7.16E+05 1.91E+05 O.OOE+00 O.OOE+00 3.50E+05 9.09E+04 N/A COW ADULT 1.25E+07 8.64E+06 2.01E+06 0.00E+00 0.00E+00 4.82E+06 4.95E+06 N/A NILK TEEN 2.22E+07 1.57E+07 3.67E+06 O.OOE+00 O.OOE+00 9.97E+06 6.80E+06 N/A CHILD 5.56E+07 2.95Et07 9. 14E+06 O.OOE+00 O.OOE+00 1.67E+07 5.47E+06 N/A INFANT 6.73E+07 4.34E+07 1.16E+07 O.OOE+00 O.OOE+00 2.12E+07 5.52E+06 N/A HEAT ADULT 1.61E+08 1.11E+08 2.60E+07 O.OOE+00 O.OOE+00 6.22E+07 6.39E+07 N/A TEEN 1.31E+08 9.29E+07 2.17E+07 O.OOE+00 O.OOE+00 5.89E+07 4.02E+07 N/A CHILD 2.51E+08 1.33E+08 4.13E+07 O.OOE+00 O.OOE+00 7.54E+07 2.47E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 1.89E+08 1.31E+08 3.05E+07 O.OOE+00 O.OOE+00 7.30E+07 7.50E+07 N/A TEEN 3.08E+08 2.18E+08 5.09E+07 0.00E+00 0.00E+00 1.38E+08 9.44E+07 N/A CHILD 7.67E+08 4.07E+08 1.26E+08 O.OOE+00 O.OOE+00 2.30E+08 7.53E+07 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ~

ADULT 3.63E+08 2.51E+08 5.85E+07 O.OOEt00 O.OOE+00 1.40E+08 1.44E+08 N/A INGEST. TEEN 4.61E+08 3.27E+08 7.62E+07 O.OOE+00 O.OOE+00 2.07E+08 1.41E+08 N/A CHILD 1.07E+09 5.70E+08 1.77E+08 O.OOE+00 O.OOE+00 3.22E+08 1.06E+08 N/A INFANT 1.52E+08 4.42E+07 1. 18E+07 O.OOE+00 O.OOE+00 2.16E+07 5.61E+06 N/A INHAL. ADULT 2.46E+04 1.70E+04 3.94E+03 O.OOE+00 O.OOE+00 7.21E+04 6.03E+03 N/A TEEN 3.34E+04 2.38E+04 5.54E+03 O.OOE+00 O.OOE+00 1.24E+05 6.39E+03 N/A CHILD 4.74E+04 2.52E+04 7.77E+03 O.OOE+00 O.OOE+00 1.11E+05 2.87E+03 N/A INFANT 1.97E+04 1. 17E+04 3.33E+03 O.OOE+00 O.OOE+00 8.69E+04 1.09E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

"*"MAXIMUMVALUES FOR PATHWAYS**"

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN . MILK: MILK: HEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 8.52E+07, 6.73E+07 2.51E+08 7.67E+08 1.07E+09 1.24E+05 PAGE: 4-6 V (34 of 124)

DATE

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIQNUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Mn-56 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN II GROUND ADULT O.OOE+00 O.QOE+00 O.OOE+00 O.OOE+00, O.OOE+00 O.OOE+00 O.OQE+00 O.OOE+00 TEEN 0.00Et00 0.00E+00 0.00E+00 0.00E+00 O.5%+00 0.00E+00 O.OQE+00 O.OQE+00 CHILD 0.'OQE+00 O.OOE+00'O.OQE+00 O.OQE+00 0'.OOE+00 0'.OOE+00 0'.QQE+OQ 0'.OOE+00 INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OQE+00 0.00E+OQ O.OOE+00 O.QOE+00 GOAT ADULT O.OOE+00 7.17E-04 1.27E-04 O.OOE+00 9.11E-04 O.OOE+00 2.29E-02 N/A MILK TEEN O.OOE+00 1.27E-03 2.26E-04 O.OOE+00 1.61E-03 O.OOE+00 8.37E N/A CHILD O.OOE+00 2.22E-03 5.01E-04 O.OOE+00 2.68E-03 O.OOE+00 3.21E-01 N/A INFANT O.OOE+00 5.43E-03 9.36E-04 O.OOE+00 4.67E-03 O.OOE+00 4.93E-01 N/A COW ADULT O.OOE+00 1.05E-03 1.86E-04 O.OOE+00 1.33E-03 O.OOE+00 3.34E-02 N/A MILK TEEN O.OOE+00 1.85E-03 3.30E-04 O.QOE+00 2.35E-03 O.OOE+00 1;22E-01 N/A CHILD O.OOE+00 3.23E-03 7.30E-04 O.OOE+00 3.91E-03 O.OOE+00 4.69E-01 N/A INFANT O.QOE+00 7.92E-Q3 1.37E-03 O.OQE+00 6.81E-03 O.OOE+00 7.19E-01 N/A MEAT ADULT O.OOE+00 5.00E-54 8.86E-55 O.OOE+00 6.34E-54 O.OOE+QO 1.59E-52 N/A TEEN O.OOE+00 4.06E-54 7.21E-55 O.OOE+00 5.14E-54 O.OOE+00 2.67E-52 N/A CHILD O.OOE+00 5.41E-54 1.22E-54 O.OOE+00 6.54E-54 O.OOE+00 7.84E-52 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT O.OOE+00 5.25E+00 9.31E-Ol O.OOE+00 6.66E+00 O.OOE+00 1.67Ew02 N/A TEEN O.OOE+00 4.73E+00 8.42E-Ol O.OOE+00 5.99E+00 O.OOE+00 3.11E+02 N/A CHILD O.OOE+00 6.19E+00 1.40E+00 O.QOE+00 7.49E+00 O.OOE+00 8.97E+02 N/A INFANT O.QOE+00 0'.OQE+00 O'.QQE+00 Q.QQE+00 O.QOE+00 O.DOE+00 O.OOE+00 N/A

" TOTAL ADULT 0.00E+00 5.25E+00 9.31E-Ql O.OOE+QO 6.66E+00 O.OOE+00 1.68E+02 N/A INGEST. TEEN O.OOE+00 4.73E+00 8.42E-Ol 0.00E+00 5.99E+00 0.00E+00 3.12E+Q2 N/A CHILD O.OOE+00 6.20E+00 1.40E+00 O.OOE+00 7.50Ei00 O.OOE+00 8.98E+02 N/A INFANT Q.OOE+00 1.34E-02 2.30E-03 O.OOE+00 1.15E-02 O.OOE+00 1.21E+00 N/A INHAL. ADULT O.OOE+00 1.24E+00 1.83E-Ol O.OOE+00 1.30000 9.44E+03 2.02E+04 N/A TEEN O.OOE+00 1.70E+00 2.52E-01 O,OOE+00 1.79E+00 1.52E+04 5.74E+04 N/A CHILD O.OQE+00 1.66E+00 3.12E-Ol O.OOE+00 1.67E+00 1.31E+04 1.23E+05 N/A INFANT O.OOE+00 1.54E+00 2.21E-Ol O.QOE+00 1.10E+00 1.25E+04 7.17E+04 N/A BONE LIVER T.BODY THYROID KIDNEY L NG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS"*"

GROUND: GROUND: GOAT COW TOTAL T ..B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OQE+00 O.QOE+00 4.93E-Ol 7.19E-Ol 7.84E-52 8.97E+02 8.98E+02 1.23E+05 PAGE: 4-7 (35 of 124)

OA<

O.D.C.H. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Co-58 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 3.75Et08 3.75E+08 3.75E+08 3.75E+08 3.75Et08 3.75E+08 3.75E+0& 4.39E+08 TEEN 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.I5008 3.75E+08 3.75E+08 4.39E+08 CHILD 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75Et08 4.39E+08 INFANT 3.75Et08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 4.39E+08 GOAT ADULT O.OOE+00 3.00E+05 6.72E+05 O.OOE+00 O.OOE+00 O.OOE+00 6.07E+06 . N/A MILK TEEN O.OOE+00 5.05E+05 1. 16E+06 O.OOE+00 O.OOE+00 O.OOE+00 6.96E+06 N/A CHILD O.OOE+00 7.71E+05 2.36E+06 O.OOE+00 O.OOE+00 O.OOE+00 4.50E+06 N/A INFANT O.OOE+00 1.54E+06 3.85E+06 O.OOE+00 O.OOE+00 O.OOE+00 3.84E+06 N/A COW ADULT O.OOE+00 1.70E+06 3.81E+06 O.OOE+00 O.OOE+00 O.OOE+00 3.44E+07 N/A MILK TEEN O.OOE+00 2.86E+06 6.59E+06 O.OOE+00 O.OOE+00 O.OOE+00 3.94E+07 N/A CHILD O.OOE+00 4.37E+06 1.34E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.55E+07 N/A INFANT O.OOE+00 8.74E+06 2.18E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.18E+07 N/A HEAT ADULT O.OOE+00 7.78E+06 1.74E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.58E+08 N/A TEEN O.OOE+00 6.00E+06 1.38E+07 O.OOE+00 O.OOE+00 O.OOE+00 8.27E+07 N/A CHILD O.OOE+00 7.01E+06 2.14E+07 O.OOE+00 O.OOE+00 O.OOEt00 4.09E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT O.OOE+00 2.61E+07 5.86E+07 O.OOE+00 O.OOE+00 O.OOE+00 5.29E+08 N/A

'EEN O.OOE+00 3.96E+07 9. 14E+07 O.OOE+00 O.OOE+00 O.OOE+00 5.47E+08 N/A CHILD O.OOE+00 5.99E+07 1.83E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.49E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 3.59E+07 8.05E+07 O.OOE+00 O.OOE+00 O.OOE+00 7.28E+08 N/A INGEST. TEEN O.OOE+00 4.90E+07 1. 13E+08 O.OOE+00 O.OOE+00 O.OOE+00 6.76E+08 N/A CHILD O.OOE+00 7.20E+07 2.20E+08 O.OOE+00 O.OOE+00 O.OOE+00 4.20E+08 N/A INFANT O.OOE+00 1.03E+07 2.56E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.56E+07 N/A INHAL. ADULT O.OOE+00 1.58E+03 2.07E+03 O.OOE+00 O.OOE+00 9.28E+05 1. 06E+05 N/A TEEN O.OOE+00 2.07E+03 2.78E+03 O.OOE+00 O.OOE+00 1.34E+06 9.52E+04 N/A CHILD O.OOE+00 1.77E+03 3.16E+03 O.OOE+00 O.OOE+00 1.11E+06 3.44E+04 N/A INFANT O.OOE+00 1.22Et03 1.82E+03 O.OOE+00 O.OOE+00 7.77E+05 1.11E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS**"

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: HEAT: VEGTBLE: INGEST: INHAL.

3..75E+08 4.39E+08 6.96E+06 3.94E+07 1.58E+08 5.47E+08 7.28E+08 1.34E+06 PAGE: 4-8 (36 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Fe-59 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 3.17E+08 TEEN 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 3.17E+08 CHILD 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 3.17E+08 INFANT 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 2.70E+08 3.17E+08 GOAT MILK ADULT TEEN CHILD 1.92E+05 3.35E+05 7.78E+05 4.52E+05 7.83E+05 1.26E+06 1.73E+05 3.02E+05 6.27E+05 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 1.26E+05 2.47E+05 3.65E+05 1.51E+06 1.85E+06 1.31E+06

'/A N/A N/A INFANT 1. 12E+08 2.54E+06 9.99E+05 O.OOE+00 O.OOE+00 7.49E+05 1.21E+06 N/A COW ADULT 9.41E+06 2.21E+07 8.47E+06 O.OOE+00 O.OOE+00 6. 18E+06 7.37E+07 N/A MILK TEEN 1.64E+07 3.83E+07 1.48E+07 O.OOE+00 O.OOE+00 1.21E+07 9.06E+07 N/A CHILD 3.81E+07 6.16E+07 3.07E+07 O.OOE+00 O.OOE+00 1.79E+07 6.41E+07 N/A INFANT 7.11E+07 1.24E+08 4.89E+07 O.OOE+00 O.OOE+00 3.67E+07 5.93E+07 N/A 1

ll MEAT ADULT 1.03E+08 2.42E+08 9.27E+07 O.OOE+00 O.OOE+00 6.76E+07 8.06E+08 N/A TEEN 8.23E+07 1.92E+08 7.41E+07 O.OOE+00 O.OOE+00 6.05E+07 4.54E+08 N/A CHILD 1.460 08 2.36E+08 1.18E+08 O.OOE+00 O.OOE+00 6.84E+07 2.46E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT - 1.02E+08 2.39E+08 9.17E+07 O.OOE+00 O.OOE+00 6.68E+07 7.97E+08 N/A TEEN 1.58E+08 3.68E+08 1.42E+08 O.OOE+00 O.OOE+00 1.16E+08 8.71E+08 N/A CHILD 3.60E+08 5.82E+08 2.90E+08 O.OOE+00 O.OOE+00 1.69E+08 6.06E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.14E+08 5.04E+08 1.93E+08 O.OOE+00 O.OOE+00 1.41E+08 1.68E+09 N/A INGEST. TEEN 2.57E+08 5.99E+08 2.31E+08 O.OOE+00 O.OOE+00 1.89E+08 1.42E+09 N/A CHILD 5.45E+08 8.81E+08 4.39E+08 O.OOE+00 O.OOE+00 2.55E+08 9.18E+08 N/A INFANT 1.83E+08 1.27E+08 4.99E+07 O.OOE+00 O.OOE+00 3.74E+07 6.05E+07 N/A t

INHAL. ADULT 1. 18E+04 2.78E+04 1.06E+04 O.OOE+00 O.OOE+00 1.02E+06 1.88E+05 N/A TEEN 1.59E+04 3.70E+04 1.43E+04 O.OOE+00 O.OOE+00 1.53E+06 1.78E+05 N/A CHILD 2.07E+04 3.34E+04 1.67E+04 O.OOE+00 O.OOE+00 1.27E+06 7.07E+04 N/A INFANT 1.36E+04 2.35E+04 9.48E+03 O.OOE+00 O.OOE+00 1.01E+06 2.48E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN "Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are .mrem-m2/yr/uCi/sec

"**MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG.'KIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

2.70E+08 '3.17E+08 1.12E+08 1.24E+08 8.06E+08 8.71E+08 1.68E+09 1.53E+06 PAGE: 4-9 (37 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Co-60 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13f+10 2.13E+10 2.13E+10 2.51E+10 TEEN 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.51E+10 CHILD 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2. 51E+10 INFANT 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.13E+10 2.51E+10 GOAT ADULT O.OOE+00 1.25E+06 2.76E+06 O.OOE+00 O.OOE+00 O.OOE+00 2.35E+07 N/A MILK TEEN O.OOE+00 2.12E+06 4.78E+06 O.OOE+00 O.OOE+00 O.OOE+00 2.77E+07 N/A CHILD O.OOE+00 3.30E+06 9.72E+06 O.OOE+00 O.OOE+00 O.OOE+00 1.83E+07 N/A INFANT O.OOE+00 6.73E+06 1.59E+07 O.OOE+00 O.OOE+00 O.OOEt00 1.60E+07 N/A COW ADULT O.OOE+00 8.29E+06 1.83E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.56E+Q8 N/A'/A MILK TEEN O.OOE+00 1.41E+07 3. 17E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.83ft08 CHIL'D O.OOE+00 2. 18E+07 6.44E+07 O.OOE+00 O.OQE+QO O.OOE+00 1.21E+08 N/A INFANT O.OOE+00 4.46E+07 1.05E+08 O.OOE+00 O.OQE+00 O.OOE+00 1.06E+08 N/A MEAT ADULT 0.00E+00 4. 19E+07 9.23E+07 Q.OQE+00 O.OOE+00 0.00E+00 7.86f+08 N/A TEEN Q.'OQE+00 3.25E+07 7.32E+07 Q.OOE+00 0.'QQE+00 O.OOE+00 4.23E+08 N/A CHILD O.OOE+00 3.86E+07 1.14E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.14E+08 N/A INFANT 0.'QQE+00 O.oof+00 O.OQE+00 O.QQE+00 0.'OQE+00 0.'Oof+00 O.OOE+00 N/A VEGTBLE ADULT Q.OOE+00 1.51E+08 3.34E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.84E+09 N/A.

TEEN O.OOE+00 2.35E+08 5.29E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.06E+09 N/A CHILD O.OOE+00 3.62E+08 1.07E+09 O.OOE+00 O.OOE+00 O.OOE+00 2.01E+09 N/A INFANT O.OQE+00 O.QOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 2.03E+08 4.47E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.81E+09 N/A INGEST. TEEN O.OOE+00 2.84E+08 6.39E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.69E+09 N/A CHILD O.OOE+00 4.26E+08 1.26E+09 O.OOE+00 O.OOE+00 O.OOE+00 2.36E+09 N/A INFANT O.OOE+00 5.13E+07 1.21E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.22E+08 N/A INHAL. ADULT O.OOE+00 1.15E+04 1.48E+04 O.OOE+00 O.OOE+00 5.97f+06 2.85E+05 N/A TEEN O.OOE+00 1.51E+04 1.98E+04 O.OOE+00 O.OOE+00 8.72f+06 2.59E+05 N/A CHILD, O.OOE+00 1.31E+04'.26E+04 O.QOE+00 O.OOE+00 7.07E+06 9.62E+04 N/A INFANT O.OOE+00 8.02E+03 1. 18E+04 O.OOE+00 O.OOE+00 4.51E+06 3.19E+04 N/A, BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• "~MAXIMUMVALUES FOR PATHWAYS""*

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

2.13E+1Q 2.51E+10 2.77E+07 1.83E+08 7.86E+08 3.06E+09 3.81E+09 8.72E+06 PAGE: 4-10 (38 of 124)

DATE

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Ni-63 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O..OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0AE4DO 0.00E+00 0.00E+00 0.00E+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 5. 19E+08 3.59E+07 1.74E+07 O.OOE+00 O.OOE+00 O.OOE+00 7.50E+06 N/A MILK TEEN 9. 11E+08 6.43E+07 3.09E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.02E+07 N/A CHILD 2.28E+09 1.22E+08 7.77E+07 O.OOE+00 O.OOE+00 O.OOE+00 8.24E+06 N/A INFANT 2.24E+10 1.66E+08 9.34E+07 O.OOE+00 O.OOE+00 O.OOE+00 8.28E+06 N/A COW ADULT 3.45E+09 2.39E+08 1. 16E+08 O.OOE+00 O.OOE+00 O.OOE+00 5.00E+07 N/A MILK TEEN 6.07E+09 4.29E+08 2.06E+08 O.OOE+00 O.OOE+00 O.OOE+00 6.82E+07 N/A CHILD 1.52E+10 8.15E+08 5.18E+08 O.OOE+00 O.OOE+00 O.OOE+00 5.49E+07 N/A INFANT 1.79E+10 1.11E+09 6.22E+08 O.OOE+00 O.OOE+00 O.OOE+00 5.52E+07 N/A MEAT ADULT 1.06E+10 7.38E+08 3.57E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.54E+08 N/A TEEN 8.56E+09 6.05E+08 2.90E+08 O.OOE+00 O.OOE+00 O.OOE+00 9.63E+07 N/A CHILD 1.64E+10 8.79E+08 5.59E+08 O.OOE+00 O.OOE+00 O.OOE+00 5.92E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 9.43E+09 6.54E+08 3. 16E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.36E+08 N/A TEEN 1.52E410 1.07E+09 5.15E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.71E+08 N/A CHILD 3.79E+10 2.03E+09 1.29E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.37E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOEt00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.40E+10 1.67E+09 8.07E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.48E+08 N/A INGEST. TEEN 3.07E+10 2.17E+09 1.04E+09 O.OOE+00 O.OOE+00 O.OOE+00 3.46E+08 N/A CHILD 7.18E+10 3.84E+09 2.44E+09 O.OOE+00 O.OOE+00 O.OOE+00 2.59E+08 N/A INFANT 4.04E+10 1.28E+09 7. 16E+08 O.OOE+00 O.OOE+00 O.OOE+00 6.34E+07 N/A INHAL. ADULT 4.32E+05 3. 14E+04 1.45E+04 O.OOE+00 O.OOE+00 1.78E+05 1.34E+04 N/A TEEN 5.80E+05 4.34E+04 1.98E+04 O.OOE+00 O.OOE+00 3.07E+05 1.42E+04 N/A CHILD 8.21E+05 4.63E+04 2.80E+04 0.00E+00 0.00E+00 2.75E+05 6.33E+03 N/A INFANT 3.39E+05 2.04E+04 1. 16E+04 O.OOE+00 O.OOE+00 2.09E+05 2.42E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS*"*

GROUND: GROUND: GOAT COW TOTAL T; B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 .O.OOE+00 2.24E+10 1.79E+10 1.64E+10 3.79E+10 7.18E+10 8.21E+05 PAGE: 4-11 (39 of 124) oar

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Zn-65 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY. LUNG G. I. SKIN GROUND ADULT 7.40E+08 7,.40E+08 7;40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 8.50E+08 TEEN 7.40E+08 7'.40E+08 7.40E+08 7.40E+08 7.40Ei98 7.40E+08 7.40E+08 8.50Ee08 CHILD 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 &.50E+08 INFANT 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 8.50E+08 GOAT ADULT 9.87E+07 3.14E+08 1.42E+08 O.OOE+00 2.10E+08 O.OOE+00 1.9&E+08 N/A MILK TEEN 1. 51E+08 5.26E+08 2.45E+08 O.OOE+00 3.37E+08 O.OOE+00 2.23E+08 N/A CHILD 2.97E+08 7.92E+08 4.93E+08 O.OOE+00 4.99E+08 O.OOE+00 1.39E+08 N/A INFANT 3.33E+09 1.37E+09 6.31E+08 O.OOE+00 6.64E+08 O.OOE+00 1. 16E+09 N/A COW ADULT 6.24E+08 1.99E+09 8.97E+08 O.OOE+00 1.33E+09 O.OOE+00 1.25E+09 N/A MILK TEEN 9.58E+08 3.33E+09 1.55E+09 O.OOE+00 2.13E+09 O.OOE+00 1.41E+09 N/A CHILD 1.88E+09 5.01E+09 3. 12E+09 0.00E+00 3. 16E+09 0.00E+00 8.80E+08 N/A INFANT 2.53E+09 8.66E+09 3.99E+09 O.OOE+00 4.20E+09 O.OOE+00 7.31E+09 N/A MEAT ADULT 1.82E+08 5.79E+08 2.62E+08 O.OOE+00 3.87E+08 O.OOE+00 3.65E+08 N/A TEEN 1.28E+08 4.44E+08 2.07E+08 O.OOE+00 2.84E+08 O.OOE+00 1.88E+08 N/A CHILD 1.92E+08 5.11E+08 3.1&E+08 O.OOE+00 3.22E+08 O.OOE+00 8.98E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOEt00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 2.83E+08 9.01E+08 4.07E+08 O.OOE+00 6.03E+08 O.OOE+00 5.68E+08 N/A TEEN 3.97E+08 1.38E+09 6.43E+08 0.00E+00 8.83E+08 0.00E+00 5.84E+08 N/A CHILD 7.73E+08 2.06E+09 1.28E+09 O.OOE+00 1.30E+09 O.OOE+00 3.62E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL 1.19E+09 3.78E+09 1.71E+09 O.OOE+00 2.53E+09 O.OOE+00 2.38E+09 N/A ADULT'NGEST.

TEEN 1.63E+09 5.68E+09 2.65E+09 O.OOE+00 3.63E+09 O.OOE+00 2.40E+09 N/A CHILD 3. 14E+09 8.37E+09 5.21E+09 O.OOE+00 5.28E+09 O.OOE+00 1.47E+09 N/A INFANT 5.85E+09 1.00E+10 4.63E+09 O.OOE+00 4.86E+09 O.OOE+00 8.47E+09 N/A INHAL. ADULT 3.24E+04 1.03E+05 4.66E+04 O.OOE+00 6.90E+04 8.64E+05 5.34E+04 N/A TEEN 3.86E+04 1.34E+05 6.24E+04 O.OOE+00 8.64E+04 1.24E+06 4.66E+04 N/A CHILD 4.25E+04 1. 13E+05 7.03E+04 O.OOE+00 7.14E+04 9.95E+05 1.63E+04 N/A INFANT 1.93E+04 6.26E+04 3. 11E+04 O.OOE+00 3.25E+04 6.47E+05 5. 14E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN "Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS*"~

GROUND: GROUND: GOAT COW TOTAL T'.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

7.40E+08.8.50E+08 3.33E+09. 8.66E+09 5.79E+08 2.06E+09 1.00E+10 1.24E+06 PAGE: 4-12 (40 of 124)

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Rb-86 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+0& 8.89E+06 8.89E+06 1.02E+07 TEEN 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89Ei06 8.89E+06 8.89E+06 1.02E+07 CHILD 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 1.02E+07 INFANT 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 1.02E+07 GOAT ADULT 0.00E+00 1.42E+08 6.63E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.80E+07 N/A MILK TEEN O.OOE+00 2.59E+08 1.22E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.84E+07 N/A CHILD O.OOE+00 4.81E+08 2.96E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.09E+07 N/A INFANT O.OOE+00 1.22E+09 6.03E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.12E+07 N/A COW ADULT 'O.OOE+00 6.78E+08 3.16E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.34E+08 N/A MILK TEEN O.OOE+00 1.24E+09 5.80E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.83E+08 N/A CHILD O.OOE+00 2.29E+09 1.41E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.47E+08 N/A INFANT O.OOE+00 5.81E+09 2.87E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.49E+08 N/A MEAT ADULT O.OOE+00 1.65E+08 7.67E+07 O.OOE+00 O.OOE+00 O.OOE+00 3.25E+07 N/A TEEN O.OOE+00 1.37E+08 6.45E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.03E+07 N/A CHILD O.OOE+00 1.95E+08 1.20E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.25E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT "0.00E+00 1.32E+08 6.17E+07 0.00E+00 0.00E+00 0.00E+00 2.61E+07 N/A TEEN O.OOE+00 1.93E+08 9.07Et07 O.OOE+00 O.OOE+00 O.OOE+00 2.86E+07 N/A CHILD O.OOE+00 3.40E+08 2.09E+08 O.OOE+00 O.OOE+00 O.OOE+00 2. 19E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 1. 12E+09 5.20E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.20E+08 N/A INGEST. TEEN O.OOE+00 1.83E+09 8.57E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.70E+08 N/A CHILD O.OOE+00 3.31E+09 2.03E+09 O.OOE+00 O.OOE+00 O.OOE+00 2.13E+08 N/A INFANT O.OOE+00 7.03E+09 3.48E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.80E+08 N/A INHAL. ADULT O.OOE+00 1.35E+05 5.90E+04 O.OOE+00 O.OOE+00 O.OOE+00 1.66E+04 N/A TEEN O.OOE+00 1.90E+05 8.40E+04 O.OOE+00 O.OOE+00 O.OOE+00 1.77E+04 N/A CHILD O.OOE+00 1.98E+05 1. 14E+05 O.OOE+00 O.OOE+00 O.OOE+00 7.99E+03 N/A INFANT O.OOE+00 1.90E+05 8.82E+04 O.OOE+00 O.OOE+00 O.OOE+00 3.04E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN 1

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposi.tion pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS"**

GROUND: GROUND: GOAT COW TOTAL T; B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

8.89E+06 1.02E+07 1.22E+09 5.81E+09 1.95E+08 3.40E+08 7.03E+09 1.98Ew05 PAGE: 4-13 DAT (41 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Sr-89 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.49E+04 TEEN 2.14E+04 2.14E+04 2;14E+04 2.14E+04 2.146+04 2.14E+04 2.14E+04 2.49E+04 CHILD 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.49E+04 INFANT 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.14E+04 2.49E+04 GOAT ADULT 1.54E+09 O.OOE+00 4.43E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.47E+08 N/A HILK TEEN 2.84E+09 O.OOE+00 8.14E+07 O.OOE+00 O.OOE+00 O.OOE+00 3.39E+08 N/A CHILD 7.04E+09 O.OOE+00 2.01E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.72E+08 N/A INFANT 6.37E+09 O.OOE+00 3.84E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.75E+08 N/A COW ADULT 4.76E+08 O.OOE+00, 1.37E+07 O.OOE+00 O.OOE+00 O.OOE+00 7.64E+07 N/A MILK TEEN 8.78E+08 O.OOE+00 2.51E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.05E+08 N/A CHILD 2. 17E+09 O.OOE+00 6.20E+07 O.OOE+00 O.OOE+00 O.OOE+00 8.'41E+07 N/A INFANT 4. 13E+09 O.OOE+00 1.18E+08 O.OOE+00 O.OOE+00 O.OOE+00 8.49Et07 N/A HEAT ADULT 1.20E+08 O.OOE+00 3.44E+06 O.OOE+00 O.OOE+00 O.OOE+00 1.92E+07 N/A TEEN 1.01E+08 O.OOE+00 2.90E+06 O.OOE+00 O.OOE+00 O.OOE+00 1.21E+07 N/A CHILD 1.92E+08 O.OOE+00 5.48E+06 O.OOE+00 O.OOE+00 O.OOE+00 7.42E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 8.19E+09 O.OOE+00 2.35E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.31E+09 N/A TEEN 1.35E+10 O.OOE+00 3.86E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.60E+09 N/A CHILD 3. 29E+10 O.OOE+00 9.39E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.27E+09 N/A INFANT 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1. 03E+10 O.OOE+00 2.96E+08 O..OOE+00 O.OOE+00 O.OOE+00 1.66E+09 N/A INGEST. TEEN 1. 73E+10 O.OOE+00 4.95E+08 O.OOE+00 O.OOE+00 O.OOE+00 2.06E+09 N/A CHILD 4. 23E+10 O.OOE+00 1.21E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.64E+09 N/A INFANT 1. 05E+10 O.OOE+00 5.02E+08 O.OOE+00 O.OOE+00 O.OOE+00 3.60E+08 N/A INHAL. ADULT 3.04E+05 O.OOE+00 8.72E+03 O.OOE+00 O.OOE+00 1.40E+06 3.50E+05 N/A TEEN 4.34E+05 O.OOE+00 1.25E+04 O.OOE+00 O.OOE+00 2.42E+06 3.71E+05 N/A CHILD 5.99E+05 O.OOE+00 1.72E+04 O.OOE+00 O.OOE+00 2. 16E+06 1.67E+05 N/A INFANT 3.98E+05 0.00E+00 1.14E+04 0.00E+00 0.00E+00 2.03E+06 6.40E+04 N/A BONE L VE T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT -

COW TOTAL T.B./ORG. SKIN MILK: MILK: HEAT: VEGTBLE: INGEST: INHAL.

2.14E+04 2.49E+04 7.04E+09 4.13E+09 1.92E+08 3.29E+10 4.23E+10 2.42E+06 PAGE: 4-14 DATE (42 of 124)

O.D.C.H. NXIHUN

~ ~ ~ ~ PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Sr-90 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+OQ O.OOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOEi00 O.OOE+00 O.OOE+00 O.OOE+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 6.30E+10 O.OOE+00 1.55E+10 O.OOE+00 O.OOE+00 O.OOE+00 1.82E+09 . N/A MILK TEEN 8.91E+10 O.OQE+00 2.20E+10 O.OOE+00 O.OQE+00 O.OOE+00 2.50E+09 N/A CHILD 1.51E+ll 0.00E+00 3.82E+10 0.00E+00 0.00E+00 0.00E+00 2.03E+09 N/A INFANT 7.80E+10 O.OOE+00 4.17E+10 O.OOE+00 O.OOE+00 O.OOE+00 2.05E+09 N/A COW ADULT 2.40E+10 O.OOE+00 5.88E+09 O.OOE+00 O.OOE+00 O.OOE+00 6.93E+08 N/A MILK TEEN 3.39E+10 O.OOE+00 8.37E+09 O.OOE+00 O.OOE+00 O.OOE+00 9.51E+08 N/A CHILD 5.72E+10 O.OOEt00 1.45E+10 O.OOE+00 O.OOE+00 O.OOE+00 7.71E+08 N/A INFANT 6.23E+10 O.OOE+QO 1.59E+10 O.OOE+00 O.OOE+00 O.OOE+00 7.78E+08 N/A HEAT ADULT 7.00E+09 O.OOE+00 1.72E+09 O.OOE+00 O.OOE+00 O.OOE+00 2.02E+08 N/A TEEN 4.53E+09 O.OOE+00 1. 12E+09 O.OOE+00 O.OOE+00 O.OOE+00 1.27E+08 N/A CHILD 5.85E+09 O.OOE+00 1.48E+09 O.OOE+00 O.OOE+00 O.OOE+00 7.88Et07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 5.48E+ll O.OQE+00 1.34E+11 O.OOE+00 O.OOE+00 O.OOE+00 1.58E+10 N/A TEEN 7.10E+ll O.OOE+00 1.75E+ll O.OOE+00 O.OOE+00 O.OOE+00 1.99E+10 N/A CHILD 1.19E+12 O.OOE+00 3.02E+ll O.OOE+00 O.OOE+00 O.OOE+00 1.61E+10 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 6.42E+ll O.OOE+00 1.58E+ll O.OOE+00 O.OOE+00 O.OOE+00 1.85E+10 N/A INGEST. TEEN 8.37E+l1 O.OOE+00 2.07E+ll O.OOE+00 O.OOE+00 O.OOE+00 2.35E+10 N/A CHILD 1.41E+12 O.OOE+00 3.56E+ll O.QOE+00 O.OOE+00 O.OOE+00 1.89E+10 N/A INFANT 1.40E+ll O.OOE+00 5.76E+10 O.OOE+00 O.OOE+00 O.OOE+00 2.82E+09 N/A INHAL. ADULT 9.92E+07 O.OOE+00 6. 10E+06 O.OOE+00 O.OOE+00 9.60E+06 7.22E+05 N/A TEEN 1.08E+08 O.OOE+00 6.68E+06 O.OOE+00 O.OOE+00 1.65E+07 7.65E+05 N/A CHILD 1.01E+08 O.OOE+00 6.44E+06 O.OOE+00 O.OOE+00 1.48E+07 3.43E+05 N/A INFANT 4.09E+07 O.OOE+00 2.59E+06 O.OOE+00 O.OOE+00 1.12E+07 1.31E+05 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: HEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 1.51E+ll 6.23E+10 7.00E+09 1.19E+12 1.41E+12 1.08Ew08 PAGE: 4-15 0AT (43 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Y-90 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 0;OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+DO 0.00E+00 0.00E+00 0.00E+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 3.83E+00 O.OOE+00 1.03E-01 O.OOE+00 O.OOE+00 O.OOE+00 4.06E+04 N/A MILK TEEN 7.03E+00 O.OOE+00 1.89E-01 O.OOE+00 O.OOE+00 O.OOE+00 5.80E+04 . N/A CHILD 1.74E+01 O.OOE+00 4.66E-01 O.OOE+00 O.OOE+00 O.OOE+00 4.95E+04 N/A INFANT 3.07E+02 O.OOE+00 9.86E-Ol O.OOE+00 O.OOE+00 O.OOE+00 5.08E+04 N/A COW ADULT 1.79E+01 O.OOE+00 4.79E-01 O.OOE+00 O.OOE+00 O.OOE+00 1.89E+05 N/A MILK TEEN 3.28E+Ol O.OOE+00 8.84E-01 O.OOE+00 O.OOE+00 O.OOE+00 2.71E+05 N/A CHILD 8.12E+01 O.OOE+00 2.17E+00 O.OOE+00 O.OOE+00 O.OOE+00 2.31E+05 N/A INFANT 1.72E+02 O.OOE+00 4.60E+00 O.OOE+00 O.OOE+00 O.OOE+00 2.37E+05 N/A MEAT ADULT 3.55E+01 O.OOE+00 9.52E-01 O.OOE+00 O.OOE+00 O.OOE+00 3.76E+05 N/A TEEN 2.99E+01 O.OOE+00 8.04E-01 O.OOE+00 O.OOE+00 O.OOE+00 2.46E+05 N/A CHILD 5.65E+01 O.OOE+00 1.51E+00 O.OOE+00 O.OOE+00 O.OOE+00 1.61E+05 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT TEEN CHILD 4.39E+03 O.OOE+00 1. 18E+02 O.OOE+00 O.OOE+00 O.OOE+00 4.65E+07

4. IOEi03 O.OOE+00 1. 10E+02 O.OOE+00 O.OOE+00 O.OOE+00 3.38E+07 7.61E+03 O.OOE+00 2.04E+02 O.OOE+00 O.OOE+00 O.OOE+00 2.17E+07

'/A N/A N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 4.44E+03 O.OOE+00 1.19E+02 O.OOE+00 O.OOE+00 O.OOE+00 4.71E+07 N/A INGEST. TEEN 4. 17E+03 O.OOE+00 1. 12E+02 O.OOE+00 O.OOE+00 O.OOE+00 3.44E+07 , N/A CHILD 7.77E+03 O.OOE+00 2.08E+02 O.OOE+00 O.OOE+00 O.OOE+00 2.21E+07 N/A INFANT 4.78E+02 O.OOE+00 5.59E+00 O.OOE+00 O.OOE+00 O.OOE+00 2.88E+05 N/A INHAL. ADULT 2.09E+03 O.OOE+00 5.61E+01 O.OOE+00 O.OOE+00 1.70E+05 5.06E+05 N/A TEEN 2.98E+03 O.OOE+00 8.00E+01 O.OOE+00 O.OOE+00 2.93E+05 5.59E+05 N/A CHILD 4. 11E+03 O.OOE+00 1.11E+02 O.OOE+00 O.OOE+00 2.62E+05 2.68E+05 N/A INFANT 3.29E+03 O.OOE+00 8.82E+01 O.OOE+00 O.OOE+00 2.69E+05 1.04E+05 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: 'units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS**"

GROUND: GROUND: GOAT COW TOTAL T; B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00-0.00E+00 5.80E+04 2.71E+05 3.76E+05 4.65E+07 4.71E+07 5.59E+05 PAGE: 4-16 DAT (44 of 124)

O.D.C.M.~

~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

I ISOTOPE: Sr-91 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OQX+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OQE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.DOE+00 O.OOE+00 0;OOE+00 O.OOE+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+OQ O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 2.73E+04 O.OOE+00 1.10E+03 O.OOE+00 O.OOE+00 O.OOE+00 1.30E+05- N/A MILK =

TEEN 5.02E+04 0.00E+00 2.00E+03 0.00E+00 0.00E+00 0.00E+00 2.28E+05 N/A CHILD 1.23E+05 O.OOE+00 4.65E+03 O.OOE+00 O.OOE+00 O.OOE+00 2.72E+05 N/A INFANT 1.22E+05 O.OOE+00 9.29E+03 O.OOE+00 O.OOE+00 O.OOE+00 3.04E+05 N/A COW ADULT 7.29E+03 O.OOE+00 2.94E+02 O.OOE+00 O.OOE+00 O.OOE+00 3.47E+04 N/A MILK TEEN 1.34E+04 O.OOE+00 5.32E+02 O.QOE+00 O.OQE+00 O.OOE+00 6.07E+04 N/A CHILD 3.28E+04 0.'OOE+00 1.24E+03 O.OQE+00 Q.QQE+00 O.QOE+00 7.25E+04 N/A INFANT 6.84E+04 O.OQE+00 2.48E+03 O.OOE+00 Q.QOE+00 O.OOE+00 8. 10E+04 N/A HEAT ADULT 5.01E-ll O.OQE+00 2.Q2E-12 O.OOE+00 O.QQE+00 O.OOE+00 2.38E-10 N/A TEEN 4.21E-ll O.QOE+00 1.68E-12 O.OOE+00 O.QOE+00 O.OOE+00 1.91E-10 N/A CHILD 7.90E-ll Q.QOE+00 2.98E-12 O.OOE+00 O.QOE+00 O.OQE+00 1.74E-10 N/A INFANT O.OQE+00 O.QOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A EGTBLE ADULT 1.01E+05 O.OOE+00 4.06E+03 O.OOE+00 O.OOE+00 O.OOE+00 4.79E+05 N/A TEEN 9.39E+04 O.OOE+00 3.74E+03 O.OOE+00 O.OOE+00 O.OOE+00 4.26E+05 N/A CHILD 1.73E+05 O.OQE+00 6.53E+03 O.OOE+00 O.OOE+00 O.OOE+00 3.82E+05 N/A INFANT O.OOE+00 O.OQE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.35E+05 O.OOE+00 5.46E+03 O.OOE+00 O.OOE+00 O.OOE+00 6.44E+05 N/A INGEST. TEEN 1.58E+05 O.OOE+00 6.27E+03 O.OOE+00 O,OOE+00 O.OOE+00 7.14E+05 N/A CHILD 3.29E+05 O.OOE+00 1.24E+04 O.OOE+00 O.OOE+00 O.OOE+00 7. 26E+05 ~

N/A INFANT 1.91E+05 O.OOE+00 1. 18E+04 O.OOE+00 O.OOE+00 O.OOE+00 3.85E+05 N/A INHAL. ADULT 6.19E+01 O.OOE+00 2.50E+00 O.OOE+00 O.OOE+00 3.65E+04 1.91E+Q5 N/A TEEN 8.80E+Ol 0.00E+00 3.51E+00 0.00E+00 0.00E+00 6.07E+04 2.59E+05 N/A CHILD 1.21E+02 O.OOE+00 4.59E+00 O.OOE+00 O.OOE+00 5.33E+Q4 1.74E+05 N/A INFANT 9.56E+Ol O.OQE+00 3.46E+00 O.OOE+00 O.OQE+OQ 5.26E+04 7.34E+04 N/A

'BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion:. units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

~*"MAXIMUMVALUES FOR PATHWAYS*""

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN 'ILK: MILK: MEAT: VEGTBLE: INGEST.: INHAL.

Q,QOE+00 O.QOE+00 3.04E+05 8. 10E+04 2.38E-10 4.79E+05 7.26E+05 2.59E+05 PAGE: 4-17 (45 of 124)

OAT

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Y-91 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.20E+06 TEEN 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E<06 1.06E+06 1.06E+06 1.20E+06 CHILD 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.20E+06 INFANT 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 l.'06E+06 1.20E+06 GOAT ADULT 5.32E+02 O.OOE+00 1.42E+01 O.OOE+00 O.OOE+00 O.OOE+00 2.93E+05 N/A MILK TEEN 9.79E+02 O.OOE+00 2.62E+Ol O.OOE+00 O.OOE+00 O.OOE+00 4.01E+05 N/A CHILD 2.42E+03 O.OOE+00 6.47E+Ol O.OOE+00 O.OOE+00 O.OOE+00 3.22 +05 N/A INFANT 3.78E+04 O.OOE+00 1.21E+02 O.OOE+00 O.OOE+00 O.OOE+00 3.25 +05 N/A COW ADULT 2.94E+03 O.OOE+00 7.85E+Ol O.OOE+00 O.OOE+00 O.OOE+00 1.62E+06 N/A MILK TEEN 5.40E+03 O.OOE+00 1.45E+02 O.OOE+00 O.OOE+00 O.OOE+00 2.22E+06 N/A CHILD 1.34E+04 O.OOE+00 3.57E+02 O.OOE+00 O.OOE+00 O.OOE+00 1.78E+06 N/A INFANT 2. 51E+04 O.OOE+00 6.6&E+02 O.OOE+00 O.OOE+00 O.OOE+00 1.&OE+06 N/A MEAT ADULT 4.65E+05 O.OOE+00 1.24E+04 O.OOE+00 O.OOE+00 O.OOE+00 2.56E+08 N/A TEEN 3.91E+05 O.OOE+00 1.05E+04 O.OOE+00 O.OOE+00 O.OOE+00 1.60E+08 N/A CHILD 7.39E+05 O.OOE+00 1.9&E+04 O.OOE+00 O.OOE+00 O.OOE+00 9.85E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 4.27E+06 O.OOE+00 1.14E+05 O.OOE+00 O.OOEi00 O.OOE+00 2.35E+09 N/A TEEN 7.05E+06 O.OOE+00 1.&9E+05 O.OOE+00 O.OOE+00 O.OOE+00 2.89E+09 N/A CHILD 1.72E+07 O.OOE+00 4.60E+05 O.OOE+00 O.OOE+00 O.OOE+00 2.29E+09 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 4.74E+06 O.OOE+00 1.27E+05 O.OOE+00 O.OOE+00 O.OOE+00 2.61E+09 N/A INGEST. TEEN 7.45E+06 O.OOE+00 2.00E+05 O.OOE+00 O.OOE+00 O.OOE+00 3.05E+09 N/A CHILD 1.79E+07 O.OOE+00 4.80E+05 O.OOE+00 O.OOE+00 O.OOE+00 2.39E+09 N/A INFANT 6.29E+04 O.OOE+00 7.88E+02 O.OOE+00 O.OOE+00 O.OOE+00 2. 12E+06 N/A INHAL. ADULT 4.62E+05 O.OOE+00 1.24E+04 O.OOE+00 O.OOE+00 1.70E+06 3.85E+05 N/A TEEN 6.61E+05 O.OOE+00 1.77E+04 O.OOE+00 O.OOE+00 2.94E+06 4.09E+05 N/A CHILD 9. 14E+05 O.OOE+00 2.44E+04 O.OOE+00 O.OOE+00 2.63E+06 1.84E+05 N/A INFANT 5.8&E+05 O.OOE+00 1.57E+04 O.OOE+00 O.OOE+00 2.45E+06 7.03E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

1.06E+06 1.20E+06 4.01E+05 2.22E+06 2.56E+08 2.89E+09 3.05Ea09 2.94Ee06 PAGE: 4-18 (46 of 124)

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Nb-95 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.59E+08 TEEN 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.59E+08 CHILD 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.59E+08 INFANT 1.35E+08, 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.35E+08 1.59E+08 GOAT ADULT 4.78E+03 2.66E+03 1.43E+03 O.OOE+00 2.63E+03 O.OOEi00 1.61E+07 N/A MILK TEEN 8. 15E+03 4.52E+03 2.49E+03 O.OOE+00 4.38E+03 O.OOE+00 1.93E+07 N/A CHILD 1.84E+04 7. 17Et03 5.12E+03 O.OOE+00 6.73E+03 O.OOE+00 1.33E+07 N/A INFANT 2.86E+05 1.42E+04 8. 18E+03 O.OOE+00 1.01E+04 O.OOE+00 1.19E+07 N/A COW ADULT 2.44E+04 1.36E+04 7.31E+03 O.OOE+00 1.34E+04 O.OOE+00 8.25E+07 N/A MILK TEEN 4.17E+04 2.31E+04 1.27E+04 O.OOE+00 2.24E+04 O.OOE+00 9.89E+07 N/A CHILD 9.41E+04 3.67E+04 2.62E+04 O.OOE+00 3.44E+04 O.OOE+00 6.78E+07 N/A INFANT ,

1.76E+05 7.24E+04 4. 18E+04 O.OOE+00 5. 19E+04 O.OOE+00 6. 11E+07 N/A MEAT ADULT 8.48E+05 4.72E+05 2.54E+05 O.OOE+00 4.66E+05 O.OOE+00 2.86E+09 N/A TEEN 6.62E+05 3.67E+05 2.02E+05 O.OOE+00 3.56E+05 O.OOE+00 1.57E+09 N/A CHILD 1. 14E+06 4.45E+05 3. 18E+05 O.OOE+00 4. 18E+05 O.OOE+00 8.23E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 1.10E+05 6.11E+04 3.28E+04 O.OOE+00 6.04E+04 O.OOE+00 3.71E+08 N/A TEEN 1.64E+05 9.10E+04 5.01E+04 O.OOE+00 8.82E+04 O.OOE+00 3.89E+08 N/A CHILD 3.63E+05 1.41E+05 1.01E+05 O.OOE+00 1.33E+05 O.OOE+00 2.61E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT: 9.87E+05 5.49E+05 2.95E+05 O.OOE+00 5.43E+05 O.OOE+00 3.33E+09 N/A INGEST. TEEN 8.76E+05 4.86E+05 2.68E+05 O.OOE+00 4.71E+05 O.OOE+00 2.08E+09 N/A CHILD 1.62E+06 6.30E+05 4.50E+05 O.OOE+00 5.92E+05 O.OOE+00 1.17E+09 N/A INFANT 4.62E+05 8.65E+04 5.00E+04 O.OOE+00 6.20E+04 O.OOE+00 7.30E+07 N/A INHAL. ADULT 1.41E+04 7.82E+03 4.21E+03 O.OOE+00 7.74E+03 5.05E+05 1.04E+05 N/A TEEN 1.86E+04 1.03E+04 5.66E+03 O.OOE+00 1.00E+04 7.51E+05 9.68E+04 N/A CHILD 2.35E+04 9.18E+03 6.55E+03 O.OOE+00 8.62E+03 6. 14E+05 3.70E+04 N/A INFANT 1.57E+04 6.43E+03 3.78E+03 O.OOE+00 4.72E+03 4.79E+05 1.27E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND'OAT COW TOTAL T:B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

1.35E+08 1.59E+08 1.93E+07.9.89E+07 2.86E+09 3.89E+08 3.33E+09 7.51E+05 PAGE: 4-19 (47 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Zr-95 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN GROUND ADULT 2. 42E+08 2. 42E+08 2;42E+08 2. 42E+08 2. 42E+08 2.42E+08 2. 42E+08 2.81E+08 TEEN 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.81E+08 CHILD 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.81E+08 INFANT 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.42E+08 2.81E+08 GOAT ADULT 5.92E+Ol 1.90E+Ol 1.28E+01 O.OOE+00 2.98E+Ol O.OOE+00 6.01E+04 N/A MILK TEEN 1.03E+02 3.26E+01 2.25E+01 O.OOE+00 4.80E+Ol O.OOE+00 7.53E+04 - N/A CHILD 2.40E+02 5.28E+Ol 4.70E+Ol O.OOE+00 7.56E+01 O.OOE+00 5.51E+04 N/A INFANT 3.56E+03 1.04E+02 7.38E+01 O.OOE+00 1.12E+02 Q.OOE+00 5.18E+04 N/A COW ADULT 3.31E+02 1.06E+02 7.18E+01 O.OOE+00 1.67E+02 O.OOE+00 3.36E+05 N/A MILK TEEN 5.79E+02 1.83E+02 1.26E+02 O.OOE+00 2.68E+02 O.OOE+00 4;21E+05 N/A CHILD 1.34E+03 2.95E+02 2.63E+02 O.OOE+00 4.23E+02 O.OOE+00 3.08E+05 N/A INFANT 2.39E+03 5.82E+02 4.12E+02 O.OOE+00 6.27E+02 O.OOE+00 2.90E+05 MEAT ADULT 7.83E+05 2.51E+05 1.70E+05 O.OOE+00 3.94E+05 O.OOE+00 7.96E+08 N/A TEEN 6.27E+05 1.98E+05 1.36E+05 O.OOE+00 2.91E+05 O.OOE+00 4.57E+08 N/A CHILD l. 11E+06 2.45E+05 2.18E+05 O.OOE+00 3.50E+05 O.OOE+00 2.55E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 9.90E+05 3.17E+05 2.15E+05 O.OOE+00 4.98E+05 O.OOE+00 1.01E+09 N/A TEEN 1.56E+06 4.91E+05 3.38E+05 O.OOE+00 7.22E+05 O.OOE+00 1.13E+09 N/A CHILD 3.57E+06 7.85E+05 6.99E+05 O.OOE+00 l. 12E+06 O.OOE+00 8.19E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.77E+06 5.69E+05 3.85E+05 O.OOE+00 8.92E+05 O.OOE+00 1.80E+09 N/A INGEST. TEEN 2. 18E+06 6.89E+05 4.74E+05 0.00E+00 1.01E+06 0.00E+00 1.59E+09 N/A CHILD 4.69E+06 1.03E+06 9.17E+05 O.OOE+00 1.47E+06 O.OOE+00 1.07E+09 N/A INFANT 5.94E+03 6.86E+02 4.86E+02 O.OOE+00 7.39E+02 O.OOE+00 3.41E+05 N/A INHAL. ADULT 1.07E+05 3.44E+04 2.33E+04 O.OOE+00 5.42E+04 1.77E+06 1.50E+05 N/A TEEN 1.46E+05 4.58E+04 3. 15E+04 O.OOE+00 6.74E+04 2.69E+06 1.49E+05 N/A CHILD 1.90E+05 4. 18E+04 3.70E+04 O.OOE+00 5.96E+04 2.23E+06 6.11E+04 N/A INFANT 1. 15E+05'2.79E+04 2.03E+04 O.OOE+00 3. 11E+04 1.75E+06 2. 17E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

"**MAXIMUMVALUES FOR PATHWAYS"**

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

2.42E+08 2.81E+08 7.53E+04 4.21E+05 7.96E+08 1.13E+09 1.&QE+09 2.69E+06 PAGE: 4-20 (48 of 124)

DAT"

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Ho-99 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 4.00E+00 O.OOE+00 O.QOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.'QQE+00 0.'OOE+00 O'.OOE+00 Q.OQE+00 0.'aOZ+00 Q.OOE+00 0'.OQE+00 0'.OOE+00 CHILD O.OOE+00 Q.OOE+QQ O.QQE+00 O.QOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+QO O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT O.OOE+00 1.34E+06 2.55E+05 O.QOE+00 3.03E+06 O.OOE+00 3.10E+06 N/A MILK TEEN O.OOE+00 2.42E+06 4.61E+05 O.OOE+00 5.53E+06 O.OOE+00 4.33E+06'.OOE+00 N/A CHILD 4.39E+06 1.Q9E+06 O.OOE+00 9.38E+06 O.OOE+00 3.63E+06 N/A INFANT O.OOE+00 1. 12E+07 2. 19E+06 O.OOE+00 1.68E+07 O.QOE+00 3.70E+06 N/A COW ADULT O.OOE+00 6.24E+06 1.19E+06 O.OOE+00 1.41E+07 O.OOE+00 1.45E+07 N/A MILK TEEN O.OOE+00 1'.13E+07 2.15E+06 O.OOE+00 2.58E+07 O.OOE+00 2;02E+07 N/A CHILD O.OQE+00 2.05E+07 5.Q7E+06 O.QOE+00 4.38E+07 O.OOE+00 1.70E+07 N/A INFANT O.OOE+00 5.24E+07 1.02E+07 O.OOE+00 7.83E+07 Q.OOE+00 1.73E+07 N/A HEAT ADULT O.OOE+00 3.30E+04 6.27E+03 O.OOE+QO 7.46E+04 O.OQE+00 7.64E+04 N/A TEEN Q.OOE+00 2.73E+04 5.20E+03 O.OOE+00 6.24E+04 O.OOE+00 4.88E+04 N/A CHILD O.OOE+00 3.79E+04 9.38E+03 O.OOE+00 8. 10E+04 O.OOE+00 3. 14E+04 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+OO O.QOE+00 O.OQE+00 O.OOE+00 O.QOE+00 N/A GTBLE ADULT O.OOE+00 2.03E+06 3.86E+05 0.00E+00 4.60E+06 0.00E+00 4.71E+06 N/A TEEN O.QQE'+00 1.86E+06 3.55E+05 O.OOE+00 4.27E+06 O.OOE+00 3.34E+06 N/A CHILD O.OQE+00 2.54E+06 6.30E+05 O.OQE+00 5.43E+06 O.QQE+00 2. 10E+06 N/A INFANT O.OOE+00 O.OOE+00 0.00E+00 O,OOE+00 O.OOE+00 O.OOE+00 Q.OOE+00 N/A TOTAL ADULT 0.00E+00 9.64E+06 1.83E+06 O.OQE+00 2. 18E+Q7 O.OOE+00 2.24E+07 N/A INGEST. TEEN 0.00E+00 1.56E+07 2.97E+06 O.OOE+00 3.56E+07 O.OOE+00 2.79E+07 N/A CHILD O.OOE+00 2.75E+07 6.80E+06 O.OOE+00 5.87E+07 O.OOE+00 2.27E+07 N/A INFANT O.OOE+00 6.37E+07 1.24E+07 O.OOE+00 9.51E+07 O.OOE+00 2.10E+07 N/A INHAL. ADULT O.OOE+00 1.21E+02 2.30E+Ol O.QQE+00 2.91E+02 9.12E+04 2.48E+05 N/A TEEN Q.OQE+00 1.69E+02 3.22E+Ol O.OOE+00 4.11E+02 1.54E+05 2.69E+05 N/A CHILD O.OOE+00 1.72E+02 4.26E+Ol O.OQE+00 3.92E+02 1.35E+05 1.27E+05 N/A INFANT O.OOE+00 1.65E+02 3.23E+01 O.OOE+00 2.65E+02 1.35E+05 4.87E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT CQW TOTAL

'T.B./ORG. SKIN MILK: MILK: NEAT: VEGTBLE: INGEST: INHAL.

Q.OOE+00 Q.QOE+00 1.68E+07 7.83E+07 .8.10E+04 5.43E+06 9.51E+07 2.69E+05 PAGE: 4-21 A Y Df.TE (49 of 124}

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Tc-99m PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOEi00'.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 CHILD 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT '.79E-Ol 5.07E-01 6.46E+00 O.OOE+00 7..70E+00 2.48E-01 3.00E+02 N/A MILK TEEN 3. 11E-01 8.68E-Ol 1.12E+Ol O.OOE+00 1.29E+01 4.82E-Ol 5.70E+02 N/A CHILD 7.13E-01 1.40E+00 2.32E+Ol O.OOE+00 2.03E+Ol 7.10E-01 7.96E+02 N/A INFANT l. 24E+01 3.06E+00 3.94E+01 O.OOE+00 3.29E+01 1.60E+00 8.89E+02 N/A COW ADULT 8.37E-01 2.36E+00 3.01E+Ol O.OOE+00 3.59E+Ol 1.16E+00 1.40E+03 N/A MILK TEEN 1.45E+00 4.05E+00 5.25E+Ol O.OOE+00 6.03E+01 2.25E+00 2.66E+03 N/A CHILD 3.33E+00 6.53E+00 1.08E+02 0.00E+00 9.49E+Ol 3.31E+00 3.71E+03 N/A INFANT 6.92E+00 1.43E+01 1.84E+02 O.OOE+00 1.54E+02 7.47E+00 4.15E+03 N/A MEAT ADULT 1.47E-21 4.14E-21 5.28E-20 O.OOE+00 6.29E-20 2.03E-21 2.45E-18 N/A TEEN 1.16E-21 3.25E-21 4.21E-20 O.OOE+00 4.84E-20 1.80E-21 2.13E-18 N/A CHILD 2.04E-21 4.01E-21 6.64E-20 O.OOE+00 5.82E-20 2.03E-21 2.28E-18 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 1.02E+00 2.89E+00 3.68E+Ol O.OOE+00 4.39E+01 1.42E+00 1.71E+03 N/A TEEN 9.03E-01 2.52E+00 3.26E+Ol O.OOE+00 3.75E+01 1.40E+00 1.65E+03 N/A CHILD 1.55E+00 3.05E+00 5.05E+Ol O.OOE+00 4.43E+01 1.55E+00 1.73E+03 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.04E+00 5.76E+00 7.34E+01 0.00E+00 8.75E+Ol 2.82E+00 3.41E+03 N/A INGEST. 2.67E+00 7.43E+00 9.63E+01 0.00E+00 1.11E+02 4. 13E+00 4.88E+03 N/A TEEN'HILD 5.60E+00 1.10E+01 1.82E+02 O.OOE+00 1.59E+02 5.57E+00 6.25E+03 N/A INFANT 1. 93E+01 1.73E+Ol 2.23E+02 O.OOE+00 1.87E+02 9.07E+00 5.04E+03 N/A INHAL. ADULT 1.03E-03 2.91E-03 3..70E-02 O.OOE+00 4.42E-02 7.64E+02 4.16E+03 N/A TEEN 1.38E-03 3.86E-03 4.99E-02 O.OOE+00 5.76E-02 1.15E+03 6.13E+03 N/A CHILD 1.78E-03 3.48E-03 5.77E-02 O.OOE+00 5.07E-02 9.51E+02 4.81E+03 N/A INFANT 1.40E-03 2.88E-03 3.72E-02 O.OOE+00 3.11E-02 8. 11E+02 2.03E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN, MILK: MILK: NEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 8.89E+02- 4. 15E+03 2.45E-18 1.73E+03 6.25E+03 6.13E+03 PAGE: 4-22 (50 of 124)

DAT

O.D.C.M.

ISOTOPE: Ru-106 MAXIMUM PATHWAY DOSE FACTORS:

PATHWAY AGE GROUP BONE LIVER T.BODY RADIONUCLIDES OTHER THAN NOBLE GASES*

THYROID KIDNEY LUNG G.I. SKIN e

GROUND ADULT 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 5.01E+08 TEEN 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08.5.01E+08 CHILD 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 5.01E+08 INFANT 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18E+08 5.01E+08 GOAT ADULT 1.50E+03 O.OOE+00 1.90E+02 O.OOE+00 2.90E+03 O.OOE+00 9.71E+04 N/A MILK TEEN 2.76E+03 O.OOE+00 3.48Et02 O.OOE+00 5.32E+03 O.OOE+00 1.32E+05 N/A CHILD 6.79E+03 O.OOE+00 8.47E+02 O.OOE+00 9.17E+03 O.OOE+00 1.06E+05- N/A INFANT 1. 17E+05 O.OOE+00 1.75E+03 O.OOE+00 1.65E+04 O.OOE+00 1.06E+05 N/A COW ADULT 9.65E+03 O.OOE+00 1.22E+03 O.OOE+00 1.86E+04 O.OOE+00 6.24E+05 N/A MILK TEEN 1.77E+04 O.OOE+00 2.24E+03 O.OOE+00 3.42E+04 O.OOE+00 8. 51E+05 N/A CHILD 4.37E+04 O.OOE+00 5.45E+03 O.OOE+00 5.90E+04 O.OOE+00 6.80E+05 N/A INFANT 9.00E+04 O.OOE+00 1.12E+04 O.OOE+00 1.06E+05 O.OOE+00 6.83E+05 N/A MEAT ADULT 1.48E+09 O.OOE+00 1.87E+08 O.OOE+00 2.85E+09 O.OOE+00 9.56E+10 N/A TEEN 1.24E+09 O.OOE+00 1.57E+08 O.OOE+00 2.40E+09 O.OOE+00 5.97E+10 N/A CHILD 2.34E+09 O.OOE+00 2.92E+08 O.OOE+00 3.16E+09 O.OOE+00 3.64E+10 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 1.73E+08 O.OOE+00 2. 19E+07 O.OOE+00 3.34E+08 O.OOE+00 1.12E+10 N/A TEEN 2.91E+08 0.00E+00 3.67E+07 0.00E+00 5.61E+08 0.00E+00 1.40E+10 N/A CHILD 7. 11E+08 O.OOE+00 8.88E+07 O.OOE+00 9.61E+08 O.OOE+00 1.11E+10 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 N/A TOTAL ADULT 1.65E+09 O.OOE+00 '2.09E+08 O.OOE+00 3. 19E+09 O.OOE+00 1.07E+11 N/A INGEST. TEEN 1.53E+09 0.00E+00 1.93E+08 0.00E+00 2.96E+09 0.00E+00 7.36E+10 N/A CHILD 3.05E+09 O.OOE+00 3.81E+08 O.OOE+00 4. 12E+09 O.OOE+00 4.75E+10 N/A INFANT 2.07E+05 0.00E+00 1.30E+04 0.00E+00 1.23E+05 0.00E+00 7.90E+05 N/A INHAL. ADULT 6.91E+04 O.OOE+00 8.72E+03 O.OOE+00 1.34E+05 9.36E+06 9.12E+05 N/A TEEN 9.84E+04 O.OOE+00 1.24E+04 O.OOE+00 1.90E+05 1.61E+07 9.60E+05 N/A CHILD 1.36E+05'0.00E+00 1.69E+04 0.00E+00'1.84E+05 1.43E+07 4.29E+05 N/A INFANT 8.68E+04 O.OOE+00 1.09E+04 O.OOE+00 1.07E+05 1. 16E+07 1.64E+05 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

~Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T..B./ORG. SKIN MI LK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

4.18E+08 5.01E+08 1.32E+05 8.51E+05 9.56E+10 1.40E+10 1.07E+11 1.61E+07 PAGE: 4-23 R Yt.V (51 of 124)

O.D.C.H.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Ag-110m PATHWAY AGE GROUP BONE "LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 3.40E+09 3.40009 3.40E+09 3.40E+09 3.40"+09 3.40E+09 3.40E+09 3.97E+09 TEEN 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.97E+09 .

CHILD 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3,97E+09 INFANT 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.40E+09 3.97E+09 GOAT ADULT 4.19E+06 3.8&Ew06 2.30E+06 O.QOE+00 7.63E+06 O.OOE+00 1.58E+09. N/A NILK TEEN 6.93E+06 6.56Ew06 3.99E+06 O.OOE+00 1.25E+07 O.OOE+00 1.84E+09 N/A CHILD 1.50E+07 1.02E+07 8.12E+06 O.OOE+00 1.89E+07 O.OOE+00 1.21E+09 N/A INFANT 2.32E+08 2.03E+07 1.34E+07 O.OOE+00 2.90E+07 O.OOE+00 1.05E+09 N/A COW 'ADULT 2.65E+07 2.46E+07 1.46E+07 O.OOE+00 4.83E+07 O.OOE+00 1.00E+10 MILK TEEN 4.39E+07 4.15E+07 2.53E+07 O.OOE+00 7.92E+07 O.OOE+00 1.17E+10 N/A CHILD INFANT 9.52E+07 1.76E+08 6.43E+07 1.2&E+08 5.14E+07 8.50E+07 O.OOE+00 1.20E+08 O.OOE+00 7.65E<09 0.00E+00 1.84E+08 Q.OOE+00 6.66E+09 '/AN/A N/A HEAT ADULT 3.42E+06 3. 17E+06 1.88E+06 O.OOE+00 6.23E+06 O.OOE+00 1.29Ew09 N/A TEEN 2.59E+06 2.45E+06 1.49E+06 O.OOE+00 4.6&E+06 O.OOE+00 6.89E+08 N/A CHILD 4.30E+06 2.90E+06 2.32E+06 O.OOE+00 5.41E+06 O.OOE+00 3.45E<08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 Q.OOE+00 Q.OOE+00 0.00E+00 N/A'TBLE ADULT 9.41E+06 8.70E+06 5.17E+06 O.OOE+00 1.71E+07 O.OOE+00 3.55E+09 N/A TEEN 1.42E+07 1.34E+07 8. 1&E+06 O.OOE+00 2.56E+07 O.OOE+00 3.7&E+09 N/A CHILD 3.06E+07 2.06E+07 1.65E+07 O.OOE+00 3.85E+07 O.OOE+00 2.46E+09 N/A INFANT O.OOE+OO O.OOE+OO O.OOE+OO O'.OOE+QO O.OOE+Oo O'.OOE+OO O.OOE+00 N/A TOTAL ADULT 4.36E+07 4.03E+07 2.39E+07 O.OOE+00 7.92E+07 O.OOE+00 1. 64E+10 N/A INGEST. TEEN 6.76E+07 6.40E+07 3.89E+07 O.OOE+00 1.22E+08 O.OOE+00 1.&OE+10 N/A CHILD 1.45E+08 9.&OE+07 7.83E+07 0.00E+00 1.83E+08 0.0QE+OQ 1.17E+10 N/A INFANT 4.07E+08 1.49E+08 9.84E+07 O.QOE+00 2.13E+08 O.OOE+00 7.71E+09 N/A INHAL. ADULT 1.08E+04 1.00E+04 5.94E+03 O.OOE+00 1.97E+04 4.63E+06 3.02E+05 N/A TEEN 1.38E+04 1.31E+04 7.99E+03 O.OOE+00 2.50E+04 6.75E+06 2.73E+05 N/A CHILD 1.69E+04 1. 14E+04 9. 14E+03 Q.OOE+OQ 2.12E+04 5.4&E+06 1.00E+05 N/A INFANT 9.9&E+03 7.22E+Q3 5.00E+03 0.00E+00 1.09E+04 3.67E+06 3.30E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./QRG. SKIN MILK: MILK: HEAT: VEGTBLE: INGEST: INHAL.

3..40E+09'.97E+09 1.84E+09 '1.17E+10 1.29E+09 3.7&E+09 1.&OE+10 6.75E+06 PAGE: 4-24 APt'V (52 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: I-131 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I.

GROUND ADULT 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 2.07E+07 TEEN 1.70E+07 1.70E+07 1..70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 2.07E+07 CHILD 1.70E+07 1.70E+07 1.70E+07 1..70E+07 1.@&07 1.70E+07 1.70E+07 2.07Et07 INFANT 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 2.07E+07 GOAT ADULT 1.60E+08 2.29E+08 1.31E+08 7.50E+10 3.92E+08 O.OOE+00 6.04E+07 N/A MILK TEEN 2.90E+08 4.06E+08 2. 18E+08 1.19E+1 1 6.99E+08 O.OOE+00 8.04E+07 N/A CHILD 7.04E+08 7.08E+08 4.02E+08 2.34E+ll 1. 16E+09 O.OOE+00 6.30E+07 .. N/A INFANT 1.22E+09 1.73E+09 7.61E+08 5.69E+ll 2.02E+09 O.OOE+00 6.18E+07 N/A COW ADULT 7.46E+07 1.07E+08 6. 12E+07 3.50E+10 1.83E+08 O.OOE+00 2.82Ei07 N/A MILK TEEN 1.35E+08 1.90E+08 1.02E+08 5. 53E+10 3.26E+08 O.OOE+00 3.75E+07 N/A CHILD 3.29E+08 3.30E+08 1.88E+08 1. 09E+1 1 5.42E+08 O.OOE+00 2.94E+07 N/A INFANT 6.86E+08 8.08E+08 3.55E+08 2.65E+1 1 9.44E+08 0.00E+00 2.88E+07 N/A MEAT ADULT 3.54E+06 5.07E+06 2.90E+06 1.66E+09 8.68E+06 O.OOE+00 1.34E+06 N/A TEEN 2.94E+06 4. 12E+06 2.21E+06 1.20E+09 7.09E+06 O.OOE+00 8. 15E+05 N/A CHILD 5.46E+06 5.49E+06 3. 12E+06 1.81E+09 9.01E+06 O.OOE+00 4.89E+05 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 2.86E+07 4. 10E+07 2.35E+07 1.34E+10 7.02E+07 O.OOE+00 1.08E+07 N/A TEEN 2.88E+07 4.03E+07 2. 16E+07 1. 18E+10 6.93E+07 O.OOE+00 7.96E+06 N/A CHILD 5.54E+07 5.57E+07 3, 17E+07 1.84E+10 9. 15E+07 O.OOE+00 4.96E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.67E+08 3.82E+08 2. 19E+08 1.25E+ll 6.54E+08 O.OOE+00 1.01E+08 N/A INGEST. TEEN 4.57E+08 6.40E+08 3.44E+08 1.87E+ll 1.10E+09 O.OOE+00 1.27E+08 N/A CHILD 1.09E+09 1. 10E+09 6.25E+08 3. 64E+1 1 1.81E+09 O.OOE+00 9.79E+07 N/A INFANT 1.91E+09 2. 54E+09 1.12E+09 8.34E+ll 2.97E+09 0.00E+00 9.06E+07 N/A INHAL. ADULT 2.52E+04 3.58E+04 2.05E+04 1.19E+07 6.13E+04 0.00E+00 6.28E+03 N/A TEEN 3.54E+04 4.91E+04 2.64E+04 1.46E+07 8.40E+04 O.OOE+00 6.49E+03 N/A CHILD 4.81E+04 4.81E+04 2.73E+04 1.62E+07 7.88E+04 O.OOE+00 2.84E+03 N/A INFANT 3.79E+04 4.44E+04 1.96E+04 1.48E+07 5.18E+04 O.OOE+00 1.06E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • "MAXIMUMVALUES FOR PATHWAYS"**

GROUND: GROUND: GOAT COW TOTAL.

T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE'NGEST: INHAL.

1.70E+07 2.07E+07 5.69E+ll 2.65E+ll 1.81E+09 1.84E+10 8.34E+ll 1. 62E+07 PAGE: 4-25 z HV (53 of 124)

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: I-132 PATHWAY AGE GROUP BONE LIVER '.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 O.OOE+00 0;OOE+00 0.005400 O.OOE+00 O.OOE+00 O.OOE+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 8.87E-02 2.37E-01 8.30E-02 8.30E+00 3.78E-01 O.OOE+00 4.46E-02 N/A MILK TEEN 1.57E-01 4. 12E-01 1.48E-01 1.39E+01 6.48E-01 O.OOE+00 1.79E-Ol N/A CHILD 3'.72E-01 6.84E-Ol 3.14E-Ol 3.17E+01 1.05E+00 O.OOE+00 8.05E-01 N/A INFANT 6.44E-01 1.57E+00 5.58E-Ol 7.35E+Ol 1.75E+00 0.00E+00 1.27E+00 N/A COW ADULT 4.14E-02 1.11E-01 3.87E-02 3.87E+00 1.76E-01 O.OOE+00 2.08E-02 N/A MILK TEEN 7.34E-02 1.92E-01 6.89E-02 6.47E+00 3.03E-01 O.OOE+00 8.37E-02 N/A CHILD 1.74E-01 3.19E-01 1.47E-01 1.48E+01 4.88E-01 O.OOE+00 3.75E-01 N/A INFANT 3.60E-01 7.31E-01 2.60E-01 3.43E+01 8.16E-01 O.OOE+00 5.93E-01 N/A MEAT ADULT 2.30E-59 6. 14E-59 2.15E-59 2. 15E-57 9.79E-59 O.OOE+00 1.15E-59 N/A TEEN 1.87E-59 4.88E-59 1.75E-59 1.64E-57 7.69E-59 O.OOE+00 2.13E-59 N/A CHILD 3.37E-596.20E-59 2.85E-59 2.88E-57 9.49E-59 O.OOE+00 7.30E-59 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 1.90E+01 5.08E+Ol 1.78E+Ol 1.78E+03 8.10E+Ol O.OOE+00 9.55E+00 N/A TEEN 1.71E+01 4.48E+01 1.61E+Ol 1.51E+03 7.06E+Ol O.OOE+00 1. 95E+01 N/A CHILD 3.04E+01 5.59E+Ol 2.57E+01 2.59E+03 8.56E+01 O.OOE+00 6.58E+Ol N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE>00 N/A I

TOTAL ADULT 1.91E+Ol 5.12Ew01 1.79E+01 1.79E+03 8.15E+01 0.00E+00 9.61E+00 N/A INGEST. TEEN 1.74E+Ol 4.54E+Ol 1.63E+01 1.53E+03 7.16E+Ol O.OOE+00 1.98E+Ol N/A CHILD 3.10E+Ol 5.69E+Ol 2.62E+Ol 2.64E+03 8.71E+01 0.00E+00 6.70E+Ol N/A INFANT 1.00E+00 2.30E+00 8.19E-01 1.08E+02 2.57E+00 O.OOE+00 1.86E+00 N/A INHAL. ADULT 1.16E+03 3.26E+03 1.16E+03 1.14E+05 5.18E+03 0.00E+00 4.06E+02 N/A TEEN 1.59E+03 4.38E+03 1.58E+03 1.51E+05 6.92E+03 O.OOE+00 1.27E+03 N/A CHILD 2. 12E+03 4.07E+03 1.88E+03 1.94E+05 6.25E+03 O.OOE+00 3.20E+03 N/A INFANT 1.69E+03 3.50E+03 1.26E+03 1.69E+05 3.95E+03 O.OOE+00 1.90E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T. B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGESJ: INHAL.

O.OOE+00 O.OOE+00 7.35E+01 3.43E+01 2.88E-57 2.59E+03 2.64E+03 1. 94E+05 PAGE: 4-26 A 0 DAT (54 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSf FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Te-132 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNfY LUNG G. I .. SKIN GROUND ADULT 0.DOE+00 D.DOE+00 D.DOE+00 D.DOE+00 O.DOE+00 O.DOE+00 D.DOE+00 Q.OQE+00 TEEN '.OOE+00 0.'DOE+00. 0.'DOE+00 0'.DOE+00 0-.'Oaf+00 0.'DOE+00 .0'.DOE+00 Q.DOE+00 CHILD 0. DOE+00 0.'DOE+00.DOE+00 0.'DOE+00 0.'Oof+00 D.DOE+00 0'.DOE+00 O.DOE+00 INFANT 0.DOE+00 O.DOE+00 O.DOE+00 O.DOE+00 O.DOE+00 O.DOE+00 O.DOE+00 O.DOE+00 GOAT ADULT 1.30E+05 8.39E+04 7.88E+04 9.27E+04 8.08E+05 O.DOE+00 3.97E+06 N/A MILK TEEN 2.'32E+05 1.47E+05 1.38E+05 1.55E+05 1.41E+06 0.'DOE+00 4.65E+06 N/A CHILD 5. 53E+05 2.45E+05 2.96E+05 3.57E+05 2.27E+06 O.DOE+00 2.47E+06 N/A INFANT 9.50E+06 5.64f+05 5.27E+05 8.33E+05 3.53E+06 Q.DOE+00 2.09E+06 N/A CQW ADULT 6.05E+05 3.91E+05 3.67E+05 4.32F+05 3.7TE+06 O.DOE+00 1.85E+07 N/A MILK TEEN 1.08E+06 6.85E+05 6.45E+05 T.22E+05 6.57E+06 O.DOE+00 2.17E+07 N/A CHILD 2.58E+06 1.14E+06 1.38E+06 1.66E+06 1.06E+07 Q.DOE+00 1.15E+07 N/A INFANT 5.32E+06 2.63E+06 2.46E+06 3.89E+06 1-.65E+07 O.DOE+00 9.74E+06 N/A HEAT ADULT 4.68E+05 3.03E+05 2.84E+05 3.34E+05 2.92E+06 0.DOE+00 1.43E+07 N/A TEEN 3.83E+05 2.43E+05 2.28E+05 2.56E+05 2.33E+06 0.DOE+00 7.68E+06 N/A CHILD 6.99E+05 3.09E+05 3.74E+05 4.51E+05 2.87E+Q6 Q.DOE+00 3.11E+06 N/

INFANT O.DOE+00 O.DOE+00 O.DOE+00 O.DOE+00 Q.DOE+00 O.DOE+00 O.DOE+00 N/

VEGTBLE ADULT 1.42E+06 9.18E+05 8.62E+05 1.01E+06 8.84E+06 0.'DOE+00 4.34E+07 N/A TEEN 1.29f+06 8.17E+05 7.69E+05 8.61E+05'.83E+06 O.OOE+OQ 2.59E+07 N/A CHILD 2.31E+06 1.02E+06 1.24E+06 1.49E+06 9.49E+06 O.DOE+00 1.03E+07 N/A INFANT 0.00E+00 0.'DOE+00 O.oof+00 0.'DOE+00 D.DOE+00 O.DOE+00 O.DOE+00 N/A TOTAL ADULT 2.62E+06 1.70f+06 1.59E+06 1.87E+06 1.63E+07 O.DOE+00 8.02E+07 N/A INGEST. TEEN 2.99E+Q6 1.89E+06 1.78f+06 1.99E+06 1.81E+07 O.DOE+00 5.99E+07 N/A CHILD 6.15E+06 2.72E+06 3.29E+06 3.96E+06 2.53E+07 O.DOE+00 2.74E+DT . N/A INFANT 1. 48f+07 3.20E+06 2.98E+06 4.TZE+06 2.00E+D7 O.DOE+00 1.18E+07 N/A INHAL. ADULT 2.60E+02 2.15E+02 1.62E+02 1.90E+02 1.46E+03 2.88E+05 5.10E+05 N/A .

TEEN 3.60E+02 2.90E+02 2.19E+02 2.46E+Q2 1.95E+03 4.49E+05 4.63E+05 N/A CHILD 4.81E+02 2.72E+02 2.63E+02 3.17E+02 1.77E+03 3.77E+05 1.38E+05 N/A INFANT 3.72E+02 2.37E+02 1.76E+02 2.79f+02 1.03E+D3 3.40E+05 4.41E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES fOR PATHWAYS**~

GROUND: GRQUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: 'EAT: VEGTBLE: INGEST> INHAL.

O.OOE+00 O.DOE+00 9.50E+06 2.17E+07 1.43E+07 4.34E+D7 8.02E+D7 5.10E+05 PAGE: 4-27 (55 of 124) l DAT

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: I-133

,PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ,ADULT O.OOE+00 O.OOE+00 0;OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00&40 0.00E+00 0.00E+00 0.00E+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 2.09E+06 3.64E+06 l. 11E+06 5.34E+08 6.34E+06 O.OOE+00 3.27E+06 N/A MILK TEEN 3.82E+06 6.48E+06 1.98E+06 9.04E+08 1. 14E+07 O.OOE+00 4.90E+06 - N/A CHILD 9.28E+06 1. 15E+07 4.34E+06 2. 13E+09 1.91E+07 O.OOE+00 4.62E+06 N/A INFANT 1.63E+07 2.85E+07 8.35E+06 5. 19E+09 3.35E+07 O.OOE+00 4.83E+06 N/A COW ADULT 9.75E+05 1.70E+06 5. 17E+05 2.49E+08 2.96E+06 O.OOE+00 1.52E+06 N/A MILK TEEN 1.78E+06 3.02E+06 9.21E+05 4.22E+08 5.30E+06 O.OOE+00 2.29E+06 N/A CHILD 4.33E+06 5.35E+06 2.02E+06 9.94E+08 8.92E+06 0.00E+00 2. 16E+06 N/A INFANT 9. 14E+06 1.33E+07 3 '0E+06 2.42E+09 1.56E+07 O.OOE+00 2.25E+06 N/A NEAT ADULT 1.20E-01 2.09E-01 6.38E-02 3.08E+01 3.65E-01 O.OOE+00 1.88E-01 N/A TfEN 1.01E-01 1.71E-01 5.21E-02 2.38E+01 3.00E-01 O.OOE+00 1.29E-01 N/A CHILD 1.87E-01 2.31E-01 8.75E-02 4.30E+01 3.86E-01 O.OOE+00 9.32E-02 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A EGTBLE ADULT 6.88f+05 1.20E+06 3.65E+05 1.76E+08 2.09E+06 O.OOE+00 1.08E+06 N/A TEEN 6.39E+05 1.08E+06 3.31E+05 1.51E+08 1.90E+06 O.OOE+00 8.20E+05 N/A CHILD 1. 17E+06 1.44E+06 5.45E+05 2.68E+08 2.40E+06 O.OOE+00 5.81E+05 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 3.75E+06 6.53E+06 1.99E+06 9.59E+08 1. 14E+07 O.OOE+00 5.87E+06 N/A INGEST. TEEN 6.24E+06 1.06E+07 3.23E+06 1.48E+09 1.86E+07 O.OOE+00 8.01E+06 N/A CHILD 1.48E+07 1.83E+07 6.91E+06 3.39E+09 3.04E+07 O.OOE+00 7.36E+06 N/A INFANT 2.55E+07 4. 18E+07 1.22E+07 7.61E+09 4.92E+07 O.OOE+00 7.08E+06 N/A INHAL. ADULT ,

8.64E+03 1,48E+04 4.52E+03 2. 15E+06 2.58E+04 0.00f+00 8.88E+03 N/A TEEN 1.22E+04 2.05E+04 6.22E+03 2.92E+06 3.59E+04 O.OOE+00 1.03E+04 N/A CHILD 1.66E+04 2,03E+04 7.70E+03 3.85E+06 3.38E+04 O.OOE+00 5.48E+03 N/A INFANT 1.32E+04 1.92E+04 5.60E+03 3.56E+06 2.24E+04 0.00f+00 2. 16E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS"*"

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MfAT: VEGTBLE: INGEST: INHAL.

.0.00E+00 0.00E+00 5. 19E+09 2.42E+09 4.30E+01 2.68E+08 7.61E+09 3.85E+06 PAGE: 4-28 (56 of 124)

DATE

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Cs-134 PATHWAY AGE GROUP BONE LIVER T.BODY -THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 7.92E+09 TEEN 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79K+09 6.79E+09 6.79Ew09 7.92E+09 CHILD

• 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 7.92E+09 INFANT 6.79E+09 6.79E+09 6.79E+09;,6.79E+09 6.79E+09 6.79E+09 6.79E+09 7.92E+09 GOAT ADULT 1. 06E+10 2. 53E+10 2.07E+10 O.OOE+00 8.19E+09 2.72E+09 4.43E+08 N/A MILK TEEN 1. 85E+10 4. 35E+10 2,02E+10 O.OOE+00 1.3&E+10 5.27E+09 5.41E+08 N/A CHILD 4. 26E+10 6. 99E+10 1.47E+10 O.OOE+00 2.17E+10 7.77E+09 3.77E+08 N/A

, INFANT 2. 29E+10 1. 28E+1 1 1.29E+10 O.OOE+00 3.30E+10 1.35E+10 3.48E+08 N/A COW ADULT 2.79E+09 6.63E+09 5.42E+09 O.OOE+00 2. 15E+09 7. 12E+08 1. 16E+08 N/A MILK TEEN 4.84E+09 1. 14E+10 5.2&E+09 O.OOE+00 3.62E+09 1.3&E+09 1;42E+08 N/A CHILD 1.12E+10 1.83E+10 3.86E+09 O.OOE+00 5.68E+09 2.04E+09 9.87E+07 N/A INFANT 1.&OE+10 3.35E+10 3.39E+09 O.OOE+00 8.63F+09 3.54E+09 9. 11E+0? N/A MEAT ADULT 3.59E+08 8.54E+08 6.9&E+08 O.OOE+00 2.76E+08 9. 17E+07 1.49E+07 N/A TEEN 2.85E+08 6.71E+08 3. 12E+08 O.OOE+00 2. 13E+08 8. 15E+07 8.35E+06 N/A CHILD 5.03E+08 8.26E+08 1.74E+08 O.OQE+00 2.56E+08 9. 18E+07 4.45E~06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/

VEGTBLE ADULT .4.21E+09 1.00E+10 8.19E+09 O.OOE+00 3.24E+09 1.0&E+09 1.75E+08 N/A TEEN 6.?OK+09 1.58E+10 ?.31E+09 0.00E+00 5.01E+09 1.91E+09 1.96E+08 N/A CHILD 1.53E+10 2.52E+10 5.31E+09 O.OOE+00 7.&OE+09 2.&OE+09 1.36E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.80E+10 4.28E+10 3.50E+10 O.OOE+00 1.39E+10 4.60E+09 7.49E+08 N/A INGEST. TEEN 3.03E+10 7.13E+10 3.31E+10 O.OOE+00 2.27E+10 8.65E+09 &.8?E+08 N/A CHILD 6.96E+10 1,14E+l1 2.41E+10 O.OOE+00 3.54E+10 1.27E+10 6. 16E+08 N/A INFANT 4.09E+10 1.62E+ll 1.63E+10 O.OOE+00 4.16E+10 1.70E+10 4.39E+08 N/A INHAL. ADULT 3.73E+05 8.4&E+05 7.2&E+05 0.00E+00 2.87E+05 9.76E+04 1. 04E+04 N/A TEEN 5.02E+05 1. 13E+06 5.49E+05 O.OOE+00 3.75E+05 1.46E+05 9.76E+03 N/A CHILD 6.51E+05 1,01E+06 2.25E+05 O.OOE+00 3.30Ew05 1.21E+05 3.85E+03 N/A INFANT 3.96E+05 7.03E+05 7.45E+04 O.OOE+00 1.90Ew05 7.97E+04 1.33E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition. pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUM 'VALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T;B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

6.79E+09 .7.92E+09 1.2&E+ll 3.35E+10 8.54E+08 2.52E+10 1.62E+11 1. 13E+06 PAGE: 4-29 DAT (57 of 124)

0.D.C.M.

~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: I-135 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+OO O.OOE+00 0.00E+00 O.OOE+00 O.OOE+Oa O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00&$ 0 0.00E+00 0.00E+00 0.00E+00 CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 6.93E+03 1.82E+04 6.70E+03 1.20E+06 2.91E+04 O.OOE+00 2.05E+04 N/A MILK TEEN 1.23E+04 3.17E+04 1.18E+04 2.04E+06 5.01E+04 O.OOE+00 3.51E+04 . N/A CHILD 2.92E+04 5.25E+04 2.48E+04 4.65E+06 8.05E+04 O.OOE+00 4.00E+04 N/A INFANT 5.05E+04 1.21E+05 4.40E+04 1.08E+07 1.34E+05 O.OOE+00 4.37E+04 N/A COW ADULT 3.24E+03 8.47E+03 3. 13E+03 5.59E+05 1.36E+04 O.OOE+00 9.57E+03 N/A MILK TEEN 5.75E+03 1.48E+04 5.48E+03 9.52E+05 2.34E+04 O.OOE+00 1.64E+04 N/A CHILD 1.36E+04 2.45E+04 1.16E+04 2. 17E+06 3.75E+04 O.OOE+00 1.87E+04 N/A INFANT 2.83E+04 5.63E+04 2.05E+04 5.05E+06 6.27E+04 O.OOE+00 2.04E+04 N/A MEAT ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 1.29E+04 3.37E+04 1.24E+04 2.22E+06 5.40E+04 O.OOE+00 3.80E+04 N/A TEEN 1. 16E+04 2.99E+04 1. 11E+04 1.92E+06 4.73E+04 O.OOE+00 3.32E+04 N/A CHILD 2.06E+04 3.72E+04 1.76E+04 3.29E+06 5.70E+04 O.OOE+00 2.83E+04 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.30E+04 6.03E+04 2.23E+04 3.98E+06 9.67E+04 O.OOE+00 6.81E+04 N/A INGEST. TEEN 2.97E+04 7.64E+04 2.83E+04 4.92E+06 1.21E+05 O.OOE+00 8.47E+04 N/A CHILD 6.34E+04 1.14E+05 5.40E+04 1.01E+07 1.75E+05 O.OOE+00 8.70E+04 N/A INFANT 7.88E+04 1.77E+05 6.4SE+04 1.59E+07 1.97E+05 O.OOE+00 6.40E+04 N/A INHAL. ADULT 2.68E+03 6.98E+03 2.57E+03 4.48E+05 1.11E+04 O.OOE+00 5.25E+03 N/A TEEN 3.70E+03 9.44E+03 3.49E+03 6.21E+05 1.49E+04 O.OOE+00 6.95E+03 N/A CHILD 4.92E+03 8.73E+03 4. 14E+03 7.92E+05 1.34E+04 0.000.00 4.44E+03 N/A INFANT 3.86E+03 7.60E+03 2.77E+03 6.96E+05 8.47E+03 O.OOE+00 1.83E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposi.tion pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS*** ~

GROUND: GROUND: GOAT COW TOTAL T; B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 .O.OOE+00 1.08E+07 5.05E+06 O.OOE+00 3.29E+06 1.59E+07 7.92E+05 PAGE: 4-30 (58 of 124)

DAT I

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Cs-136 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN I

GROUND ADULT 1.49E+08 1.49E+08 1:49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 TEEN 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49808 1.49E+08 1.49E+08 1.69E+08

\

CHILD 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 INFANT- 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 GOAT ADULT 3.57E+08 1.41E+09 1.01E+09 O.OOE+00 7.84E+08 1.07E+08 1.60E+08 N/A MILK TEEN 6.07E+08 2.39E+09 1.61E+09 O.OOE+00 1.30E+09 2.05E+08 1.92E+08- N/A CHILD 1.37E+09 3.77E+09 2.44E+09 O.OOE+00 2.01E+09 2.99E+08 1.32E+08 N/A INFANT 8.93E+08 7.88E+09 2.94E+09 O.OOE+00 3. 14E+09 6.42E+08 1.20E+08 N/A COW ADULT 6.69E+07 2.64E+08 1.90E+08 O.OOE+00 1.47E+08 2.02E+07 3. OOE+07 N/A MILK TEEN 1. 14E+08 4.48E+08 3.01E+08 O.OOE+00 2.44E+08 3.85E+07 3.'61E+07 N/A CHILD 2.57E+08 7.07E+08 4.58E+08 O.OOE+00 3.77E+08 5.62E+07 2.48E+07 N/A INFANT 5.02E+08 1.48E+09 5.52E+08 O.OOE+00 5.89E+08 1.20E+08 2.24E+07 N/A MEAT ADULT, 4.00E+06 1.58E+07 1. 14E+07 O.OOE+00 8.78E+06 1.20E+06 1. 79E+06 N/A TEEN 3. 12E+06 1.23E+07 8.24E+06 O.OOE+00 6.68E+06 1.05E+06 9.87E+05 N/A CHILD 5.38E+06 1.48E+07 9.57E+06 O.OOE+00 7.87E+06 1. 17E+06 5.20E+05'.OOE+00 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00f+00 N/A VEGTBLE ADULT 2.03E+07 8.01E+07 5.76E+07 O.OOE+00 4.46E+07 6. 11E+06 9. 10E+06 N/A TEEN 2.43E+07 9.58E+07 6.43E+07 O.OOE+00 5.21E+07 8.22E+06 7. 71E+06 N/A CHILD 4.96E+07 1.36E+08 8.82E+07 O.OOE+00 7.26E+07 1.08E+07 4.79E+06 N/A INFANT O.OOE+00 O.OOE+00 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 4.48E+08 1.77E+09 1.27E+09 O.OOE+00 9.84E+08 1.35E+08 2.01E+08 N/A INGEST. TEEN 7.49E+08 2.95E+09 1.98E+09 O.OOE+00 1.60E+09 2.53E+08 2.37E+08 N/A CHILD 1.68E+09 4.63E+09 2.99E+09 O.OOE+00 2.46E+09 3.67E+08 1.63E+08 N/A INFANT 1.40E+09 9.35E+09 3.49E+09 O.OOE+00 3.73E+09 7.62E+08 1.42E+08 N/A INHAL. ADULT 3.90E+04 1.46E+05 1.10E+05 O.OOE+00 8.56f+04 1.20E+04 1.17E+04 N/A TEEN 5. 15E+04 1.94E+05 '1.37E+05 0.00f+00 1. 10E+05 1.78E+04 1.09E+04 N/A CHILD 6.51E+04 1.71E+05 1. 16E+05 O.OOE+00 9.55E+04 1.45E+04 4. 18E+03 N/A INFANT 4.83E+04 1.35E+05 5.29E+04 O.OOE+00 5.64E+04 1. 18E+04 1.43E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T. B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

.1.49E+08* 1.69E+08 7.88E+09 1.48E+09 1.58E+07 1;36f+08 9.35E+09 1.94E+05 PAGE: 4-31 (59 of 124)

OAV

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Cs-137 PATHWAY AGE'GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 1.02E+10 1.02E+10 1;02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.19E+10 TEEN 1.02E+10 1.02E+10 1.02E+10 1;02E+10 1.OR&40 1.02E+10 1.02E+10 1.19E+10 CHILD 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.19E+10 INFANT 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.02E+10 1.19E+10 GOAT ADULT 1.42E+10 1.94E+10 1.27E+10 O.OOE+00 6.59E+09 2.19E+09 3.76E+08 N/A MILK TEEN 2.58E+10 3.43E+10 1.19E+10 O.OOE+00 1.17E+10 4.53E+09 4.88E+08 -

N/A CHILD 6.20E+10 5.94E+10 8.77E+09 O.OOE+00 1.94E+10 6.96Et09 3.72E+08 N/A INFANT 3.30E+10 1.16E+l1 8.22E+09 O.OOE+00 3.11E+10 1.26E+10 3.62E+08 N/A COW ADULT '.78E+09 5.17E+09 3.39E+09 O.OOE+00 1.76E+09 5.84E+08 1.00E+08 N/A MILK TEEN 6.86E+09 9.12E+09 3. 18E+09 O.OOE+00 3.10E+09 1.21E+09 1.30E+08 N/A CHILD 1.65E+10 1.58E+10 2.33E+09 O.OOE+00 5.15E+09 1.85E+09 9.90E+07 N/A INFANT 2.64E+10 3.09E+10 2.19E+09 O.OOE+00 8.28E+09 3.35E+09 9.65E+07 N/A MEAT ADULT 4.91E+08 6. 71E+08 4.40E+08 O.OOE+00 2. 28E+08 7.58E+07 1.30E+07 N/A TEEN 4.08E+08 5.42E+08 1.89E+08 O.OOE+00 1.85E+08 7.17E+07 7.72E+06 N/A CHILD 7.51E+08 7. 19E+08 1.06E+08 O.OOE+00 2.34E+08 8.42E+07 4.50E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 5.76E+09 7.88E+09 5.16E+09 O.OOE+00 2.68E+09 8.89E+08 1.53E+08 N/A TEEN 9.58E+09 1.27E+10 4.44E+09 0.00E+00 4.34E+09 1.69E+09 1.81E+08 N/A CHILD 2.29E+10 2.19E+10 3.24E+09 O.OOE+00 7.15E+09 2.57E+09 1.37E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 2.42E+10 3.32E+10 2.17E+10 O.OOE+00 1.13E+10 3.74E+09 6.42E+08 N/A INGEST. TEEN 4.26E+10 5.67E+10 1.97E+10 O.OOE+00 1.93E+10 7.49E+09 8.06E+08 N/A CHILD 1.02E+ll 9.79E+10 1.44E+10 O.OOE+00 3.19E+10 1.15E+10 6.13E+08 N/A INFANT 5.94E+10 1.47E+ll 1.04E+10 O.OOE+00 3.94E+10 1.60E+10 4.59E+08 N/A INHAL. ADULT 4.78E+05 6.21E+05 4.28E+05 O.OOE+00 2.22E+05 7.52E+04 8.40E+03 N/A TEEN 6.70E+05 8.48E+05 3.11E+05 O.OOE+00 3.04E+05 1.21E+05 8.48E+03 N/A CHILD 9.07E+05 8.25E+05 1.28E+05 O.OOE+00 2.82E+05 1.04E+05 3.62E+03 N/A INFANT 5.49E+05 6. 12E+05 4.55E+04 O.OOE+00 1.72E+05 7. 13E+04 1.33E+03 N/A BONE LIVER T.BODY THYROID KIDNEY L NG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• "*MAXIMUMVALUES FOR PATHWAYS***

GROUND'ROUND: GOAT COW TOTAL

.T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

.1.02E+10'.19E+10 1.16E+ll 3.09E+10 7.51E+08 2.29E+10 1.47E+11 9.07E+05 PAGE'-32 (60 of 124)

O.D.C.H. MAXIMUM-PATHWAYDOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Ba-140 PATHWAY AGE GROUP BONE 'IVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 2.03E+07 2.03E+07 2;03E+07 2.03E+07 2.03D07 2.03E+07 2.03E+07 2.32E+07 TEEN 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03B97 2.03E+07 2.03E+07 2.32E+07 CHILD 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.32E+07 INFANT 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.32E+07 GOAT ADULT 1.46E+06 1.83E+03 9.54E+04 O.OOE+00 6.22E+02 1.05E+03 3.00E+06 N/A NILK TEEN 2.63E+06 3.22E+03 1.69E+05 O.OOE+00 1.09E+03 2. 17Et03 4.05E+06 . N/A CHILD 6.35E+06 5.56E+03 3.70E+05 0.00E+00 1.81E+03 3.31E+03 3.22E+06 N/A INFANT 1.09E+08 1.31E+04 6.73E+05 O.OOE+00 3. 10E+03 8.02E+03 3.21E+06 N/A COW ADULT 6.83E+06 8.58E+03 4.47E+05 O.OOE+00 2.92E+03 4.91E+03 1.41E+07 N/A HI LK TEEN 1.23E+07 1.51E+04 7.94E+05 O.OOE+00 5.12E+03 1.02E+04 1.90E+07 N/A CHILD 2.97E+07 2.61E+04 1.74E+06 O.OOE+00 8.48E+03 1.55E+04 1.51E+07 N/A INFANT 6. 12E+07 6. 12E+04 3. 15E+06 O.OOE+00 1.45E+04 3.76E+04 1.50E+07 N/A MEAT ADULT 9.52E+06 1.20E+04 6.24E+05 O.OOE+00 4.07E+03 6.85E+03 1.96E+07 N/A TEEN 7.87E+06 9.65E+03 5.07E+05 O.OOE+00 3.27E+03 6.49E+03 1.21E+07 N/A CHILD 1.45E+07 1.27E+04 8.48E+05 O.OOE+00 4. 14E+03 7.59E+03 7.36E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 5.98Et07 7.51E+04 3.92E+06 O.OOE+00 2.55E+04 4.30E+04 1.23E+08 N/A TEEN 7.50E+07 9.19E+04 4.83E+06 O.OOE+00 3.12E+04 6.18E+04 1.16E+08 N/A CHILD 1.62E+08 1.42E+05 9.48E+06 O.OOE+00 4.63E+04 8.48E+04 8.23E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 7.76E+07 9.75E+04 5.08E+06 O.OOE+00 3.31E+04 5.58E+04 1.60E+08 N/A INGEST. TEEN 9.78E+07 1.20E+05 6.31E+06 O.OOE+00 4.07E+04 8.06E+04 1.51E+08 N/A CHILD 2. 13E+08 1.87E+05 1.24E+07 O.OOE+00 6.08E+04 l. 11E+05 1.08E+08 N/A INFANT 1.70E+08 7.43E+04 3.83E+06 O.OOE+00 1.76E+04 4.56E+04 1.82E+07 N/A INHAL. ADULT 3.90E+04 4.90E+Ol 2.57E+03 O.OOE+00 1.67E+01 1.27E+06 2.18E+05 N/A TEEN 5.47E+04 6.94E+Ol 3.52E+03 O.OOE+00 2.28E+01 2.03E+06 2.29E+05 N/A CHILD 7.40E+04 6.48E+Ol 4.33E+02 O.OOE+00 2. 11E+01 1.74E+06 1.02E+05 N/A INFANT 5.60E+04 5.60E+01 2.90E+03 O.OOE+00 1.34E+01 1.60E+06 3.84E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3, Deposition pathways: units are mrem-m2/yr/uCi/sec

• "*MAXIMUMVALUES FOR PATHWAYS*"*

GROUND: GROUND: GOAT COW TOTAL-T'.B./ORG. SKIN MILK: MILK: NEAT: VEGTBLE: INGEST: INHAL.

.2.03E+07 2.32E+07. 1.09E+08 6.12E+07 1.96E+07 1.62E+08 2. 13E+08 2.03E+06 PAGE: 4-33 OAV (61 of 124)

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: La-140 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.oof+00 0;Oof+00 O.OOE+00 0.00<boa O.DOE+00 O.DOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.08&NO O.OOE+00 O.OOE+00 O.OOE+00 CHILD 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 2.44E-Ol 1.23E-01 3.25E-02 0.00fw00 O.OOE+00 O.OOE+00 9.02E+03 N/A HILK TEEN 4.38E-Ol 2. 15E-01 5.72E-02 O.OOE+00 O.OOE+00 O.OOE+00 1.24E+04 N/A CHILD 1.05E+00 3.66E-01 1.23E-01 0.00E+00 0.00E+00 0.00E+00 1.02E+04 N/A INFANT 1.82E+01 8.63E-01 2.22E-01 O.OOE+00 O.OOE+00 O.OOE+00 1.01E+04 N/A COW ADULT 1.14E+00 5.73E-Ol 1.51E-Ol O.OOE+00 O.OOE+00 O.OOE+00 4.2lf+04 N/A MILK TEEN 2.04E+00 1.00E+00 2.67E-Ol 0.00E+00 0.00E+00 0.00E+00 5.'76E+04 N/A CHILD 4.89E+00 1.71E+00 5.76E-01 O.OOE+00 O.OOE+00 O.OOE+00 4.76E+04 N/A INFANT 1.02E+Ol 4.03E+00 1.04E+00 O.OOE+00 O.OOE+00 O.OOE+00 4.73E+04 N/A HEAT ADULT 1.22E-02 6. 16E-03 1.63E-03 O.OOE+00 O.OOE+00 O.OOE+00 4.53E+02 N/A TfEN 1.01E-02 4.94E-03 1.32E-03 O.OOE+00 O.OOE+00 O.OOE+00 2.84E+02 N/A CHILD 1.84E-02 6.44E-03 2.17E-03 O.OOE+00 O.OOE+00 O.OOE+00 1.79E+02 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A EGTBLE ADULT 6.53E+02 3.29E+02 8.69E+Ol O.OOE+00 O.OOE+00 O.OOE+00 2.41E+07 N/A TEEN 5.96E+02 2.93E+02 7.79E+Ol O.OOE+00 O.OOE+00 O.OOE+00 1.68E+07 N/A CHILD 1.07E+03 3.74E+02 1.26E+02 O.OOE+00 O.OOE+00 O.OOE+00 1.04E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 0 OOE+00 O.OOE+00 O.OOE+00 O.OOE+00

~ N/A TOTAL ADULT 6.54E+02 3.30E+02 8.71E+Ol O.OOE+00 O.OOE+00 O.OOE+00 2.42E+07 N/A INGEST. TEEN 5.99E+02 2.94E+02 7.83E+Ol 0.00f+00 O.OOE+00 O.OOE+00 1.69E+07 N/A CHILD 1.08E+03 3,76E+02 1.27E+02 O.OOE+00 O.OOE+00 O.OOE+00 1.05E+07 N/A INFANT 2.85E+Ol 4.89E+00 1.26E+00 O.OOE+00 O.OOE+00 O.OOE+00 5.74E+04 N/A 1.74E+02 4.58f+01 O.OOE+00 O.OOE+00 1.36E+05 4.58E+05 N/A INHAL. ADULT TEEN 3.44E+02 4.79E+02 2.36E+02 6.26f+01 O.OOE+00 O.OOE+00 2. 14E+05 4.87E+05 '/A CHILD 6.44E+02 2.25E+02 7.55E+01 O.OOE+00 O.OOE+00 1.83E+05 2.26E+05 N/A INFANT 5.05E+02 2.00E+02 5.15E+Ol O.OOE+00 O.OOE+00 1.68E+05 8.48E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS*"*

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: NEAT: VEGTBLf: INGEST: INHAL.

O.OOE+00 O.OOE+00 1.24E+04 5.76E+04 4.53E+02 2.41E+07 2.42E+07 4.87E+05 PAGE: 4-34 (62 of 124) oar

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Ce-141 PATHWAY AGE GROUP BONE- LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E007 1.35E+07 1.52E+07 TEEN 1.35E+07 1.35E+07 1.35E+07 1.35E+07 14%+07 1.35E+07 1.35E+07 1.52E+07 CHILD 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35007 1.35EE07 1.52E+07 INFANT 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35Ew07 1.35E+07 1.52E+07 GOAT ADULT . 2.78E+02 1.88E+02 2. 13E+01 O.OOE+00 8.73E+01 O.OOE+00 7. 19E+05 N/A MILK TEEN 5. 10E+02 3.40E+02 3.91E+01 O.OOE+00 1.60E+02 O.OOE+00 9.74E+05 N/A CHILD 1.26E+03 6.26E+02 9.30E+Ol O.OOE+00 2.75E+02 O.OOE+00 7.81E+05 N/A INFANT 2.07E+04 1.52E+03 1.79E+02 O.OOE+00 4.68E+02 O.OOE+00 7.84E+05 N/A COW ADULT 1.41E+03 9.51E+02 1.08E+02 O.OOE+00 4.42E+02 O.OOE+00 3.64E+06 N/A MILK TEEN 2.58E+03 1.72E+03 1.98E+02 O.OOE+00 8. 11E+02 O.OOE+00 4.93E+06 N/A CHILD ,6.35E+03 3. 17E+03 4.70E+02 O.OOE+00 1.39E+03 O.OOE+00 3.95E+06 N/A INFANT 1.26E+04 7.68E+03 9.04E+02 O.OOE+00 2.37E+03 O.OOE+00 3.97E+06 N/A MEAT ADULT 5.11E+03 3.46E+03 3.92E+02 O.OOE+00 1.61E+03 O.OOE+00 1.32E+07 N/A TEEN 4.29E+03 2.87E+03 3.29E+02 O.OOE+00 1.35E+03 O.OOE+00 8.20E+06 N/A CHILD 8.08E+03 4.03E+03 5.99E+02 O.OOE+00 1.77E+03 O.OOE+00 5.03E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/

VEGTBLE ADULT 1.49E+05 1.01E+05 1.14E+04 O.OOE+00 4.69E+04 O.OOE+00 3.86E+08 N/

TEEN 2.38E+05 1.59E+05 1.83E+04 O.OOE+00 7.49E+04 O.OOE+00 4.55E+08 N/A CHILD 5.73E+05 2.86E+05 4.'25E+04 O.OOE+00 1.25E+05 O.OOE+00 3.57E+08 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.56E+05 1.06E+05 1.20E+04 O.OOE+00 4.90E+04 O.OOE+00 4.03E+08 N/A INGEST. TEEN 2.46E+05 1.64E+05 1.88E+04 O.OOE+00, 7.72E+04 O.OOE+00 4.69E+08 N/A CHILD 5.89E+05 2.94E+05 4.36E+04 O.OOE+00 1.29E+05 O.OOE+00 3.67E+08 N/A INFANT 3.33E+04 9.20E+03 1.08E+03 O.OOE+00 2.84E+03 O.OOE+00 4.75E+06 N/A INHAL. ADULT 1.99E+04 1.35E+04 1.53E+03 O.OOE+00 6.26E+03 3.62E+05 1.20E+05 N/A TEEN 2.84E+04 1.90E+04 2. 17E+03 O.OOE+00 8.88E+03 6. 14E+05 1.26E+05 N/A CHILD 3.92E+04 1.95E+04 2.90E+03 O.OOE+00 8.55E+03 5.44E+05 5.66E+04 N/A INFANT 2.77E+04 1.67E+04 1.99E+03 O.OOE+00 5.25E+03 5. 17E+05 2.16E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Depos.ition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

1.35E+07 1.52E+07 9.74E+05 4.93E+06 1.32E+07 4.55E+08 4.69E+08 6.14E+05 PAGE: 4-35 DAT (63 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Pr-143 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O,OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00@00 O.OOE+00 O.OOE+00 O.OOE+00 CHILD O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.056+00 0.00E+00 0:00E+00 0.00E+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 8.57E+00 3.44E+00 4.25E-01 O.OOE+00 1.98E+00 O.OOE+00 3.75E+04 N/A MILK TEEN 1.57E+Ol 6.28E+00 7.83E-Ol O.OOE+00 3.65E+00 O.OOE+00 '5.18E+04 N/A CHILD 3.89E+01 1.17E+Ol 1.93E+00 O.OOE+00 6.33E+00 O.OOE+00 4.20E+04 N/A INFANT 6.71E+02 3.01f+Ol 3.99E+00 O.OOE+00 1.12E+Ol O.OOE+00 4.25f+04 N/A COW ADULT 4.02E+Ol 1.61E+01 1.99E+00 O.OOE+00 9.31E+00 O.OOE+00 1.76E+05 N/A MILK TEEN 7.39E+Ol 2.95E+01 3.68E+00 O.OOE+00 1.71E+01 O.OOE+00 2.,43E+05 N/A CHILD 1.83E+02 5.49E+01 9.07E+00 0.00E+00 2.97E+Ol 0.00E+00 1.97E+05 N/A INFANT 3.78E+02 1.41E+02 1.87E+01 O.OOE+00 5.26E+Ol O.OOE+00 2.00E+05 N/A MEAT ADULT 6.96E+03 2.79E+03 3.45E+02 O.OOE+00 1.61E+03 O.OOE+00 3.05E+07 N/A TEfN 5.86E+03 2.34E+03 2.92E+02 O.OOE+00 1.36E+03 O.OOE+00 1.93E+07 N/A CHILD l. 11E+04 3.33E+03 5.50E+02 O.OOE+00 1.80E+03 O.OOE+00 1.20E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT 3.04E+04 1.22E+04 1.51E+03 O.OOE+00 7.04E+03 O.OOE+00 1.33E+08 N/A TEEN 4.00E+04 1.60E+04 1.99E+03 O.OOE+00 9.27E+03 O.OOE+00 1.31E+08 N/A CHILD 8.98fw04 2.69E+04 4.45E+03 O.OOE+00 1.46E+04 O.OOE+00 9.68E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 3.74E+04 1.50E+04 1.86E+03 O.OOE+00 8.67E+03 O.OOD 00 1.64E+08 N/A INGEST. TEEN 4.59E+04 1.83E+04 2.28E+03 O.OOE+00 1.07E+04 O.OOE+00 1.51E+08 N/A CHILD 1.01E+05 3.03E+04 5.01E+03 O.OOE+00 '1.64E+04 O.OOE+00 1.09E+08 N/A INFANT 1.05E+03 1.72E+02 2.27E+Ol O.OOE+00 6.38E+01 O.OOE+00 2.42E+05 N/A INHAL. ADULT 9.36E+03 3.75E+03 4.64E+02 O.OOE+00 2.16E+03 2.81E+05 2.00E+05 N/A TEEN, 1.34f+04 5.31E+03 6.62E+02 O.OOE+00 3.09E+03 4.83E+05 2.14E+05 N/A CHILD 1.85E+04 5.55E+03 9.]4E+02 O.OOE+00 3.00E+03 4.33E+05 9.73E+04 N/A INFANT 1.40E+04 5.24E+03 6.99E+02 0.00f+00 1.97E+03 4.33E+05 3.72E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 5. 18E+04 2.43E+05 3.05E+07 1.33E+08 1.64E+08 4.83E+05 PAGE: 4-36 (64 of 124)

OAV

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Ce-144 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 6.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88E+07 7.96E+07 TEEN 6.88E+07 6.88E+07 6;88E+07 6.88E+07 6.88B07 6.88E+07 6.88E+07 7.96E+07 CHILD 6.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88%07 6.88E+07 6.88E+07 7.96E+07 INFANT '.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88E+07 6.88E+07 7.96E+07 GOAT ADULT 2.60E+04 1.09E+04 1.39E+03 O.OOE+00 6.44E+03 O.OOE+00 8.78E+06 N/A MILK TEEN '.78E+04 1.98E+04 2.57E+03 O.OOE+00 1. 18E+04 O.OOE+00 1.20E+07 N/A CHILD 1. 18E+05 3.69E+04 6.28E+03 O.OOE+00 2.04E+04 O.OOE+00 9.63E+06 . N/A INFANT 1.41E+06 6.91E+04 9.46E+03 O.OOE+00 2.79E+04 O.OOE+00 9.68E+06 N/A COW ADULT 1.65E+05 6.91E+04 8.88E+03 O.OOE+00 4.10E+04 O.OOE+00 5.59E+07 N/A MILK TEEN 3.04E+05 1.26E+05 1.63E+04 O.OOE+00 7.52E+04 O.OOE+00 7.65E+07 N/A CHILD 7.50E+05 2.35E+05 4.00E+04 O.OOE+00 1.30E+05 O.OOE+00 6. 13E+07 N/A INFANT 1.07E+06 4.40E+05 6.02E+04 O.OOE+00 1.78E+05 O.OOE+00 6. 17E+07 N/A MEAT ADULT 7.55E+05 3. 16E+05 4.05E+04 O.OOE+00 1.87E+05 O.OOE+00 2.55E+08 N/A TEEN 6.36E+05 2.63E+05 3.42E+04 O.OOE+00 1.57E+05 O.OOE+00 1.60E+08 N/A CHILD 1.20E+06 3.76E+05 6.40E+04 O.OOE+00 2.08E+05 O.OOE+00 9.80E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 2.94E+07 1.23E+07 1.58E+06 O.OOE+00 7.30E+06 O.OOE+00 9.95E+09 N/A TEEN 4.95E+07 2.05E+07 2.66E+06 O.OOE+00 1.22E+07 O.OOE+00 1.24E+10 N/A CHILD 1.21E+08 3.80E+07 6.46E+06 O.OOE+00 2. 10E+07 O.OOE+00 9.90E+09 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 3.04E+07 1.27E+07 1.63E+06 O.OOE+00 7.53E+06 O.OOE+00 1.03E+10 N/A INGEST. TEEN 5,.05E+07 2.09E+07 2.71E+06 O.OOE+00 1.25E+07 O.OOE+00 1.27E+10 N/A CHILD 1.23E+08 3.86E+07 6.57EE06 O.OOE+00 .2.14007 O.OOE+00 1.01E+10 N/A INFANT 2.48E+06 5.09E+05 6.97E+04 O.OOE+00 2.06E+05 O.OOE+00 7. 14E+07 N/A INHAL. ADULT 3.43E+06 1.43E+06 1.84E+05 O.OOE+00 8.48E+05 7.78E+06 8. 16E+05 N/A TEEN 4.89E+06 2.02E+06 2.62E+05 O.OOE+00 1.21E+06 1.34E+07 8.64E+05 N/A CHILD 6.77E+06 2. 12E+06 3.61E+05 O.OOE+00 1. 17E+06 1.20E+07 3.89E+05 N/A INFANT 3. 19E+06 1.21E+06 1.76E+05 O.OOE+00 5.38E+05 9.84E+06 1.48E+05 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUM.VALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL .

T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

6.88E+07 7.96E+07 1.20E+07 7.65E+07 2.55E+08 1.24E+10 1.27E+10 1.34E+07 PAGE: 4-37 DAT (65 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Pr-144 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 TEEN 0.00E+00 O.OOE+00 0;OOE+00 O.OOE+00 O.OOEi00 O.OOE+00 O.OOE+00 O.OOE+00 CHILD 0. OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00640 0.00E+00 0.00E+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A MILK TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A CHILD 0. OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 ~

N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A COW ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A MILK TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A MEAT ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A GTBLE ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOEt00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INGEST. TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A CHILD O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A INHAL. ADULT 3. 01E-02 1.25E-02 1.53E-03 O.OOE+00 7.05E-03 1.02E+03 2.15E-08 N/A TEEN 4.30E-02 1.76E-02 2. 18E-03 O.OOE+00 1.01E-02 1.75E+03 2.35E-04 N/A CHILD 5.96E-02 1.85E-02 3.00E-03 O.OOE+00 9.77E-03 1.57E+03 1.97E+02 N/A INFANT 4.79E-02 1.85E-02 2.41E-03 O.OOE+00 6.72E-03 1.61E+03 4.28E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS***

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: 'EAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 4.28E+03 PAGE: 4-38 (66 of 124)

O.D.C.M. MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHfR THAN NOBLE GASES*

ISOTOPE: Nd-147 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06 TEEN 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06 CHILD 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06 INFANT 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06 GOAT ADULT 5.09E+00 5.89E+00 3.52E-Ol O.OOE+00 3.44E+00 O.OOE+00 2.83E+04 N/A MILK TEEN 9.80E+00 1.07E+Ol 6.38E-01 O.OOE+00 6.26E+00 O.OOE+00 3.84E+04 N/A CHILD 2.40E+01 1.95E+01 1.51E+00 0.'OOE+00 1.07E+01 O.OOE+00 3.09E+04 N/A INFANT 3.97E+02 4.90E+Ol 3.00E+00 O.OOE+00 1.89E+Ol O.OOE+00 3. 10E+04 N/A COW ADULT 2.38E+01 2.75E+Ol 1.65E+00 O.OOE+00 1.61E+01 O.OOE+00 1. 32E+05 N/A MILK TEEN 4.58E+Ol 4.98E+Ol 2.98E+00 O.OOE+00 2.93E+Ol O.OOE+00 1. 80E+05 N/A CHILD 1.12E+02 9.11E+Ol 7.05E+00 O.OOE+00 5.00E+Ol O.OOE+00 1.44E+05 N/A

'NFANT 2.23E+02 2.29E+02 1.40E+Ol O.OOE+00 8.82E+Ol O.OOE+00 1.45E+05 N/A MEAT ADULT 2.34E+03 2.70E+03 1.62E+02 O.OOE+00 1.58E+03 O.OOE+00 1. 30E+07 N/A TEEN 2.06E+03 2.24E+03 1.34f+02 O.OOE+00 1.31E+03 O.OOE+00 8.08E+06 N/A CHILD 3.86E+03 3. 13E+03 2.42E+02 0.00f+00 1.72E+03 O.OOE+00 4.96E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 N/

VEGTBLE ADULT 1.39E+04 1.61E+04 9.61E+02 O.OOE+00 9.39E+03 O.OOE+00 7. 71E+07 N/A TEEN '1.72E+04 1.87E+04 1. 12E+03 O.OOE+00 1. 10f+04 O.OOE+00 6.74E+07 N/A CHILD 3.65E+04 2.95E+04 2.29E+03 O.OOE+00 1.62E+04 O.OOE+00 4.68E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 N/A TOTAL ADULT 1.63E+04 1.88E+04 1. 12E+03 O.OOE+00 l. 10E+04 O.OOE+00 9. 03E+07 N/A INGEST. TEEN 1.93E+04 2. 10E+04 1.26E+03 O.OOE+00 1.23E+04 O.OOE+00 7.57E+07 N/A CHILD 4.05E+04 3.28E+04 2.54E+03 O.OOE+00 1.80E+04 O.OOE+00 5. 19E+07 N/A INFANT 6.20f+02 2.78E+02 1.70E+Ol O.OOE+00 1.07E+02 O.OOE+00 1.76E+05 N/A INHAL. ADULT 5.27E+03 6.10E+03 3.65E+02 O.OOE+00 3.56E+03 2.21E+05 1.73E+05 N/A TEEN 7.86E+03 8.56E+03 5. 13E+02 O.OOE+00 5.02E+03 3.72E+05 1.82E+05 N/A CHILD 1.08E+04 8.73003 6.81E+02 O.OOE+00 4.81E+03 3.28E+05 8.21E+04 N/A INFANT 7.94E+03 8..13f+03 5.00E+02 O.OOE+00 3. 15E+03 3.22E+05 3.12E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tritium ingestion: units are. mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

• • • MAXIMUMVALUES FOR PATHWAYS"*"

GROUND'ROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

8.31E+06 9.97E+06 3.84E+04 1.80E+05 1.30E+07 7.71E+07 9.03E+07 3.72E+05 PAGE: 4-39 (67 of 124)

(

o.

O.D.C.M.

~ ~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE: Np-239 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I; SKIN GROUND ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 CHILD 0.00f+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 1.98E-01 1.95E-02 1.08E-02 O.OOE+00 6.08E-02 O.OOE+00 4.00E+03 N/A MILK TEEN 3.79E-01 3.57E-02 1.98E-02 O.OOE+00 1.12E-01 O.OOE+00 5.74E+03 N/A CHILD 9.32E-Ol 6.69E-02 4.70E-02 O.OOE+00 1.93E-01 O.OOE+00 4.95E~03 N/A INFANT 1.64E+Ol 1.76E-01 9.96E-02 O.OOE+00 3.5lf-01 O.OOE+00 5.09E+03 N/A COW ADULT 9. 26E-01 9. 10E-02 5. 02E-02 0. OOE+00 2.84E-01 O.OOE+00 1.87E+04 N/A MILK TfEN 1.77E+00 1.67E-01 9.25E-02 O.OOE+00 5.23E-01 0.00E+00 2.68E+04 N/A CHILD 4.35E+00 3. 12E-Ol 2. 19E-Ol O.OOE+00 9.02E-Ol O.OOE+00 2. 31E+04 N/A INFANT 9. 19E+00 8.22E-01 4.64E-Ol O.OOE+00 1.64E+00 O.OOE+00 2.38f+04 N/A MEAT ADULT 8.54E-02 8.40E.-03 4.63E-03 O.OOE+00 2.62E-02 O.OOE+00 1. 72E+03 '/A TEEN 7.47E-02 7.04E-03 3.91E-03 O.OOE+00 2.21E-02 O.OOE+00 1.13E+03 N/A CHILD 1.41E-01 1.01E-02 7.09E-03 O.OOE+00 2.92E-02 O.OOE+00 7.47E+02 N/A INFANT 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A VEGTBLE ADULT 4.71E+02 4.63E+01 2.55E+01 O.OOE+00 1.45ft02 O.OOEw00 9.50006 N/A TEEN 4.57E+02 4.31E+Ol 2.40E+Ol O.OOE+00 1.35E+02 O.OOE+00 6.94E+06 N/A CHILD 8.44E+02 6.06E+Ol 4.26E+Ol O.OOE+00 1.75E+02 O.OOE+00 4.49E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOBOO N/A TOTAL ADULT 4.72E+02 4.64E+01 2.56E+Ol O.OOE+00 1.45E+02 O.OOE+00 9.53E+06 N/A INGEST. TEEN 4.60E+02 4.33E+Ol 2.41E+01 O.OOE+00 1.36E+02 O.OOE+00 6.97E+06 N/A CHILD 8.50E+02 6.10E+Ol 4.29E+Ol 0.00E+00 1.76E+02 0.00E+00 4.52E+06 N/A INFANT 2.56E+01 9.98E-Ol 5.64E-Ol O.OOE+00 1.99E+00 O.OOE+00 2.89E+04 N/A INHAL. ADULT 2.30E+02 2.26E+Ol 1.24E+Ol O.OOE+00 7.00E+Ol 3.76E+04 1.19fw05 N/A TfEN 3.38E+02 3,19E+Ol 1.77E+Ol O.OOE+00 1.00f+02 6.49E+04 1.32E+05 N/A CHILD 4,66E+02 3.34E+01 2.35E+Ol O.OOE+00 9.73E+01 5.81E+04 6.40E+04 N/A INFANT 3.71E+02 3.32E+Ol 1.88E+01 O.OOE+00 6.62E+Ol 5.95E+04 2."49E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN

• Airborne pathways and tntium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec

-""*MAXIMUMVALUES FOR PATHWAYS*"*

'ROUND: GROUND: GOAT COW TOTAL

'.B./ORG. SK IN MILK: MILK: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 O.OOE+00 5.74E+03 2.68E+04 1.72E+03 9.50E+06 9.53906 1.32E+05 PAGE: 4-40

( OAr (68 of 124)

5.0 U

- THE DOSE OR DOSE COMMITMENT TO A MEMBER OF THE PUBLIC FROM RADIOACTIVE MATERIALS IN LIQUID EFFLUENTS RELEASED FROM EACH REACTOR UNIT TO UNRESTRICTED AREAS (SEE FIGURE 5.1.3-1) SHALL BE LIMITED:

a. DURING ANY CALENDAR QUARTER TO LESS THAN OR EQUAL TO 1.5 MREM TO THE TOTAL. BODY AND TO LESS THAN OR EQUAL TO 5 MREM TO ANY ORGAN, AND

b. DURING ANY CALENDAR YEAR TO LESS THAN OR EQUAL TO 3 MREM TO THE TOTAL BODY AND TO LESS THAN OR EQUAL TO 10 MREM TO ANY ORGAN.

The calculations of dose received by the hypothetical maximally exposed individual from the ingestion of fish and drinking water are based on the nearest public drinking water intake location (Danville Mater Authority).

Dose contributions from recreation, boating, and swimming have been shown to be negligible in the NRC 10 CFR 50 Appendix I dose analysis (June "1976) and do not need to be routinely evaluated.

The following expression is used to calculate the ingestion pathway dose contributions for the total release period for each batch release from all radionuclides identified in the liquid effluents released to unrestricted areas:

D Z) A) (ht Ci F) (Eq. 10) where:

D, the cumulative dose commitment to the total body or any organ (v) from the liquid effluents for the time period, ht, of each batch release (mrem).

ht the length ot" the time period for a batch release over which Ci and F are averaged for all liquid releases (hr).

Ci the average. concentration of radionuclide (i) in undiluted liquid effluent during time period, ht, for any liquid effluent batch release (uCi/ml).

21 DAT (69 of 124)

F the discharge line dilution factor for C during any liquid effluent batch release. Defined as the latin of the maximum undiluted liquid radwaste effluent line flow during release to the average flow from the plant discharge line to unrestricted receiving waters.

A the composite dose parameter for the total body or any organ (c) for each identified principal gamma and beta emitter (i)

(mrem/hr per uCi/ml) (see Equation 11, Table 5).

A(,~ k ((U + Uf BFi)/O ) OF), (Eq 11) where:

k I f t f l.l 10 5

till6~cc 3 0 MIMk 8760 hr/yr U a receptor person's water consumption by age group from Regulatory Guide 1.109, Table E-5.

Ow the dilution factor from the near field area of the release point to potable water intake 321. (The nearest potable water intake is located at Oanville; dilution factors and transit times based on river level are also given in Table O-l of Appendix O. These dilution factors are based on fluorescent dye tracer studies conducted at various river levels during 1985.)

Uf a receptor person's fish consumption by age group from Regulatory Guide 1.109, Table E-5.

BFi the bioaccumulation factor for nuclide (i) in fish (pCi/kg per pCi/l) from Regulatory Guide 1.109, Table A-l.

OF<< the dose conversion factor for nuclide (i) in a receptor person for pre-selected organ (v), (mrem/pCi) from Regulatory Guide 1.109, Tables E-ll, E-12, E-13, and E-14.

The projected quarterly dose contribution from batch releases for which radionuclide concentrations are determined by periodic composite sample analysis, as stated in Table 4.11. 1.1.1-1 of the SSES Technical Specification may be approximated by assuming an average concentration based on the previous monthly or quarterly composite analysis.

(70 of 124) 22

However, for reporting purposes, the calculated dose contributions from radionuclides shall be based on the actual composite analysis. The cumulativ dose commitment to the total body or any organ for a quarterly or annual analysis shall be based on the calculated dose contributions from each batch release occurring during that time period.

In actual practice, the LADTAP computer code developed by the NRC to implement the liquid dose methodology of Regulatory Guide 1. 109 will be used to perform the individual liquid pathway dose calculations for the SSES. The methods outlined above are consistent with those of the LADTAP code; site specific dose factors have been computed and are available for implementing the method described above, if required.

A discussion of the LADTAP code is given in Section A.3.1 of Appendix A.

OEG g i egg 23 (71 of 124)

TABLE 5 MATERBORNE EFFLUENT DOSE PARAMETERS FOR ADULTS Fresh Mater Fish Ingestion Dose Factor Bioaccumulation Factor for Critical Organ Critical Dose Parameter (A. )

Radionuclide i k r Ci liter mrem Ci Or an mrem hr r uCi/hl H-3 .9 1.05E-7 Total )ody 2.446E-1 Mn-54 400 1.40E-5 GI-LLI 1.294E4 Fe-55 100 2.75E-6 Bone 6.360E2 Co-58 50 1.51E-5 GI-LLI 1.248E3 Fe-59 100 3.40E-5 GI-LLI 7.863E3 Co-60 50 4.02E-5 GI-LLI 4.653E3 Zn-65 2000 1.54E-5 Liver 7.115E4 Sr-89 30 3.08E-4 Bone 2. 142E4 Sr-90 30 7.58E-3 Bone 5.272E5 Ho-99 10 9.99E-6 GI-LLI 2.333E2 I-131 15 1.95E-3 Thyroid 6.806E4

~ Cs-134 2000 1.48E-4 Liver 6.838E5 Cs-137 2000 1.09E-4 Liver 5.036E5 Ce-141 1 2.42E-5 GI-LLI 6.196E1 Ce-144 1 1.65E-4 GI-LLI 4.224E2 Additional factors for isotopes not included in Table 5 may be calculated using the methodology described in NUREG-0133.

b GI-LLI gastro-intestinal tract. lower large intestine.

6.0 6.1

- THE AIR DOSE DUE TO NOBLE GASES RELEASED IN GASEOUS EFFLUENTS, FROM EACH REACTOR UNIT, TO AREAS AT AND BEYOND THE SITE BOUNDARY (SEE FIGURE 5.1.3-1) SHALL BE LIMITED TO THE FOLLOWING:

a. DURING ANY CALENDAR QUARTER: LESS THAN OR EQUAL TO 5 HRAD FOR GAMMA RADIATION AND LESS THAN OR EQUAL TO 10 MRAD FOR BETA RADIATION, AND

b. DURING ANY CALENDAR YEAR: LESS THAN OR EQUAL TO 10 HRAD FOR GNMA RADIATION AND LESS THAN OR EQUAL TO 20 HRAD FOR BETA RADIATION.

The air dose in unrestricted areas beyond the site boundary due to noble gases released in airborne effluents from the site shall be determined by the following equation for gama radiation during any specific time period:

D317x10$i Hi (X/Q)vQiv (Eq. 12) and by the following equation for beta radiation during any specified time period:

~ Ni ("/Q)v Qiv (Eq. 13)

Where:

the air dose factor due to gamma emissions for each identified noble g~s radionuclide (i)

(mrad/yr per uCi/m ) from Table 2.

Ni the air dose factor due to beta emissions for each identified noble ga~ radionuclide (i)

(mrad/yr per uCi/m ) from Table 2.

(X/Q)v the highest calculated annual average relative concentration for any area at or beyond the site boundary in an u]restricted area from vent release point (v) (sec/m ) such as from Table 3.

D a the total gamma air dose from gaseous effluents for g specified time period (mrad).

25 oAT (73 of 124)

Db the total beta air dose for gaseous effluents for a specified time period (mrad).

the integrated release of each identified noble gas radionuclide (i) in gaseous effluents from all vents (v) for a specified time period (uCi).

3.17 x 10 the inverse of seconds in a .year (yr/sec).

A discussion of the method used to calculate the individual dose from gaseous effluents is given in Section A.3.2 of Appendix A.

Also, sample calculations for determining gamma and beta air doses from noble gas radionuclides released from the SSES are given.

6.2 RAD ONUC T AN NOB G S CI CA ON 3 . .3 - THE DOSE TO A MEMBER OF THE PUBLIC FROM IODINE-131, TRITIUM, ANO ALL RADIONUCLIDES IN PARTICULATE FORM WITH HALF-LIVES GREATER THAN 8 DAYS IN GASEOUS EFFLUENTS RELEASED, FROM EACH REACTOR UNIT, TO AREAS AT ANO BEYOND THE SITE BOUNDARY (SEE FIGURE 5.1.3-1) SHALL BE LIMITED TO THE FOLLOWING:

a. DURING ANY CALENDAR QUARTER: LESS THAN OR EQUAL TO 7.5 MREMS TO ANY ORGAN, AND

b. DURING ANY CALENDAR YEAR: LESS THAN OR EQUAL TO 15 MREMS TO ANY ORGAN.

The critical organ dose to an individual from I-131, tritium, and radioactive materials in particulate form with half-lives greater than 8 days released in airborne effluents from the site to unrestricted areas can be determined by the following equation during any specified time period:

Dc 3.17 x 10 g, (Ri) (W ) (Qi ) (Eq. 14) 26 A V DAY C (74 of 124)

where:

p c

s the total dose to a critical organ from radio-nuclides other than noble gases for a specified time period (mrem).

Ri the dose parameter for each identified radionucli)e (i) .for the inhalation pathway (mrem/yr p~r uCi/m )

and for food and ground plane pathways (m mrem/yr per uCi/sec) from Table 4.

W v

the highest annual average dispersion parameter for estimating the dose to the critical3individual; relative concentration (X/g) (sec/m ) for the inh~lation pathway and relative deposition rate (p/g)

(m ) for the food and ground pathways such as from Table 3.

the integrated release of each identified radio-nuclide other than noble gases (i) in gaseous effluents from all vents (v) for a specified time period (uCi).

3.17 x 10 the inverse of seconds in a year (yr/sec).

In actual practice, the GASPAR computer code developed by the NRC to implement the airborne dose methodology of Regulatory Guide 1.109 will be used to perform the individual airborne pathway dose calculations for the SSES. The methods outlined above are consistent with those of the GASPAR code; site specific dose factors have been computed and are available for implementing the method described above, if required.

A discussion of the GASPAR code is given in Section A.3.2 of Appendix A; ~

27 (75 of 124)

. 4 4444 S C F 3 - THE ANNUAL (CALENDAR YEAR) 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 MREMS TO THE TOTAL BODY OR ANY ORGAN EXCEPT THE THYROID, MHICH SHALL BE LIMITED TO LESS THAN OR EQUAL TO 75 MREMS.

The cumulative dose to any member of the'ublic due to radioactive releases from the SSES site is determined by summing the calculated doses to critical organs from the previously discussed effluent sources. The annual dose to critical organs of a real individual for the liquid effluents is determined by using Equations 10 and ll of Section 5. The annual dose to critical organs of a real individual for the noble gases released in the gaseous effluents is determined by using Equation 12 modified by replacing Mi with Ki from Table 2 for the whole-body dose and by Equation 13 modified by replacing Ni by (Li + 1.1 Mi) from Table 2 for the skin dose of Section 6.0:

D3 41 1 7x 10Ki (X/Q)vQiv (Eq. 15)

Db3 1 7x1 0(Li +1 i )( /Q) (Eq 16)

The annual dose to critical organs of a real individual for the radionuclides other than noble gases released in the gaseous effluents is determined by using Equation 14 of Section 6.0. For all dose calculations from airborne effluents, the deposition rate used in the analysis should be at the receptor location of the individual being evaluated, not the highest calculated annual average relative concentration or relative deposition rate for any area at or beyond the site boundary as-given in Table 3. The direct radiation from the site should be determined from the environmental monitoring program's direct radiation (TLD) monitors. Since all other uranium fuel cycle sources are greater than 20 miled away, only the SSES site need be considered as a uranium fuel cycle source for meeting the EPA regulations.

In actual practice, the LADTAP and GASPAR computer code developed by the 28 Pl'AT (76 of 124)

NRC to implement the liquid and gaseous dose methodology of Regulatory Guide 1.109 will be used to perform the total dose calculations for the SSES. The methods outlined above are consistent with those of the LADTAP and GASPAR codes; site specific dose factors have been computed and are available for implementing the method described above, if required.

A discussion of the methods used to calculate the total dose to critical organs of a real individual is given in 'Section A.4 of Appendix A.

29 hdl'V DAT (77 of >24)

S.O 8.1 S 0 3. - THE LIQUID RADWASTE TREATMENT SYSTEM, AS DESCRIBED IN THE OOCM, SHALL BE OPERABLE. THE APPROPRIATE PORTIONS OF THE SYSTEH SHALL BE USED TO REDUCE THE RADIOACTIVE MATERIALS IN LIQUID MASTE PRIOR TO THEIR DISCHARGE MHEN THE PROJECTED DOSES DUE TO THE LIQUID EFFLUENT, FROM EACH REACTOR UNIT, TO UNRESTRICTED AREA (SEE FIGURE 5.1.3-1) MOULD EXCEED 0.06 HREH TO THE TOTAL BODY OR 0.2 MREH'O ANY ORGAN IN A 31-DAY PERIOD.

The SSES liquid waste treatment system utilizes two 300 ft horizontal centrifugal discharge type filters with 200 gpm norma'l flow. Liquid from the filters enter a mixed bed demineralizer with a volume of 140 ft and normal flow rate of 200 gpm. High conductivity waste is treated in two stainless steel "pot boiler" evaporators which are heated with auxiliary steam. There are two chemical waste neutralization tanks with 28,000 gal capacity. Low conductivity liquid wastes are collected in three pairs of LRM surge tanks. A flow diagram of the liquid radwaste treatment system is shown in Figure 1.

Appropriate treatment for liquid effluents from SSES is defined in ODCN Policy Statement 10.6. In cases when a batch of liquid waste must be released with treatment less than that specified in Section 10.6, a dose assessment using LADTAP or the methodology of Section 5.0 shall be performed prior to release to ensure that the limits of Specification 3.11. 1.3 are not exceeded.

8.2 G S OUS M

- THE GASEOUS RADMASTE TREATMENT SYSTBl SHALL BE IN OPERATION.

A~PC T'IIIIEAEEER TIIE EA)E CIIIIOEACER AIR EJECTOR )EEACOATIOE)

SYSTEM IS IN OPERATION.

SP C C 0 3 THE APPROPRIATE PORTIONS OF THE VENTILATION, EXHAUST TREATMENT SYSTEM SHALL BE OPERABLE AND SHALL BE USED TO REDUCE RADIOACTIVE MATERIALS IN GASEOUS MASTE PRIOR TO THEIR DISCHARGE MHEN THE PROJECTED DOSES DUE TO GASEOUS EFFLUENT RELEASES FROM EACH REACTOR UNIT TO AREAS AT AND BEYOND THE SITE BOUNDARY (SEE 30 (78 of 124)

FIGURE $ .1.3-1) MHEN AVERAGED OVER 31 DAYS MOULD EXCEED 0.3 NREM TO ANY ORGAN IN A 31-DAY PERIOD.

The SSES offgas treatment system operates with four steam jet air ejectors maintaining. condenser vacuum. Noncondensible gases are passed through one of three recombiners (one for each reactor unit plus a common recombiner), reducing the amount of gases to be filtered and released. Gases pass through a two to nine minute holdup pipe before entering the offgas treatment system, which consists of one 100 percent capacity system per reactor unit. Each system consists of precoolers, chillers, reheaters, guard beds, and five charcoal absorbers and an outlet HEPA filter. Monitored, filtered air then exits to the turbine building vent. A flow diagram of the offgas and recombiner system"is shown in Figure 2.

Filtered exhaust systems serve selected areas of Zone I, II, and III of the SSES reactor building. The Zone I and Zone II equipment compartment and Zone III filtered exhaust systems each consist of two 100X capacity redundant fans and two 55X capacity filter trains.

Each filter train has, in the direction of air flow, roughing filters, upstream HEPA filters, a charcoal filter bed, and downstream HEPA filters. Exhaust fan discharge is then routed to the atmosphere via the reactor building vents, where effluents are continuously sampled and monitored.

The turbine building filtered exhaust system draws air from those areas of the building that are most likely to become contaminated.

Two 100X capacity fans serve each system, which contains two 50X capacity filter housings made up of a particulate prefilter, an upstream HEPA filter, a charcoal filter, and a downstream HEPA filter. Discharged air is released via the turbine building vents, which are continuously sampled and monitored.

The radwaste building filtered exhaust system draws potentially 31 DAT (79 of 124)

(

contaminated air from selected areas of the radwaste building. The system contains two 100X capacity fans and two SOX capacity filter housings, each containing a particulate filter bank and a HEPA filter. Filtered air is discharged via the turbine building vent.

In order to minimize the quantities of radioactivity in airborne effluents from the station, the ventilation exhaust treatment (filtered exhaust) systems are normally kept in service at SSES.

As the need arises, these systems are periodically rendered inoperable for maintenance or testing activities. If the most recent 31-day dose projection indicates that dose may exceed 0.3 mrem to any organ when averaged over the projected 31-day period, treatment systems rendered inoperable will be restored to operable status as quickly as is practicable.

The dose projections are performed at least once per 31 days based on the most recently available effluent data. If it is known prior to performing the dose projection that a treatment system will be out of service, and if data exists which indicates how the lack of treatment will impact effluents, these factors, will be considered when performing the dose projection.

8.3 S C C T 0 3 - THE SOLID RADWASTE SYSTEM SHALL BE USED IN ACCORDANCE WITH A PROCESS CONTROL PROGRN, FOR THE PROCESSING AND PACKAGING OF RADIOACTIVE WASTES TO ENSURE MEETING THE RE(UIREHENTS OF 10 CFR PART 20, 10 CFR PART 71, AND FEDERAL REGULATIONS COVERING THE DISPOSAL OF THE WASTE.

The SSES solid r adwaste system was designed to solidify all wet wastes for ultimate offsite disposal. There are two Backwash Receiving Tanks, one per unit, which collect two filter-demineralizer backwashes per tank (2450 gal capacity). Air spargers for resin mixing are driven by instrument air. Regeneration Waste Surge Tanks (4) and Phase Separators (3) have internal mixing 32 A rV OAT (80 of 124)

eductors for sludge mixing driven by recirculation flow. The Spent Resin Tank has a reversible progressing cavity pump and internal mixing eductors. Two solidification trains have waste mixing tank progressing cavity feed and mixing pumps, and screw conveyors for feeding of dry Portland cement. Mixing is facilitated by the addition of sodium silicate. Common solidification equipment includes waste container fillport, transfer cart, capper washdown station, and swipe tool; cement silo with rotary feed valve, aeration blower, baghouse, and exhaust fan; sodium silicate tank and pump.

Vendor solidification services may be used in accordance with the SSES Process Control Program to supplement the plant solidification system or to take the place of the plant system when the plant system is out of service.

A flow diagram of the SSES solid radwaste treatment system is shown in Figure 3. Dry contaminated waste processing is depicted in Figure 4.

Dry contaminated solids may be compacted with a drum compactor into 55-gallon drums or with a box compactor into steel boxes. The trash compactors utilize hydraulic press pistons with exhaust fans and HEPA filters. In addition, dry contaminated solids may.be processed using vendor supercompaction and incineration services. An automated dry active waste (DAM) monitoring system is used to segregate radioactive from.non-radioactive solid waste.

k 33 A

DAT (81 of 124)

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CO CQCENTSILTE VhPORATOS h

STOhhOE TIWf.

O 01SCHhhOE OP QTS

FIMK 5 SSES Nk CLNININIED ISIE PltXESMI pe/fr) yleetlcg ps+i' s Clothing Second+ rt Cmtaainatld Dry Solid kste Dry Solid Rste Pry Scrive lhste (NN) itaring System Iexhr Services Miolctive Box Qpsreeepetim Gepehr InciteratitN N. ~

Free lhleasld 55~1. 0nas or Saxss 37.

A DAT (85 of 124)

9.0 R NTA MON TOR NG OGRA

9.1 Meekly

Once in each calendar week at intervals of approximately 7 days, plus or minus 2 days.

Semi-Monthly: Twice each calendar month at intervals of approximately 15 days, plus or minus 4 days.

Monthly: Once each calendar month at intervals of approximately 30 days, plus or minus 6 days.

quarterly: Once in each three month period of a calendar year at intervals of approximately 13 weeks, plus or minus 3 weeks.

9.2 AT 3 . - THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SHALL BE CONDUCTED AS SPECIFIED IN TABLE 3.12.1-1.

Environmental samples shall be collected and analyzed (as a minimum) according to Table 6 at locations shown in Figures 5 and 6.

Analytical techniques used shall ensure that the detection capabilities in Table 7 are achieved.

A dust loading study (RMC-TR-81-01) was conducted to assure that the proper transmission factor was used in calculating gross beta activity of air particulate samples. This study concluded that the sample collection frequency of once per week was sufficient and that the use of 1 for the transmission correction factor for gross beta analysis of air particulate samples is valid.

h The charcoal sampler cartridges used in the airborne radioiodine sampling progr am (Science Applications, Inc., Model CP-100) are designed and'ested by the manufacturer to assure a high quality of radioiodine capture. A certificate from the manufacturer is supplied and retained with each batch of cartridges certifying the percent retention of radioiodine versus air flow rate through the cartridge.

38 cw4 ~

7 DAT (86 of 124)

The results of the radiological environmental monitoring program are intended to supplement the results of the radiological effluent monitoring by verifying that the measurable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and modeling of the environmental exposure pathways. Thus,. the specified environmental monitoring program provides measurements of radiation and of radioactive materials in those exposure pathways and for those radionuclides which lead to the highest potential radiation exposures of individuals resulting from station operation. Program changes may be proposed based on operational experience. Deviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment,Pand other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, an 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 documented in the annual report.

Reporting requirements for the radiological environmental su} veillance program are given in Appendix B.

9.3 ~UNRUR PRIIN SP C C 0 - A LAND-USE CENSUS SHALL BE CONDUCTED AND, SHALL IDENTIFY WITHIN A DISTANCE OF 8 KH (5 MILES) THE LOCATION IN EACH OF THE 16 HETEOROLOGICAL SECTORS OF THE NEAREST MILK ANIMAL, THE NEAREST RESIDENCE AND THE NEAREST GARDEN* OF GREATER THAN 50 M~

(500 FT~) PRODUCING BROAD LEAF VEGETATION.

• Broad leaf vegetation sampling of at least three different kinds of vegetation may be performed at the site boundary in each of two direction sectors with the highest predicted 0/g's in lieu of the garden census. Specifications for broad leaf vegetation sampling in Table 3.12.1-1, item 4C shall be followed, including analysis of:.control, samples.

39 OAT

,(87 of 124)

If a land use census identifies a location(s) with a,higher average annual deposition rate (D/Q) than a current indicator location, the following shall apply:

l. If the D/Q is at least 20 percent greater than a previously high D/Q, the new location shall be added to the program within 30 days of documented identification of sampling feasibility. The indicator location having the lowest D/Q may be dropped from the program after October 31st of the year in which the land use census was conducted.

2. If the D/Q is gyt 20 percent greater than the previously highest D/Q, direction, distance, and D/Q will be considered in deciding whether to replace one of the existing sample locations. If applicable, replacement shall be within 30 days.

Any evaluations of possible location replacement should include the past history of the location, availability of sample, milk production history, and other applicable environmental conditions.

A land use census will be conducted at least once per calendar year by a door-to-door or aerial survey, by consulting local agricultural authorities, or by any combination of these methods.

9.4 I T BO CO P ISON OG SP C T 0 3. 3 - ANALYSES SHALL BE PERFORMED ON RADIOACTIVE MATERIALS SUPPLIED AS PART OF AN INTERLABORATORY COMPARISON PROGRAM WHICH HAS BEEN APPROVED BY THE COMMISSION.

The laboratories of the licensee and licensee's contractors which perform analyses shall participate in the Environmental Protection

. Agency's (EPA's) Environmental Radioactivity Laboratory

.. Intercomparisons Studies (Crosscheck) Program or an equivalent program which has been approved by the Comnission. This participation shall include some of the determinations (sample medium-radionuclide combination) that are offered by EPA and that are 40 DAT (88 of 124)

also included in the monitoring program. The results of the analyses of the'se crossch'eck samples shall be included in the annual report.

If the results of analyses performed by the licensee or licensee's contractor in conjunction with the EPA crosscheck program (or equivalent program) are outside the specified control limits, the laboratory shall investigate the cause of the problem and take steps to correct it. The results of this investigation and corrective action shall be included in the REHP annual report.

(89 of'124)

DAT

FIGURE 5 ENVIRONMENTAL MONITORING LOCATIONS WITHIN ONE MILE OF THE SSES GOUI.D ISLAND iS I 1 W 1 I

I i4 1SS4 P%M&W T LAKE Q 16S1

~a ~ ~TAW T~ 1g I

3S3 / 3S4 14 ~ iE/;

l G 13S2i T SS4 T

$.1m @ 5SS I

I 01 ~~1

~

T Sl I

I 18S1 I I

I /oTI

~ ~l I

I I I'

~s m m a a a eP I SITE BOUNDARY iB 1 NILE 8

SUSQUEHANNA Qh. RIVER Ae SVRFACE IATER T THERMOLUMINE9CENT DOSIMElRY A 42 DAy ~ c (90 of 124)

FIGURE 8 ENVIRONMENTAL MONITORING LOCATIONS GREATER THA'N ONE MILE FROM THE SSES 15F1 SUSQUEHANNA NANTICOKE T

RIVER I

T GLEN LYON 15F1 T SHICKSHINNY P i4 MOCANAQUA 4 Te%1 iaaf POND HILL

~T 1283

~f

/882 WAPWALLOPEN 5Ei T

BERWICK ill:1 7E1 TQ T MIFFLINVILLE NESCOPECK gg T

l2H2 lilt CON YNGHAM 7

HAZLETON 18 EXILES

~m AlR DRSIQNG 1ATER SEOr MENT nsa THERWOLUMNE9CENT

~n DOSQtETRY 43 DATE~~~ (91 of 124)

Page 1 of 3 TABLE 6 OPERATIONAL RADIOL06ICAL ENVIRONMENTAL NNITORING PROGRAN Exposure Pathways Number of Samples Sac@ling and a 0 e ~a~oc~togs~ Co ect

~lrborne Continual sampler operation with Radioiodine Canister: analyze Radioiodine and 12S2 (0.4 mi VSV - E.O.F. Building) sample collection weekly.*~ weekly for I-131 Particulates 981 (1.3 mi S - Transm1ssion Line) 5S4 (0.8 mi E - V of Bio. Consult.)

12E1 (4.7 mi VSV - Berwick Hospital) 7G1 (14 mi SE - PPLL Hazleton Chem (0.5 mi NE - Lab)'S2 SSES Backup Het. Tower Particulate Sample:

'SS4 (0.6 mi NV - Transmission Corridor Analyze for gross beta radioactivity 102 (3.9 mi N - Hocanaqua Substation) less than .24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> following filter 3D1 (3.4 mi NE - Pond Hill) change. Perform isotopic analysis on 1261 (15 mi VSV - Bloansburg Serv1ce composite sample (by locat1on) quarterly.

Center)'S2 rec Radiat o Perimeter Fence - 0.2 mi N S)uarterly Ganma Dose: S)uarterly.

102 Nocanaqua Substation - 4.0 m1 N 2S3 Perimeter Fence - 0.2 mi NNE 283 Durabond Corporation - 1.3 m1 NNE 2Fl St. Adalberts Cemetery - 5.9 mi NKE 3S4 Perimeter Fence - 0.3 mi NE 3D1 Pond Hill - 3.4 mi KE 3Fl Stalanla Resident (Nant1coke) - 9.1 mi NE 3G3 Vilkes-Barre-Horton St. Substat1on-16 ai Perimeter Fence - 0.2 mi ENE NE'S3 4E1 Ruckles Hill Road Pole (8) 46422/N35197 - 4.8 mi ENE 461 Hountain Top - Industrial Park-14 ai Perisater Fence - 0.3 ENE'S7 mi E SE2 Bloss Farm - 4.5 mi E 6S4 Perimeter Fence - 0.2 mi ESE 6A4 Forser State Police - 0.6 mi ESE

Page 2 of 3 Exposure Pathways Nuaber of Samples Sampling and and or e ~Nd oc4t ~ Co ect 6E1 St. James Church - 4.7 ml ESE 6S9 Perimeter Fence - 0.2 mi ESE 7S6 Perimeter Fence - 0.2 mi SE 7E1 Harwood Transmission Line Pole 82-4.2 mi SE 7G1 Hazlcton Chemical Lab - 14 mi Perismter Fence - 0.2 ml SSE SE'S2 882 LaVall Residence - 1.4 ml SSE 803 Nowry Residence - 4.0 mi SSE 9S2 Security Fence - 0.2 ml S 904 Country Folk Store - 3.6 ml S 10S1 Perimeter Fence - 0.4 ml SSV 1002 Ross Ryman Farm - 3.0 mi SSV 11S3 Security Fence - 0.3 ml SV 11E1 Thomas Residence - 4.7 ml SM 12S3 Perimeter Fence - 0.4 ml VSV 12E1 Berwlck Hospital - 4.7 ml VSV 1261 Bloansburg - 15 ml Perimeter Fence - 0.4 ml V VSV'352 13E4 Kessler Farm - 4.1 ml V 14SS-Site Pole 43996/N34230 0.5 mi VNV 14E1 Canouse Fare - 4.1 ml VNV 15F1 Zawatski Farm - 5.4 ml NV 15SS Perimeter Fence - 0.4 ml NV 16S1 Perimeter Fence - 0.3 ml NNV 16S2 Perimeter Fence - 0.3 ml NNV 16F1 Hldlay Residence (Huntington Hills)-

7.8 NNV

~ate ~o Surface 6S6 river water intake Nonthly composl te Games isotopic analysis.

trltias line'$

7 cooling tower blowdown discharge line Nonthly compos 1 te Caaposlte analysis at least quarterly.

Orlnking 12H2 Oanvllle Vater Co. Honthly composite Gross beta and gasma isotopic (Approximately 30 mlles downstream) analyses monthly. Composite for trltias analysis at least quarterly.

Sediment fras Shoreline 78 Bell Bend - 1.2 ml SE Semi-annually Ganma isotopic analysis semi-annually.

Page 3 of 3 Exposure Pathways Number of Samples Sampling and Type and and o e Coll ection o I s Hilk*** 1283 Young Farm - 2.0 mi MSM Semi-monthly when animals are on Ganna isotopic and 1-131 analysis 10Gl Davis Farm - ll mi. SSW' pasture, monthly otherwise of each sample.

1481 Stola Farm - 1.8 mi. MNM 1202 Oagostin Farm - 3.7 mi. MSM Fish and Invertebrates Outfall area Semi-annually. One sample'rom Genoa isotopic on edible portions.

2H Falls, each of two reacreationally PA'Approximately 30 mi HNE) important species from any of the following families: bullhead catfish, sunfish, pikes, or perches.

Food Products 1101 Zehner Farm - 3.3 mi SM At time of harvest Gamna isotopic on edible portions.

vegetable

<<The location of samples and equipment were designed using the guidance in the Branch Technical Position to NRC Rev. Guide 1.8, Rev. I, Nov. 1979, Reg. Guide 48. 1975 and ORP/SIO 72-2 Enviroraental Radioactivity Surveillance Guide. Therefore, the airborne sampler locations were based upon X/Q and/or 0/Q.

• <<A dust loading study (RHC-TR-81-01) concluded that the assumption of 1 for the transmission correction factor for gross beta analysis of air particulate samples is valid. Air particulate samples need not be weighed to determine a transmission correction factor.

• • • Ifa milk sample is unavailable for more than two sampling periods fran one or more of the locations, a vegetation sasyle shall be substituted until a suitable milk location is evaluated. Such an occurrence will be documented in the REHP annual report.

a cn Control sample location.

b Two-week composite if calculated doses due to consmsption of water exceed one millirem per year. In these cases, 1-131 analyses will be performed.

The san@le collector will determine the species based upon availability, which may vary seasonally and yearly.

TABLE 7 DETECTION CAPABILITIES FOR ENVIRONNENTAL SNPLE ANALYSIS Lower Limit of Detection (LLD)

Airborne Particulate

~ness Mater Q~mCL1l or Gas C

m'x10-lacedFish Hilk IBU~> C'et Food Products Sediment laJCCdl ',

gross beta H-3 2000 Hn-54 15 130 Fe-59 30 260 Co-58 15 130 Zn-65 30 260 Zr-95 30 1-131 1b 7x10 60 Cs-134 15 5 x 10 130 15 60 150 Cs-137 18 6 x 10 150 18 80 180 I

Ba-140 60 60 La-140 15 15

TABLE 7 (Continued)

The LLD is the smallest concentration of radioactive material in a sample that will be detected with 95 percent probability and with 5 percent probability of falsely concluding that a blank observation represents a "real" signal.

For a particular measurement system (which may include radiochemical separation):

LLD 4.66 s~

2.22 EVY exp (-A 6 t) where:

LLD is the "a priori" lower limit of detection as defined above (as pCi per uit mass or volume).

sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (as counts per minute)

E is the counting efficiency (as counts per transformation)

V is the sample size (in units of mass or volume) 2.22 is the number of disintegrations per minute per picocurie Y is the fractional radiochemical yield (when applicable) is the radioactive decay constant for the particular radionuclide, and

~t is the elapsed time between sample collection (or end of the sample collection period) and time of counting.

In calculating the LLD for a radionuclide determined by gamma-ray spectrometry, the background should include the contributions of other radio-nuclides normally present in the samples (e.g., potassium-40 milk samples).

Typical values for E, V, Y, and t should be used in the calculations.

It should be recognized that the LLD is defined as an a priori (before the

~ I l(ft th f t)liitf fact) limit representing the capability of a measurement system and not as p tl 1 t.

a LLD for drinking water. a 48 (96 of 124)

I DAT

10.0 DOSE SS SS E T POLICY S EMEN S 10.1 Selection o a s es ts fo ose C c 1 tio s For determination of compliance with SSES Technical Specification dose limits, effluent totals shall be based only on activity positively detected at the 95X confidence level.

10.2 Assi nment of eleases to t e Reacto Units For determination of compliance with SSES radioactive effluent dose limits which are on a "per reactor unit" basis:

a. Effluents from the Unit 1 Reactor Building vent and the Unit 1 Turbine Building vent shall be included as Unit 1 releases.

b. Effluents from the Unit 2 Reactor Building vent and the Unit 2 Turbine Building vent shall be included as Unit 2 releases.

c. Effluents from the Standby Gas Treatment System vent shall be equally divided between Unit 1 and Unit 2 release totals.

d. Waterborne effluents shall be equally divided between Unit 1 and Unit 2 release totals.

10.3 Eva uat'on a d Mon torin C iteria or Effluent athwa s Potential unmonitored effluent pathways will be evaluated on a case-by-case basis. Periodic sampling and/or realistic evaluation will be performed in order to demonstrate the significance of a potential effluent pathway. Results of sampling and/or evaluation may be used to. classify a potential unmonitored effluent pathway into one of the following categories:

a. Not an Effluent Pathwa : Realistic evaluation (e.g.,

engineering design, system operation, radionuclide inventory) 49 (97 of 124)

DAT

demonstrates that the pathway has no potential for release of radioactive material. Although not required, periodic sampling may at times be performed to confirm the result of the evaluation.

b. Insi ni ica t E flue t Pathwa : Evaluation and/or periodic sampling demonstrate that the pathway may contain radioactive effluents, however, these effluents may not be reasonably expected to exceed 10 percent of the appropriate unrestricted area HPC value (fractional HPCs summed when appropriate) listed in Table II of Appendix B to 10 CFR 20. A release pathway which falls in this category will be sampled periodically.

c. Si i icant Effluent Pathwa  : Evaluation and/or periodic sampling demonstrate that the pathway may contain radioactive effluents, and these effluents may be reasonably expected to exceed 10 percent of the appropriate unrestricted area HPC value (fractional MPCs summed when appropriate) listed in Table II of Appendix B to 10 CFR 20. A release pathway which falls in this category will be sampled continuously.

Analyses of samples will be performed consistent with techniques used for samples of the same types collected from normal effluent pathways. Any radioactive materials detected in samples collected from either the Insignificant or the Significant Release Pathways will be included in determining compliance with site dose limits.

Additionally, any such occurrences will be reported in the Semiannual Effluent Report.

10.4 Flow from the SGTS Vent when the S stem I,

is Not in Use When the Standby Gas Treatment is not being used, there remains a small amount of flow from the SGTS vent. This residual flow is exhaust from the battery rooms in the control structure. Because there are no identifiable sources of radioactivity in these rooms, 50 (98 of 124)

auxiliary particulate and iodine sample and noble gas grab sample at 4-hour intervals are not required from the SGTS vent when the SGTS continuous vent monitor is out of service, nrovided that a~ the Standby Gas Treatment System is nqt being used, v

b. there are proper administrative controls in place to ensure that the required sampling will begin within 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br /> if the treatment system is operated.

10.5 ODCM Set pints are U er Limit Values Effluent monitor alarm/trip setpoints calculated in accordance with the ODCH shall be considered upper limit values. Higher (less conservative) setpoints shall not be used, however lower (more conservative) setpoints may be used as required to maximize the utility of the monitor.

10.6 Definition of "A ro riate Treatment" for Li uid Wastes Technical Specification 3. 11. 1.3 requires that the appropriate portions of the liquid waste treatment system be operable and be, used to reduce radioactivity in liquid wastes prior to their release when projected doses from each reactor unit to unrestricted areas would exceed 0.06 mrem to the total body or 0.2 mrem to any organ in a 31 day period. Appropriate treatment is defined as follows:

a. Filtration combined with demineralization is considered appropriate treatment for batches which yield projected doses greater than 6.45E-04 mrem to the total body or 2.15E-03 mrem to any organ.

b. Filtration alone is considered appropriate treatment for batches which yield projected doses less than or equal to 51 0 (99 of 124)

DAT

6.45E-04 mrem to the total body and 2. 15E-03 mrem to any organ.

BASES A

The projected dose threshold values used are derived by dividing the site-total maximum projected doses without treatment (0. 12 and 0.4 mrem) by 31 days and by 6, the maximum possible number of batches released per day, to yield per-batch dose action levels.

The two levels of "appropriate" treatment are in place so as not to require application of demineralization for treating low activity, high conductivity water (e.g., from Circulating or Service Mater leakage). This would increase the overall efficiency of the solid radwaste program while ensuring calculated doses remain at a suitable fraction of 10 CFR 50 design objectives.

10.7 onitor Line Loss Corrections In order to correct for airborne effluent monitor sample line loss, the following correction factors shall be applied to monitor data and sample analysis results:

CORRECTION FACTORS ROUTINE EFFLUENT MONITORS TOOIEE EAATICUIATEE Reactor Building Unit 1 1.5 3.2 Reactor Building Unit 2 1.5 3.2 Turbine Building Unit 1 1.6 3.6 Standby Gas Treatment 1.5 3.9 Turbine Building Unit 2 1.6 3.6 52 (100 of 124)

e T S V N MON ORS LEJK AT Turbine Building Unit 1 1'.7 4.2 Standby Gas Treatment 1.6 4.4 Turbine Building .Unit 2 1.7 4.3 Each indicated iodine and particulates concentration shall be multiplied by the appropriate correction factor to estimate the actual concentration at the inlet,to the sample line.

10.8 Selection of Data for Determination of Dose Rate Com ian e Airborne effluent monitor setpoints are maintained in accordance with Section 2.2 to alarm before the dose rate limits of Specification 3. 11.2. 1 are exceeded. Station alarm response procedures contain instructions for investigation and verification of monitor alarms. Because setpoint calculations must include assumptions about the composition of the monitored effluent, a monitor high alarm does not necessa'rily indicate that a dose rate limit has been exceeded.

Valid ten-minute averaged data should be the primary information used to determine the compliance status of an incident. One-minute averaged data should also be reviewed if available, but they may or may not provide additional information depending on the magnitude of the release due to the manner in which the monitors update values to be stored and associated statistical considerations. Averages over a longer period should be used only when data with higher resolution is not available. Grab sample analyses should be performed whenever possible to confirm or disprove monitor data, and to provide indication of the nuclide-specific composition of the effluent. When grab sample data're available which, based on vent monitor data, are indicative of the period of elevated release, dose rate calculations should be 53 (101 of 124)

performed using the actual effluent mix. The determination of comp1iance status should not be based on monitor. data alone when it is possible to collect and analyze a vent sample which will be representative of the period of elevated release.

10.9 Low-Level Radioactivit in the Sewa e reatment Plant Like all sewage processing facilities, the SSES sewage treatment plant can under certain conditions receive low levels of radioactive materials. The most notable scenario is when individuals who work on-site have been subjected to the of radiopharmaceuticals for diagnostic or medical'dministration therapeutic purposes. In these cases, normal biological elimination processes can easily result in levels of radioactivity in sewage treatment plant solutions and suspensions which are within the detection capabilities of the associated sampling and analysis program.

Because disposal of sewage treatment plant sludge by controlled dispersal on specified tracts of land is a common practice, the following guidelines have been established:

a. All sludge collected in the sludge holding tank should be sampled and analyzed prior to land disposal to quantify any radioactivity present above natural background levels.

b. Sludge containing nuclides with short half-lives, for example iodine-131, should be contained on-site to permit decay to less than detectable levels.

c. When sludge; is contaminated with nuclides which have half-lives sufficiently long to make hold-up for decay impractical, the following options should be considered:

1. Dispose of the sludge as low level radioactive waste.

54 (102 of 124)

OAT

2. Obtain a special permit pursuant to the requirements of 10 CFR 20.302.

d. The sewage treatment plant effluent should be sampled monthly for radioactivity. This can be accomplished by drawing a sample from the chlorine contact chamber.

11.0 ODCH'EVIEW AND REVISION CONTRO The Supervisor-Environmental Services-Nuclear, shall ensure that a total review of the ODCH is performed during each even-numbered year.

Comments shall be documented and revisions initiated as appropriate.

Each ODCH page shall be numbered and provided with an approval and date box. The ODCH Table of Contents shall present the current revision date for each page so that any'anual holder can check manual completeness based on a current Table of Contents.

All ODCH revisions shall be reviewed by PORC before approval by the Manager-Nuclear Technology. PORC review shall be indi,cated by PORC chairperson or designee signature on ODCH cover.

ODCH copies shall be issued in a controlled fashion by the staff of the Nuclear Department Library. The distribution list shall be maintained by the Nuclear Department Library Staff.

Any comments on ODCH contents or proposed revisions should be directed to the Supervisor-Environmental Services-Nuclear.

55 (103 of 124)

APPENDIX A SAMP CALCULATIONS OF ODCM ARA S A. 1 ~SETPOI S A. 1. 1 Wate borne fluent onitors A.l.l.l Li uid Radwaste Dischar e Line Monitor For an unidentified mixture with an assumed MPC of lE-7 uCi/ml, an actual activity concentration of lE-5 uCi/ml, and a blowdown flow setpoint of 5000 gpm, the high radiation setpoint concentration, c, can be determined from c x(A). If x 3, then the actual high radiation setpoint concentration is:

c 3 (A) 3 (1E-5) c - 3E-5 uCi/ml The Alert radiation setpoint is 0.8 times the high radiation setpoint, or 1.6 times the actual activity concentration. The setpoint value for the liquid effluent monitors is then determined by Equation 3 in the ODCM. For the above release conditions, the setpoint value, assuming a typical calibration factor of 1.3 x 10 uCi/ml per cpm, would be:

Setpoint

-~

cpm + Background (cpm)

Cal. Factor gtgit g ~ t tg d 1.3 x 10 Setpoint cpm 2.3E3 + Background

.The LRW discharge flow setpoint is then determined as follows:

A-1 (104 of 124)

I DAT

z+f r(s) .

MPC where Y is made equal to 10.

5000+5 10 (1E-5) f 18-7 f 5 gpm For an identified mixture with an actual MPC of 7.22E-7 uCi/ml and the same activity concentration, blowdown flow and X and Y values as above, the LRW discharge-monitor setpoint value and LRW discharge flow setpoint become:

High radiation setpoint concentration (c) - 3E-5 uCi/ml High radiation setpoint value 2.3E3 cpm + Background LRW discharge flow setpoint (f) 36 gpm A.l.l.2 Service Water Monitor Sam le Data Background 300 cps Calibration Factor 1.5E-8 uCi/ml per cps Activity concentration 2E-5 uCi/ml (2E-5)/Cal. Factor 1333 cps Because 300 cps is less than 1333 cps:

HI RAD Setpoint 0.5 Background + (2E-5)/Cal. Factor

~ 0.5 (300 cps) + (2E-5)/(1.5E-8)

~ 150 cps + 1333 cps 1483 cps DOWNSCALE Setpoint 0.5 Background (0.5)(300 cps) 150 cps B kg d 1400 p Calibration Factor 1.5E-8 uCi/ml per cps (2E-5)/Cal. Factor 1333 cps Because 1400 cps is greater than 1333 cps:

HI RAD Setpoint Background + (0.5)(2E-5)/Cal. Factor 1400 cps + (1E-5)/(1.5E-8) 2067 cps A-2 (105 of 124)

DOWNSCALE Setpoint = Background - 0.5 (2E-5)/Cal.

Factor

= 1400 cps - 0.5 (2E-5)/1.5E-B)

= 1400 cps - 667 cps = 733 cps A.1.1.3 RHR Service Water Monitor

~00 0 0: 0 k d = 160 cpm Calibration Factor = 3.9E-9 uCi/ml per cpm 0

(2E-5)/Cal. Factor = 5128 cpm Because 160 cpm is less than 5128 cpm:

HI RAD Setpoint = 0.5 Background + (2E-5)/Cal. Factor

= 0.5 (160 cpm) + (2E-5)/(3.9E-9)

= 80 cpm + 5128 cpm = 5208 cpm LOW RAD Setpoint = 0.5 Background

= 0.5 (160 cpm) = 80 cpm ALERT Setpoint = 0.8 HI RAD Setpoint = 4166 cpm 0:0 kd d=dddd Calibration Factor 0

= 3.9E-9 uCi/ml per cpm (2E-5)/Cal. Factor = 5128 cpm Because 6000 cpm is greater than 5128 cpm:

HI RAD Setpoint = Background + (0.5)(2E-5)/Cal. Factor

= 6000 cpm + (1E-5)/(3.9E-9)

= 6000 cpm + 2564 cpm

= 8564 cpm LOW RAD Setpoint Background - 0.5 (2E-5)/Cal. Factor

= 6000 cpm - 0.5 (2E-5)/(3.9E-9)

= 6000 cpm - 2564 cpm = 3436 cpm ALERT Setpoint - 0.8 HI RAD Setpoint 6851 cpm Gaseous Effluent Monitors A.1.2.1 .Noble Gas Monitor

~, 4 To determine the release rate limit for noble gases, an isotopic mixture representative of plant effluents is selected. For example, the following mixture from A-3

-GEO g t 589 (106 of 124)

Argon-41, 25 Ci/yr per reactor Krypton-83m 4 Krypton-85m 1,700 Krypton-85 270 Krypton-87 32.

Krypton-88 660 Xenon-131m, 71 Xenon-133m 14 Xenon-133 12,500 Xenon-135m 220 Xenon-135 590

,.,~Xe e - 38 ~90 Total 16,376 Ci/yr per reactor The above annual release quantities are entered into GASPAR with the following annual average dispersion estimates (

Reference:

1982 SSES Meteorology Report):

Relative Concentration 4.1E-5 sec/m 3 Decayed Relative Concentration 4.1E-5 sec/m 3 Decayed Depleted 'Relativd Concentration 3.8E-5 sec/m 3 Deposition Rate 4.2E-8 m This set of annual average meteorological parameters is the most conservative over the period 1973-1982.

The total body dose via the plume pathway which results is 18.3 mrem. Equation 5 of the ODCM is then used to calculate the limiting release rate from each of the five plant release points:

r Limiting Release Rate 32 752 Ci 500 mrem 8.95E4 Ci/yr per vent (36;6 mrem) (5 vents)

A-4 (107 of 124)

I DAT

This limiting release rate is then converted to limiting (setpoint) concentrations using Equation 6 of the ODCH and high limit vent flow rates.

Sample High Limit Vent Flow .Rates:

Unit 1 Reactor Building Vent . 4.75E9 cc/min Unit 2 Reactor Building Vent 4.75E9 cc/min Standby Gas Treatment System Vent 5.04EB cc/min Unit 1 Turbine Building Vent 8.63E9 cc/min Unit 2 Turbine Building Vent -6.50E9 cc/min Limiting Vent Concentration 8.95 4 C r vent 1E6 uCi Ci 3 58E-5 uCi/cc (5.26E5 min/yr) (4.75E9 cc/min) for Reactor Buildings 152 Substituting the other vent flow rates into Equation 6 as above, the following noble gas high radiation set-point concentrations are calculated for the remaining vents:

. Standby Gas Treatment System 3.37E-4 uCi/cc Unit 1 Turbine Building 1.97E-5 uCi/cc Unit 2 Turbine Building 2.62E-5 uCi/cc A.1.2;2 od e - 3 Mo to Mhen the FES expected annual release quantity for I-131 (2.40E-1 curies) is entered into GASPAR with the dispersion estimates of A.1.2.1, the maximum calculated organ dose via the inhalation pathway is 4.88 mrem to the child thyroid. Using Equation 5 of the ODCH, the limiting 1-131 release rate is calcu-lated as follows:

A-5 (108 of 124)

DAT

Limiting Release Rate

.24 Ci 500 rem 1 48E1 Ci/yr/vent (4.88 mrem) (5 vents)

Using Equation 6 of the ODCH, the limiting (setpoint) 1-131 concentrations can be calculated for each of the five plant vents.

Limiting Vent Concentration 14.8 Ci r vent 1E6 uCi Ci 5.92E-9 uCi/cc for (5.26E5 min/yr) (4.75E9 cc/min) Reactor Buildings 152 Substituting the other vent flow rates into Equation 6 of the ODCM above, the high radiation setpoints for the remaining plant vents are calculated to be the following:

Standby Gas Treatment System 5.58E-8 uCi/cc Unit 1 Turbine Building 3.26E-9 uCi/cc Unit 2 Turbine Building 4.33E-9 uCi/cc A.l.2.3 Particulate Monitor Following are the SSES Final Environmental Statement (FES) expected annual release quantities for particu-late radionuclides:

A-6 DAT (109 of 124)

I

Cr-51 1.2E-4 Ci/yr per reactor Hn-54 3.6E-4 Fe-59 1.6E-4 Co-58 5.8E-5 Co-60 1.1E-3 Zn-65 5.5E-5 Sr-89 1.8E-5 Sr-90 3. 1E-6 Zr-95 8.7E-6 Sb-124 5.1E-6 Cs-134 1.3E-4 Cs-136 1.3E-3 Cs-137 2.1E-4 Ba-140 4.2E-5 Ce-141 2.9E-5 Total 3.6E-3 Ci/yr per reactor When the above annual release quantities are entered into GASPAR with the annual average dispersion esti-mates of A.1.2.1, the maximum calculated organ dose via'he inhalation pathway is 1.33E-2 mrem to the teen lung. Using Equation 5 of the ODCH, the limiting release rate of particulates can be calculated:

Limiting Release Rate 7.2E-3 Ci 1500 mrem r 8.12E1 Ci/yr/vent

,(2.66E-2 mrem) (5 vents)

Using Equation 6 of the ODCH, .the limiting (setpoint) particulate concentrations can be calculated for each of the five plant vents.

Limiting Vent Concentration 8 12 1 Ci r vent 1 6.uC C 3.25E-8 uCi/cc for (5.26E5 min/yr) (4.75E9 cc/min) Reactor Buildings 152 A-7 DAT (110 of 124)

When the vent flow rates for the remaining five plant vents are substituted into Equation 6 as above, the following high radiation setpoint concentrations result.

Standby Gas Treatment System 3.06E-7 uCi/cc Unit 1 Turbine Building 1.79E-8 uCi/cc Unit 2 Turbine Building 2.38E-8 uCi/cc A.2 AIRBORNE FFLUENT DOSE RATE CALCULATIONS A.2.1 Noble Gases To evaluate the annual whole-body or skin dose from noble gas release rates, the highest calculated annual average relative concentration for any sector is selected from Table 3. For the SSES site, the critical downwind sector is .the West sector with an annual dispersion factor of 2.6 x 10 sec/m . The expected release rate of the principal noble gas radionuclide, xenon-133, is 396 uCi/sec. To calculate the annual whole-body dose due to the release of any noble gas in the gaseous effluent, Equation 7 in the ODCM should be used. The whole-body dose factor (K.)i 2

from Table 2 for xenon-133 is 2.94 x 10 mrem/yr per uCi/m . Substituting these values in Equation 7, the whole-body dose contribution from xenon-133 releases from the SSES would be 3.0 mrem/yr:

wb (Ki)(X/g v iv (Equation 7) 2 -5 Dwb (2.94 x 10 p~em~r) (2.6 x 10 ~se )

uCi/m m X (396 uCi/sec) 3.0 mrem/year To calculate the annual skin dose due to release of any noble gas in the gaseous effluent, Equation 8 in A-8 DAi (111 of 124)

'he ODCH should be used. 'he skin dose factor (Li) from Table 2 for xenon-133 is 3.06 x 10 2 mrem/yr, 3

per uCi/m . The air dose factor (Hi) from Table 2 for xenon-133'is 3.53 x 10 mrad/yr per uCi/m .

Substituting these values and the previous values for release rate and annual dispersion factor in Equation 8, the'kin dose contribution from xenon-133 from the SSES would be 7.1 mrem/yr:

D (Li + 1.1 Hi) (X/g) g iv) (Equation 8)

D s

(3.06 x 102 premier uCi/m

+ 1.1 (3.53 x'10 ~~)) (2.6 x 10 )

uCi/m m x (396 uCi/sec) 7.1 mrem/year A-9 (112 of 124)

OAV

A.2.2 Radionucl des Other a Noble Gases To evaluate the annual critical organ dose from radionuclides other than noble gases, the highest annual average dispersion parameter for estimating the dose to the critical receptor is selected from Table 3. The highest annual dispersion factor is 2.6 x 10 sec/m in the West sector . The expected release rate of iodine-131 is 3.8 x 10 uCi/sec. The expected release rate of cesium-137 is 6.66 x 10 uCi/sec.

To calculate the annual critical organ'ose due to the release of radionuclides other than noble gases in the gaseous effluent, Equation 9 in the ODCM should be used. The inhalation pathway parameter (R.) from Table 4 for iodine-131 is 1.62 x 10. mrem/yr per uCi/m . Substituting these values in Equation 9, the maximum thyroid dose contribution from iodine-131 would be 1.6 mrem/yr from the inhalation pathway.

Dc(Rj)(Wv)(q i v) (Equation 9) 0 (1.62 x 10 ~mrem r) (2.6 x 10 sec)

'Ci/m m X (3.8 x 10 uCi/sec) 1.6 mrem/year INHALATION PATHWAY, I-131

~

~

fl A-10 (113 of 124)

DA1

A. 3 INDIVIDUAL DOSE

. A.3.1 Waterborne Effluents The liquid effluent dose calculations are performed using the Liquid Annual Dose To All Persons (LADTAP) computer program.

This program may be used to calculate the quarterly (or any other time period) doses to both the maximum individual and the 50-mile population due to radionuclides released in liquid effluents from the SSES. The procedure involves the use of the computer code LADTAP which was developed by the NRC to perform

'I dose calculations in accordance with Regulatory Guide 1. 109.

The User's Hanual for the LADTAP program contains details of the calculational procedures. The total number of curies released for each radionuclide during the time period being evaluated must be supplied from the SSES radiation monitoring program.

A.3.2 Airborne Effluents The airborne effluent dose calculations are performed using th GASPAR computer program. This program may be used to calculate the maximum individual and population doses due to radionuclides in gaseous effluents from the SSES. The code 'eleased implements the semi-infinite cloud model and the dose calculational models of Regulatory Guide 1.109 and is used to calculate all maximum individual and population doses and maximum individual organ doses from the SSES. A more detailed description of the GASPAR code can be found in the GASPAR dose code manuals dated October 17, 1975, and February 20, 1976. The total number of curies released for each radionuclide during the time period being evaluated must be supplied from the SSES radiation monitoring program. The meteorological parameters must be provided from the SSES meteorology program.

A-11 OEG g t l889 (114 of 124)

To evaluate the air dose from noble gas release rates, the highest calculated annual average relative concentration for any sector is selected from Table 3. This critical downwind sector is the West sector with an annual dispersion factor of 2.6 x

-5 3 10 sec/m . The expected release rate of the principal noble gas radionuclide, xenon-133, is 396 uCi/sec. The total release 6

in a calendar quarter would be 7.9 x 10 seconds times 396 uCi/sec or 3.13 x 10 uCi. To calculate the quarterly gamma air dose due to the Xenon-133 release in the gaseous effluent, Equation 12 in the ODCM should be used. The gamma air dose factor (M~) from Table 2 for xenon-133 is 3.53 x 10 2 mrad/yr per uCi/m . Substituting these values in Equation 12, the quarterly gamma'air dose contribution from xenon-133 releases from the SSES would be 0.9 mrad:

Dg 3.17 x 10 Zr Mi (X/P)v Qiv (Equation 12) sec 0 = (3.17 x 10 ~r)(3.53 x 10 ~mrad r)(2.6 x 10 sec) sec uCi/m m 9

X (3.13 x 10 uCi/qtr)

= .9 mrad/quarter To calculate the quarterly beta air dose due to the xenon-133 release in the gaseous effluent, Equation 13 in the ODCM should be used. The beta air dose factor (Ni) from Table 2 for 3

xenon-133 is 1.05 x 10 3 mrad/yr per uCi/m . Substituting these

~

values in Equation 13, the quar terly beta air dose contribution from xenon-133 releases from the SSES would be 2.7 mrad:

'..3'.l7 x -8 Db 10 ~r Ni (X/g)v P iv (Equation 13) sec 0b (3.17 x 10 yr )(1.05 x 10s r)(2.6 x 10 sec) mead uCi/m . m A-12 DEC ~ < l989 (115 of 124)

X (3. 13 x 10 uCi/qtr) = 2.7 mrad/quarter Since the beta air dose is greater than the gamma air dose by a factor of 3 for xenon-133 and the dose limits are only a factor of 2 greater for beta than gamma radiation, the beta air dose would be controlling for xenon-133 releases.

A.4 TOTAL DOSE The total cumulative annual dose to any member of the public from operations at the SSES should be determined by summing the critical organ doses,to real individuals from all three sources of radiation. Only the maximum dose or dose commitment to a real individual needs to be evaluated.

A.4.1 ~Li id Eff1 The cumulative dose to any member of the public due to liquid effluents from the SSES should be determined from the LADTAP program used for evaluating the individual doses as stated in Section A.3.1 of this Appendix.

A.4.2 Gaseous Effluents The cumulative dose to any member of the public due to gaseous effluents from the SSES should be determined from the GASPAR program used for evaluating the individual doses as stated in

'Section A.3.2 of this Appendix.

A.4.3 Direct Radiation The direct radiation to any member of the public due to operations at the SSES should be determined from the

.environmental monitoring "program results.

OF.G g t 1989 A-13 (116 of 124)

APPENDIX B REPORTING RE UIREMENTS-8.1 ANNUAL ENVIRONMENTAL OPERATING REPORT, PART B, RADIOLOGICAL A repor t on the radiological environmental surveillance program for the previous calendar year shall be submitted to the Director of the NRC Regional Office (with a copy to the Director, Office of Nuclear Reactor Regulation) as a separate document by Nay of each year. The period of the first report shall begin with the date, of initial criticality. The reports shall include a summary (format of Table B-1), interpretations, and an analysis of trends from the results of the radiological environmental surveillance activities for the report period, including a comparison with operational controls, preoperational studies (as appropriate), and previous environmental surveillance reports and an assessment of the observed impacts of the station operation on the environment.

In the event that some results are not available, the report shall be submitted noting and explaining the reasons for the missing results. The missing data shall be submitted as soon as possible in a supplementary report.

QZC ~ < ~989 B-1 (117 of 124)

B.2 NONROUTINE RADIOLOGICAL ENVIRONMENTAL OPERATING REPORTS

.When the level of radioactivity in an environmental sampling medium averaged over any quarterly sampling period exceeds the reporting level given in Table B-2, a written report shall be submitted to the Director of the NRC Regional Office (with a copy to the Director, Office of Nuclear Reactor Regulation) within 30 days from the end of the quarter.

If it can be demonstrated that the level is not a result of station effluents (i.e., by comparison with control station or preoperational data) a report need not be submitted, but an explanation shall be given in the annual report.

When more than one of the radionuclides in Table B-2 are detected in the medium, the reporting level will have been exceeded if:

concentration 1 + concentration (2 + ... + 1 repor ng eve repor ng eve If radionuclides other than those in Table B-2 are detected and are due from station effluents, a reporting level is exceeded if the potential annual dose to an individual is equal to or greater than the design objective doses of 10 CFR Part 50, Appendix I. This report shall include an evaluation of any release conditions, environmental factor, or other aspects necessary to explain the anomalous result.

B-2 OEG 1< l9SS (118 of 124)

TABLE B-1 SAMPLE ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM ANNUAL

SUMMARY

Reporting Period: 1/1/79 - 12/31/79 All Indicator Location with Highest Medium or Type and Lower Limit Locations Annual Mean Control Locations Number of Pathway Sampled Total Number of Name, ,Nonroutine (Unit of of. Analyses Detection Mean Distance 5 Reported Measurement Performed LLD ~R 03 Mean Ran e Measurements Air Particulates (10 pCi/m ) Gross Beta 336 26'.6(234/234) 102 29.9(52/52) 28.2(102/102)

(7.7-71) 3.7 mi N (11-71) (9.8-64)

CD I

4D Gamna 28 Be-7 81(20/20) 3D1 82(4/4) 85(8/8)

(37-130) 3.2 mi NE (54-130) (51-140)

Cs-137 0.6 1.6(4/20) 1D2 5.7(2/4) 2.7(I/8)

(1.1-1.8) 3.7 Qi NE (2.3-9.0) (2.7)

Air Iodine 1-131 160 1.5 - (0/109) N/A N/A -(0/51)

(10 pci/m )

O o e: e examp e a a are provided for illustrative purposes only.

TABLE B-2

'REPORTING LEVELS FOR NONROUTINE OPERATING REPORTS Broad, Lea f Water Airborne Particulate Fish Milk Vegetation

~Anal sis Q~Ci t+1 of Gases Ci m3 Ci k , wet Q)~Ci (~l Ci k wet H-3 2 x 10 Hn-54 1 x.s'10 3x10 Fe-59 4x10 1x10 Co-58 1x10 3 3x10 2

Co-60 3 x 10 1x10 Zn-65 3 x 10 2 x 10 Zr-Nb-95 4x10 I-131 2 0.9 3 1x10 3

Cs-134 30 10 1x10 60 1x10 Cs-137 50 20 2 x 10 70- 2 x 10 Ba-La-140 2 x 102(b) 3 102(b) s CD fll For drinking water samples. This is 40 CFR Part 141 value.

C) o ~

Total for parent and daughter.

APPENDIX C SITE SPECIFIC INFORMATION USED BY GASPAR CODE

1) The distance from the facility to the NE corner of the U.S. (Maine) in miles 590 miles.

2) Fraction of year leafy vegetables are grown 0.33

3) Fraction of year cows are on pasture 0.60 (April-Nov.)

4) Fraction of crop from garden 0.76

5) Fraction of daily intake of cows derived from pasture while on pasture 0.42

6) Absolute humidity over growing season ~9.0 /m-Relative humidity is 67.66 if T is supplied.

7) Average temperature over growing season 60.2'F

8) Fraction of year goats are on pasture 0.60

9) Fraction of daily intake of goat from pasture while on pasture 0.75

10) Fraction of year beef cattle are on pasture 0.60 ll) Fraction of daily intake of beef cattle derived from pasture while on pasture 0.55 DEC g t $ 89 (121 of 124)

C-1

APPENDIX D S S E IC INFORMA 0 US D BY ADTA COD

1) Total discharge from all units: 22 cubic feet per second

2) 50-mile Population: 1,608,000

3) Blowdown Rate: 22 cubic feet per second

4) Total Annual Blowdown Volume: 6.94E8 cubic feet

5) Dose to Maximum Hypothetical Individual; Location - Danville, PA

a. Shorewidth factor: .2

b. Dilution factors: 321.0

c. Transit time to drinking water intake: See Table D-1

6) Sport Fish Harvest:

a. Zero to ten miles:

i. 7,000 kg/yr usage ii. 219 dilution iii. 2.9-hour transit time

b. Ten to twenty miles:

8,500 kg/yr usage ii. 263 dilution iii. 6.8-hour transit time

c. Twenty to thirty miles:

i. 8,000 kg/yr usage ii. 306 dilution iii. 11.6-hour transit time

d. Thirty to forty miles:

i. 13,000 kg/yr usage ii.'332 dilution iii. 16.1-hour transit time

e. Forty to fifty mAes:

i. 6,800 kg/yr usage ii. 361 dilution iii. 20.8-hour transit time D-1 (122 of 124)

7) Population Drinking Water Danville, PA (Closest active drinking water supplier)

a. Population: 9,000 served

b. Dilution factor: 321.0

c. Transit time: See Table D-1

8) Population Shoreline (Recreation)

a. Zero to ten miles:

i. Usage: 354,000 manhours per year 219 dilution iii. "2.9-hour transit time Shorewidth factor: .2 iv.

b. Ten to twenty miles:

i. Usage: 268,800 manhour s per year ii. 263 dilution iii. 6.8-hour transit time iv. Shorewidth factor: .2

c. Twenty to thirty miles:

i. Usage: 259,200 manhours per year 306 dilution iii. 11.6-hour transit time Shorewidth factor: .2 iv.

d. Thirty to forty miles:

i. Usage: 422,400 manhours per year ii. 332 dilution iii. 16. 1-hour transit time iv. Shorewidth factor: .2

e. Forty to fifty miles:

i. Usage: 211,200 manhours per year 361 dilution iii.

iv.

20.8-hour transit time Shorewidth factor: .2 t

9) Population Boating:

a. Location: 0-10 miles

b. Usage: 96,000 manhours per year

c. Dilution: 219

d. 2.9-hour transit time

10) Biota Dose P

a. Location: Plant discharge

b. Dilution: 5 c..1-hour transit time D-2 OAV (123 of 124)

TABLE D-I DILUTION FACTORS AND TRANSIT TIMES FOR SSES EFFLUENTS TO DANVILLE, PA.

TRANSIT TINES (HRS)

IIIEEW* XILta-RIVER LEVEL DILUTION LEADING

~DG CO CE PEAK IO TRAILING

~EDG 147.6 125 70.7 76.3 143.5 147.7 136 68.7 74.3 141.2 147.8 156 66.8 72.3 138.9 147.9 168 64.8 70.3 136.5 148.0 179 61.1 66.5 131.9 148.1 208 59.2 64.4 129.6 148.2 211 57.2 62.3 127.2 148.3 225 45.9 52.4 112.9 148.4 251 40.7 46.8 106.3 148.5 257 35.5 41.2 99.7 148.6 262 34.5 40.0 95.6 148.7 279 33.8 39.2 92.9 148.8 295 33.0 38.3 90.2 148.9 297 31.4 36.4 84.0 149.0 324 30.5 35.4 80.4 149.1 342 29.5 34.3 76.7 149.2 367 26.9 31.3 66.7 149.3 425 25.0 29.3 59.7 149.4 457 23.0 27.2 52.7 149.5 588 21.5 25.6 46.8 149.6 700 20.0 24.0 40.8 149.7 870 16.5 20.5 27.5 149.8 980 15.9 19.9 25.9 149.9 1000 15.3 19.3 24.3 150.0 1072 14.7 18.7 23.7 150.1 1174 14.5 18.5 23.7 150.2 1260 14.2 18.2 23.7 150.3 1285 13.5 17.5 22.5

• Mean Sea Level as measured at SSES.

D-3 (124 of 124)

I DAT

PENNSYLVANIA POMER & LIGHT COMPANY SUSQUEHANNA STEAM ELECTRIC STATION OFFSITE DOSE CALCULATION MANUAL

~~choate

<~~~ ~

. /j~

Reviewed By Date Supervisor-Environmental Services Nuclear Reviewed By g.-D 6 Oate 7 S ng 0~

Approved By Date Manager-Nuc ar T chnology (1 of ll)

SUNNLRY OF ODCII CHANGES Changes other than those of a minor, editorial nature are summarized below.

1. Section 10.6 "Definition of 'Appropriate Treatment'or Liquid Mastes" has been revised to provide for the use of the atmospheric demineralizer, prior to the startup and use of this system. The atmospheric demineralizer is considered appropriate treatment for the liquid radwaste chemical processing subsystem, specifically intended for organically-contaminated or other high-conductivity liquid waste. For batches containing no identified gamma activity above T. S. Table 4. 11.1. 1.1-1 LLO level release without treatment is considered appropriate.

2. Figure 1, "Liquid Radwaste System Flow Diagram," has been changed to include the atmospheric demineralizer system. CST berm water has been added as an influent sour ce to the chemical waste system.

(2 of 11)

Revision

~ate 9.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM. 38 2/21/92 9.1 DEFINITIONS............................... 38 2/21/92 9.2 MONITORING PROGRAM........................ 38 ~

2/21/92 9.3 CENSUS PROGRAM............................ 39 2/21/92 9.4 INTERLABORATORY COMPARISON PROGRAM.......; 40 2/21/92 41 2/21/92 10.0 DOSE ASSESSMENT POLICY STATEMENTS............ 49 2/21/92 10.1 SELECTION OF ANALYSIS RESULTS FOR 49 2/21/92 DOSE CALCULATIONS 10.2 ASSIGNMENT OF RELEASES TO THE REACTOR 49 2/21/92 UNITS 10.3 EVALUATION AND MONITORING CRITERIA FOR 49 2/21/92 EFFLUENT PATHWAYS 10.4 FLOW FROM THE SGTS VENT WHEN THE SYSTEM 50 2/21/92 IS NOT IN USE 10.5 ODCM SETPOINTS ARE UPPER LIMIT VALUES 51 2/21/92 10.6 DEFINITION OF "APPROPRIATE TREATMENT" 51 3/6/92 FOR LIQUID WASTES 10.7 MONITOR LINE-LOSS CORRECTIONS 52 2/21/92 10.8 SELECTION OF DATA FOR DETERMINATION OF 53 2/21/92 DOSE RATE COMPLIANCE 10.9 LOW-LEVEL RADIOACTIVITY IN THE SEWAGE 54 2/21/92 TREATMENT PLANT 11.0 ODCM REVIEW AND REVISION CONTROL............. 55 2/21/92 APPENDIX A - SAMPLE CALCULATIONS OF ODCM PARAMETERSe ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ A-1 2/21/92 A-2 2/21/92 A-3 12/11/89 A-4 2/21/92 A-5 2/21/92 A-6 2/21/92 A-7 2/21/92 A-8 2/21/92 A-9 2/21/92 A-10 2/21/92 A-11 12/11/89 A-12 12/11/89 A-13 12/11/89 APPENDIX B - REPORTING REQUIREMENTS............... B-l 12/11/89 B-2 12/11/89 B-3 12/11/89 8-4 12/11/89 (3 of ll) ii

LIST OF FIGURES Revision

~a ~at Figure 1 Liquid Radwaste System Flow Diagram......... 34 3/6/92 Figure 2 Offgas and Recombiner System Flow Diagram... 35 2/21/92 Figure 3 Solid Maste Management System Flow Diagram.. 36 2/21/92 Figure 4 SSES Dry Contaminated Maste Processing...... 37 2/21/92 Figure 5 Environmental Monitoring Locations Mithin One Mile of SSES............................ 42 2/21/92 Figure 6 Environmental Monitoring Locations Greater than One Mile from SSES..................... 43 2/21/92

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auxiliary particulate and iodine sample and noble gas grab sample at 4-hour intervals are not required from the SGTS vent when the SGTS continuous vent monitor is out of ser vice, ~~ ~-

a. the Standby Gas Treatment'System is not being used,

b. there are proper administrative controls in place to ensure that the required sampling will begin within 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br /> if the treatment system is operated.

10.5 ODCH Set pints are U er Effluent monitor alarm/trip setpoints calculated in accordance

, with the ODCH shall be considered upper limit values. Higher (less conservative) setpoints shall not be used, however lower (more conservative) setpoints may be used as required to maximize the utility of the monitor.

10.6 Oefinit'on of "A o riate reatment" o Technical Specification 3. 11. 1.3 requires that the appropriate portions of the liquid waste treatment system be operable and be used to reduce radioactivity in liquid wastes prior to their release when projected doses from each reactor unit to unrestricted areas would exceed 0.06 mrem to the total body or 0.2 mrem to any organ in a 31 day period.

o The normal treatment, which is considered appropriate for each subsystem, is as follows:

Filtration is considered appropriate treatment for. the Liquid Radwaste Laundry Processing Subsystem, which consists of high conductivity liquid wastes, such as those from equipment washdown and personnel decontamination facilities, or laundry.

51 (6 of 11)

DAT

The atmospheric demineralizer (a vendor-supplied system which is directed to the Distillate Sample Tank) is considered appropriate for the Liquid Radwaste Chemical Processing Subsystem.

Demineralization and filtration are considered appropriate treatment for low conductivity/low organic contaminant liquid wastes entering the Liquid Radwaste Processing Subsystem (LRW collection tanks), except for batches which yield projected doses prior to treatment of less than or equal to 6.45-04 mrem to the total body and 2. 15E-03 mrem to any organ, where filtration alone is appropriate, or o For batches which have no identified gamma activity above the Technical Specification Liquid Effluent LLD level (Table

4. 11. l. l. 1-1), release without treatment is considered appropriate.

BASES The projected dose threshold values used are derived by dividing the site-total maximum projected doses without treatment (0. 12 and 0.4 mrem) by 31 days and by 6, the maximum possible number of batches released per day, to yield per-batch dose action levels. The two levels of "appropriate" treatment are in place so as not to require application of demineralization for treatin'g low activity, high conductivity water (e.g., from Circulating or Service Water leakage). This would increase the overall efficiency of the solid radwaste program while ensuring calculated doses remain at a suitable fraction of 10 CFR 50 design objectives and Technical Specification 3. 11.1.2 52 (7 of ll)

10.7

'n order to correct for airborne effluent monitor sample line loss, the following correction factor s shall be applied to monitor data and sample analysis results:

OU N FU MN R lQDNK Reactor Building Unit 1 1.5 3.2 Reactor Building Unit 2 1.5 3.2 Turbine Building Unit 1 1.6 3.6 Standby Gas Treatment 1.5 3.9 Turbine Building Unit 2 1.6 3.6 POST ACC D NT V T HONITO L99&K R U Turbine Building Unit 1 1.7 4.2 Standby Gas Treatment 1.6 4.4 Turbine Building Unit 2 1.7 4.3 Each indicated iodine and particulates concentration shall be multiplied by the appropriate correction factor to estimate the actual concentration at the inlet to the sample line.

"'Reference Calculation No. OT-RKB-92.001: Calculation of Liquid Isotope Offsite Dose Consequences for for Use of Atmospheric Demineralizer System, PLI-70360, 2/4/92.

'Reference Letter R. K. Barclay to R. A. Breslin: Atmospheric Demineralizer Effluent Results, PLI-70612, 3/4/92.

53 (8 of 11),

10.8 Se ct of D t for ermi ati n of o e te Com Airborne effluent monitor setpoints are maintained in accordance with Section 2.2 to alarm before the dose rate limits of .

Specification 3. 11.2. 1 are exceeded. Station alarm response procedures contain instructions for investigation and 'verification of monitor alarms. Because setpoint calculations must include assumptions about the composition of the monitored effluent, a monitor high alarm does not necessarily indicate that a dose rate limit has been exceeded.

Valid ten-minute averaged data should be the primary information used to determine the compliance status of an incident. One-minute averaged data should also be reviewed if available, but they may or may not provide additional information depending on the magnitude of the release due to the manner in which the monitors update values to be stored and associated, statistical considerations. Averages over a longer period should be used only when data with higher resolution is not available. Grab sample analyses should be performed whenever possible to confirm or disprove monitor data, and to provide indication of the nuclide-specific composition of the effluent. When grab sample data are available which, based on vent monitor data, are indicative of the period of elevated release, dose rate calculations should be performed using the actual effluent mix. The determination of compliance status should not be based on monitor data alone when it is possible to collect and analyze a vent sample which will be representative .of the period of elevated release.

54 (9 of ll)

OAV

10.9 Like all sewage processing facilities, the SSES sewage treatment plant can under certain conditions receive low levels of radioactive materials. The most notable scenario is when individuals who work on-site have been subjected to the medical administration of radiopharmaceuticals for diagnostic or therapeutic purposes. In these cases, normal biological elimination processes can eas'ily result in levels of radioactivity in sewage treatment plant solutions and suspensions which are within the detection capabilities of the associated sampling and analysis program.

Because disposal of sewage treatment plant sludge by controlled dispersal on specified tracts of land is a common practice, the following guidelines have been established:

a. All sludge collected in the sludge holding tank should be sampled arid analyzed prior to land disposal to quantify any radioactivity present above natural background levels.

b. Sludge containing nuclides with'hort half-lives, for example iodine-131, should be contained on-site to permit decay to less than detectable levels.

c. When sludge is contaminated with nuclides which have half-lives sufficiently long to make hold-up for decay impractical, the following options should be considered:

1. Dispose of the sludge as low level radioactive waste.

2. Obtain a special permit pursuant to the requirements of 10 CFR 20.302.

d. The sewage treatment plant effluent should be sampled monthly 55 (10 of ll)

DAT

J for radioactivity. This can be accomplished by drawing a sample from .the chlorine contact chamber.

11.0 OD V AND R S 0 CON R The Supervisor-Environmental Services-Nuclear shall ensure that a total review of the ODCM is performed during each even-numbered year.

Comments shall be documented and revisions initiated as appropriate.

Each ODCM page shall be numbered and provided with an approval and date box. The ODCM Table of Contents shall present the current revision date for each page so that any manual holder can check manual completeness based on a current Table of Contents.

All ODCM revisions shall be reviewed by PORC before approval by the Manager-Nuclear Technology. PORC review shall be indicated by PORC chairperson or designee signature on ODCM cover.

ODCM copies shall be issued in a controlled fashion by the staff of the Nuclear Department Library. The distribution list shall be maintained by the Nuclear Department Library Staff.

Any comments on ODCM contents or proposed revisions should be directed to the Supervisor-Environmental Services-Nuclear.

56 (11 of 11)

PAT

PENNSYLVANIA POWER 5 LIGHT COMPANY SUSQUEHANNA STEAM ELECTRIC STATION OFFSITE DOSE CALCULATION MANUAl Prepared By Date Reviewed By Date ~ 2-Supervisor-Environmental Services Nuclear 92-/os oate C 2l eet ng o.

Approved By Date Mana -Nuc ear Technology

LIST OF TABLES Revision

~Pa e Date Table 1 Radiological Effluent Objectives and Standards.. 3 12/11/89 Table 2 Dose Factors for Noble Gases ................... 18 2/21/92 Table 3 Sample Annual Average Relative Concentrations and Deposition Rates............................ 19 12/11/89 Table 4 Dose Factors for Inhalation, Ingestion and Ground Exposure Pathways: Radionuclides Other Than Noble Gases................................ 20 2/21/92 Table 5 Waterborne Effluent Dose Parameters for Adults.. 24 12/11/89 Table 6 Operational Radiological Environmental Monitoring Program.............................. 44 2/21/92 45 2/21/92 46 6/25/92 Table 7 Detection Capabilities for Environmental Sample Analysis................................. 47 2/21/92 48 2/21/92 Table B-1 Radiological Environmental Monitoring Program Annual Summary.................................. B-3 12/11/89 Table B-2 Reporting Levels for Nonroutine Operating R eportso ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ o ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ o B 4 12/11/89 Table D-1 Dilution Factors and Transit Times for SSES Effluents to Danville, PA....................... D-3 2/21/92 (2 of 6)

PAT iv

LIST OF FIGURES Revision

~Pa ~Dat Figure 1 Liquid Radwaste System Flow Diagram......... 34 3/6/92 Figure 2 Offgas and Recombiner System Flow Diagram... 35 2/21/92 Figure 3 Solid Waste Management System Flow Diagram.. 36 2/21/92 Figure 4 SSES Dry Contaminated Waste Processing...... 37 2/21/92 Figure 5 Environmental Monitoring Locations Within One Mile of SSES............................ 42 2/21/92 Figure 6 Environmental Monitoring Locations Greater than One Mile from SSES. 43 6/25/92 (3 of 6)

SUNNRY OF ODCN CHANGES Changes other than those of a minor, editorial nature are summarited below.

1. Figure 6, "Environmental Monitoring Locations'reater than One Mile from the SSES," has been changed to include the Lupini Farm, location 12F7, 8.3 miles WSW of the SSES. The addition of this sampling station is made pursuant to Tech. Spec. Table 3. 12.1-1(4c). The Lupini Farm has been added as a vegetable sampling location because it was identified in the 1991 Land Use Census as a location that is irrigating with Susquehanna River water downstream of the SSES discharge. Table 6 was also changed to include the Lupini Farm.

(4 of 6)

FIGURE 6 ENVIRONMENTAL MONITORING LOCATIONS GREATER THA'N ONE MILE FROM THE SSES SUSQUEHANNA NANTICOKE 18F1 RIVER T

I T

GLEN LYON I'iT SF%

SHICKSHINNY MOCANAQUA T.an POND HILL QE1

~T

@pj's (g~).v WAPWALLOPEN

~'r Q

BERVICK IK NESCOPECK gg T+~~

MIFFLINVILLE 5 gg~

CON YNGHAM 7

HAZLETON 18 IlILES T~m Q DRMGNG '1ATER

~F ma (5 of 6)

Page 3 of 3 Exposure Pathways Nueber of Samples Sampling and Type and and or e and Locations~ Collection F 0 Hilk*** 1283 Young Farm - 2.0 mi VSM Semi-monthly when animals are on Gamna isotopic and 1-131 analysis 10G1 Davis Farm - 14 mi. pasture, monthly otherwise of each sample.

Stole Farm - 1.8 mi. 'MN SSM'481 1202 Oagostin Farm - 3.7 mi. llSM Fish and Invertebrates Outfall area Semi-annually. One sample'ran Gamna isotopic on edible portions.

2H Falls, each of two reacreationally PA'Approximately 30 mi HHE) important species from any of the following families: bullhead catfish, sunfish, pikes, or perches.

Food Products 1101 Zehner Farm - 3.3. mi Sll At time of harvest Gamna isotopic on edible portions.

vegetable 12F7 Lupini Farm - 8.3 mi MSV vegetable

'The location of samples and equipment were designed using the guidance in the Branch Technical Position to HRC Rev. Guide 4.8, Rev. 1, Nov. 1979, Reg. Guide 48. 1975 and ORP/SIO 72-2 Enviroanentai Radioactivity Surveillance Guide. Therefore, the airborne sampler locations were based upon X/Q and/or 0/Q.

"A dust loading study (RHC-TR-81-01) concluded that the assumption of 1 for the transmission correction factor for gross beta analysis of air particulate samples is valid. Air particulate samples need not be weighed to determine a transmission correction factor.

• • • Ifa milk sample is unavailable for sere than two sampling periods from one or more of the locations, a vegetation sample shall be substituted until a suitable milk location is evaluated. Such an occurrence will be docw>>nted in the REHP annual report.

a Control sample location.

b Two-week composite if calculated doses due to consumption of water exceed one millirem per year. In these cases, 1-131 analyses will be performed.

c The sample collector will determine the species based upon availability, which may vary seasonally and yearly.

I

CHANGES TO THE SOLID W STE P OCESS CONTROL PROGRA The following Procedure Change Approval Forms (PCAF's) to the SSES Plant Procedure AD-(A-311, Solid Radioactive Waste Process Control Program, were prepared and approved. during the report period. A copy of the changes are attached.

PCAF 1-92-0432 incorporates a new High 'Integrity Container type to be used in packaging and disposal of cartridge filter waste types. Also included is the use of vendor-provided services for volume reduction of Bead Resin Waste Stream.

PCAF 1-92-0548 incorporates documentation requirements to ensure 10 CFR 61 composite samples are collected.

PCAF 1-92-0866 incorporates changes to maximize container packaging efficiency for Cartridge Filter Waste types. Each individual waste streams radionuclides concentration must be individually analyzed to properly classify the final waste form for disposal.

The changes incorporated provide assurance the waste form is acceptable for disposal.

34

PROCI)URR CXLXOR LPPRtÃ%L POMC 1.

.~9-A 2.'

3.. PRocEDURE Ho. ~b- <<I-3 ff SOllg PadIo(hCAile WClge. ~

6.

PROCEDURE TYPg:

Pvocess Cease- 'I PvaTvcvvs PORC ( Jf NOH PORC ( )

7 ~ REQUESTED CHANCE DELETE PChFI ( ) HO (~) YES P I ~l a II AftacIssaC qs. / // /c,Jsvvs3v~ +82/+8 Cont;rued I

8. RKhSOsV FOR CHAHCK~aC'~pena~ Pt 8 I( f- fl lOgf IQ HF Ada, ~~~ ~l I,~n+v+t CoA4in~ tyI ~f ~c. ,ll 't Pvvssss

~~ ack a ccwI9~dfe riM ~est ~j e(es>ga j(saved s eamsv ACCcis k.

I 7o fvoceatIa Al(hc.h~+ b 5 inc.lulu. )~

~

av'oocAi~. ~< c~p

~In

~~ <>(p~c y ussng sn l~C ce.

vy< C

(

isaac v (~M 6y 5

~sofas. C/~a f Contj.nued se,

9. RECONNEHDED FOR PERHAHENT SThTU$ 2 EEPZRLTZON DhTE 0 DLY NhXINUN FOR TKNPO Y'SThTUS)

10. CONPLETE ITENS 11 TNRU 1$ OF TRIS PORNa

16. PER ITEN 15'S hUTBORI 12 ~ N1NLOEÃENT REVIEII FOR INPLENENThTION OF I I. ( ) QLDR NOT REQUIRED(NON-PORC)

ZNZTZhTORi~

( ) YES a ~Z-9Z j be{ ) QQR PSRÃOR)(ED (SEE REVERSE SIDS) ~ NO "OQIO(ENTS ce Qf) NQL OLDR RSCIOIRED PRIOR TO htPROVLZ FSR SXOCX 21 18s 1UTBO ELTI SNIFT SUFRRVZSOR DhTE 19a NQL QLDI-'. 20e RSVISNS a" lW NOL QLDa Not be (jf) aROOIRm NOL OLDI PSRFOSNIDy R) CCSOQNTS XNC le 1a

~ RSSP SECTION %Rgb/MR INITILLSc O

- c. { ) NQL 0%0% PIRFOS)lN4 LTTL(~ RSCCSS(ENDED! {Q YES (~ NO ssnRORI ~< + ssssI RIVISSDa (+ ERS (g) NO

~~~'1

+ N k IF RRSte SR ~ SIONSD KAKR 1b

~ SUPT OF KANT LPtN5%1 a INITXALS)

IIIImmllilllilll NING INv".

OT)(EA UNIT-SAME CHANGE HOTBOX FORM AD-gA-000-l, Rev. 2; Duplex, Page 1 of 2 (File Rl6) PCt NONE

PCAF 0 1.>>-~~~

PAGE < OF<~

AO-gA-311 Revision 11 Page .7 of 48 3.31 QHEC-HIC-PL-005 SSouthuth Carolina Certificate of Compliance for WHNI RAOLOK-100, -179 and -195 Containers 3.32 OHEC-HIC-PL-004 South RAOLOK-55 Container Carolina Certificatee ofo Com omp 1 > ance for WHNI WHN

3. 33 QHEC-HIC-PL-00 14 South Carolina Certificate of Compliance fot WHNI RAOLOK-500 Container 3.34 OHEC-HIC-PL-007 South Carolina Certificate of Compl' mp >ance or WHNI RAOLOK-200 3.35 DH<C-H<D-PL-DID S>>A'h C>>>>et'>>>> CWfl>>>>'P>>>>f +4>>>>>>>> f>>>>'

TF,C WH(c. -SS -lent -t3cr,~-Z'~h Ce "4<ncNo 3.4t TFC tlJclccw'csndls aPd NOI-gA-6. 5>>1 Radwaste Program

~ RaP ~i'egvP> C t i>>>>>>>>>>D 3B 3.BENT. AO-(A-210, Procurement Control Activities 3.~ NTP-RA-42.3, Radwaste Worker Training .

40 3.38 NTP-gA-41.2, Chemistry Technician Certificat/on Training

+l 3.39 Generic Letter 91-02, Reporting Mishaps Involving LLM Forms.

Prepared for Oisposal >>

~I' T I 4.1 Pow er Production Engineer-Radwaste responsibilities:

4.1.1 Ensure. procedur es are:"adequate to provide, for: proper solidification and dewatering of waste.

4.1.2 Ensure'est data or rationale is. available'to justify applicable solidification and dewatering functions of each waste type or any combination t6'ddress ' disposal and regulatory agencies requirements.

4.1.3 Evaluate services provided by various vendors. to ensure contracted solidification, and dewatering operations are performed in the most efficient and economical method as required by applicable regulatory'gendies.

4.1.4

'nPerform the duties of Radwaste this procedure in his absence.

Supervisor as specifi 4.1.5 Oefine waste streams based ori generator, filtration media and means of Processing. .(2 of:.13)

~ >> h

PCAF 0 i:~ nezz PAGE ~ 0F g~ AO-gA-311 Revision ll Page ll of 48 4.8 Solidification/Oewatering Services Vendor responsibilities:

4.8.1 'rovide solidification,and~ oll4/bv vie~ vcckcgi~

dewateringaservices in accordance with a valid contract for said services and provide test data or make same available for PPKL review during vendor audits to demonstrate that their services and equipment meet the applicable regulatory and disposal facility limitations for the service they are providing.

4 ' ' Provide training documentation to demonstrate that the personnel being provided, to conduct the applicable service; are in fact trained and knowledgeable in the applicable services.

4.8.3 Provide procedures that are or can be placed into the SSES procedure format for the services being provided.

4.8.4 Ensure an approved guality Assurance Program exists that covers the services being provided The vendor shall work within the SSES guality Assurance Program when applicable.

4.8.5 Complete applicable sections of Solidification and Oewatering Records required for each container processed.

4.8.6 Ensure prequalification test data for each waste form shall be submitted to the Nuclear Regulatory Commission. ~e W1 4.8.7 Provide an equipment/process description that is used in. processing waste.

8.8-:='4'- Obtain waste samples from processing equipment in

=

4

"'-": -" -".'". a'ccordance with approved 'operating procedures.

4' ', Perform all pre and post treatment determined by Radwaste Supervisor.

activities as 4.9 Nuclear guality Assurance responsibilities:

4~9~ 1 Receipt inspection of High Integrity Containers and document review to ensure conformance.

4~9~2 Ensure Ce'rtificate of Compliance (C of C) is received with High Integrity Container.

(3 of 13)

AO-gA-3]1 Revision I]

Page ]6 of RWCU Filter Hedr'a shall be dewatered in High Integrity Containers. If this waste must solidified, Technical Specification 3/4.11.3be action statement must be performed.

6. I.4 , Condensate/Rao>>ast.e Deminrrr alizer Bead Resin

a. Resins from the Condensate Oemineralizers Liquid Radwaste Oemineralizer are collectedandin the Spent Resin Tank or transferred a liner/container.

directly to This is considered to be Condensate/Radwaste Oemineralizer Bead Resin.

b. The constituents of this waste stream include various types of anion, cation may and mixed bead resin.

c. Bead Resin may be solidified in steel liners or dewatered for final~isposal in either steel liners or High Integrity Contai'ners.

d. Bead Resin may be used to demineralize Chemical Maste in epoxied steel liners. The Bead Resin may be solidified m dewateredpfor final disposal. ~ vestal~ vccl~d

e. Condensate-.denineral izer"bead r es in may,be

, ultrasonicaTT> cleaned prior to collection in the Spent Resin Tank. " .r Bescl Reran <nay.'.'bbcr.gwccsseb by vol~~c.

vokdien iacthocls aA~c.h~ee4dc. dvywg 4

L Ilc>nev~4i~,~brac.how~ .

s ~

'6.1.5..:.-: -

Cartridge . Fl1 ters ~

%4@ >9 a.. Cartridge'Filter waste type consists of the following waste streams and constituents:

Filters -

A

"(1) CRO CRO or other.fi,lters and small unirradiated primary system equipment such as valves, CRO filters, Rinse Tank filters and 'other lift pump V/ ~

metal components.

(2) RWCU Septa - Septa. from RMCU. Fi-lter Oemineralizer including septa from Fuel Pool Cleanup Filter Deminerahizer.

(3) Radwaste Filters - including degasifier filters and other fiber or paper filters other than primary system.

r (q} uw~t~ v~w~~~~~

PCAF I i-<> - 8'~a~

PAGE ~ OF AO-gA-311 Revision 11 Page 30 of 48 Radioactive Waste Oewatering Records A.Oewatering Record Sheet '(Form AO-qA-311-2) shall be completed for each container filled with dewatered waste streams,. Parts of the form shall be completed by the following responsible individuals or groups:

a. The Radwaste Supervisor is responsible for initiating this form and completing Parts 1 and 2.

b. Chemistry Group shall complete Part 3 Sampling and Analysis.

C. Health Physics, Chemistry and Solidification(

Dewatering Services Vendor personnel shall provide and checkoff the required documentation specified in Part 4.

d. guality Control shall provide verjfication as required for the Dewatering Record Sheet.

High Integrity Containers (HIC)

a. Storage of High Integrity Co'ntainers chic'.

(I) Radlok,"and CNSI High Integrity Containers (BIC) stored in ditect sunlight or in areas- where there is a strong source of ultraviolet radiation 'shall be filled within one year of manufacturing date.

~ p (2) Radlok,High Integrity Containers stored away. from any sources of ultraviolet radi'aOon'hall '.be,".filled'.wi thin two year s

'of manufacturing date .'or specific gu'idance from the vendor must be obtained.

(3) Once filled a Radlok High Integrity Container may be stored in an approved storage facility for up to (S) five years prior to burial.

(4) . Once filled a CNSI High Integrity Container may be stored for a period until one. (I) year of ultraviolet radiation is received..

(5 of '13)

S

1

~CAP@ ->>-~" AD-gA-311 Revision 11 Page 33 of 48

'"iE > OF (e) Radl ok 200 1 oaded weight: g5500 lb (f) Radlok 55 loaded weight  : <950 lb (g) CNSI 14-195 loaded weight  : <12200 lb (h) CNSI 14-170 loaded weight : <10800 lb CNSI 8-120 loaded weight: <7500 lb (i) CNSI 6-80 loaded weight: <5000 lb (k) CNSI 24-INCH FRP loaded weight <1600 lb (1) Radlok 500 loaded weight  : <9500 lb (m) Radlok 179 loaded weight  : gl4000 lb (n) Radlok 195 loaded weight  : <15500 lb (0) MVNLC. iso laake'd ~cia ' 8Soo fg

([) N<R<c. (g4:laiickccL-.

/~

areghfs-'& 8<on (4 (2) The maximum.concentration .of radionuclides with'half 1'ives greater than .(5) five

..years that may be disposed of in a High Integrity Container is 350 pCi(cc;.. "'

(3) The following chemicals are peohihited:and

--;::::::~;" 'may not be-disposed of in High+$ ntegrftg Containers.

(a) . Aqua Regia

" .a~gV (b) Bromine (c) Chromic/Sulfuric Acid' t'. kl

~>

P

~ - ~: . -'(d)'uming'Sulfuric Acid (e) Nitric Acid >50% concentratt (f) Organic peroxides (g) Phenol-concentrated etone - -- .,";"

(i)

(j)

Butane Carbon Disulphide e

(6 of. 13),

PCAF

-"-r:

I 7

~-~'~'~

~"

OF Att.achment 0 PCP IMPLEMENTING PROCEOURE MATRIX AO-gA-311 Revision 11 Page 46 of 48 WASTE PROCESSING Eva orator Concentrates - Solidified SEG STO-'-05-008 (Steel Liner)

OP-068-105 CH-RC-047 Mixed Solids - Solidified SEG STO-P-05-025 (Steel Liner) SEG STO-P-05-051 (Steel Liner)

(High Torque)

OP-068-103 OP-068-133 CH-RC-051 CH-RC-054 LRW Filter Media URC Waste RWCU Filter Media -Dewatered SEG STO-P-03-646 (HIC) V OP-068-116 OP-068-140 Condensate Radwaste Oemineral Bead Re'si --'Solidified':'

SEG STD-P-.05-054 (Steel Liner)';

,OP-068-113 CH-RC-049 * .

Condensate Radwaste Oemineral'd e

" "~> e " te d",..- .

SEG STD-P.-03-048 (Steel'iner}-'.-'->;=':-, 5= -"-'" EG-'.$ TQ-.'P.-:03-010:-( C)~"-'

~ ~

CNS

~

HP-TP-875

I 'O-OP-019, (Ov'er pack)

~ .'

h

'-'! "s'"."': QP~999-'7

~

Page I of 3

." . 'r"'w...'z.'j,

'h j': i.-f"7 of 13}'

J

PQ+ g WB~OF8~ Attachment. 0 PCP IHPL MENTING PROCEDURE HATRI AQ-gA-311 Revision ll Page 48 of 48 RADIOACTIVE WASTE DEWATERING - GEN RAL SEG STO- P-01-005 (Equi pment.) SEG STD-P-04-004 OP-068-114 OP-068-119 OP-068-115 SEG STO-P-03-022 OP-068-128 OP-068-129 HIGH INTEGRITY CONTAINERS - CLOSURE SEG STO-P-03-003 SEG STO-P-03-004 OP-068-123 OP-068-124

'ISPOSAL'AC Y R UIREHENTS HP-TP-806

-'". HP-TP-807 V 1

.:HP-TP-809,.'".;.":-PACKAGING",'hS:.

1 ~ '

~ ~ ~

sf "", ~ '<:') 1 ~ . )~ i *- ~ a~ n e ~ ~

.'='

HP.-TP-'826:(HN-'142} HP-TP-.836 .(HN-190-1}

.,:. ':.;.,;,-::,:.'-; ~,. HP-,TP-.827" (LN-;142) HP-'TP-837 (CNSI. 14-170}

':j>i>'-.'~~!.'=": j"..~$.HP-..TP,, 830'~'('HN'00 I I I) '~:

HP-TP-838 (H¹200)"

...-'-'." ':,"i":HP-';TP.'='831...(CNSE 14-195) '.".;.;.-'-,.';

" HP-TP-840 (CNSI

'.:jPX:.'".":-'.~:.:--,, '.. HP-TP,,832'.':. (CNSI'1-300) (Closed Transport)14-215)'P-TP-842 f.-'TP,'-":833..- (CNSI" 8-120A) HP-TP-852 (HN 215H)

(CNSI 3-55) 'P-TP-996

.":::"-'::-',:..;"::";:Pi P."'J Qg(CNSL8-120B) HP-TP-99$ .'(CNSI'= 1'-'13) r Tcg "')bl+4nch~

'\ f+

~ '0 ~ ~

'j,,~.:

V pA vg

~. ~ .'

(8 of 13)

)

~r

~,

' 4'~

~ ~ + ',) W'. )~~)' -' ~ r

PROCmURS CERN'PPRCVMoI FORX 1. 2~

PCAt NO. / + 4 ~ PAGE 1 Ot

3. PROCEDURE NO. AG-QA-Sll anr. 4 FORM NO

5. PROCEDURE TITLE Solid. RaChoach ym Ihk<tc fracas Gn &a/ Proyro~ PROCEDURE TYPE-PORC (~)

NON-PORC (

7 ~ REQUESTED CHANGE DELETE PCAte ( ) NO (

04'. Ioaq.gof'+ac'4~e> ~

P~ +<f

) YES noa'. Iazn Iz~~~

Continued ( )

8 ~ REASON FOR CHANGE 7y sIIovu koc~~fo.how OF cbrrIloos)kw . fcA/bet'Ircnr

~err ic ~~ re fs 'nrem roc Fa'r Continued ( )

9. RECOMMENDED FOR PERMANENT STATQS2 IIOg'ZDZIIDTZOII DIITIO 60 DAY MAXIMUM tOR TEMPO Y STATUS) 10 ~ .COMPLETE ITEMS 11 THRU 25. IDE Ovi@ST Ami. -...

16o PER ITEM 15o IS AUTHORI 17o MANAGEMENT REVIEW FOR IMPLEMENTATION Ot ao ( ) QADR NOT REQUIRED(NON-PORC)

( ) YES bo ( ) QADR PERtORMED (SEE REVERSE SIDE) o NO COlNENTS INITIATOR< DATE! Qf) NQh QADI REQUIRED PRIOR TO APPENVMo PER BLOCK 21

18. AUTHORIZATION SHItT SUPERVISOR DATE

'19 ~ NQA, QADR 20o REVIEWS a.

~

ho c

~

(

(

) NQA QADR SOT REQUIRED NQA QADR PERFORMEDo

) NQA QADR PERtORMED NO COi&ENTS COMMENTS ATTACHED i RESP PORC lCTO Pc SECTION HEjQ)/MGR INITIALS' RECXNONNDEDC (DI ) YES ( ) NO REVXSEDc ( ) YES (Q NO REVIEWER< DATE!

• N h IF RESPO SH MGRo SIGNED BLOCK 18

21. SUPT. Ot PLANT APPROVALa (9 of l3)

( ITIALS) ATE FORM AD~ 000-1, REV 2o MP o Page 1 of 2 (tZLE R16l IIIISIIRSIIIIII 1 "92-8548

R6F Ho.

~s Attachment B AD-gA-311 DEWATERING RECORD SH ET Revision ll Page 42 of 48 PART 3: Sampling and Analysis Tank/Liner sampled

2. Sample Number

3. Waste Stream Oil Content (Check one)

a. None

b. less than IX Isotopic Analysis attached 6.

7.

8 Specific activity of Dewatered Sample a.

b.

c.

Dewatered Volume Dewatered Weight Sample density Coropoo~g.akhcL/loyeot'rgrncuke. an <H ~J

~ ~

'gm gm/cc e

<++ !;..;..

pCi/gm t

The above tank/liner containing solids l$as been. analyzed in',accordance with CH-RC-075 and found to contain the isotopes and speci.fic'ctivities as indicated on the. attached data sheets. -.. --

'm>stry upervssson

't*

i+i

~

+

l3

~ FORM AD-gA-311-2 Rev. JR', (DUPLEX) Page 2 of 3 (File R24-1):;;.'-:,, '.;.-.-;;-..

~ 4

PROCII)QJN CSM(OI APPROVE tORX 1~ 2~

. /~F

3. PROCEDURE NO.Ab- A-8)( IIZV. (I 4 ~ FORM NO, 5 ~ PROCEDURE TITLE Q(iA P~i~~fi~ Elks* Pr~~ ~<<Pg~ 6~

PROCEDURE PORC NON PORC TYP~

(~)

( )

7. REQUESTED CHANGE DELETE PCAFa ( ) NO ( ) YES AtlOZ.4~ Pgs Cont).nued (

8 ~

~~

REASON FOR CHANGE

~~+ ~S'f y'xzmzZ<gac g )~ (~ ~0~

Q$ (S VlC gf~efS j AC+ /J7 C(i oS< f ~foiccP L

~ce 9~ COHHENDED, Vi PERMANENT STATUS? (

ce 7 f lpo)/ cr/oZf@

ZRlLTION DATE DAY MAXIMUM tOR TEMPORARY STATUS) 10 'OMPLETE ITEMS 11 THRU 15 ON Ot 5 FORM+

~

16 ~ PER ITEH 15 i IS AUTHORIXA 17 ~ MANAGEMEllT REVI&l FOR IMPLEHENTATZON Ot THI Le ( ) QADR NOT REQUIRED(NON PORC)

( ) YES be ( ) QADR PERtORHED (5EE REVERSE i

SZDE) NO CXR(MENTS INITIATORe e MM< ce (Q) NQA QlLDR REQUIRED PRIOR TO APPROVAL PER ELOCX 21 18+ AUTHORZXATZO 92.

SHItT SUPERVISOR DZZZ 19 NQh QADR';..:;z ~ ..

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21. SUPT. Ot LANT APPR5%Le

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NIP g / -Pz -01gg PAO~op AO-OA-311 Revision 11 Page 17 of 48 4

Cartridge Filters are collected and disposed of by emplacement in .a cement matrix in a steel drum/liner or by placing in a High Integrity Container.

c. Cartridge Filters to be solidified for fina1 disposal shall not be mixed with any other waste type.

d. Cartridge Filters to be placed in High Integrity Containers shall be dried. Absorbent material may be included to absorb unintentional and incidental amounts of liquids.

e. Cartridge Filters may be dewatered in High Integrity Containers if drying is impractical.

Each cartridge filter waste stream should be packaged separately.

Irradiated Hardware

a. Irradiated hardware removed from the internal area of'the reactor pressu're vessel is processed and packaged in the spent fuel pool(s)/cask storage pit. This waste stream is considered Irradiated Hardware.

b. The'onstituents 'of this waste stream may include control. rod'blades; LPRMSs, IRMs, TIPs and .components expended during hardware.

processing. and packagin'g activi'ties.

may also be processed. as part of this Startup'ources waste stream. "

c. Irradiated hardware'-is packaged .in .steel'iners for disposal.

d. Liquid shall be drained to ensure free liquid Acceptance Criteria are met.

e. Irradiated hardware shall not be mixed with any other waste type in final processing.

Ory Active Haste (OAK)

• f

a. Ory Active Haste is a'aste stream'consisting of contaminated paper," plastic, wood, metal and other discarded material.

'l12 of-13)

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8:~., y (" ~Z ~ >~ AD-gA-311 Revision 11 PAG~~OF~> p, Page 20 ef 48 6.2.5 of waste for sampling or analysis

+i<'reparation

a. Tanks shall be recirculated in accordance with approved operating procedures prior to sampling or analysis.

b. Bead resin processing in liners shall be mixed in accordance with approved operating procedures prior to sampling or analysis.

c. waste to be processed may also be mixed, recirculated and sampled or analyzed from mobile processing equipment.

6.2.6 Final waste form containing a mixture of waste types or streams shall be individually analyzed to determine radionuclide concentrations. The summation of each individual radionuclide concentration shall be used to characterize the Anal waste form for shipping and disposal. Waste types or streams of different waste classes (estimated by historical precedent or projected analysis) shall not be mixed.

6.2.7 Deviations from sampling and analysis requirements shall be approved by the Chemistry Supervisor and .

Effluents Management Super'vision.

6.3 Testing/Treatment of Radioactive"Haste Var Combtfstible Gases 6.3. 1 Processed waste shall be tested .and/or treated to ensure it. is not capable of generating quaqtities of flaneable or toxic gases,'apors or fumes which may be harmful to persons transporting, handling or disposing of the waste; 1

6:4 R'adioactive Maste Solidification "

'"6.'4.."1.: "; 'General Requirements

.a. Wet Maste Types which. may be solidified are

~ '..-.- Evaporator Concentrates, Hixed Solids,

~ . . " 'KCU Filter Condensate(Radwaste pemineralizer Bead Resin, Media and l.iquid Oily Maste or Petroleum Based Haterials.

b. Solidification processing shall be conducted by qualified SSES or Solidi fication/Oewatering

'Services Vendor personnel.

C. The solidification process shall be operated in accordance with approved operating procedures.

Procedures shall specify waste stream, amounts

. of solidification agent and"addiC'ives or method for determination..

(13 of 13)

SECTION 4 REPORT OF EXCEPTIONS TO THE SSES EFFI UENT MONITORING PROGRAM

'35

J REPORTS OF EXCEPTION TO THE SSES EFFLUENT MONITORING PROGRAM There were no exceptions to the SSES Effluent Monitoring Program to report for the subject period.

36

SECTION 5 CHAlVGES TO RADIOLOGICALElVVIRONMENTAL MONITORING LOCATIONS AS IDENTIFIED IN THE OFFSITE DOSE CALCULATIONMAlVUAL(ODCMj 37

CHANGES TO RADIOLOGICAL ENVIRONMENTAL MONITORING LOCATIONS AS IDENTIFIED IN THE OFFSITE DOSE CALCULATION MANUAL ODCM One food products sampling point, the Lupini farm (Location 12F7) was added in the category of Environmental Monitoring Locations Greater than One Mile from the SSES. This addition was made pursuant to Tech. Spec.

Table 3. 12. 1-1(4c). This farm was identified in the 1991 Land Use census as a location which irrigates with Susquehanna River water downstream of the SSES discharge. The ODCM was revised appropriately to accommodate this new sampling point, as described in Section 3 of this report.

All the requirements of SSES Technical Specifications are being met following the changes discussed above.

38