ML18017A269

Annual Effluent & Waste Disposal Rept for Jan-Dec 1993. W/940331 Ltr

ML18017A269
Person / Time
Site:	Susquehanna
Issue date:	12/31/1993
From:	Barclay R, Doty R, Shank K PENNSYLVANIA POWER & LIGHT CO.
To:	Martin T NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION I)
References
PLA-4114, NUDOCS 9404050332
Download: ML18017A269 (300)

Text

~yS ANNUAL EFFLUENT &

VfASTE DISPOSAL REPORT FOR JANUARY - DECEMBER 1 993 Pennsylvania Power & Light Company Two North Ninth Street Allentown, Pennsylvania 1 81 O1 -1 79 1

March 1 994 9404050332

SUSQUEHANNA STEAM ELECTRIC STATION ANNUAL EFFLUENT AND MASTE DISPOSAL REPORT REPORT PERIOD: 01/01/93 - 12/31/93 Prepared by.

arc ay Health Physicist Reviewed by:

E.Sa Supervisor - Environmental Services - Nuclear Approved b .

Supervis Operations Tec nology Pennsylvania Power L Light Company Two North Ninth Street Allentown, Pennsylvania 18101

TABLE OF CONTENTS SECTION PAGE

l. Introduction and Supplemental Information . .

2. Effluent and Waste Disposal Data 13

3. Meteorological Data and Dispersion Estimates ~ ~ ~ ~ 34

4. Dose Measurements and Assessments . . . . . . 55

5. Changes to the Offsite Dose Calculation Manual 66 and the Solid Waste Process Control Program

6. Reports of Exception to the SSES Effluent . 188 Monitoring Program 7., Correction to Dose Reported in Previous. . . . . . ., . 190 Semiannual Effluent and Waste Disposal Report

LIST OF TABLES PAGE Table 1: Technical Specification Limits . . . . . . . . . . . . 10 Table 2: Airborne Effluent-Summation of All Releases. . . . . . 15 Table 3: Airborne Effluent. . . . . . . . . . . . . . . . . . . 16 Table 4: Waterborne Effluent Summation of All Releases. . . . 18 Table 5: Waterborne Effluent. . . . . . . . . . . . . . . . . . 19 Table 6: Annual Effluent and Waste Disposal Report. . . . . . . 24 Solid Waste and Irradiated Fuel Shipments Table 7: Solid Radioactive Waste Class A. . . . . . . . . . . 25 Principal Radionuclides and Percent Composition Atmospheric Demineralizer Carbon Steel Liner (Dewatered)

Table 8: Solid Radioactive Waste - Class A. . . . . . . . . . 26 Principal Radionuclides and Percent Composition Condensate Demineralizer/Radwaste Demineralizer-HIC (Dewatered)

Table 9: Solid Radioactive Waste - Class A. . . . . . . . . . . 27 Principal Radionuclides and Percent Composition Ultrasonic Resin Cleaning Waste - HIC (Dewatered)

Table 10: Solid Radioactive Waste - Class A. . . . . . . . . . . 28 Principal Radionuclides and Percent Composition Liquid Radwaste Filter Media - HIC (Dewatered)

Table 11: Solid Radioactive Waste - Class A. . . . . . . . . . . 29 Principal Radionuclides and Percent Composition Processed DAW Strong Tight Container Table 12: Solid Radioactive Waste - Class A. . . . . . . . . . . 30 Principal Radionuclides and Percent Composition Cartridge Filters - HIC Table 13: Solid Radioactive Waste - Class C. . . . . . . . . . . 31 Principal Radionuclides and Percent Composition RWCU Filter Media - HIC (Dewatered)

Table 14: Estimated Total Errors Associated with . . 32 Effluent Measurements Table 15: Data Not Reported in Previous. . . . . . . . 33 Semiannual Report

PAGE Table 16: Meteorological Data Availability........... 36 Table 17: Joint Wind Frequency Distribution by . . . . . . . . . 40 Stability Class Table 18: Average Annual Relative Concentrations . . . . . . . . 50 Table 19: Site-Specific Parameters Used for Ladtap II Calculations (Danville Receiver) for each quarter and Entire Year: 1993 . . . . . . . . . . . . 56 Table 20: Summary of Maximum Individual Offsite. . . . . . . . . 58 Doses and Dose Commitments to Members of the Public Table 21: Calculated Collective Doses to Members . . . . . . . . 61 of the Public Within the Riverlands/Information Center Complex Table 22: Calculated Doses for Residences. . . . . . . . . . . . 62 Within the SSES Site Boundary (NNE and ESE sectors)

Table 23: Calculated Doses for the Residences. . . . . . . . . . 63 Within the SSES Site Boundary (SE and WSW sectors)

Table 24: Calculated Doses for Residences. . . . . . . . . . . . 64 Within the SSES Site Boundary (W and WNW sectors)

Table 25: Calculated Doses for Residences. . . . . . . . . . . . 65 Within the SSES Site Boundary (NNW sector)

LIST OF FIGURES PAGE Figure 1: SSES Airborne Effluent Release Points . . . . 5 Figure 2: SSES Waterborne Effluent Release Pathway. . . 6 Figure 3: Susquehanna River Monthly Average Flow Rates. 20 Figure 4: SSES Monthly Liquid Radwaste Discharge Totals 21 Figure 5: SSES Wind Rose: 10-meter Sensors. 37 Figur'e 6: SSES Wind Rose: 60-meter Sensors. 38 Figure 7: SSES Pasquill Stability Class Prevalences ~ ~ ~ o 39 Figure 8: Areas Within the SSES Site Boundary Open. 60 to Members of the Public

SECTION 1 INTRODUCTION AND SUPPLEMENTAL INFORMATION

INTRODUCTION 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, 1993 to December 31, 1993.

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. A section containing a correction to a previously reported dose is also included.

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 (ODCH).

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 r adionuclide categories of gases, particulates, iodines, and,tritium. Average release rates are presented and compared to the applicable limits. Table 3 presents the totals of specific radionuclides in airborne effluents.

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. Figure 3 lists the Susquehanna River monthly flow rates for 1993 while Figure 4 presents the monthly discharge totals of liquid radwaste from SSES during 1993.

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 semi'annual repor t.

Section 3 of this report contains the meteorological data associated with the year 1993. Availability data for the SSES meteorological data are shown in Table 16. Heteor ological data for the calendar year is presented in the form of joint wind frequency distributions by atmospheric stability class. These distributions are presented in Table 17. Figures 5 and 6 are wind rose plots for the SSES primary meteorological 10-meter and 60-meter sensors, respectively.

Figure 7 presents the relative prevalences of the Pasquill stability classes. In addition, the meteorological data from the report year were used to generate annual average relative concentrations (X/gs) and deposition rates (D/gs). These values are presented in Table 18, and are required input for use of the GASPAR code for calculation of the doses resulting from airborne releases.

Section 4 of this report contains an assessment of the calculated doses attributed to the reported radiological effluents for the calendar year. The LADTAP II code was used for calculation of doses from waterborne effluents. Table 19 contains site-specific parameters used for LADTAP II calculations, for the Danville receiver. The GASPAR code was used for calculation of doses from airborne effluents. The calculated doses and direct radiation estimates can be used to estimate the doses to maximally exposed members of the public. Table 20 summarizes maximum calculated doses and dose commitments to members of the public from waterborne and airborne effluents and direct radiation. Table 21 presents calculated collective doses to members of the public within the Riverlands/Information Center Complex. Tables 22 through 25 summarize the calculated doses for residences and other occupied areas within the SSES site boundary.

Section 5 of this report is reserved for documentation of changes to the Offsite Dose Calculation Manual and the Solid Waste Process Control Program.

Section 6 presents a listing of cases (if any) in which airborne or 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 7 contains a correction to a dose reported for liquid effluent foi the year 1982.

FIGURE 1 SSES AIRBORNE EFFLUENT RELEASE POINTS III Q I ZZg HICIOIC Z I

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SUSQUEMANhDS, RIVER ~ &&USER I RAINPALL GENERATED INTAKE CL I(poOCPMDCI PLOW S$ ,121 CPM I POYAOLC CL WCTEII 145 CPM Db) 0 COO CPM ICIONC Otoo LOT RADIOACTIVE RADwASTR TREATMENT POND AREA WATER IISES AL, C P 4C6 CPM RAw WATER l45CPLI CFJKRAL WASTE TREATMENT TREATMENT PLANT V SES 45 CPI4 CEMINEIIAUZERWASTES RAIN'C ALL GENER ATRO A FLDWDQ 50 CPM NOTE:

EYAPOR ATION I+>S50 GPM EVAPORATION I+,550 CPM CHEMICAL WASTE TREATMENT FLOWS SNOW WATER ~~~LI I) RAINFALL GENERATED PLOWS TIRS OIAGR~.

RAW WATER TREATMENT WASTES NOT SHOWN ON 4 T6.000 c pM OIIRING IOYA AKTUAN STOAM 4TOOOOCPM fLOW IA MAY bc. INCRKASCO S50 50 CPM RCCIWCA CPM AIID FLOW lb I4AY bE INCREASEO FILTER 12OO CPM, IL) OUAINS PETCODC DAAOIACE OF COOLINC TOWER SAS!NS FLOW Eb 1>IAY SE SICREASED 5OOO CPM SI CHEMICAL ADDITIONS AL ALES>I A ACID C CALISTIC P - POLYMER CL CHLQAINE b ORCHLC&IATCN CH CI>CCAL F Fll TEA AID POND 45GP14 MA>LE UP EMERGENCY EMEICCNIY RAT I N CAT

~

EVAPOAATI ON T--~-~yOI>NCCRSL ~bOI>NCERS I. A SPRAY I CRROOOCY I POND +5 GPM I O'CSCLS I P I L I 4 I

J COOI INO T Io.ooo GPM Cc*)

SUPPLENENTAL INFORMATION

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 l.

2. Maximum Permissible Concentrations in Waterborne Effluents The concentrations of radioactive materials in waterborne effluents are 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 entrained noble gases, the concentrations are limited to the following values, as stated in the applicable Technical Specification:

Nuclide MPC uCi ml "Kr 2.0E-04 "Kr 5.0E-04 Kr 4.0E-05 MKr 9.0E-05

'Ar 7.0E-05 133mX 5.0E-04 133X 6.0E-04 135mX 2.0E-04 135X 2.0E-04

3. ~A" E Based on gaseous effluent releases for the report period average beta energy is 0. 136 MeV and average gamma energy is 0.046 HeV.

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.

5. Methods of uanti in fluents Fission and Activation Gases: Gas samples are routinely collected monthly and analyzed with a high resolution (Ge[Li] or HPGE) 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 high resolution (Ge[Li]

or HPGE) 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 high resolution (Ge[Li] or HPGE) 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 the 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 high resolution (Ge[Li] or HPGE) 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. Tritium: Airborne tritium is collected montly via bubbler sampler. The sample is collected for one hour at a flow rate of approximately 1000 cc/min. Tritium activity in the bubbler sample is determined by liquid scintillation counting. The liquid sample tritium concentration is converted to air concentration by volume proportion, then compared to the Technical Specification Table 4. 11.2.1.2-1 Lower Limit of Detection (1 E-6 uCi/cc).

e. 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 high resolution (GeI'Li] or HPGE) system and release permits are'enerated 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 pe'riod, and is then multiplied by the volume of the 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.

TABLE 1

1. TECHNICAL SPECIFICATION LIMITS A. ~NNBL NANEB:

1. g 500 mrem TOTAL BODY g 3000 mrem SKIN annual site total "instantaneous" limits (Tech Spec. 3.11.2.1)

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

. quarterly air dose limits per reactor unit (Tech Spec. 3. 11.2.2)

3. ~ 10 mrad - AIR GAMMA

< 20 mrad AIR BETA

- annual air dose limits per reactor unit (Tech Spec. 3. 11.2.2)

B. IRBORNE I-131 TRITIUM PARTICULATES WITH HALF- I ES > 8 DAYS:

1. < 1500 mrem ORGAN (inhalation pathways only) annual site total "instantaneous" limits (Tech Spec. 3.11.2.1)

2. 6 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)

~LI II N EFFL ENF:

1. Concentration g 10CFR20 Appendix B, Table II, Column 2 site total "instantaneous" limits (Tech Spec. 3.11.1.1) 10

2. 6 1.5 mrem TOTAL BODY 6 5 mrem ORGAN

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

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

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

AI BORNE EFFLUENT: BASES FOR PERCENT OF APPLICABLE TECHNICAL SPECIFICATION LIMIT 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 Environmental 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 (2.35E+00 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 unrystricted 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).

11

F. WATERBORNE EFFLUENT: BASES FOR PERCENT OF APPLICABLE TECHNICAL SPECIFICATION LIMIT 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 then 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 unrestricted 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. l. 1-1.

12

SECTION 2 EFFLUENT AND WASTE DISPOSAL DATA 13

Airborne Effluents Summaries of the radionuclide total curie activities, average release rates are included in Tables 2 and 3.

Third Fourth guarter guarter

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 Abnormal 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 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 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 14

TABLE 2 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT (1993)

AIRBORNE EFFLUENT SUMMATION OF ALL RELEASES First Second Third Fourth A. Fission and Activiation Gas Unit Quarter Quarter Quarter Quarter Total Release Ci 7.680<<00 7.21e+00 0.000<<00 2.04e+00 Average Release Rate for Period uCi/sec 9.88e.01 9.17e-al O.aae+00 2.57e-01 Percent of Technical S cification Limit 6.960.03 6.46e-03 D.aae+00 1.81e-03 B. Iodines Total l-131 Ci 8.740.09 0.000<<00 O.aae+00 0.00e+00 Average Release Rate for Period uCi/sec 1.12e.09 0.00e+00 O.aae+00 0.000<<00 Percent of Technical S cification Limit 4.78e.08 0.00e+00 O.aae+00 O.aae+00 C. Particulate Particulate uith Half-Lives > 8 Days* Ci 3.13e.04 3 '8e-05 7.09e-04 2.270-04 Average Release Rate for Period uCi/sec 4 '3e.05 4.68e-06 8.93e-05 2.86e-05 Percent of Technical S cification Limit 3.12e-04 3.63e-05 6.92e-aC 2.210.04 Gross Al a Radioactivity<< 3.01e-08 6.40e-07 3.810-07 3.73e-07 D. Tritiua Total Release Ci 8.050+00 1.75e+01 7.190<<00 1.090+01 Average Release Rate for Period uCi/sec 1.04~00 2.230<<00 9.050.01 1.37e+00 Percent of Technical S cification Limit 2.120.02 C.56e.02 1.85e-02 2.810.02

<<Sr-89, Sr-90 and Gross Alpha values for the fourth quarter 1993 are estimated based on third quarter 1993 sarrTrle analyses and fourth quarter 1993 ventilation exhaust rates.

15

TABLE 3 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT (1993)

AIRBORNE EFFLUENT Releases in Continuous Hode First Second Third Fourth Huclidcs Released Unit Quarter Quarter Quarter Quarter A. Fission and Activation Gases Ar-41 Ci 0.00e+00 0.00e+00 0.00e+00 0.00et00 Kr.85m Ci 0.00e+00 0.00e+00 0.00e+00 0.00e+00 Kr-88 Ci 0.00et00 0.00e+00 0.00e+00 0.00e+00 Xe-133 CI 7.68e+00 7.21e+00 0.00e+00 2.04et00 Total for Period CI 7.68e+00 7.21e+00 0.00e+00 2.04et00

8. Iodines I-131 8.74e-09 0.00e+00 0.00e+00 0.00e+00 1-133 Ci 0.00e+00 0.00e+00 0.00e+00 0.00e+00 1-135 Ci 0.00e+00 0.00e+00 0.00e+00 0.00u00 Total for Period Ci 8.74e-09 0.00c+00 0.00e+00 0.00e+00 C. Particulate Cr-51 0.00e+00 0.00e+00 0.00e+00 0.00e+00 Nn-54 Ci 1.23e-04 1.54e-05 2.23e-04 1.42e-04 Fe-59 CI 0.00e+00 0.00e+00 0.00~00 0.00e+00 Co-58 Ci 0.00e+00 0.00c+00 5.82e-05 2.88c-06 Co-60 Ci 1.90e-04 2.14e.05 2.10e-04 6.82e-05 2n-65 Ci 0.00e+00 0.00e+00 2.18e-04 1.37e-05 Ci 0.00e+00 0.00c+00 0.00e+00 0.00e+00 Sr-8P'r-90*

Ci 2.60e-07 0.00e+00 0.00e+00 0.00e+00 Cs-134 CI 0.00e+00 0 '0w00 0.00e+00 0.00e+00 Cs-137 Ci 0.00e+00 0.00c+00 0.00e+00 0.00c+00 Ce-141 Ci 0.00e+00 0.00e+00 0.00e+00 0.00e+00 Ce-144 Ci 0.00e+00 0.00e+00 0.00e+00 0.00w00 Total for Perl~ Ci 3.13e-04 3.68e-05 7.09e-04 2.27e.04

~Reported values for the fourth quarter 1993 are estimated based on third quarter 1993 sample analyses and fourth quarter 1993 ventilation exhaust rates.

16

Waterborne Effluents Summaries of the radionuclide total curie activities, average diluted concentrations, and percent of applicable Technical Specification limits are included in Tables 4 and 5.

Batch Releases gtr.l gtr.2 gtr.3 gtr.4

l. Number of Batch Releases 89 96 129 104

2. Total Time Period for a Batch Release 5.77E+03 6.85E+03 1.52E+04 1.03E+04

3. Maximum Time Period for a Batch Release 2.70E+02 2.86E+02 2.70E+02 2.65E+02

4. Average Time Period for a Batch Release 6.48E+Ol 7.13E+01 1. 18E+02 9.89E+01

5. Minimum Time Period for a Batch Release 2. OOE+01 1.00E+00 5.00E+00 2.30E+01

6. Average Stream Flow During Period of Release of Effluent into a Flowing Stream 6.98E+03 8.29E+03 6.90E+03 6.34E+03 (Cooling Tower Blowdown Flow Rate) 8.55E+06 1.92E+07 9.79E+05 6.20E+06 (Susquehanna River Flow Rate)

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

respectively.

Abnormal Releases

1. Number of Releases: 0 0

2. Yolume Released: NA NA 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. 11.1. 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 uCi ml Mn-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 Mo-99 1.7 E-07 I-131 2.0 E-08 .

Cs-134 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 17

TABLE 4 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT (1993)

WATERBORNE EFFLUENT SUMMATION OF ALL RELEASES A. Fission and Activation Products First Second Third Fourth Unit Quarter Ouarter auarter Ouarter

1. Total Release (not including Tritiun, Gases Al a)>> Ci 6.95e.03 1.95e-02 8.91e-03 1.39e-02

2. Average Diluted Concentration During Period uCi/ml 4.54e-08 9.32e-08 2.17e-08 5 44e-08

3. Percent of A licable Limit 5.40e-02 4 '0e-02 1.72e-01 2.45e-01 8~ Tritiun

1. Total Release Ci 8.64w00 9.42et00 2.95e+01 2.03et01

2. Average Diluted Concentration During Period uCi/ml 5.66e-05 4.51e.05 7.57e-05 8.00e.05

3. Percent of A licable Limit 1.89e+00 1.50e+00 2.52e+00 2.67+%0 C. Dissolved and Entrained Gases

1. Total Release Ci 2.44e-05 1.03e.05 4.50e-04 1.47e-04

2. Average Diluted Concentration During Period uCi/ml 1.60e.10 4.93e-11 1.46e-09 5.80e-10 3 ~ Percent of A licnble Limit 4.00e-04 1.23e-04 3.64e-03 1.45e-03 D. Gross Al n Radioactivity

1. Total Release Ci 0.00e+00 0.00e+00 0.00e+00 0.00et00 E. Volune of llaste Released Gallons 3.95e+05 4.84e+05 1 ~ 15et06 7.72e+05 (Prior to Dilution) Liters 1 ~ 50et06 1.83e+06 4.35e+06 2.92~06 F. Volune of Dilution Unter Gallons 4.03e+07 5.52e+07 1.03e+08 6.70e+07 Used During Period of Release Liters 1.53e+08 2.09e+08 3.90e+08 2.54~08 G. Volcano of Dilution lister Gallons 9.05e+08 1.09e+09 9.14e+08 8.40e+08 Used Over Entire Period Liters 3.42e+09 4 '1e+09 3.46e+09 3.18e+09

• Reported values for the fourth quarter 1993 are estimated based on third quarter 1993 sample analyses nnd fourth quarter 1993 discharge volwes.

18

TARLE 5 AIDNAL EFFUKNT ARD MASTE DISPOSAL REPIRT (1993)

MATERRQINE EFFUJEMT f 18 0.00e t 00 1.22o07 1Al1e07 3A2e07 No 24 t 0.00o 00 7Aoo07 OAOo 00t 0.00o t 00 Ct61 1~ 1.07403 1.22o03 2.78o04 3.73o03 $ .55o03 $ .24o03 1.8140$

8.87o04 1.28o02 0.00e t 00 0.00e t 00 fe.68 4.12o04 4S2o04 3A8o04 5.78405 4Ar7e06 3.06o06 8.80o04 1.81403 1.6~ 1.08402 2.27406 0.21 o04 4.81o04 Am78 t OANo 00 1.14406 2.14e06 0.00o t 00 8.82408 t OAOo 00 OANot00 0.00o t 00 t

OANo 00 t 0.004 00 OANot00 0.00e t 00 Sr 82 0.004 t 00 0.00o t 00 7.11o07 $ A2o07 0.00o t 00 120o06 t 0.00o 00 t 0.00o 00 To.OOm 0.00o t 00 430408 0.00e t 00 t 0.004 00 Alpl10m 0.00o t OO 2.10o08 3.15o04 1.25e05 Te 1$ 1 t OANo 00 t OANe 00 4N012 OANo 00t 11$ '1 t OAee 00 5ANe07 OAXe 00t 0.00o t 00 Co 1$ 4 OAOotOO 0.00o t 00 0.00o t OO 8.84o07 Co 137 SA 2407 3.44407 1A8e08 2.84406 08141 OANot00 0.00e t 00 6.58o07 0.00o t 00 Hr5147 1.07406 0.00o t 00 OANe OOt 0.004 t 00 W.187 t OANo 00 0.00e t 00 0.00e t OO 0.00e t 00 Terre lor Porroe' 1.05e02 8.8 1 e03 7%kerr H0 a 8.84et00 OA2ot00 285ot01 2A1$ e t 01 Terri lor Porreo a 8.84o t 00 OA24 t OO 2.05e t 01 t 2.0$ 4 01 0.00e t 00 0.00e t 00 0.00e t 00 OANot00 OAOe t 00 OANet00 t 0.00o 00 000o 00t 0.00e t 00 0.00e t 00 0.00e t 00 0.00o t 00 Xo87 OAee t 00 OANo t 00 OANo t 00 OANo t 00 OAOo t 00 OANe t 00 1.10t08 0.00o t 00 Xe 131m OANo t 00 0.00o t 00 SA~ 0.00e t 00 Xo 133m OANe t 00 334o08 t 0.00o 00 0.00o t 00 Xo.13$ 1.77e06 0.00o t 00 2A7o04 8.75e05 Xe.135m 0.00o t 00 0.00e t 00 0.00o t 00 t 0.00o 00 Xo 135 8.74408 8.88t06 1.20o04 5.81o05 Total for Porreo 2A4o06 4.50o04 1.47o04

<<Reported values for the fourth quarter are estimated based on third quarter 1993 sample analyses and fourth quarter 1993 discharge voluaes.

FIGURE 3 SUSQUEHANNA RIVER MONTHLY AVERAGE FLOW RATES DATA PERIOD: 1993 GALLONS PER MINUTE x 1E6 60 50 40 4x:xxx ;xxx 30 ':ix':i'i!i'xi!

c x 20 xxxx:xxxxx t xxx:t x':x 10 xxx 0

J F M A M J J A S 0 N D 1993 20

FIGURE 4 SSES MONTHLY LIQUID RADWASTE DISCHARGE TOTALS DATA PERIOD: 1993 GALLONS X 1E3 500,-,::,,:,::,

400  ::'::,:-::::::,:-::::::::

300 200 100 0

J F M A M J J A S 0 N D 1993

SUSQUEHANNA STEAM ELECTRIC STATION RADIOACTIVE WASTE REPORT ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT SOLID RADIOACTIVE WASTE DATA PERIOD Janua 1 1993 December 31 1993 PREPARED BY P. L S H TH PHYSICIST APPROVED BY: C. D. Markley FLUENTS MANAGEMENT SUPV.

22

REPORT NOTES

l. All activities 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 was disposed during this report period.

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

Any Solidified Waste Liquid Oily Waste (Petroleum Based Material)

Non-Processed Dry Active Waste

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).

23

TABLE 6 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT SOLID WASTE AND IRRADIATED FUEL SHIPMENTS Data Period: January 1, 1993 December 31, 1993 A.* SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL Number of Sh ments Node of Trans ortation Destinatio 41 Truck Barnwell, SC Number of Shi ments ode of Trans ortation ~H 20 Truck Scientific Ecology Group Oak Ridge, TN B. IRRADI TED FUEL SHIPNENTS Number of Shi ments Node of Trans ortation Destination None Not Applicable Not Applicable

• The number of shipments listed in A include only the shipments from SSES to a disposal site. It does not include shipments made to or from volume reduction vendors.

TABLE 7 CLASS A SOURCE OF WASTE: ATMOSPHERIC DBQNERALIZER TYPE OF CONTAINER: CARBON STEEL LINER METHOD OF PROCESS: DEWATERED ISOTOPES ACTIVITY (mCi) OF TOTAL Ag-110m 5.762E-01 0. 024'.004 Am-241 3.000E-03 C-14 1.954E+01 0.744 Cm-242 O.OOOE+00 0.004 CIR-244 3.000E-03 0.004 Co-58 1.939E+01 0.

Co-60 6.379E+02 744'4.324 Cr-51 8.391E+00 0.324 Cs-134 O.OOOE+00 0.00t Cs-137 1.179E+00 0.

Fe-55 6.914E+02 044'6.

364'.

Fe-59 3 009E+Ol 154 H-3 1 554E+02 5.934 I-129 +1.645E+00 0.064 I-131 O.OOOE+00 0.004 Mn-54 9 853E+02 37.564'.404 Ni-63 1.044E+01 Pu-238 1.060E-02 0.004 Pu-239 6.500E-03 0.004 Pu-241 3.300E-04 0.004 Sb-124 O.OOOE+00 0.004 Sr-89 O.OOOE+00 0.004 Sr-90 O.OOOE+00 0.

Tc-99 +1. 316E+00 004'.054 Zn-65 6.023E+01 2.

TOTAL ACTIVITY (Ci) 2.623 ft3 304'00.004'1.976 CONTAINER VOLUME 1129.200 m3 25

TABLE 8 CLASS A SOURCE OF WASTE: CONDENSATE DEMINERALIZER/

RADWASTE DEMINERALIZER TYPE OF CONTAINER: HIC METHOD OF PROCESS: DEWATERED ISOTOPES ACTIVITY (mCi) 4 OF TOTAL Ag-110m 2.003E+02 0.23%

Am-241 2.328E-01 0.004 C-14 8.588E+02 1.014 Cm-242 O.OOOE+00 0.004 Cm-244 2.138E-01 0.00%

Co-58 7.849E+03 9.254 Co-60 2.755E+04 32.45%

Cr-51 3.593E+02 0.424 Cs-134 2.517E+00 0.004 Cs-137 1.147E+Ol 0 ~

Fe-55 1.487E+04 014'7.

514 Fe-59 2.733E+02 0.32%

H-3 6.113E+02 0.72%

I-129 1.782E+00 0.

I-131 2.668E+01 004'.03%

Mn-54 1.899E+04 22.37%

Ni-63 4.595E+02 0.544 Pu-238 6.047E-01 0.00%

-Pu-239 3.915E-01 0.004 Pu-241 O.OOOE+00 0.

Sb-124 00%'.

O.OOOE+00 Sr-89 O.OOOE+00 00%'.

Sr-90 1.145E-01 004'.00%

Tc-99 g 1.379E+00 0.00%

Zn-65 1.284E+04 15.124 Co-57 7.745E+00 0.014 La-140 1.295E+01 0.014 Na-24 6.945E-01 0.004 Xe-131m 1.895E-01 0.00%

TOTAL ACTIVITY (Ci) 84.923 100.00%

CONTAINER VOLUME 5778.100 163.621 m3 26

TABLE 9 CLASS A SOURCE OF WASTE: ULTRASONIC RESIN CLEANING WASTE TYPE OF CONTAINER: HIC METHOD OF PROCESS: DEWATERED ISOTOPES ACTIVITY (mCi) OF TOTAL Ag-110m 9.592E+01 0. 08%

Am-241 5.863E-02 0.

C-14 1.807E+02 00%'.16%

Cm-242 1.289E-02 0.00%

Cm-244 O.OOOE+00 0.00%

Co-58 6.535E+02 0.57%

Co-60 1.489E+04 13.08%

Cr-51 1.561E+03 1.374 Cs-134 O.OOOE+00 0.00%

Cs-137 7.537E+01 0.07%

Fe-55 6.369E+04 55.95%

Fe-59 1.617E+03 1.424 H-3 5.941E+01 0.05%

I-129 K3. 816E-01 0.

I-131 O.OOOE+00 00%'.004 Mn-54 2.813E+04 24.714 Ni-63 3.838E+02 0.344 Pu-238 O.OOOE+00 0.

Pu-239 5.003E-02 00%'.00%

Pu-241 3.893E+01 0. 034 Sb-124 3.173E+01 0. 034 Sr-89 O.OOOE+00 0.00%

Sr-90 1.952E-01 0.004 Tc-99 3 '93E-01 0.00%

Zn-65 2.427E+03 2.134 TOTAL ACTIVITY (Ci) 113.830 CONTAINER VOLUME 527.500 ft3 100.00%'4.937 m3 27

TABLE 10 CLASS A SOURCE OF WASTE: LIQUID RADWASTE FILTER MEDIA TYPE OF CONTAINER: HIC METHOD OF PROCESS: DEWATERED ISOTOPES ACTIVITY (mCi) OF TOTAL Ag-110m 4.916E+02 0. 12%

Am-241 1.908E-02 0.004 C-14 4.169E+00 0.00%

Cm-242 1.638E-02 0.004 Cm-244 1.297E-02 0.004 Co-58 4.925E+03 1.214 Co-60 3.328E+04 8.16%

Cr-51 2.776E+04 6. 814 Cs-134 O.OOOE+00 0.

Cs-137 004'.

O.OOOE+00 Fe-55 2.129E+05 004'2.204 Fe-59 1.677E+04 4.114 H-3 7.667E+01 0.

I-129 024'.

4 3.241E-01 004 I-131 O.OOOE+00 0.00%

Mn-54 9.551E+04 23.424 Ni-63 7.264E+02 0.

Pu-238 184'.

O.OOOE+00 004 Pu-239 O.OOOE+00 0. 004 Pu-241 7.896E+00 0.004 Sb-124 3.009E+02 0.

Sr-89 074'.

O.OOOE+00 Sr-90 00%'.

O.OOOE+00 Tc-99 4 004'.

2.243E-01 00%

Zn-65 1.497E+04 3.674 Ce-144 6.280E+00 0.004 Hf-181 8.662E+01 0.024 La-140 1.127E+01 0.004 Nb-95 6.938E+01 0. 014 NI-65 2.072E-02 0.

TOTAL ACTIVITY (Ci 407.877 00%'00.00%

CONTAINER VOLUME 706.400 20.003 m3 28

TABLE 11 CLASS A SOURCE OF WASTE: PROCESSED DAW TYPE OF CONTAINER: STRONG TIGHT CONTAINER METHOD OF PROCESS: N/A ISOTOPES ACTIVITY (mCi) OF TOTAL Ag-110m 0-OOOE+00 0.004 Am-241 8.800E-04 0.004 C-14 1.130E+00 0.Z.7%

Cm-242 1.030E-03 0. 004 Cm-244 6.200E-04 0.004 Co-58 6.374E+00 0.

Co-60 9.416E+01 944'3.86%

Cr-51 5.395E+00 0.794 Cs-134 O.OOOE+00 0.00%

Cs-137 O.OOOE+00 0.004 Fe-55 1.040E+02 15.314 Fe-59 4.465E+01 6.

H-3 4.742E+01 574'.

I-129 C9.587E-01 984'.

144 I-131 O.OOOE+00 0.004 Mn-54 3.546E+02 52.204 Ni'-63 2.148E+00 0.324 Pu-238 1.660E-03 0.004 Pu-239 6.200E-04 0.

Pu-241 3.103E-01 00%'.

Sb-124 O.OOOE+00 054'.004 Sr-89 O.OOOE+00 0.004 Sr-90 O.OOOE+00 0.004 Tc-99 3.543E-01 0.054 Zn-65 1.778E+Ol 2.624 TOTAL ACTIVITY (Ci) 0.679 CONTAINER VOLUME 1148.300 ft3 100.004'2.517 m3 29

TABLE 12 CLASS A SOURCE OF WASTE: CARTRIDGE FILTERS TYPE OF CONTAINER: HIC METHOD OF PROCESS: N/A ISOTOPES ACTIVITY (mCi) O'F TOTAL Ag-110m O.OOOE+00 0.004 Am-241 2.210E-05 0.

7.372E-03 004'.

C-14 00%

Cm-242 1.909E-03 0. 004'.004 Cm-244 9.683E-04 Co-58 3.667E+00 0.

Co-60 4.762E+02 244'1.594 Cr-51 6.335E+00 0. 42>o Cs-134 O.OOOE+00 0.004 Cs-137 4.824E-01 0.

Fe-55 8.549E+02 034'6.

71%

Fe-59 4.367E+00 0.294 H-3 1.235E-01 0. 014'.004 I-129 +1.807E-02 I-131 O.OOOE+00 0.

Mn-54 8.291E+01 004'.50%

Ni-63 9.740E+00 0.

Pu-238 1.283E-06 654'.00%

Pu-239 O.OOOE+00 0. 004' Pu-241 1.031E-02 F 004 Sb-124 O.OOOE+00 0.004 Sr-89 3.781E-02 0.004 Sr-90 9.186E-04 0.

Tc-99 4 2.359E-02 004'.

Zn-65 6.878E+01 004'.564 TOTAL ACTIVITY (Ci)

CONTAINER VOLUME 1 '08 ft3 114.900 100.004 3.254 m3 30

TABLE 13 CLASS A SOURCE OF WASTE: RWCU FILTER MEDIA TYPE OF CONTAINER: HIC METHOD OF PROCESS: DEWATERED ISOTOPES ACTIVITY (mCi) OF TOTAL Ag-110m O.OOOE+00 0.004 Am-241 2.466E-02 0.004 C-14 5.302E+00 0.004 Cm-242 8.136E-03 0.004 Cm-244 1.736E-02 0.004 Co-58 4 004E+03 0.664 Co-60 2.795E+05 46.32%

Cr-51 2.515E+03 0.424 Cs-134 O.OOOE+00 0.00%

Cs-137 O.OOOE+00 0.004 Fe-55 1.263E+03 0.21%

Fe-59 2 745E+03 0.45%

H-3 2.793E+02 0.054 I-129 +1.326E+00 0.004 I-131 0 ~ OOOE+00 0.

Mn-54 2.674E+05 00%'4.324 Ni-63 3.535E+03 0.

Pu-238 4.405E-02 594'.

Pu-239 4 '17E-02 004'.004 Pu-241 8.625E+00 0.004 Sb-124 O.OOOE+00 0.00%

Sr-89 O.OOOE+00 0.004 Sr-90 5.459E-01 0.004 Tc-99 1.944E+01 0.

Zn-65 4.211E+04 004'.984 TOTAL ACTIVITY (Ci) 603.337 CONTAINER VOLUME 204 '00 100.004't:3 5.794 m3 31

TABLE 14 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT ESTIMATED TOTAL ERRORS ASSOCIATED WITH EFFLUENT MEASUREMENTS Data Period: January 1, 1993 - December 31, 1993 5 Est mated Total Er or

1. Airborne Effluents a ~ Fission and Activation Gases 15.9X

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

d. Tritium 13.6X

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 6.0X

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

Volume of Dilution Water Used During 15.0X Period

3. Solid Wastes a ~ Condensate Demineralizer/ 15.1X Radwaste Demineralizer (Dewatered - Carbon Steel Liner)

b. Condensate Demineralizer/ 15.1X Radwaste Demineralizer (Dewatered - HIC)

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

d. RWCU Filter Media 15.1X (Dewatered - HIC)

e. Ultrasonic Resin Cleaning Waste 15.1X (Dewatered HIC)

f. Processed DAW 25.0X (Strong Tight Container)

g. Cartridge Filters 25.0X (HIC) 32

TABLE 15 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT DATA NOT REPORTED IN PREVIOUS SEMIANNUAL REPORT NUCLIDE CATEGORY UNIT FOURTH QUARTER 1992 A. Airborne Effluents

1. Sr-89 Ci O.OOE+00

2. Sr-90 Ci O.OOE+00

3. Gross Alpha Ci 1.00E-06 B. Waterborne Effluents

1. Sr-89 Ci O.OOE+00

2. Sr-90 Ci O.OOE+00

3. Fe-55 Ci 5.70E-03

3. Gross Al ha Ci O.OOE+00 33

SECTION 3 METEOROLOGICAL DATA AND DISPERSION ESTIMATES 34

NETEOROLOGY AND DISPERSION DAT Heteorological data have been collected at the Susquehanna SES site since the early 1970s. At the present time, the meteorological system is based on a 300-foot high tower located approximately 1,000 feet to the southeast of the plant. Wind sensors are mounted at the 10-meter and 60-meter elevations on this tower. Vertical temperature differential is measured with redundant sensor pairs between the 10m and 60m levels. Sigma theta (the standard deviation of horizontal wind direction) is calculated from wind direction at

. both levels. Dew point and ambient temperature sensors are present at the 10m level. Precipitation is measured at ground level.

A back-up meteorological tower was erected in 1982. It is a 10-meter tower providing alternate measurements of wind speed, wind direction, and sigma theta.

SSES meteorological data is transmitted to the plant control room, Technical Support Center, and Emergency Operations Facility for emergency response availability. The data is also transmitted via telephone line data-link to the PP&L corporate computer in Allentown. On the corporate computer, the data is available for preparation of summary reports, wind rose plots, and dispersion estimates.

Dispersion modeling for effluents from normal operation of SSES is done using XOQDOQ, a straight-line air flow Gaussian plume model designed to estimate average relative concentrations. The model was developed in accordance with Regulatory Guide l. 111. Calm periods are distributed as the first non-zero wind-speed class in the input joint frequency distribution file.

XOQDOQ uses terrain correction factors to account for the temporal and spatial variations in the airflow in the region, since a straight-line trajectory model assumes that a constant mean wind transports and diffuses effluents in the direction of air flow at the release point within the entire region of interest. The SSES terrain correction factors were determined by the ratio of the results of the straight-line model to the puff-advection model, and are incorporated into Table 18.

35

TABLE 16 ANNUAL EFFLUENT AND WASTE DISPOSAL REPORT METEOROLOGICAL DATA AVAILABILITY Data Period: 1993 Parameter Percent of Valid Hours During Period Wind Speed

a. All Sensors Combined 99.6%

b. 10-Meter Sensors 99.6%

c. 60-Meter Sensor 99.6%

Wind Direction

a. All Sensors Combined 99.1%

b. 10-Meter Sensors 99.6%

c. 60-Meter Sensor 99.1%

Indicator of Atmospheric Stability

a. Temperature Differential 98.9%

between 10 and 60 meters (Delta-TA)

b. Temperature Differential 98.9%

between 10 and 60 meters (Delta-TB)

c. Sigma Theta @ 10 Meters 99.6%

Percent of hours for which valid 98.9%

10-meter wind speed. 10-meter wind direction, and temperature differential were available.

Percent ot hours for which valid 98.4%

60-meter wind speed. 60-meter wind direction. and temperature differential were available.

36

FIGURE 5 N

0 0 s CALM O.O ANNUAL .

8724 OSSA 5NS WXNO OXRECTXQN FREQUENCY (PERCENT)

K2Z3MEAN WXNO SPEEO (Mj'SEC )

SSES Pr imar y Tower I 993 IO-meter 1 eve 1 37

FIGURE 6 0,

0 0

CALM O.O ANNUAL.

8881 QBS ~

MSHQ WXND DZRECTZON FREQUENCY (PERCENT)

IZ2~MEAN WXND SPEED (M/SEC )

SSES Pr %mar y Tower 1993 60-meter leve 1 38

Figure 7 SES PASQUILL STABILITYCLASS PREVALENCES Data Period: 1993 Based on Joint Frequency Distributions at 10 Meters (8668 Hourly Values)

Moderately Unstable Slightly Unstable 312 355 3.6%

4.1% Very Unstable 589 Neutral 6.8%

3407 39.3% Very Stable 633 7;3%

Moderately Stable Slightly 1057 Stable 12.2%

2314 26.7%

39

PENNSYLVANIA POMER & LIGHT COMPANY (PP&L) - Susquehanna Steam Electric Station PAGE 2 PROGRAN: JFO VERSIOH: PC-'1.2 Primary ToMer Data - 10-meter level SITE IDENTIFIER:

DATA PER100 EXANINEDt 1/ 1/93 - 12/31/93

• • • ANNUAL ***

STABILITY CLASS A STABILITY BASED ON: DELTA T BETWEEN 60.0 AND 10.0 NEIERS WIND NEASURED AT: 10.0 NETERS WIND THRESHOLD AT: .23 N/S JOINT FREQUENCY DISTRIBUTION OF WIND SPEED AND DIRECTION IH HOURS AT 10.00 NETERS SPEED (N/S) N NHE HE EHE E ESE SE SSE S SSM S'W MSM 'W WNM HW HHW TOTAL D

CALN 0 I/l

.24- 1.50 1 0 0 2 8 7 3 5 3 3 2 0 0 0 0 41 1.51- 3.00 4 13 4 6 4 12 12 21 33 89 29 7 5 0 3 246 3.01- 5.00 0 6 4 0 4 7 5 16 19 77 73 30 11 2 5 260 CU O 5.01- 7.50 1 1 0 0 0 0 0 0 0 5 28 6 0 0 0 41 7.51-10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o-c ~

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CU 'R TOTAL 6 20 8 8 16 12 26 20 42 55 174 132 43 16 2 8 588 K D CU I rTl I/l ll STABILITY CLASS B W Pl M CU AD STABILITY BASED OH: DELTA T BETWEEN 60.0 AND 10.0 METERS M+

'WIND NEASURED AT: 10.0 NETERS I rtl WIND THRESHOLD AT: .23 N/S HA C JOINT FREQUENCY DISTRIBUTION OF WIND SPEED AND DIRECTION IH HOURS AT 10.00 NETERS SPEED (N/S) N NNE HE EHE E ESE SE SSE S SSW S'M MS'W W WHM NM NHM TOTAL l C/l CALM 0 C/l

.24- 1.50 0 0 2 3 4 3 1 2 2 6 1 0 1 0 0 27 1.51- 3.00 3 13 15 4 1 4 3 12 18 38 18 5 7 4 2 148 3.01- 5.00 6 10 1 1 2 3 6 3 8 16 19 8 6 19 7 116 5.01- 7.50 0 1 0 0 0 0 0 0 0 3 9 5 0 0 0 18 7.51-10 ~ 00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 9 24 18 8 7 4 10 10 17 28 63 47 18 14 23 9 309

PENNSYLVANIA POMER & LIGHT COHPANY (PP&L) - Susquehanna Steam Electric Station PAGE 3 PROGRAH: JFD VERSION: PC-1.2 Primary Toxer Data - 10-meter level SITE IDENTIFIER:

DATA PERIOD EXANINED: 1/ 1/93 - 12/31/93

~** ANNUAL ~**

S1'ABILITY CLASS C STABILITY BASED OH: DELTA T BETMEEN 60.0 AHD 10.0 KETERS MIND HEASURED AT: 10.0 METERS IIIHD THRESHOLD AT: .23 II/S JOIHI'REQUENCY DISTRIBUTION OF WIND SPEED AND DIRECTION IH HOURS AT 10.00 NETERS SPEED (H/S) H HNE HE EHE E ESE SE SSE S SSM SM MSM M WHM H'M NNM TOTAL CALH 0

.24- 1.50 0 1 4 7 5 3 4 5 8 5 6 0 2 0 0 54 1.51- 3.00 6 18 10 4 7 6 8 9 14 21 35 20 8 4 7 3 180 3.01- 5.00 14 8 3 2 0 1 1 1 1 2 12 14 12 17 10 9 107 5.01- 7.50 0 0 0 0 0 0 0 0 0 0 3 5 3 2 1 0 14 7.51-10.00 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 20 27 17 13 12 10 13 15 19 31 55 45 24 25 18 12 356 STABILITY CLASS D STABILITY BASED OH: DELTA T BETMEEH 60.0 AHD 10 ~ 0 HE TERS lIIND HEASURED AT: 10.0 HETERS MIND THRESHOLD AT: .23 II/S JOIHI'REQUENCY DISTRIBUTION OF MIND SPEED AND DIRECTION IN HOURS AT 10.00 HETERS SPEED (H/S) N NHE HE ENE E ESE SE SSE S SSM SM MS'M ll MNM NM NHM TOTAL CALH 0

~ 24- 1.50 35 100 120 84 99 80 61 43 54 62 50 20 12 7 9 9 845 1.51- 3.00 115 178 181 68 46 45 67 53 76 93 135 78 68 67 62 84 1416 3.01- 5.00 104 85 33 28 28 27 24 18 14 15 94 94 71 93 104 126 958 5.01- 7.50 5 8 1 7 4 7 2 0 3 2 1 53 32 11 18 33 187 7.51-10.00 0 0 0 0 0 0 1 0 0 0 0 0 1 0 0 1 3

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TO'IAL 259 371 335 187 177 159 155 114 147 172 280 245 184 178 193 253 3409

PENNSYLVANIA POWER &, LIGHT COHPANY (PP&L) - Susquehanna Steam Electric Station PAGE 4 PROGRAH: JFD VERSION: PC-1.2 Primary Tower Data - 10-meter level SI1E IDENTIFIER:

DATA PERIOD EXAMINED: 1/ 1/93 - 12/31/93

• • • ANNUAL ***

STABILITY CLASS E STABILITY BASED ON: DELtA T BETWEEN 60.0 ANO 10.0 METERS MIND MEASURED AT: 10.0 METERS MIND 1HRESHOLD At: ~ 23 H/S JOINT FREOUEHCY DISTRIBUTION OF MIND SPEED AND DIRECI'ION IN HOURS AT 10.00 METERS SPEED (H/S) N NNE NE ENE E ESE SE SSE S SSW SM MSW M MNM NM NNW TOtAL CALH 0

.24- 1.50 43 99 179 253 189 91 86 87 100 124 82 25 9 6 9 14 1396 1.51- 3.00 52 87 72 28 11 9 25 20 75 137 124 59 19 15 24 24 781 3.01- 5.00 6 7 1 2 3 1 3 2 7 10 27 31 8 1 2 5 116 5.01- 7.50 1 0 3 6 1 1 2 0 0 1 0 0 0 0 0 0 15 7.51-10.00 0 0 2 1 0 1 1 0 0 0 0 0 0 0 0 0 5

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 102 193 257 290 204 103 117 109 182 272 233 115 36 22 35 43 2313 STABILITY CLASS F StABILITY BASED ON: DELTA 1 BETMEEH 60.0 AND 10.0 METERS MIND MEASURED AT: 10.0 METERS .

MIND 1HRESHOLD At: .23 H/S JOINt FREQUENCY DISTRIBUTION OF MIND SPEED AND DIRECTION IN HOURS At 10.00 ME1ERS SPEED (H/S) N NHE HE ENE E ESE SE SSE S SSM SM MSM W MNM NW NNM TOTAL CALH 0

.24- 1 ~ 50 11 15 118 388 185 57 45 25 30 24 9 5 4 0 6 6 928 1.51- 3.00 4 6 19 57 0 0 0 0 2 6 12 5 2 0 2 1 116 3.01- 5.00 0 1 1 0 0 0 0 0 0 0 0 1 0 2 2 0 7 5.01- 7.50 0 0 1 0 0 0 0 0 0 0 0 0 0 1 3 0 5 7.51-10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 15 22 139 445 185 57 45 25 32 30 21 11 6 3 14 7, 1057

PENHSYLVAHIA POWER & LIGHT COMPANY (PP&L) - Susquehanna Steam Electric Station PAGE 5 PROGRAM: JFO VERSION: PC-1.2 Primary Tower Data - 10-meter level SITE IDENTIFIER:.

DATA PERIOD EXAMINED: 1/ 1/93 - 12/31/93

• • • ANNUAL *~~

STABILITY CLASS G STABILITY BASED ON: DELTA T BETIIEEH 60.0 AND 10.0 METERS WIND MEASURED AT: 10.0 METERS

'WIND THRESHOLD AT: ~ 23 M/S JOINT FREQUENCY DISTRIBUTION OF WIND SPEED AND OIREC'TIOH IN HOURS AT 10.00 METERS SPEED (M/S) N HNE NE ENE E ESE SE SSE S SSW SW WSW W WNW NW NNW TOTAL CALM 0

.24- 1.50 3 8 82 325 87 17 10 16 11 0 1 0 0 1 563 1.51- 3.00 0 1 4 53 1 0 0 0 0 2 1 0 0 0 0 63 3.01- 5.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5.01- 7.50 0 0 0 0 0 0 0 0 0 0 0 5 4 1 0 10 7.51-10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 3 9 86 378 88 17 10 16 11 2 2 2 5 4 2 1 636 STABILITY CLASS ALL STABILITY BASED ON: DELTA T BETWEEN 60.0 AHD 10.0 METERS WIND MEASURED AT: 10. 0 METERS WIND THRESHOLD AT: .23 M/S JOINT FREQUENCY DISTRIBUTION OF WIND SPEED AHD DIRECI'ION IH HOURS AT 10.00 METERS SPEED (M/S) N NHE HE EHE E ESE SE SSE S SSW SW WS'W W WHW NW NH'W TOTAL CALM 0

~ 24- F 50 93 223 505 1062 577 257 216 180 206 224 155 60 25 16 25 30 3854 1.51- 3.00 184 316 305 220 70 65 116 97 200 309 435 210 109 98 99 117 2950 3.01- 5.00 130 117 43 33 37 31 38 32 41 54 226 232 129 130 139 152 1564 5.01- 7.50 7 10 5 13 5 8 4 0 3 3 12 95 51 18 23 33 290 7.51-10.00 0 0 2 1 0 1 2 0 0 0 0 0 2 0 1 1 10

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 414 666 860 1329 689 362 376 309 450 590 828 597 316 262 287 333 8668

PENNSYLVANIA POMER & LIGHT COHPAHY (PP&L) - Susquehanna Steam Electric Station PAGE 6 PROGRAN: JFD VERSION: PC-1.2 Primary ToMer Data - 10-meter level SITE IDEHTIFIER:

DATA PERIOD EXANINEDt 1/ 1/93 - 12/31/93 AHHUAL ~~*

STABILITY BASED ON: DELTA T BETMEEN 60.0 AHD 10.0 ME'TERS IIIND NEASURED AT: 10.0 HETERS IIIND THRESHOLD AT: .23 k/S TOTAL NUNBER OF OBSERVATIONS: 8760 TO'IAL NUHBER OF VALID OBSERVATIONS: 8668 TOTAL NUMBER OF HISSING OBSERVATIONS: 92 PERCENT DATA RECOVERY FOR THIS PERIOD: 98.9 X NEAN MIND SPEED FOR THIS PERIOD: 2.1 H/S NUMBER OF OBSERVATIONS MITH BACKUP S'IABILITY: 1 TOTAL NUHBER OF OBSERVATIONS MITH BACKUP DATA:

PERCENTAGE OCCURRENCE OF STABILITY CLASSES A 8 C D E F G 6.78 3.56 4.11 39.33 26.68 12.19 7.34 DISTRIBUTION OF MIND DIRECTION VS STABILITY N NHE HE EHE E ESE SE SSE S SSM SM MSM M MNM NM NNM CALH A 6 20 8 8 16 12 26 20 42 55 174 132 43 16 2 8 0 8 9 24 18 8 7 4 10 10 17 28 63 47 18 14 23 9 0 C 20 27 17 13 12 10 13 15 19 31 55 45 24 25 18 12 0 D 259 37'I 335 187 177 159 155 114 147 172 280 245 184 178 193 253 0 E 102 193 257 290 204 103 117 109 182 272 233 115 36 22 35 43 0 F 15 22 139 445 185 57 45 25 32 30 21 11 6 3 14 7 0 G 3 9 86 378 88 17 10 16 11 2 2 2 5 4 2 1 0

'IOTAL 414 666 860 1329 689 362 376 309 450 590 828 597 316 262 287 333 0

PENHSYLVAHIA PSJER 8 LIGHT COMPANY (PP&L) - Susquehanna Steam Electric Station PAGE 2 PROGRAM: JFD VERSION: PC-1.2 1993 Primary Tower Data meter level SITE IDENTIFIER:

DATA PERIOD EXAMINEDt 1/ 1/93 - 12/31/93

• aa ANNUAL as*

STABILITY CLASS A STABILITY BASED OH: DELTA T BETNEEH 60.0 AND 10.0 METERS IIIND MEASURED AT: 60.0 METERS IIIHD THRESHOLD AT: .23 M/S JOIHT FREQUENCY OISTRIBUTIOH OF WIND SPEED AND DIRECTION IN HOURS AT 60.00 METERS SPEED (M/S) H HHE NE EHE E ESE SE SSE S SSH SH WSW IJ LINW HH HHH TOTAL CALM 0

.24- 1.50 0 0 5 7 4 3 2 2 0 4 1 1 0 0 0 29 1.51- 3.00 2 3 7 5 2 9 6 7 17 22 14 1 2 0 3 105 3.01- 5.00 4 14 0 1 2 3 5 15 14 88 57 20 3 2 4 233 5.01- 7.50 2 3 2 0 3 4 3 10 19 46 71 20 1 0 2 186 7.51-10.00 0 0 0 0 0 0 0 0 6 4 19 4 0 0 0 33

>10.00 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 2 TOTAL 8 20 14 13 11 6 19 16 34 56 164 164 46 6 2 9 588 STABILITY CLASS 8 STABILITY BASED ON: DELTA T BETNEEN 60.0 AHD 10.0 METERS 1IIND MEASURED AT: 60.0 METERS NHD THRESHOLD AT: .23 M/S JOINT FREQUENCY DISTRIBUTION OF iIIND SPEED AHD DIRECTION IN HOURS AT 60.00 METERS SPEED (M/S) H NHE NE EHE E ESE SE SSE S SSM SW MSH U INll NM HNH TOTAL CALM 0

.24- 1.50 0 2 4 2 0 0 1 2 2 1 0 0 0 1 17 1.51- 3.00 2 10 8 2 2 3 1 2 12 23 9 4 2 3 1 84 3.01- 5.00 7 16 3 0 2 1 1 9 6 21 28 7 13 14 3 132 5.01- 7.50 0 3 0 1 0 3 5 2 10 6 17 8 3 3 2 63 7.51-10.00 0 1 0 0 0 0 0 0 1 1 6 3 0 0 0 12

>10.00 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 1 TOTAL 9 32 15 5 5 2 7 7 14 31 54 61 22 18 20 7 309

PENNSYLVAHIA POWER 8 LIGHT COMPANY (PAL) - Susquehanna Steam Electric Station PAGE 3 PROGRAM: JFD VERSION: PC-'1.2 1993 Primary Touer Data meter level SITE IDENTIFIER:

DATA PERIOD EXAMINEDt 1/ 1/93 - 12/31/93

• • • ANNUAL <<*>>

STABILITY CLASS C STABILITY BASED ON: DELTA T BETWEEN 60.0 AND 10.0 ME'TERS WIND MEASURED AT: 60.0 HETERS WIND THRESHOLD AT: .23 M/S JOINT FREQUENCY DISTRIBUTION OF WIND SPEED AND DIRECTION IN HOURS AT 60.00 METERS SPEED (H/S) N NNE NE EHE E ESE SE SSE S SSW SW WSW 'W WHW NW NHW TOTAL CALM 0

.24- 1.50 0 3 5 1 3 1 2 2 4 2 4 2 1 0 0 32 1.51- 3.00 3 14 4 6 7 2 4 2 14 27 9 3 0 0 2 101 3.01- 5.00 14 9 9 1 0 6 5 7 10 20 20 11 13 19 6 152 5.01- 7.50 4 4 1 1 0 1 0 3 6 6 13 12 5 1 1 58 7.51-10.00 0 0 0 0 0 0 0 0 0 1 6 2 0 0 0 9

>10.00 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 1 TOTAL 21 30 19 9 10 8 10 11 14 34 56 52 31 19 20 9 353 STABILITY CLASS D S1'ABILITY BASED ON: DELTA T BETWEEN 60.0 AND 10.0 METERS

'WIND MEASURED AT: 60.0 METERS WIND THRESHOLD AT: .23 M/S JOINT FREOUEHCY DISTRIBUTION OF WIND SPEED AND DIRECTION IN HOURS AT 60.00 METERS SPEED (H/S) N NNE NE ENE E ESE SE SSE S SSW SW WSW W WHW NW HNW TOTAL CALM 0

.24- 1.50 29 68 77 48 24 23 21 18 21 20 32 18 7 4 7 12 429 1.51- 3.00 62 114 119 57 26 32 22 32 17 44 100 54 39 18 38 27 801 3.01- 5.00 132 140 113 39 37 37 43 32 41 58 86 114 95 110 105 118 1300 5.01- 7.50 37 76 26 16 20 22 18 17 18 37 40 140 73 64 52 61 717 7.51-10.00 3 7 1 4 2 7 2 0 5 5 2 40 21 3 6 11 119

>10.00 0 3 0 2 0 1 1 0 0 1 0 5 2 0 0 0 15 TOTAL 263 408 336 166 109 122 107 99 102 165 260 371 237 199 208 229 3381

PENNSYLVANIA POMER & LIGHT COMPANY (PP&L) - Susquehanna Steam Electric Station PAGE 4 PROGRAM: JFD VERSION: PC-1.2 1993 Primary Tower Data meter level SITE IDENTIFIER:

DATA PERIOD EXAMINED: 1/ I/93 - 12/31/93

<<<<<< ANNUAL <<*<<

STABILITY CLASS E STABILITY BASED OH: DELTA T BETIIEEH 60.0 AHD 10.0 METERS MIND MEASURED AT: 60.0 METERS IIIND THRESHOLD AT: .23 H/S JOINT FREQUENCY DISTRIBUTION OF WIND SPEED AND DIRECTION IN HOURS AT 60.00 HETERS SPEED (H/S) H NHE NE ENE E ESE SE SSE S SSW SW WSW W WNW HW NHW TOTAL CALM 0

.24- 1.50 51 106 109 48 31 29 17 26 24 36 37 24 14 8 9 15 584 1.51- 3.00 51 182 107 42 20 21 26 27 29 59 82 68 25 16 20 15 790 3.01- 5.00 31 47 55 10 9 6 18 22 58 101 120 130 25 17 30 15 694 5.01- 7.50 1 7 1 1 1 5 4 1 14 40 24 82 15 0 2 1 199 7.51-10.00 1 0 0 2 1 0 2 0 0 5 2 0 0 0 0 14

>10.00 0 0 5 5 0 2 0 0 0 0 0 0 0 0 0 13 TOTAL 135 342 277 108 62 63 68 76 125 241 264 306 79 41 61 46 2294 STABILITY CLASS F STABILITY BASED OH: DELTA T BETMEEH 60.0 AND 10.0 METERS IIIHD MEASURED AT: 60.0 METERS WIND THRESHOLD AT: .23 H/S JOIHI'REQUENCY DISTRIBUTION OF IIIKD SPEED AND DIRECTION IH HOURS AT 60.00 HETERS SPEED (H/S) N HNE NE ENE E ESE SE SSE S SSW SM WSW M MNM HM NNM TOTAL CALH 0

.24- 1.50 35 109 91 46 22 21 20 15 18 20 19 4 2 6 7 9 444 1.51- 3.00 70 220 64 8 3 2 3 6 16 23 39 12 6 6 4 4 486 3.01- 5.00 7 16 10 4 0 0 0 0 1 18 14 22 4 5 3 1 105 5.01- 7.50 0 1 0 0 0 0 0 0 1 1 1 10 0 1 0 0 15 7.51-10.00 0 0 2 0 0 0 0 0 0 0 0 0 0 1 4 0 7

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 112 346 167 58 25 23 23 21 36 62 73 48 12 19 18 14 1057

PENNSYLVANIA POWER & LIGHT COMPAHY (PP&L) - Susquehanna Steam Electric Station PAGE 5 PROGRAM: JFD VERSION: PC-1.2 1993 Primary Tower Data meter level SITE IDEHTIFIER:

DATA PERIOD EXAMIHEDt 1/ 1/93 - 12/31/93 ANNUAL ~*~

STABILITY CLASS G STABILITY BASED ON: DELI'A T BETWEEN 60.0 AND 10.0 METERS MIND MEASURED AT: 60.0 METERS WIND THRESHOLD AT: .23 M/S JOINT FREQUENCY DISTRIBUTION OF MIND SPEED AND DIRECTION IN HOURS AT 60 F 00 METERS SPEED (M/S) H HNE NE EHE E ESE SE SSE S SSM SM WSM M MNM NM NNM TOTAL CALM 0

.24- 1.50 11 55 60 28 13 19 10 10 19 9 7 6 4 3 0 3 257 1.51- 3.00 21 144 52 15 8 3 11 10 14 28 1C 2 0 0 5 1 328 3.01- 5.00 3 8 1 0 0 0 0 0 3 11 3 9 1 0 0 0 39 5.01- 7.50 0 0 0 0 0 0 0 0 0 0 0 2 1 0 0 0 3 7.51-10.00 0 0 0 0 0 0 0 0 0 0 0 0 4 5 0 0 9

>10.00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 TOTAL 35 207 113 43 21 22 21 20 36 48 24 19 10 8 5 . 4 636 STABILITY CLASS ALL STABILITY BASED ON: DELTA T BETWEEN 60.0 AND 10.0 METERS MIND MEASURED AT: 60,0 METERS MIND THRESHOLD AT: .23 M/S JOINT FREQUEHCY DISTRIBUTION OF MIND SPEED AND DIRECTION IH HOURS AT 60.00 KE'TERS SPEED (M/S) N NNE NE ENE E ESE SE SSE S SSM SM IISM M MNll HM NNM TOTAL CALM 0

.24- 1.50 126 3C3 351 180 9S 95 72 73 87 91 103 58 30 22 23 40 1792 1.51- 3.00 211 687 361 135 68 67 76 S6 87 197 307 168 78 44 70 53 2695 3.01- 5.00 198 250 191 55 50 47 71 65 134 218 352 3SO 163 161 173 1C7 2655 5.01- 7.50 44 94 30 19 24 27 30 26 48 113 123 335 129 74 58 67 1241 7.51-10.00 4 8 3 6 3 7 4 0 5 17 9 73 3C 9 10 11 203

>10.00 0 3 5 7 0 3 2 0 0 1 1 7 3 0 0 0 32 TOTAL 583 1385 941 402 243 246 255 250 361 637 895 1021 437 310 334 318 8618

PENNSYLVANIA PSIER 8 LIGHl'OMPANY (PPBL) - Susquehanna Steam Electric Station PAGE 6 PROGRAM: JFO VERSION: PC-1.2 1993 Primary ToNer Data meter level SITE IDENTIFIER:

DATA PERIOD EXAMINED: 1/ 1/93 - 12/31/93

• +* ANNUAL **~

STABILITY BASED ON: DELTA T BETNEEN 60.0 AND 10.0 METERS

'HIND MEASURED AT: 60.0 METERS NHD THRESHOLD AT: .23 M/S TOI'AL NUMBER OF OBSERVATIONS: 8760 TOTAL NUMBER OF VALID OBSERVATIONS: 8618 TOTAL NUMBER OF MISSING OBSERVATIONS: 142 PERCENT DATA RECOVERY FOR THIS PERIOD: 98.4 X MEAN MIND SPEED FOR THIS PERIOD: 3.3 M/S NUMBER OF OBSERVATIONS NITH BACKUP STABILITY: 1 TOTAL NUMBER OF OBSERVATIONS IIITH BACKUP DATA: 1 PERCENTAGE OCCURRENCE OF STABILITY CLASSES A 8 C D E F G 6.82 3 ~ 59 4.10 39.23 26.62 12.27 7.38 DISTRIBUT ION OF HIND DIRECTION VS STABILITY N NNE HE ENE E ESE SE SSE S SSN SN NSW II NNN HN HHM CALM A 8 20 14 13 11 6 19 16 34 56 164 164 46 6 2 9 0 8 9 32 15 5 5 2 7 7 14 31 54 61 22 18 20 7 0 C 21 30 19 9 10 8 10 11 14 34 56 52 31 19 20 9 0 D 263 408 336 166 109 122 107 99 102 165 260 371 237 199 208 229 0 E 135 342 277 108 62 63 68 76 125 241 264 306 79 41 61 46 0 F 112 346 167 58 25 23 23 21 36 62 73 48 12 19 18 14 0 G 35 207 113 43 21 22 21 20 36 48 24 19 10 8 5 4 0 TOTAL 583 1385 941 402 243 246 255 250 361 637 895 1021 437 310 334 318 0

TABLE 18 AVERAGE ANNUAL RELATIVE CONCENTRATIONS Page 1 of 5 SutquNIanna Sttae fleCtr(C Stat ten ~ GYSSD.LEVEL RELEASE . 1993 ND DECAY, UNDEPLEIED C(NRKCYEO FOR OPEN TERRAIN RECIRCULAYICN USING SPECIAL IERRAIN ADJUSIHENY FACIDRS ANNUAL AVERAGE CHI/O (SEC/HE'IER CU)(D) DISTANCE IN HILES SKCYDR .250 .SOO ..50 1.000 1.500 2.000 2.500 3.000 3.500 C.ooo C.500 S 1.403'5 c.bscf.oe Z.rsrf oe I.rbsf.oe 9.368K or s.99rf.or C.?00K.or 2.944K or Z.lslf.or 1. 650E 07 1. 302E OT SQI 2.(i47E-OS 8.669E.O& 5.112E.O& 3.223K ~ 06 '1.8&DE.06 1.202K 06 d.sCIE.OT 5.93&E 07 C.t30E Ol 3.2C&E 07 2.519E 07 SV 5. ICSE.OS 1.616E ~ 05 9.5&SE ~ 06 6.25$ E.O& 3.CTSE.06 2.282K 06 1.655E 06 1 ~ 20SE 06 9.0?SE 07 T.Clif 07 $ .636K 07 VQI 1.149E.04 3.586E F 05 Z.ll3KF 05 I.CTIE-OS 8.392E F 06 5.800E-O& C.422K ~ 06 3.2C3f.ob 2.4388.06 1.986K 06 1.650E 06

'V 6.$ 06E ~ 0$ Z.oobf.os I.o-'cf.os &.seed-ob 3.491K.M Z.trbf-ob $ .&35K.ob $ .179K ob 8.760K or 7.073f OT $ .78&E Ol YNY Z.rrcf ~ 0$ b.dorE ~ 06 4.894K 06 3.112E 06 1.772E.O& 1. IC2K.O& 8.0CSE 07 S.bbrf 07 C.C&)E.OT 3.607E-OT Z.M3E.OT t.bstE ~ 05 8.990E 06 5.$ 8GK ~ Ob 3.27&E.O& 1.8&If.ob 1.207'6 8.623E.OT &.CSCK.OT $ .021K.OT 4.03?f 07 3.293E 07 NNY 1.DICE ~ 0$ &.C?3E'Ob 3.77CE'06 2.662K 06 I ~ C2&E 06 9.C1CE'l 6.8C9E Ol C.96&E'07 3.713E Ol 3.112K.OT 2.65&E.OT N 2.1CtE 0$ 6.731( 06 ).Tlrf.ob 2.3$ SE.O& ).389K Ob 9.60M.OT 7.288E Ol 5.329K ~ Or C.OC?E Ol 3.336K Ol 2.80ZE F 07 NME 2 '52E 05 8.317K ~ De C.TS?E ~ 06 3.279K Ob 'I.lllE-O& 1.21CE-D& 9.09&E.OT 6.6$ IE.OT S.OSIE-ol C.ITCE Ol 3.$ $ 3f.ol NE 2.118E 0$ 6.952E ~ De C.049E 06 2.579K 06 I.C79K ~ 06 1.009E 06 7.521E.OT $ .&OCE Ol 4.349K.OT 3.629E 07 3.08SE.OT ENK 1.209K.OS 3.9C9f 06 2.2$ CE.06 1.5248.06 8.142E 07 S ~ 555E 07 C.166K 07 3.1'PBE'Ol Z.SSIE'07 2.152E Ol l.d57E.OT E &.ICSE 06 2.ob3E.06 I.ICSE.06 6.880E Ol 3.&CSE Ol 2.363E OT 1.687K ~ 07 1.2tCE ~ Ol 9.t43E 08 r.(esf-ob 6.168K.M ESE 5.711E 06 I ~ bdtf 06 I.OC?E.06 6.210E 07 3.1CCE.OT $ .919E 07 1.289K.or 9.227K'08 6.876K 08 5.17CE-08 3.959E.08 SE 6.917E ~ 06 2 ~ 312K 06 1.338E.06 8.711E 07 C.SCSE.OT 2.860K.or 1.970K.OT 1.339E 07 9.336K 08 6.928E 08 5.203E 08 SSE 8.320E'06 2 ~ 972E.O& 1.713E 06 1.038E 06 5 ~ 380K.or 3.51CE.OT 2.516E.OT I ~ 7dlf 07 I ~ 3'lof.or 9.619E 08 7.088E 08 ANNUAL AVERAGE CHI/O (SEC/HEIfR CUBED) DISYANCE IN HILES BEARING 5.000 7.500 ID.COO Is. 000 20. 000 25. 000 30. 000 35.000 Co.ooo 45.000 50.000 S I ~ 076K F 07 4 ~ 839E ~ 08 Z.C8$ E F 08 5.830K 09 2.628E 09 9.2&SE 10 C.978E 10 2.23CE.IO $ .486K.lo 9.C7CE.II 8.197K I'I SQI 2.084E Ol 9.CODE.DB 5.09CE.08 1.60&E 08 7.159E'09 2.6248.09 1.2drK 09 C.336K 'lo Z.bbrf.lo 1.228E 10 1.063E 10 SY 4.735K ~ 07 2.335E.OT 1.28IE 07 s.dssf 08 1.927E 08 8.737E.09 5.106E 09 2 ~ lllf'09 1.870E 09 I ~ Ortf 09 9.379K 10 YQI 1.COSE 06 l.stlf.ol C.CCBE ~ 07 1.1SZE.OT S.37&E 08 1.938E.OB 1.059E ~ Ob C.ocrf.09 t.291E 09 9.920E 10 8.72CE 10 Y C.b&9E.OT 2.311E.OT 1.252K.OT 3.$ 05E 08 I.C86E 08 4 '38K 09 2.297E 09 8.096K 10 4.$ 598 10 1.965E 10 1.721E-IO YNV 2.500E 07 1.Z&TE Ol T.Clef 08 Z.CZCE.08 1.121K.ob C.2COK.09 $ .83M.09 2.8)cf lo 1.STCE 10 5.398E 1$ C ~ TOCE 11 NV 2.790K Ol I.ccbf.or 8.219E.08 2.935K 08 '1.25$ E.08 3.8CBE 09 $ .8508.09 4.7$ 9E 10 t.bsdE.IO 1.138E 10 9.900E 11 NNV 2.278K.or 'I ~ 263E Ol 7.100K 08 2.C19E.08 1.065E.08 3.5blf.09 2.218E 09 'I 25CE 09 7.(iolE.IO

~ C.OIOK 10 3.C95E.10 N 2.536K 07 1.790K 07 9.589K 08 2.666E 08 1 ~ 321K ~ Od 6.049E.09 3.025E.09 1.067K 09 6.$ 8&f~ 10 2.939E.10 t.557E.10 NNE 2.998E Ol 1.616E ol 8.77IE 08 2 689E'08 '1.205K M C ~ 437E 09

~ 2.C86E ~ 09 1.139K 09 7.306K. 10 C.SS9E 10 3.780E 10 NE 2.&COE OT I.C6&f.ol B.C)CE 08 3.265K.od ).398E 08 4.338K 09 2.399E 09 1.079E 09 6.$ 988.$ 0 3.S77E 10 3.101'0 ENE 1.59CE.OT b.795E.OB $ .667E ~ 08 2.dSOE 08 '1.538E 08 8.5&CE.09 C.668E ~ 09 2.1608.09 1.3$ 1f.09 7.C2OE.IO 6 434K 10 E 5.223E 08 Z.TCOE M 1.559E.M $ .958E 09 3.089K ~ 09 1.618K 09 8.277K 10 3.245K F 10 1.9C&E F 10 1.016K.lo 8.78CE 11 ESE 3.220K ~ 08 1.3C9f 08 7.&TCE.09 2.990K 09 I.S93E 09 8.81&E 10 C.?DOE 10 I ~ 166E 10 d.C2$ E ll 2 '17E I'I 2.340K 11 SK C ~ ?08K 08 1.63$ K'08 9.St&8 09 3.8C3K 09 1.&SOE 09 S.39&E 10 2.707E 10 9.930E 11 4.9$ 1E.11 I.C02E 11 1.213E 11 SSE $ .737K 08 2.307E.od 1.30tE.OB 4.9)sf'09 Z. ISSE 09 7.663E-IO 3.9C&E 10 'I.SBTE 10 9.397K 11 C.779K 11 C.IZCE 11 CHI/O (SEC/HEIER CUBED) FDR EACH $ (GHENI SECHENY B(XNOARIES IN HILES DIRECTION .5 ~ I I~2 2.3 3~C C 5 5 10 10.20 20 30 30.40 40 50 FROH SIYE 8 2.791E 06 9 ~ 7$ 5E Ol C. ITTE Ol 2.180E 07 1.321E Or 5. 109E. 08 8.633K 09 1.209K 09 2.73)E 10 1.060K 'lo SSV $ .0638.06 I.dlof.o6 B.C?SE 07 C.)CZE 07 Z.STSE F 07 1.003E 07 1.9858.08 3.299E 09 6.223E 10 $ .&SBE 10 Ql 9.559E.O& 3.562K ~ 06 '1.6C2E 06 9.1C6E Ol 5.728E 07 2.CDOE.OT C.982E 08 1.009E 08 3.07$ E 09 $ .2598 09 YSV 2.17SE.OS d.&CCE ~ 06 4.3'IBK 06 2. C9&E.O& 1.659K 06 7.362K 07 1.523E 07 2.503E M $ .2C9E 09 1.333E 09 V $ .0858.05 3.63$ 06f 1.62CE.06 8.98CE 07 5.8288.07 2.409K Ol 4.611E 08 6.2618.09 1. I oof . 09 2.&C3E 10 YNV 4.972E 06 I ~ 790E'06 d.oblE.OT 4.$ 44E'07 2.983E.OT 1. 292E ~ 07 2.879E 08 $ .137E 09 6.790E 10 B.ZO&E 11 NV 5.181E.O& 1.88$ E ~ 06 8.674E.DT 5.054K 07 3.326K-or 1.CME Ol 3.363E F 08 5.370E 09 T,M3E 10 1.$ 33E 10 NNV 3.869E 06 I.CBSE 06 6.78DE.ol 3.842E.OT 2.6$ 1E 07 $ .243K OT 2.8$ 7E 08 C.9?OE 09 1.341E 09 C.MSE 10 N 3.80ZE.O& 1.413f 06 7.122E.OT C.ICIE 07 2.8&ZE 07 1.586E Ol 3.&DYE.08 6.7CBE 09 1. 456K. 09 3.7&DE 10 NNK 4.8898 06 $ .86)f 06 8.93IE Ol 5.17CE.OT 3.S I BK.OT 1.595E 07 3.381E.08 5.688E 09 1.368E 09 S.OIBE 10 NE 4.0CIE 06 I.S ICE ~ 06 7.438K.OT 4,433E 07 3 ~ Oblf Ol 1. 450E. 07 3.SBCE M 6.133E 09 1.297E 09 4. 2968.10 ENE 2.306E ~ 06 8.$ 69E Ol C. IC9E.OT t.584E.OT 1.8CTE 07 8.992E 08 2.893E 08 8.82CK 09 t.568E 09 d.bS9f 10 E I.ISOE 06 3 ~ 79CE Ol 1.682E OT 9.C22E 08 6.202E F 08 2.767K 08 6.823E.09 1.69CE 09 C. Ibdf . 10 $ .2CIE 10 ESE 1.0CZE.O& 3 ~ 2818 07 1.31DE 07 6.899E 08 4.0CSE M 1.50&E.08 3.CIOE 09 8.867E 10 1.833E 10 3.676K 11 SE 1.3CTE ~ 06 C ~ 722K OT 1.955E Ol 9.ST&E 08 5 ~ 34SE Od 1.903K 08 C.13'IE 09 7.2dof F 10 1.293E 10 2.384K I'I SSE 1.693E 06 5.662K Ol Z.C90( F 07 1.31CE 07 7.338E.08 2 '22E 08 S.CCRE 09 9.879E $ 0 2.015E 10 5.905K 11 VKNI AND BUILDING PARAIIEIERSI RELEASE HF. ICHY (HEIERS) 6'I 30 REP. VINO HEIGHT (IIEYERS) 10.0 DIANE YER (HEYERS) 00 BUILDING NEICHY (IIEIERS) 61.3 EXIT VELOCITY (H/SEC ) 00 BLOC.HIN.CRS.SEC.AREA (SO.HKYERS) 257S.O HEAT KHI SS ION RAIE (CAL/SEC) ~ 0 AT THE RELEASE HEIGHT) AT YNE HEASUREO VINO NEICHY ( 10.0 HEYERS)t VENY RELEASE INX)f VINO SPKED (HflfRS/SIC) VENT RELEASE HCDE VIIO SPEED (HEIERS/SEC) YIND SPEED (HEYERS/SEC)

I S FABLE CONDITIONS UNSTABLE/NEUIRAL COO IYIONS ELEVAIED LESS THAN . COO ELEVAlfo LESS YNAN .000 LESS THAN .000-HIXED ~ BEYVEEN .000 AND .000 i HIXED BEYVEEN .000 AND .000 BElVEEN .000 AND .000 GROUND LFVEL ABOVE . 000 GR(XNO LEVEL ABOVE .000 ABOVE .000 50

Page 2 of 5 Susquenuns Steaa Electric B(Ation ~ GROUND. LEVEL RELEASE ~ 1993 2.260 DAT D(CAT, CADIPLEI(D CORRECIED IDR OPEN IERRAIN RECIRCUlATION USING SPECIAL I(BRAIN ADJUSIHENI fACIDRS ANNUAL AVERAGE CHI/O (SEC/HKIER CUBED) DIS'(ANCE IN HILES SECIOR ~ 250 .500 .750 1.000 1.500 2.000 2.500 3.000 3.500 C.OOO C.SDO S I.C02E OS C.843E-OS Z.TCTE-GS 1.777E-OS 9.30CE.OT $ .9C2E.OT C.152E.OT 2.903E 07 2.096K 07 1.619E 07 1.27CK Ol SIV Z.644( 0$ 8.6CTE 06 $ .093K 06 3.206E M 'I.BCSE 06 1.189E 06 B.C)lf Ol S.BCCE'07 C ~ ISCf'07 3 ~ 179E 07 2 ~ CSIE Ol SV 5.13TE.051.611K ~ 05 9.523E ~ OS d.218E.06 3.CC2E ~ 06 2.255E ~ 06 1.630K-OS 1.184E OS b.d37E 07 6.90tE 07 S.CBSE ~ Ol VSV I. ICTE OC 3.575K ~ 05 2.162K.OS I.C62E 0$ 8.313E 06 S.727K.06 C.352E.06 3 'd2E 06 2 '84K'OS 1.937E OS I 603E 06

~

V 6.496(.0$ t.OOOE 05 1.039E.OS 6.50CE.OS 3.CUE 06 t.ZC9K 06 I.d09E 06 I ~ ISTE 06 8.564E'Ol 6.892E 07 S.SZOE Ol GNV 2.770(.0$ 8.780K 06 C.BTIE 06 3.093K 06 I ~ TSSE 06 1.12dE 06 7.920K 07 S ~ TTTE Ol C ~ 366E 07 3.518E'07 Z.MIE 07 NV 2.82dK.OS 8.963E-06 $ .157K.OS 3.257E.06 1.84CE 06 1.193E 06 B.CBCE ~ 07 6.339K Ol 4.916K Ol 3.935E 07 3 ~ 205E OT xwV 1.911E'0$ 6.C03E.06 3.757E ~ 06 2.646E 06 I.C13E ~ 06 9.301E Ol S.TCSE ~ OT C.bllf Ol 3.635E 07 3.037E'Ol 2.584E OT N 2.139E 05 6.712E.06 3.761K 06 2.3C2E 06 1.3llf 06 9.C95E OT 7.185E OT 5.239K 07 3.962E Ol 3.261E 07 t.731E Ol NNE 2.3C9E 05 8.29$ E.OS C.733E 06 3.2dlE OS 1.763E 06 1.201E.DS 8.976E 07 6.5CSE.OT C.957E ~ Ol C.086E 07 3.430K.OT NE 2.115E 0$ d.937K'06 4.035E 06 2.568E OS I.C69f 06 9.99CE Ol 7.CSSE OT $ .5288.07 C.tdOE 07 3.5S3f Ol 3.022E.07 ENK I ~ 208E'0$ 3.9C2E ~ 06 Z.ZC7E 06 1.51dE 06 8.096K Ol S.512K ~ 07 C.12SE Ol 3.1dlE 07 2.517E.OT 2.119E 07 $ .825K.OT E 6.139E ~ 06 2.079E ~ 06 I. ICOE ~ 06 d.856K.OT 3.62SE OT 2.3C6E 07 1.672E ~ Ol 1.211E 07 9.128E ~ 08 7.357E 08 6.069K.08 Kff 5 ~ 707E 06 I.MOE ~ 06 1.039E ~ OS 6.192E 07 3.130E Ol 1.907K Ol 1.279E Ol 9.1CSE 08 6.80CE ~ 08 5.112E 08 3.906E.M SE 6.910E.OS 2.3ME.OS 1.335E ~ 06 8.680E Ol C.521E-OT 2.8COE.OT 1.9$ 2E.OT $ .324K 07 9.217E 08 6.827E'08 5 ~ 117E 08 SSK 8.313E'06 2.967E'06 1.708E 06 1.035E OS 5.352E OT 3.C89E'07 2.C93E OT 1.767E Ol 1.293E ~ OT 9.CTBE 08 6.970E.08 ANNUAL AY(RACK Cxl/0 (S(C/HKIER CUBKD) DISfANCE IN HILES BEARING 5.000 7.500 10.000 15.000 20.000 25.000 30.000 3S.OOO CO.OOO C5.000 50.000

$ $ .051( DT C.669( 08 2.369E.Dd 5.424K 09 2.386E 09 8.210K ~ 10 C.)OCE' 10 1.885f 10 1.22CE ~ 10 T.SISE ~ 11 S.C)IE ~ 11

$ $V 2.030'7 9.03dE 08 C.M3E F 08 I.C84E.08 S.CCZK.09 2.300K.09 $ .099K.09 3.60SE 10 2.33M. $ 0 9.686K ll B. Ibdf ~ 11 SV 4.594K Ol 2.231E F 07 I ~ 205f 07 3.C99E.DB 1.70$ E.OB T.C96E-09 C.ZCBE-09 2.187E 09 I.C62E 09 8.135E 10 d.899E 10 VSV 1.361E ~ 06 6.98ZE.OT S.dOOK Ol 1.048E 07 C.736E 08 1.6$ CE 08 B.ldlE.09 3.2C2E 09 1.778E 09 T.CSIE 10 d.358E 10 V C.TICE 07 t.ZOZE.OT 1.173K Ol 3.179E.08 1.305K.M 3.$ )TE.09 $ .890K.09 d.4CTE 10 3.51CE ~ 10 I.CSSE 10 1.243K.IO vxv 2.C22E 07 1.208K F 07 d.642K F 08 2.204E ~ 08 9.869E 09 3.dllE ~ 09 $ .$ $ 9E 09 t.252E 10 1.220E ~ 10 4.0$ 3E 11 3.C21E 11 xv Z.TOTE 07 1.383E F 07 7.733E F 08 2.678E 08 1.111E-OB 3.302E.09 $ .$ 398.09 3.839K 10 Z.MOE 10 d.6)OE 11 7.28CE 11 NNV 2.209E F 07 1.206E 07 S.dlbE.08 2.2068.08 9.CIZE 09 3.068K.09 $ .842K ~ 09 I.OIOE 09 5.93CE.IO 3.035E 10 2.565E 10 N Z.CSCE.OT 1.TICK 07 9.053K 08 2.CCSE M $ .176K 08 S.236E 09 2.SCIE 09 8.717E 10 C.909K 10 2.267E 10 1.916E 10 xxE 2.919E.OT 1.553E F 07 8.313E F 08 2.CBIE 08 I.MSE 08 3 88ZE 09 ~ t.llbf 09 9.CSOE 10 S.905E 10 3 ~ C32E 10 2.899E 10 NE 2.5dDK.OT I.CISE F 07 8.057K F 08 3.049E 08 I.ZTSE.M 3.873K ~ 09 2.09SE.09 9.219K 10 5.512f.10 2.92CE 10 t.CBOE 10 fxE 1.563E Ol B.SC3E 08 S.CSZE 08 Z.dbbf M I.CZSK 08 7.773K.09 C.ISSE 09 I.MTK 09 1.1$ dE ~ 09 d.2COK 10 5.311E 10 E'.130K 08 2.667E 08 1.503E 08 S.SCOE 09 t.bllf 09 I.CTTE.09 7.419K 10 Z.dSlE 10 $ .683K 10 8.637K 'I'I 7.333K 11 ESE 3.172'8 1.319E 08 7.CCSE.09 2.8$ 8E 09 1.500E ~ 09 8.'ITBE 10 3.838K 10 1.050E 10 5 702E 11 2.376E 11 2.017K 11 BE C.13'lf M I.SB'PE 08 9.171E 09 Sebtbf 09 1.527E 09 4.89dE 10 Z.C09E 10 8.665E 11 C.237E ~ 11 1.177K ~ 11 9.980E 12 Sff 5.63IE.DB 2.2CtE M, 1.253E F 08 4.635K 09 '1.992E ~ 09 6.9CCE-IO 3 ~ SOCE 10 I ~ 38IE 10 B.DICE.II 3.99CE 11 3.378K I'I CHI/O (SEC/HE'IKR CUB(D) fOR EACH SKCHKNI I(CHEN'f BCUNDARIKS Ik HILfS DIRECIIDN .5 ~ I I~2 2~3 3 ' C 5 5 IO 10 20 20 30 30 40 CO 50 TRON BIIE S 2.782E 06 9 '91E.OT C.129K 07 Z. 14$ E.OT $ .29CE F 07 C.94SE.OB 8.132E 09 I . 082E. 09 2.32CE 10 d.SC7K. II SQI S.OCCK ~ 06 I.b56E 06 8.319E.OT 4.265E 07 2. 5 ICE ~ 07 9.672E 08 f 1.85$ 08 Z.92CE.09 5. 232E. 10 1.318E 10 Qi 9. S I TE ~ 06 3.$ 31E 06 1.618E F 06 8.957E OT 5.57$ E 07 2.300E 07 C.SO)E 08 d.TCCE 09 2. SOOE.09 9.600K 10 vQJ 2. 165 E.DS 8.$ 6$ E 06 C.251E 06 Z.CCZE 06 1.612K 06 7.041K ~ 07 'I.C04E ~ Ol Z. ISSE 08 4.2blf.09 1. 011K.09 V 1.080E ~ 05 3.S97K.06 $ .599K 06 8.78$ E 07 5.661E. Ol 2.303E 07 C.ZCTE 08 S.COBE.09 8.887K. 10 1.990K-I 0 vxv C.949E.OS 1.77CE.06 T. 958E. Ol C.CCSE.OT 2. 900K. 07 1.236E Ol 2.6C9f 08 4.CCSE 09 5. 556K . 10 6.234K 1$

NV 5.158E 06 1.868'6 8.547E.OT C.9C9E Ol 3.237E'07 I.C06E.OT 3.10$ E M 4.678E.09 d. CSBE. 10 1.174E.IO xxv 3.8SIE.06 I ~ 472K Od 6.679E F 07 3.762K 07 2.580E 07 1.190K.OT 2.637E 08 C.269E 09 1.089E 09 3.720E. 10 N 3.786K 06 I.C02E.OS 7.022E 07 C.OSDE F 07 2.789K 07 $ .521E 07 3.350E 08 $ .900K.09 1.204E.09 t.920K-IO NNE C.STIES 06 I.BCSK 06 8.814E OT 5.079E 07 3.43$ E F 07 t.SSSK.OT 3.1$ 6E 08 5.030K.09 I.ICSE 09 3.968E 'IO xf C.OZBE ~ OS I.SOCK.OS 7.35$ E 07 C.363E 07 3.019E Ol I.C04E 07 3.374E.OB S.532E.09 1.116E 09 3.527E 10 (NE 2.300E ~ DS 8.522E ~ OT C.I ICE 07 2.$ C9E 07F 1.8'ISE 07 B.TCCE F 08 2.7COE F 08 8.048E ~ 09 Z. 257E ~ 09 T.CTBE 10 E I.ICTE 06 3.775'7 1.667K 07 9.30SE 08 6.103E 08 2.697E.OB d.C96E ~ 09 1.555K.09 3. 713K ~ 10 1.058E 10 EBE 1.039K 06 3.267'7 1.301E 07 S.btdf.ob 3. 991E. 08 I.CTSE.OB 3.2lCK 09 8.261E 10 1. 664 E. 10 3.229E 11 SE 1.3CCE 06 C.698'7 1.938E 07 9.CSSE.OS S.tSdK 08 $ .8$ $ E 08 3.926K 09 d.66BE 10 1. 139K .10 2. 017E. 1$

SSK 1.689K.06 5 '33K.OT 2.CSBE.OT I ~ 297K 07 7.217E.M 2.556K 08 5.215E 09 9.029K.IO 1. 767E. 10 C.9$ 7E. I I VENT AND BUILDINC PA RAHEIERB(

RELEASE HEIGHf (HKIERS) 61 30 RKP. VIXD HEIGHI (HEIERB) lb.0 DIAHEIER If (Hf RS) 00 BUILDING HKIGHt (HKIERB) 61.3 EXlf V(LOCI IT (H/$ (C ) 00 BLOC.NIN.CRB.BEC.AREA (BD.HEffRS) 25TS.O HEAT fNISS(ON RAIE (CAL/SEC) .0 Af THE RELEASE HEIGHT( I At 'IHK HKASURED VIND HEICxf ( 10.0 HKIERS)f VENt RELEASE HCDE VIXD SPE(0 (HKTERS/SEC) VENt RELEASE HCDK VINO BPfED (HEIERS/SEC) VINO SPEED (HEIERS/SEC)

I I SIABLE CONDITIONS UNSTABLE/N(VIRAL CCNDlflDNS ELEVAIK0 LESS IHAN . 000 ELEVATED LKSS IHAN .000 LESS THAN 000 I F HI XKD Bf flfEN .000 AND .000 NIXK0 BEIN(EN .000 AND .000 BEIVKEN .000 NO .000 GR(XWO LKVKL ABOVE .000 I GR(X/ND LEVEL ABOVE .000 ABOVE .000 51

Page 3 of 5 Suso~cccvs Slece Electric SIR(ien ~ GROUND ~ LEVEL RELEASE - 1993

8. CD OAY DECAY, DEPLETED CC'IRICIKD FDR OPEII IERRAIN RKCIRCULAIIDN USINC SPECIAL IERRAIN ADJUSIN(HI FACIORS ANNUAL AVERAGE CNI/O (SEC/HETER CUBED) DIS'IANCK IN HILES lf'ICR .250 .500 .750 1.000 1.500 2.000 2.500 3.000 3.500 C.ooo C.SDO I 1.3tBE.OS 4.4)of.od Z.CSCE.06 I.SSIE 06 7.94'IE.DT C.DS3E.OT 3.391E Ol 2.329K 07 I.dSSE 07 1.26DE Ol 9.78)E 08

$$V 2.5GSK.OS 7.911E 06 4.551E ~ 06 Z.SITE.06 I.S76E.06 9.921K ~ 07 d.69)E OT C.694E 07 3.254E'OT 2.471E'07 '1.692E OT IV 4.667K 05 I.CTCE 05 6.513E ~ 06 $ .466E 06 2.9C2E 06 I.MSE 06 I ~ 335E 06 9.526K Ol T.DOGE Ol 5.391K 07 C.ttdf.or elV 1.067K 04 S.tltf 05 1.933E.OS I.tdSE 05 T.lodf 06 C ~ TSSE 06 3.566E 06 2.562E 06 I.d90E.06 1.51CE ~ Ob 1.237E.Ob J 6.155E 05 1.831K 05 9.290E.06 5.72OE.06 2.957E 06 1.879E 06 I ~ 319E 06 9.316E.OT 6.792E ~ 07 $ .390f.ol C.339E.OT dsV 2.62CE F 05 6.036K F 06 4.355E-06 2.719E.06 1.501K-ob 9.CZIE.OT 6.C88E.OT 4.65)E 07 3.C61E.OT 2.750E OT 2.223E 07 vV 2.679E-OS 6.202E ~ 06 C.SIDE 06 t.863K.ob I.SM.06 9.960E ~ Ol 6.955K.ol $ .101E 07 3.59$ E or 3.074E'or Z.CTIE 07 vI V I.dllf OS $ .660E ~ 06 3.359E 06 2.327E 06 I.ZMK.06 7.769K ~ 07 5.52CE OT 3.92$ E Ol Z.ddof Ol 2.373E'07 1.99)K 07 2.026E.OS 6.1C2E Ob 3.362E 06 t.oSSE 06 1.177E 06 7.927E Ol S bdof 07 4.212E'Ol 3 ~ )36K 07 t.S45E'Ol

~ t.loCE Ol 2.225E OS T.Sd9E 06 C.230E 06 2.866E 06 1.506E 06 1.002E ~ 06 7.3CIE Ol 5.259E.OT 3.921E 07 3.165E Ol 2.636K.OT 2 003E 0$ d.SCSE.06

~ 3.605E.ob Z.ZSSE 06 I.ZSCE 06 8.3308.07 d.oltE ~ 07 4.43CE.DT 3.378E 07 2.771E 07 2.319E.OT cvf I.ICCE.OS 3.60$ E-ob 2.007E.06 1.332E 06 6.904E Ol C.S90f 07 3.365E 07 2.532K OT 1.983E Ol 1.6CSE 07 $ .39)K.OT l S.SICE 06 I ~ 901K 06 I ~ 018E 06 d.oldE'07 3.091E ~ 07 1.952K.ol 1.363E.OT 9.694K OS T.ldlE'08 5.706E 05 4.642K ~ 08 Il E 5.C04E 06 1.718E.06 9.278f 07 S.C32E Ol 2.667E Ol 1.566E ~ 07 I.OC2E 07 7.311K 05 5.3C9E 08 3.955E 08 t.962E 05 lf b.SCCE ~ 06 2.110E.06 1.192E.06 7.617E Ol S.SSCK 07 2.363E ~ 07 1.592E 07 1.060E Ol 7.255E 08 5 ~ 296E'05 3.91SE 08 Ilf 7.8738.06 2.713E.06 1.525E-06 9.079E.OT C.562E.OT 2.904E OT 2.032E 07 I.C15E 07 1.018E 07 7.3$ 3E'05 5.33(E 05 AVVUAL AVERAGE CHI/O (SEC/HKIKR CUBED) DISIANCE IN NILES BEARING 5.000 7 ~ $ 00 10.000 15.000 20.000 25.000 30.000 35.000 Co.ooo 45 ~ 000 50.000 1 7.966E 08 3 ~ 377E ~ 08 1.647K Od 3.552E.09 1.4935-09 4.953E 10 t.519E 10 1.07CE ~ 10 6.816E 11 4.156K.II S.CCSE 11 I IV 1.542E F 07 6.55CE.OS 3.372E F 05 9.76SE.09 4.056K ~ 09 $ .399K ~ 09 6.491K 10 Z.DTTE 10 1.3ldE 10 5.358E ~ ll C.C4tE 'll IV 3.500E.or 1.625E 07 8.460E F 06 2.32CE.od 1.087E.08 C.629K 09 Z.SS6E 09 '1.288E 09 S.CSSE.ID 4.631K 10 3.67CE ~ 10

~ IV I ~ 03M 06 5.092E 07 2.671E 07 6.9M Od 3.029E.OS 1.025K.08 5.295K 09 1.919K 09 1.03CE 09 C ~ ZTSE ~ 10 3.59CE.IO 1.596K Ol 1.607E 07 8.258E 08 2.120E 08 6 ~ 366E 09 2 ~ 167E 09 I ~ IC7E 09 3.d33E 10 2 ~ OSCE 10 S.CCSE 11 7.073K 11

~ 'liV I.SCTE 07 S.610E 05 C.669E 08 I.C68E 08 6.313K 09 Z.ZCSE.09 9.156E 10 1.33CE ~ 10 7.10CE 11 2.3ZCE 11 1.937E 11 NV 2 ~ 0628 07 1.008E.OT S.C2lE ~ 08 I.lldf 05 7.082K 09 2.039K'09 9.259K 10 2.261K 10 1.202E 10 C.912E 11 C.069K ll vvV 1.653K 07 6.789E 08 C.6ME 08 I.C66E.OS 6.005E ~ 09 1.697K.09 1.110K 09 5.953K 10 3.436K 10 1.73OE 10 I.CC3E.IO N 1.675K 07 1.2CSE 07 6.33SE 08 1.616E Od 7.464K 09 3 ~ 213K ~ 09 $ .5198.09 $ .087K 10 2.809K 10 1.27SL ~ 10 1.061E ~ 10 vvf Z.ZISE 07 1.127'7 S.SOCE.08 1.63CE 05 6.530K 09 2.36CE 09 1.2535.09 S.C52f.lo 3.33CE ~ 10 1.901E ~ 10 1.$ 79E ~ 10 vf 1.955E F 07 1.023K.OT 5.593E.OS 1.991E 08 7.955E ~ 09 2.32CE ~ 09 1.2178.09 S.210f 10 3.0398.$ 0 $ .577K ~ 10 1.310E ~ 10 cvl I.lbtf Ol 6.$ 49E 05 S.rdbf ~ Od I.TC)E 06 8.786E 09 C.dlof 09 2.381E.D9 I.OC9E 09 6.267K.ID 3.296E ~ 10 Z.TC3E 10

( 3.674f 05 1.917K.M $ .0)bf.od $ .648E 09 I.ldlE ~ 09 d.ltCE ~ 10 4.231K ~ 10 1.56OE.IO 9.049E 11 C.529E ll 3.757K ~ 11

!SE 2.3(OE 08 9.CSIE.09 $ .112E 09 $ .636K ~ 09 9.1CBE.IO C.TTSK.IO Z.IS9E 10 S.TISE I'I 3.011K II 1.221E.II 1.0108.11 I'E 3.) Zof.ob I. IC3E.DS 6.33)E 09 2.3518.09 9.C2CK 10 2.905K 10 1.361E 10 C.SZIE 11 2.296E ~ 11 b.ttbf ~ $ 2 S.lbbf lt llf C.ZSCf.o6 1.613E.05 d.bSSE.09 3.005E 09 1.231E 09 C.lttE ~ 10 2.012E-IO 7.702E.II C.SSSE.II 2.119E ~ 11 I.TSCK 11 CHI/O (BE C/NEIER CUBED) FDR KACH SKCHKNI SKCNENI B(ANOARIES IN HILKS 0 IRECI I CH .5~ I I~ 2 2~3 3~4 C ~

5 5-10 10.20 20 30 30 CO 40 $ 0 FRCN Sllf 5 2.496K od 8.316K.or 3.383E.07 1.69lE 07 9.945E.OS 3.628E.OS 5.507K.09 6.6COE 10 1.337E 10 C,661E.II 11V C.52lf ~

06 1.592E Ob 6.521K 07 3.379E.OT $ .936K.OT 7.109K 08 I.ESSE 05 I.dobf 09 3.0CBE 10 7.336E I I lv S.SC3E.06 3.03tE.06 1.328K 06 l. $ 098.ol 4.30!E.ol 1.695E 07 3.13ff.od S.CSCE 09 I.CSZE 09 5.464K 10

's)v $ .9C3E 05 7.3528.06 3.490E.06 $ .939K 06 1.2CSE 06 5.192E 07 9.608K 05 1.3dlE 05 Z.SCTE 09 S.dtof 10 v 9.707E 06 3.092E 06 I . 313E. Od 6.979E ~ Ol C.3758.07 $ .702E 07 2.91CE 05 3.4198.09 5.336E 10 I.IS2f 10 VW C.C46E-Db ).523E 06 6.535E 07 S.SSOE.OT 2.2COE F 07 9. I 1bf . 05 1. 507E. 05 2.799K 09 3.3COE 10 3.597K.II vv C.632f Db 1.604E.06 7.015E 07 3.927E Ol 2.C96E.DT 1.0)SE Ol t.llCE 05 2.939K 09 3.557K Io 6. 714 E. I 'I vvV 3.456K.ob 1.265K F 06 5.463E F 07 2.9dSE F 07 1.99IE 07 S.TSCE Od 1.797K 05 2.67SE 09 6.46CK 10 2.129E 10 v S.COIE.Db 1.202f 06 5.759E.OT 3.216E 07 2.150K ~ 07 1.11(E 07 2.280K 08 3.669E 09 7.105K.lo 1.6SOE.IO vvf C.370K 06 I.SSCE 06 7.22CE.OT C.023E OT 2.645E ~ or 1. )26K .07 2.138E 08 3.110E 09 b. 66lE ~ 10 Z.tolf.lo vl 3.61CE Ob 1.289E Ob 6.019'7 S.C49E F 07 2.318E 07 1. 024 E. 07 2.260K 08 3.383E 09 6.372K 10 1.911E 10 Evf 2.062E 06 7.302E 07 3.358E OT 2.011E 07 1.391E 07 6.349E 08 1. SOSE. 08 4.6328.09 '1.269E 09 3.971E 10 E 1.029E 06 3.235E OT 1.363E.OT 7.339K 05 C.673E.OS 1.960K 05 4. 304 E. 09 9.3$ 1E 10 2.060K F 10 S.SSZE I'I

-:IE 9.325E Ol 2.50'IE Ol $ .063K 07 5.3608.08 3.052E.DS 1.073K 05 2.15CE 09 4.69CE 'Io 9.219E 11 $ .673E 11 lf 1.205E 06 C.026K ~ Ol 1.585E 07 T.C65E ~ 08 4.0305.08 1.3Sbf ~ 08 2.609K 09 C.03CE 10 6.C27E 11 1.079E 11 IIE 1.515K'06 4.829E 07 2.018E 07 I.OZCE.OT 5.532E F 08 1.865E 05 3.471K 09 S.CSIE 10 9.974E 11 t 646E 11 VENT Avo BUILDING PARAHEIERS(

RELEASE HEICHI (NEIERS) 6 1.30 REP, VINO NEICHI (NEIERS) 10.0 CIAHEIER (NEIERS) BUILDING NEICNF (NEIERS) 61.3 c/II VELOCIIY (H/SEC ) BLOC.NIN.CRS.SEC.AREA (SD.NEIERS) 257S.O NEAT EHI SS ION RAIf (CAL/SEC) .0 AI I I RELEASE NEICNI) I AI INK NEASURED VINO NEICHI ( 10.0 NEIKRS)c VENI e(LEASE HCDE VINO SPEED (NEIERB/BKC) I VENT RELEASE HOOK VINO SPEED (NKIKRS/BEC) HIND SPEED (NKIKRS/SEC)

I BIAS(f CONDITIONS UNSIABLE/NEUIRAL COND I IIONS c'cyAIED LESS THAN .000 I KLEVAIED LESS IHAN .000 LESS 'IHAN .ODD II I X(D BE)VEEN .000 AND .000 HIRED SFIVKEN .000 AND .000 BEIVKEN .ODO AND .000 CCCUND LEVKL ABOVE .000 I GROUND LEVEL ABOVE .000 ABOVE . 000

BILEVEL Page 4 of 5 5 V5 +INIMhhw SteMH f(ectrie SfafioII ~ GROUND RELEASE ~ 1993 CORRECTED fDR OPEN fERRAIN RECIRCUI ATICM USING SPECIAL TERRAIN ADJUSIHKNI FACTORS RELATIVE D(POSITION PKR Uwlf AREA (N 2) A'I FIXED POINIS SY DOVMMIMD SECTORS DIRECTION DISTANCES IN MILES f RON SITE .25 .SO ?5 I OO 150 200 R50 300 350 .00 C50 S 6.C99E.OB 2.282E.CB 1.200(.08 7.25)E.09 J.C25E 09 2.02CE.N $ .3265.09 b. 779E 10 6.0CCE 10 C.474E ~ 10 3.3NE 10 SSM '$.023K.OT $ .415E 05 I.fbtf 08 I.N6E 05 5.699K 09 J.$ 99E 09 t.259E ~ 09 1.453K N 1.00CE N 7.366E 10 5.486E 10 SM I.NIE.OT 3.730E.OB 2.15CE ~ 08 $ .323E ~ 05 6.53CE 09 3 ~ 589K 09 2 ~ 5795.09 1.742E N '1.221E.09 9.022E ~ 10 d.b20t.10 MSM 1.536E Ol J.C64E ~ 08 3.391E.OB 2.177E ~ 08 1.099E.OB d.782E.09 C.bCCE.N 3.113E ~ 09 2.164E.09 1.646E.N 1.285K.09 M 1.05CE 07 3.611E.CB 1.562E 08 1.09CK.OB S. I JTE 09 3.012E.09 1.966E-09 1.308E.N 9.065f.$ 0 d.bBDE.IO 5 ~ $ 235.10 VMM 6.166E 08 2.093E ~ 08 1.117E 05 6.626E ~ 09 3.3CZE N 1.957E.09 1.270E.09 8.669K 10 6.185E ~ 10 4.7365.$ 0 J.TOCf.10 MM 7.535E ~ 08 2.5CBE.OB 1.395E 08 8,22lf ~ 09 C.135E.09 Z.C45E ~ 09 1.615E.09 1.131E-N d.295E.10 6.321K-IO 4.925K-$ 0 M N'M C.BSIE ~ 08 I.TCJE 08 9.712(.09 6.COCE ~ 09 3.0615.09 1.843t-09 1.237E.N B.JTBE 10 5.900K.IO C.687E.ID 3.blDE 10 N 6.523E 08 2.185E 08 I ~ 148E 05 6.666E'09 3 ~ C99E'09 2 2NE 09 I 553E N

~ ~ 1.063K ~ 09 7.617E 10 5.97ZE ~ 10 4 789E ~ 10~

MM( 8.395E ~ 08 3.132E 08 I.b(ZE.DB 1.05GE 08 5.069E.N 3.176E.N 2.216E-N 1.525K.N 1.098K.N 8.651E ~ 10 6.973E ~ 10 NE 1.200E.07 4.03E ~ 05 Z.ZZBE-OB 1,327E-CB d,bJOE 09 4 315K 09 3.01Ct.09 ~ 2 ~ IZJE N $ .565K.N 1.2515-09 1.0215.09 fME 9.451E'08 3 2NE'08 I 717E'05 1.09)E ~ 08 5 299E'09 3.35SE 09 2.364E.09

~ ~ ~ 1.719E 09 I.JCTE 09 1.056E 09 8.766E 10 E C 876E Od 1.656E.OB d.539E.N C.BJBE N 2.3 34K 09 I.C09E-09 9.CTTE ~ 10 6.53CE 10 C.TISf 10 3.655E ~ 10 2.910E 10 KSE 4.7C3E-OB 1.527E Ob 7.901K 09 C.C59K N Z.OBCE 09 1.196t.09 7.629E ~ 10

~ ~ 5,22CK 10 3.741K-IO Z.Tlbf 10 Z.OIIE 10 SE C.697E-OB 1.575E 08 5.58BE.N 5.253E N 2.C86E.N I.C52E ~ 09 9.401K 10

~ 6.056E-IO C.029K ~ 10 2.866K ~ 10 2.0?OE 10 SSE 5.69CE 08 2.016E Ob I.CSIF ~ Ob 6.142K 09 2.585K 09 1.?JOE N 1.$ ?bf 09 7.940K 10 5.556E 10 3.914K ~ 10 Z.lllf 1D DIRECTION DISTANCES IN MILES IROH Sl'IF. 5.00 7.50 10.00 15.00 20.DD 25.00 30.00 35.00 40.00 45.00 50.00 S 2.698E 10 1.06$ E.IO 5.172E ~ lt 1.0895 11 C.CSOE.12 I.C37K 12 7. Itbf 13 2.973E-IJ I.BC9E ~ 13 1.108E.I 3 9.0C3f.lC SSM C.369E 10 1.727E ~ 10 B.BCDK.II 2.C97E ~ II 1.008E 11 3.378K 12 1.529K ~ 12 C.783f 13 2.975E 13 1.188E.13 9.698K.IC SM J.CBOK 10 2.265E-IO 1.142E ~ 10 2.942E 11 1.30'If.ll 5.280E 12 2.796E 12 $ .359E 12 8.6C3E 13 4.603E ~ 13 J.757E 13 VSM 1.035E 09 4 CIOE $ 0

~ 2 ~ 196E 10 5 ZCSE 11 2 116E 11 6.7COE 12 3.JOCK 12 I.ICSE ~ 12 $ .936K 13

~ ~ 2.371('13 1.935E 1$

M 4 ~ 2$ 7E ~ 10 I 686K ~ 10 8 339K-11 $ .994K 11 T,C06E ~ 12 $ ,839E

~ ~ lt 9.225E ~ 13 2.969E 1$ 1,539K ~ 13 6.1Cbf.lC 5.016E.1C VMM 2.9SBE 10 1.291E 10 6.689E 11 Z.CODE ~ II 8.215K 12 2.802E t2 I ~ 10dE 12 1.560E 1$ 8.055K.IC 2.583E $ 4 2.109E ~ IC MM 3.994K 10 1.7?BE 10 9.395K 11 t.943K 11 1.123E 11 3.111E 12 1.366E ~ 12 3.240K ~ 1$ 1.679E ~ 13 6.708E ~ 14 5.475E ~ 14 MMM 3.126E 10 I.CBDE ~ 10 7.72lf.ll 2.297E I'I d.980E ~ 12 2.722E ~ 12 I.JJTE ~ 12 7.988E 13 C.486E 13 2.205E ~ 13 I.dOOE 1$

N 4.152K-10 2.520E 10 1.259E 10 3.0?BE II $ .362E 11 5.645E.12 2.582E 12 B.C02E 13 C.523K 13 Z.COTE 13 $ .635K 13 NME 5.715E 10 2.68OE.IO 1.367K.IO 3.726E 11 1.503E ~ 11 S.OCOE tt 2.595E.12 1.102K.IZ 6.585E 13 3.6BCE ~ 13 3.007E ~ IJ NE B.CIDE.IO C ~ OBTE.IO 2 220K 10 7.679E.II 2.96?E.11

~ 5.395K.IZ C.tlbE 12 I.TBCE.IZ I.CITE ~ It 5.17OE ~ 13 C ~ 220E ~ 13 (ME 7.251E 10 3.516K 10 2.1CCE 10 9.66OE. 11 4.706E ~ 1$ 2.3905.11 1.199E 11 S. ICCE.IZ 3.000E ~ 12 1.5CCE.12 1.2615.12 E 2.3dlf 10 $ .108E ~ 10 d.OOCE 11 2.079E ~ 11 9.8$ 3E ~ IR C.723E 12 2.236K It 8.169E 13 C.JSTE 13 2.255E ~ 13 $ .541E 13 KSE I 586E-10

~ 5.977E 11 3 ~ 273E 11 1.172t'l 5.73?f ~ 12 Z.OJTE ~ 12 1.303K.12 3.38?E 13 1.755E ~ 13 7.011E 14 5 ~ ?23K IC SE I.dlSE 10 5.536K 11 3.063E 11 I.IICE 11 C.3CZE ~ 12 I ~ 302E 12 6.038E 13 2.061E 13 9.dlSE IC 2.560f 14 2.NOE IC SSE 2.170E 10 T.TJJE 11 C ~ 16CE ll 1.CZCK 11 5.TOlt ~ 12 I.fd?f lt 5.917E ~ 13 3.3485.$ 3 1.559E.13 8.911E 14 7.273f 14

~ 001100110t RELATIVE DEPOSITION PER UNIT AREA (H~~ 2) BT OONIIND SKCIORS SECHENT SCUNDARIES IN MILES DIRECTION .5 I I~ 2 2 ' 3 ' 4 ' F 10 10.20 20 30 JO.CO 40 50 IRON SITE 5 1.230K F 08 3.653E.N $ ,333E 09 6.228E 10 3.CSSE. 10 1. 184 E ~ 10 1. TIDE. 11 1.95lf 12 3.73ZE 13 1.25ZE 13 SSM I. 866E. 08 5. BCSE. N 2.252E 09 1.039K N 5.629E. 10 1.9395.$ 0 3.2CJE Il CD 42CE.IZ 7.095K 13 1.63TE 13 SM 2.135K 08 6.846E.09 2.59Cf N 1.248E.09 6.969K 10 2.476E.10 4.095E 11 6.3CBE 12 1.581E 12 5.487K 13 MSM 3.312E 08 1.152K ~ 08 C.602K 09 2.238K.N 1.299E 09 C. 746E. 10 T.JTOE $ 1 9 '12E.12 1.552E ~ 12 J.266E 1$

M 1.909K.OB 5.4835.09 1.982E.09 9.381E F 10 5. 390K. 10 1. 879K. 10 2.d47E 11 2 95?f 12 C 211E-13

~ B.C66E 14 MMM 1. 132K. 08 3. 456E ~ 09 l.292E N 6.3C3E.IO 3.74CE 10 1.392E 10 2.518E 11 3 568E.lt 3.993E.I3 4.037E IC

$ .397E 08 4.293E 09 1.643E N d.403E 10 C.99Ct 10 1.8985 10 3. 568E ~ 11 C ~ JTTE-12 5.624E.IJ 9.240E IC MMM 9.961E.09 3.262K.N I ~ 239K 09 6.1Cbf.10 J.blbf.10 1.531E 10 R.BBDE 11 3 ~ 917E. I 2 8. 762E ~ 13 2.731E 13 N 1.165'8 3.630E.N 1.532E.09 7.853E ~ 'IO 4.90CE. 10 2.322E.IO C.C295.11 6 ~ SCJE 12 1.$ 90E ~ 12 2. 616E '13 Mwf I.TIDE Od 5.436E N Z.$ 96E.09 I . 131E. 09 7.005 E. 10 2.771E 10 C.947E ll 6.72lf ~ 12 1. 360( ~ 12 C.ZBCf 13 ME 2.25lf.08 T. tC9E 09 3.OOCt.09 1.605E.N 1.022E 09 4.2ISK 10 8.5'IIE 11 I.ZCZE 11 2.20CE.IZ d.300E 1$

ENE 1.7?IE.OB 5.686E.N Z.3?IE 09 I.JJCE.09 B.?38K.10 3.7$ ?K.10 1.DOBE 10 2.531E 11 6.28)K.12 1.871E 12 8.67?E.N 2.479K N 9.529K 10 4.831E F 10 Z.935E 10 '1.165E.IO 2.463K-II 5.086E 12 1. 086K ~ 12 2.793K 1$

KSK 8.009f 09 '.21lE.N T.BZZK 10 3.7?CE.IO 2.062E.10 6. 971K . 11 1. 373 E. I I 3.03DE 12 5. $ 205-13 9.655K 14 Sf 8.698K 09 2.6C2f -09 9.C29E 10 C.165E 10 2.1385.10 6.796E 11 1.2CJE.II I.SJJE 12 2.?TBE 1$ C.C76E 14 SSK 1.081E 08 J. IOCE 09 I ~ 177E 09 5.612E F 10 2. 889E ~ 10 9.250E 'll 1.652E 11 2.C99E.12 4.372E IJ I.lllf 13 VENI AMD BUILDING PARANETERSI RELEASE HEIGHT (HKTERS) 6$ .30 REP ~ MIND REICH'I (HETERS) 10.0 OIAHt'TER (HETERS) .00 BUILDING HEIGHT (METERS) 61.3 EXIT VELOCITT (H/SEC ) .00 BLOC.HIN.CRS.SEC.AREA (SO.HETERS) 2575.0 MKAT ENI SCION RAfE (CAL/SEC) .0 AT THE RELEASE HEIGHTI At THE MEASURED MIND HEIGHT ( 10.0 HtfERS)I V(MI RELEASE HCDE MIND SPEED OIEIKRS/5(C) I VKNI RKLtASE HODE MIND SPEED (HfffRS/SEC) 'MIND SPEED (METERS/SEC)

I STABLE COMDI IONGf UNSTABLE/N(UIRAL CONDIf tONS KLEVAIKD I.fSS THAN . OOO I ELEVAI(D LESS THAN .DOO Lt'SS THAM .ODO MIMIC Bt INKfN .000 AMD .DOO MIX(D BEtMKEN .OOO AND .OOO BETH(EN .OOO AND .OOO CRCUMD LEVEL ABOVE . OOO GR(XIMD LEVEL ABOVE .OOO ABOVf .OOO 53

Susquehanna Stean Electric Station ~ c(QAA) LEYEL RELEASE ~ )003 SPECIFtc POINIS OI latfaEST OA'ELKASE IYPK OI I (CIION DIS'IAN(K X/0 Page 5 of 5 10 LOCA I ION <Ntlfs) (NftfRS) (SEC/CUC.HETER) <SEC/CUD.NflfR) <5( ICUS.NEIER) <P(a SO,NEI(R)

No DECAY t.tbo DAY DECAY S.C 0 DAY DECAY

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I StARK CONDITIONS UNSIASLE/NfUIRAL COO IT IDNS ELKVAI(0 lESS INAN .000 ELEVAIKD LESS THAN .000 lESS 'IRAN ~ 000 NIXKD S(t&(N .000 ANO NI XKD St(VEEN .000 NO .000 SEINE(a ~ OCO AND .000 CRQNO lEVEL ASOVE,000 CRQNO LEVEL ASOVC .000 ASOVK 000

SECTION 4 DOSE MEASUREMENTS AND ASSESSMENTS 55

Radiolo ical Im act on Han Sampling and analysis of airborne and waterborne effluents were performed in accordance with the frequencies, types of analysis, and Lower Limit of Detection (LLD) outlined in the SSES Technical Specifications.

Radioactive material was detected in some of the airborne and waterborne effluent samples analyzed. Dose calculations using measured effluent activity levels, meteorological data from the current reporting period and quarterly averaged .river flow dilution factors resulted in estimated doses to individuals at levels below 10 CFR 20 and 10 CFR 50, Appendix I limits.

Direct radiation resulting from plant operation, as measured by environmental thermoluminescent dosimeters located around the plant, did not contribute any measurable dose to members of the public for the reporting period. Since there are no other fuel cycle sources within 8 km of SSES, 40 CFR 190 limits were neither approached nor exceeded.

Doses to a maximally exposed member of the public from waterborne effluents are calculated for fish ingestion and shoreline exposure at the plant outfall, and drinking water ingestion at Danville, PA. Site specific parameters used in the calculations for the Danville receiver, specific for actual average blowdown and river level in each quarter and the entire year, are shown in Table 19.

TABLE 19 SITE-SPECIFIC PARAHETERS USED FOR LADTAP II CALCULATIONS (DANVILLE RECEIVER)

FOR EACH UARTER AND ENTIRE YEAR: 1993 First Second Third Fourth Entire Parameter Qtr. Qtr. Qtr. Qtr. Year Cooling Tower Blowdown 15.6 18.4 15.4 14.1 15.8 CFS Average Net River Level 7.4 10.1 3.5 6.7 6.9 ft 1 Dilution Factor at 456.6 1285.3 280.9 378.8 413.2 Danville 2 Transit time to 23 13.5 45.9 26.2 24.7 Danville hr 2 (1) Net River Level Depth (ft above HSL) -

Table 5-4 483'2)

From ODCH

Summaries of maximum individual doses resulting from airborne and waterborne radioactive effluent releases are given in Table 20.

Heteorological data from Section 3 were used to calculate the dose from airborne effluents.

Technical Specification 6.9. l. ll requires assessment of radiation doses from radioactive airborne and waterborne effluent to members of the public within the site boundary. There are no significant exposure pathways from waterborne effluents in these areas. Onsite doses are assessed relative to offsite dose values and are adjusted for appropriate dispersion and occupancy factors. Summaries of the calculated maximum onsite doses resulting from airborne effluents are presented in Tables 21 through 25.

57

TABLE 20

SUMMARY

OF MAXIMUM INDIVIDUAL OFFSITE DOSES AND DOSE COMMITMENTS TO MEMBERS OF THE PUBLIC DATA PERIOD: I/1/93 TO 12/31/93 EST IHATED LOCATIQI PERCENT NAXIIRH( DIST AFFECTED OF LINIT EFFLUEHT DOSE (HILES) SECTOR LINIT (NREN)

LIOUIDro TEEN TOTAL BODY 6.96E-03 (3) 0.23 (NREN)"'IOUID"'DULT GI-LLI 1.49E.02 (3) 0.15 10 AIR DOSE 2.68E-03 1.03 MSM 0.03 10 NOBLE GAS (GANNA-HRAD)

NOBLE GAS N/A AIR DOSE 7.96E-03 1.03 MSM 0.04 20 (BETA-HRAD)

NOBLE GAS H/A TOTAL BODY 1.56E-03 1.03 MSM 0.03 NOBLE GAS N/A SKIN 4.40E.03 1.03 MSM 0.03 15 ICOINE AND TEEN LUNG 1.69E-02 1.10 MSM 0.12 15 PARTICULATES

"'Estimated dose is based on n site total activity release.

'"10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

'Doses from liquid effluent are estimated from fish ingestion and shoreline exposure at the site outfall and from the drinking water pathway at Danville, PA.

AIRBORNE PATH'MAYS ANALYZED: 1.03 (MSM) PLUNE, GROUND, INHALATIOH 1.10 (MSM) PLUNE, GROUND, VEGETATION, IHHALATIOH MATERBORNE PATHMAYS ANALYZED: FISH, DRINKIHG MATER, SHORELINE The maxlaua calculated dose from all 1993 SSES waterborne effluent (combined pathways) was 1.49-02 mrem (ADULT, G I -LLI ) .

The maxiaxan calculated dose from all 1993 SSES airborne effluent (both units) nt 1.03 miles (MSM sector) was 3.83-02 mrem (TEEN, SKIN).

The mnxiaxxa calculated dose from all 1993 SSES airborne effluent (both units) nt 1.10 miles (MSM sector) was 3.46E-02 mrem (TEEN, SKIN).

58

DOSES TO MEMBERS OF THE PUBLIC WITHIN THE SITE BOUNDARY SSES Technical Specification 6.9. 1.11 requires that the Annual Effluent Release Reports include an assessment of the radiation dose from radioactive effluents to members of the public within the site boundary. Within the SSES site boundary there are seven areas which are open to members of the public (See Figure 8):

~ The Susquehanna Riverlands Recreation Area/

Energy Information Center

~ Residences in the north-northeast, east southeast, southeast, west southwest, west, west northwest and north northwest sectors In the area comprising the Riverlands recreation area, which surrounds the Energy Information Center, four pathways of radiation exposure can be identified; plume, ground, inhalation, and direct radiation. There are no significant exposure pathways from waterborne effluents in this area. There are approximately 100,000 visitors to the Riverlands/Information Center complex each year. In order to visitor facilitate dose calculations, it is assumed that each stays in the area for one hour.

Use of the GASPAR code yields calculated doses for the Riverlands area for the report period. These doses are the total doses at the location from gaseous effluents during the report period. In order to compute doses to members of the public who stay for only short periods of time, these doses are converted to dose rates. Taking into account the estimated 100,000 person-hours of occupancy, the collective (person-rem) doses shown in Table 21 are calculated.

Calculated doses for residences within the SSES site boundary for the following sectors are presented in Tables 22 through 25.

~ north northeast (0.90 miles)

~ east southeast (0.50 miles)

~ southeast (0.40 miles)

~ west southwest (1.10 miles)

~ west (1.20 miles)

~ west northwest (0.80 miles) and

~ north northwest (0.60 miles) 59

FIGURE 8 i

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LEGEND SUSQUEHANNA STEAM ELECTRIC STATION SITE BOUNDARY DISTANCES . P&L Property BounderV IDISTANCES IN FEET) Sector Wheel <22.54egree)

PENNSYLVANIA POWER 5 LIGHT Ro!rroeds Score in F et IV HALLIBURTON NUS 0 600 1000 2000 60

TABLE 21 CALCULATED COLLECTIVE DOSES TO MEMBERS OF THE PUBLIC MITHIN THE RIVERLANDS/INFORMATION CENTER COMPLEX Data Period: 1/1/93 12/31/93 MAXIMUM COLLECTIVE EFFLUENT AGE APPLICABLE DOSE RATE+ DOSE GROUP ORGAN MREM HR PERSON-REM NOBLE GAS N/A TOTAL BODY 5.61E-OS 5.61E-06 NOBLE GAS N A SKIN 1.59E-07 1.59E-05 IODINE AND TEEN SKIN 2.11E-06 2.11E-04 PARTICULATES

<<Estimated maxisam dose rate is based on a site total activity release.

PATHMAYS AHALYZED: PLUHE, GROUHD, 1HHALATiOH

TABLE 22 CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 0.90 NILES NNE SECTOR Data Period: 1/1/93 12/31/93 EST I HATED PERCENT NAXIILMDOSE OF LINIT EFFLlKNT (NREH) LINIT (NREH)

NOBLE GAS H/A TOTAL BODY 4.07E.04 0.01 NOBLE GAS N/A SKIN 1.15E 03 0.01 15 IODINE AND TEEN LUNG 5.91E-03 0.04 15 PARTICULATES 10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

PATHMAYS ANALYZED'LUHEy GROUND~ INHALATION The maxiaua calculated dose from all 1993 SSES airborne effluent (both mits) at this location was 1.29E-02 mrem (TEEH, SKIN).

CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 0.50 NILES ESE SECTOR DATE PERIOD: 1/1/93 TO 12/31/93 ESTIMATED PERCENT APPL I CABLE NAXIILMDOSE OF LIHIT EFFLUENT ORGAN (NRBI) LIHIT (NRBI)

N/A TOTAL BODY 2.07E-04 <0.01 NOBLE GAS N/A SKIM 5.84E-04 <0.01 15 NOBLE GAS IODINE AND TEEN SKIN 5.26E.03 0.04 15 PARTICULATES 10 CFR 50, Appendix I limits are in terms of mrad or mrem!reactor-year.

PATHNAYS ANALYZED! PLUME, GROUND, IHHALATIOH The maxim'alculated dose from all 1993 airborne effluent (both mits) at this location Has 1.04E-02 mrem (ADULT/TEEH, SKIN).

62

TABLE 23 CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 0.40 WILES SE SECTOR DATA PERIOD: 1/1/93 - 12/31/93 EST INATED PERCENT NAXIIRMI DOSE OF LIHIT LIHIT EFFLUENT (NREII) (NREN)

NOBLE GAS M/A TOTAL BODY 3.59E-04 0.01 NOBLE GAS M/A SKIN 1.01E-03 0.01 15 IODINE AMD TEEN, SKIN 8.15E-03 0.05 15 PARTICULATES ADULT 10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

PATHMAYS ANALYZED: PLUME, GROUND, IHHALATIOM The maxisua calculated dose from all 1993 airborne effluent (both units) at this location Has 1.64E-02 mrem (ADULT/TEEM, SKIN).

CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 1.10 EXILES WSW SECTOR DATA PERIOD: 1/1/93 TO 12/31/93 EST INATED PERCENT APPLICABLE NAXIIRMI DOSE OF LIHIT LIMIT EFFUKNT ORGAN (NRBI) (HRBI)

NOBLE GAS H/A TOTAL BOOT 1.42E.03 0.03 NOBLE GAS M/A SKIN 4.00E-03 0.03 15 IODINE AND PARTICULATES TEEM LUHG 1.69E-02 0.11 15 10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

PATHMAYS ANALYZED: PLUME, GROUND, VEGETATION, INHALATION The maxismm calculated dose from all 1993 SSES airborne effluent (both units) at this location Has 3.46E-02 mrem (TEEN, SKIN).

63

TABLE 24 CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 1.20 HILES W SECTOR DATA PERIOD: 1/1/93 - 12/31/93 EST I HATED PERCENT AGE APPLICABLE MAXIMUM DOSE OF LIHIT EFFLUENT GROUP ORGAN (MREH) LIHIT (HREM)

NOBLE GAS N/A TOTAL BODY 5.44E-04 0.01 NOBLE GAS N/A SKIN 1.53E-03 0.01 15 IODINE AND TEEN LUNG 5.74E-03 0.04 15 PARTICULATES 10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

PATNMAYS ANALYZED: PLUHE, GROUND, INHALATION The maximum calculated dose from all 1993 SSES airborne effluent (both units) at this location was 1.36E-02 mrem (TEEN, SKIN).

CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 0.80 MILES WNW SECTOR DATA PERIOD: 1/1/93 - 12/31/93 EST IHATEO PERCENT AGE APPLICABLE MAXIHUM DOSE OF LIMIT EFFLUENT GROUP ORGAN (MREH) LIMIT (HREM)

NOBLE GAS N/A TOTAL BODY 5.03E-04 0.01 NOBLE GAS N/A SKIN 1.42E-03 0.01 15 IODINE AND TEEN LUNG 6.54E-03 0.04 15 PARTICULATES 10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

PATNAYS ANALYZED: PLUHE, GROUND, INHALATION The maximum calculated dose from all 1993 SSES airborne effluent (both units) at this location was 1.38E-02 mrem (ADULT/TEEN, SKIN).

TABLE 25 CALCULATED DOSES FOR RESIDENCES WITHIN THE SSES SITE BOUNDARY 0.60 NILES NNW SECTOR DATA PERIOD: 1/1/93 - 12/31/93 =

EST INATED PERCENT NAXI)RNI DOSE OF LIHIT EFFLLKNl'OBLE (NREH) LINIT (NREN)

GAS N/A TOTAL BODY 5.45E-04 0.01 NOBLE GAS H/A SKIN 1.54E.03 0.01 15 IODINE AND TEEN LUHG 7.38E.03 0.05 15 PARTICULATES 10 CFR 50, Appendix I limits are in terms of mrad or mrem/reactor-year.

PATHMAYS ANALT2ED: PLUHE, GROUND, INHALATION The maxicus calculated dose from all 1993 SSES airborne effluent (both units) at this location was 1.588-02 mrem t(ADULT/TEEN, SKIN).

65

SECTION 5 CHANGES TO THE OFFSITE DOSE CALCULATIONMANUAL AND THE SOLID WASTE PROCESS CONTROL PROGR&lf 66

CHANGES TO THE OFFSITE DOSE CALCULATION NANUAL The SSES ODCN was not revised during 1993. The document was in the process of a major revision to the liquid dose calculation methodology and parameters during this time. The revision was approved rece'ntly (3/10/94). Since the revised methodology and parameters are applied to liquid dose calculations herein for 1993, however, the revision is discussed in this report, rather than next year.

The rationale for this revision was that the use of the LADTAP II code for liquid effluent dose calculations was not consistent with the methodology then listed in Section 5 of the ODCH. Also, the stated methodology did not permit calculation of both near and far field doses using appropriate dilution factors. The liquid dose calculation methodology (Section 5) was expanded. Liquid dose calculation factors for Fish, Water ingestion, Shoreline Exposure, and Composite (Projected) pathways have been included for the appropriate age groups in Tables 5-1a, b, c, 5-2a, b, c, d, 5-5, and 5-6a, b, c, d. Decay constants are included in Table 5-3. Dilution factor Table D-1 has been replaced by Table 5-4. This table lists dilution factors at Danville, PA (applied to water ingestion pathway) for a wide range of river depths. The bases for these tables and methodology are PP&L Calculations OT-93-RKB-019 and OT-93-RKB-021. These calculations have been developed using Reg. Guide 1.109, Rev. 1, 10/77, consistent with Technical Specification 6.9.1.8. Appendix D (Site Specific Information Used by the LADTAP II code) has been changed to include factors consistent with these calculations. Population dose calculation methodology will no longer be included based on no Technical Specification requirement for this determination.

Other changes to the ODCM include the following:

Based on recent revision to'.Technical Specifications, the Semiannual Effluent and Waste Disposal Report has been changed to Annual Effluent and Waste Disposal Report where this term appears in the ODCH.

Hilk sampling station 14B1 has been deleted and replaced by station 10D2. This revision was necessary because the farm supplying milk as station 14B1 left the dairy business. The revision is shown in Table 6 and Figure 6. Other descriptive changes have been made to Table 6 which are descriptive, and do not involve actual changes to sampling locations.

Gaseous monitor setpoints in Appendix A have been revised slightly to be consistent with calibration of the SPING flow channels. These changes are minor (third decimal place).

Figures 1, 2, 3 and 4 have been restored for legibility. Clarity had been lost through repeated photocopying in previous revisions.

Figure 3 (Solid Waste Management System Flow Diagram) has been revised to include dry contaminated waste, to be consistent with Chapter ll of the FSAR.

The reference to high conductivity waste treatment in evaporators (Section 8. 1) has been removed, since this equipment is no longer in service.

Table 3, Sample Annual Average Relative Concentrations and Deposition Rates, has been updated with recent (1992) meteorological data.

Table 1, Radiological Effluent Objectives and Standards, has been revised to eliminate quantities released per Gigawatt-Year, which has no basis in Technical Specifications.

Appendix B.2 has been revised to make the reporting requirement consistent with wording in Technical Specifications: submitted "within 30 days from the end of the quarter" has been changed to "within 30 days".

The Table of Contents has been expanded to show both approval and revision dates of the individual pages.

Consistent with the requirements of Technical Specification 6.14.2.2, the revised methodology and parameters do not reduce the accuracy or reliability of dose calculations or setpoint determinations.

68

PENNSYLYANIA POMER R LIGHT COMPANY SUSQUEHANNA STEAM ELECTRIC STATION OFFSITE DOSE CALCULATION MANUAL Prepared By Date Reviewed By C Date Supervisor-Environmental Services Nuclear /

Reviewed By . <<c<<<<~~ PWd >7 ee o.

Date > WQr'P~

ng Approved By Bale <</>> />

Manager-Nuclear Technology

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

Pursuant to EDR G30004, liquid dose calculation methodology and parameters (Section 5) has been expanded. Liquid dose calculation factors for Fish, Water Ingestion, Shoreline Exposure, and Composite (Projection) Pathways have been included for the appropriate age groups in Tables 5-1a,b,c, 5-2a,b,c,d, 5-5, and 5-6a,b,c,d. Decay constants are included in Table 5-3. Dilution factor Table D-l has been replaced by Table 5-4. The bases for these tables and methodology are PP&L Calculations OT-93-RKB-019 and OT-93-RKB-021. Appendix D (Site Specific Information Used by LADTAP Code) has been changed to include factors consistent with these calculations. Population dose calculation methodology will no longer be included based on no Tech. Spec.

requirement for this calculation.

2. Based on recent revision to Technical Specifications, the Semiannual Effluent and Waste Disposal Report has been changed to Annual Effluent and Waste Disposal Report where this term appears.

3. Hilk sampling station 14Bl has been deleted and replaced by station lOD2. This revision is shown in Table 6 and Figure 6. Other changes which are descriptive only (do not involve changes to actual sampling locations) have been made to Table 6.

Gaseous monitor setpoints in Appendix A have been revised slightly to be consistent with calibration of the SPING flow channels.

5. Figures 1, 2, 3 and 4 have been restored for legibility; clarity had been lost due to repeated photocopying. Figure 3 (Solid Waste Hanagement System Flow Diagram) has been revised to include dry contaminated waste, to be consistent with Chapter ll of the FSAR.

6. The reference to high conductivity waste treatment in evapor ators (Section 8.1) has been removed, since this equipment is no longer in service.

7. Table 3, Sample Annual Average Relative Concentrations and Deposition Rates, has been updated with recent (1992) meteorological data.

8. The Table of Contents has been expanded to show both approval and revision date of individual pages.

9. Table 1, Radiological Effluent Objectives 8 Standards, has been revised to eliminate quantities released per Gigawatt-Year, which has no basis in Technical Specifications.

10. Appendix B.2 has been revised to make the reporting requirement consistent with wording in Technical Specifications: submitted "within 30 days from the end of the quarter" has been changed to "within 30 days."

TABLE OF CONTENTS APPROVAL REVISION PAGE ~OE ~DE I

1.0 INTRODUCTION

...........................-... ~ ~ 0 1 10/29/93 3/11/94 2 2/5/92 2/21/92 3 ll/9/93 3/11/94 t 2.0 SETPOINTS.................................. ~ ~ ~ 4 2/5/92 2/21/92 2.1 WATERBORNE EFFLUENT MONITORS......-.... ~ ~ ~ 4 2/5/92 2/21/92 5 12/11/89 12/ll/89 6 2/5/92 2/21/92 7 12/11/89 12/ll/89 8 12/11/89 12/11/89 2.2 AIRBORNE EFFLUENT MONITORS..........." ~ ~ ~ 2/5/92 2/21/92 10 12/11/89 12/11/89 11 12/11/89 12/11/89 12 11/21/92 11/25/92 3.0 WATERBORNE EFFLUENT CONCENTRATION MEASUREMENTS 13 2/5/92 2/21/92 14 2/5/92 2/21/92 4.0 AIRBORNE EFFLUENT DOSE RATES .....--....... ~ ~ ~ 15 2/5/92 2/21/92

4. 1 NOBLE GASES...........'................. ~ ~ ~ 15 2/5/92 2/21/92 4.2 RADIONUCLIDES OTHER THAN NOBLE GASES... ~ ~ ~ 16 2/5/92 2/21/92 17 2/11/92 2/21/92 18 2/5/92 2/21/92 19 12/ll/&9 12/ll/&9 20 12/1/92 12/4/92 5.0 INDIVIDUAL DOSE DUE TO WATERBORNE EFFLUENT. ~ ~ 21 lo/29/93 3/11/94 5.1 FISH PATHWAY LI(UID EFFLUENT DOSE CALCU ATION METHODOLOGY.....-.-.......- 22 2/18/94 3/11/94 5.2 POTABLE WATER PATHWAY EFFLUENT DOSE CALCULATION METHODOLOGY................ ~ ~ ~ 23 ll/9/93 3/ll/94 5.3 SHORELINE EXPOSURE PATHWAY....-........ ~ ~ ~ 24 ll/9/93 3/ll/94 5.4 PROJECTED DOSE FROM LIQUID EFFLUENT.... ~ ~ ~ 24 11/9/93 3/11/94 25 2/18/94 3/ll/94 26 11/9/93 3/11/94 6.0 INDIVIDUAL DOSE DUE TO AIRBORNE EFFLUENT... ~ ~ ~ 27 10/29/93 3/ll/94 6.1 NOBLE GASES...................-.-...... ~ ~ ~ 27 10/29/93 3/ll/94 6.2 RADIONUCLIDES OTHER THAN NOBLE GASES... ~ ~ 28 10/29/93 3/11/94 29 10/29/93 3/ll/94 7.0 TOTAL DOSE............................ ~ ~ ~ 30 10/29/93 3/11/94 31 10/29/93 3/11/94 8.0 OPERABILITY OF WASTE TREATMENT SYSTEMS..... ~ ~ 32 10/29/93 3/ll/94 8.1 LI(UID WASTE TREATHENT........ -........ ~ ~ ~ 32 10/29/93 3/11/94 8..2 GASEOUS WASTE TREATMENT................ ~ ~ ~ 32 10/29/93 3/ll/94 33 10/29/93 3/ll/94 33 10/29/93 3/11/94 8.3 SOLID WASTE TREATMENT ................. ~ ~ ~ 34 10/29/93 3/ll/94 35 10/29/93 3/ll/94

APPROVAL REVISION PAGE DATE ~DE 9.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM. 40 10/29/93 3/ll/94 9.1 DEFINITIONS 40 ll/9/93 3/11/94 9.2 MONITORING PROGRAM........................ 40 10/29/93 3/11/94 9.3 CENSUS PROGRAM............................ 41 10/29/93 3/11/94 9.4 INTERLABORATORY COMPARISON PROGRAM........ 42 10/29/93 3/ll/94-43 10/29/93 3/ll/94 10.0 DOSE ASSESSMENT POLICY STATEMENTS............ 51 10/29/93 3/ll/94 10.1 SELECTION OF ANALYSIS RESULTS FOR 51 10/29/93 3/ll/94 DOSE CALCULATIONS 10.2 ASSIGNMENT OF RELEASES TO THE REACTOR 51 10/29/93 3/11/94 UNITS 10.3 EVALUATION AND MONITORING CRITERIA FOR 51 10/29/93 3/11/94 EFFLUENT PATHWAYS 10.4 FLOW FROM THE SGTS VENT WHEN THE SYSTEM 52 10/29/93 3/11/94 IS NOT IN USE 10.5 ODCH SETPOINTS ARE UPPER LIMIT VALUES 53 10/29/93 3/11/94 10.6 DEFINITION OF "APPROPRIATE TREATMENT" 53 10/29/93 3/ll/94 FOR LIQUID WASTES 10.7 MONITOR LINE-LOSS CORRECTIONS 55 10/29/93 3/11/94-10.8 SELECTION OF DATA FOR DETERMINATION OF 56 10/29/93 3/ll/94 DOSE RATE COMPLIANCE 10.9 LOW-LEVEL RADIOACTIVITY IN THE SEWAGE 57 10/29/93 3/11/94=

TREATMENT PLANT 11.0 ODCH REVIEW AND REVISION CONTROL............. 10/29/93 3/11/94 APPENDIX A - SAMPLE CALCULATIONS OF ODCH PARAMETERS........................... A-1 2/5/92 2/21/92 A-2 2/5/92 2/21/92 A-3 12/11/89 12/11/89 A-4 2/5/92 2/21/92 A-5 10/29/93 3/ll/94 A-6 10/29/93 3/ll/94 A-7 10/29/93 3/ll/94 A-8 10/29/93 3/ll/94 A-9 2/5/92 2/21/92

\

A-10 2/5/92 2/21/92 A-11 10/29/93 3/11/94 A-12 10/29/93 3/ll/94 A-13 10/29/93 3/ll/94 APPENDIX 8 - REPORTING REQUIREMENTS............... 8-1 12/ll/89 12/11/89 8-2 10/29/93 3/11/94 8-3 12/11/89 12/11/89 8-4 12/11/89 12/11/89 11

APPROVAL REVISION PAGE DATE DATE APPENDIX C SITE SPECIFIC INFORHATION USED BY GASPAR CODE.................. C-1 12/11/89 12/11/89 APPENDIX D SITE SPECIFIC INFORNTION USED BY LADTAP CODE.................. D-1 11/9/93 3/11/94 111

APPROVAL REVISION T BLE PAGE ~DTE DATE Radiological Effluent Objectives and Standards.. 3 ll/9/93 3/11/94 Dose Factors for Noble Gases ................... 18 2/5/92 2/21/92 Sample Annual Average Relative Concentrations and Deposition Rates............................ 19 ll/9/93 3/ll/94 Dose Factors for Inhalation, Ingestion and Ground Exposure Pathways: Radionuclides Other Than Noble Gases................................ 20 12/1/92 12/4/92 5-la Dose Factors for Fish Pathway, Maximum Hypothetical Adult (2pp).......................5-la(1,2) 2/18/94 3/11/94 5-lb Dose Factors for Fish Pathway, Maximum Hypothetical Teen (2pp)........................5-lb(1,2) 10/29/93 3/11/94 5-lc Dose Factors for Fish Pathway, Maximum Hypothetical Child (2pp).......................5-lc(1,2) 10/29/93 3/11/94 5-2a Dose Factors for Potable Water Pathway, Maximum Hypothetical Adult (2pp).......................5-2a(1,2) 10/29/93 3/ll/94 5-2b Dose Factors for Potable Water Pathway, Maximum Hypothetical Teen (2pp)........................5-2b(1,2) 10/29/93 3/11/94 5-2c Dose Factors for Potable Water Pathway, Maximum Hypothetical Child (2pp}. .... .... .........5-2c(1,2) 10/29/93 3/ll/94 5-2d Dose Factors for Potable Mater Pathway, Maximum Hypothetical Infant (2pp)......................5-2d(1,2) 10/29/93 3/11/94 5-3 Radioactive Decay Constants.....................5-3 10/29/93 3/11/94 5-4 Dilution Factors and Transit Times for SSES Effluents to Danville, PA..................-..-5-4(1,2) 10/29/93 3/11/94 Dose Factors for Shore Exposure Pathway, All Age Groups (2pp)...................................5-5(1,2) 10/29/93 3/11/94 5-6a Composite Dose Factors: Maximum Hypothetical Adult (2pp}....................................5-6a(1,2) 10/29/93 3/ll/94 5-6b Composite Dose Factors: Maximum Hypothetical Teen (2pp).....................................5-6b(1,2) 10/29/93 3/11/94

APPROVAL REVISION

~TBLE ~GE ~DE ~DT 5-6c Composite Dose Factors: Maximum Hypothetical Child (2pp)....................................5-6c(1,2) 2/18/94 3/11/94 5-6d Water Ingestion Dose Factors: Maximum Hypothetical Infant (2pp)......................5-6d(1,2) 2/18/94 3/ll/94 6 Operational Radiological Environmental Monitoring Program.............................. 46 2/18/94 3/11/94 47 10/29/93 3/ll/94 48 2/18/94 3/ll/94 7 Detection Capabilities for Environmental Sample Analysis................................. 49 10/29/93 3/11/94 50 10/29/93 3/11/94 B-1 Radiological Environmental Monitoring Program Annual Summary.................................. B-3 12/11/89 12/11/89 B-2 Reporting Levels for Nonroutine Operating R eports......................................... B-4 12/11/89 3/ll/94 D-1 Dilution Factors and Transit Times for SSES Effluents to Danville, PA..........,............ 0-1 11/9/93 3/ll/94

LIST OF FIGURES APPROVAL REVISION PAGE DATE DATE Figure 1 Liquid Radwaste System Flow Diagram.......................... 36 10/29/93 3/11/94 Figure 2 Offgas and Recombiner System Flow Diagram.......................... 37 10/29/93 3/11/94 Figure 3 Solid Waste Hanagement System Flow Diagram.......................... 38 10/29/93 3/11/94 =

Figure 4 SSES Dry\ Contaminated Waste P rocesslng........,,,xiii,...,...,,... 39 10/29/93 3/11/94 Figure 5 Environmental Honitoring Locations Within One Hile of SSES............... 44 10/29/93 3/11/94 Figure 6 Environmental Honitoring Locations Greater than One Hile from SSES....... 45 2/18/94 3/11/94.

The purpose of this manual is to provide the parameters and methodology to be used in calculating offsite doses and effluent monitor setpoints for the Susquehanna Steam Electric Station, Units I 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 Specifications. Methods are included for performing dose calculations to ensure compliance with the waterborne and airborne treatment system operability sections of the Technical Specifications. This manual includes the methods used for determining quarterly individual doses for inclusion in Annual Effluent and Waste Disposal 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 design objectives. Compliance with the 10 CFR 20 maximum permissible concentrations is done on a batch-by-batch basis prior to discharge.

This manual discusses the methodology to be used in determining effluent monitor alarm/trip setpoints to be used to ensure compliance with the instantaneous release rate limits in the Technical Specifications.

Hethods are described for determining the annual cumulative dose to a real individual from liquid effluents, gaseous effluents, and direct radiation for critical organs to ensure compliance with 40 CFR 190 limits. The calculational methodology for doses are based on models and data that make it unlikely to substantially underestimate the actual

exposure of an individual through any of the appropriate pathways.

The Radiologica'l 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 Superintendent of P1ant-Susquehanna to ensure that this manual is used in performance of the survei11ance requirements and for compliance with the limiting conditions of operations stated in the Technical Specifications. It is the responsibility of the Hanager-Nuclear Technology to ensure adequacy and correctness of calculational approaches.

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

DESIGN OBJECTIVES (BOTH REACTOR (BOTH REACTOR (PER REACTOR UNIT) UNITS COHBINED) UNITS COHBINED)

WATERBORNE EFFLUENTS Dose to Total Body From all Pathways 3 mrem/year Dose to any Organ From all Pathways 10 mrem/year AIRBORNE NOBLE GAS EFFLUENTS Dose Rate to Total Body 500 mrem/year Dose Rate to Skin 3000 mrem/year Gamma Dose in Air- 10 mrad/year Beta Dose in Air 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 Dose to any Organ From all Pathways 15 mrem/year TOTAL URANIUH 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

• As currently reflected in Technical Specification 3.11.4.

• • Technical Specification limits set to ensure compliance with 10 CFR 20 limits

2. 0 ~SPOINTS 2.1 WATERBO N F U T ON 0 S SP C ICAT ON 3.3.7.10 THE RADIOACTIVE LIQUID 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 CNNNELS 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 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 ar ea. The calculated alarm and trip action setpoints for the liquid effluent monitor and each flow measurement device must satisfy the following equation:

cf F+f S C (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.

the radwaste discharge flow setpoint, in volume per unit time, in 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 time.

Radioactive liquid 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 NPC value -used for the liquid effluent concentration limit (C) in the above expression for the liquid radwaste effluent line monitor setpoint is 1 x 10 uCi/ml or the actual MPC for identified mixtures. Therefore, for determining the setpoint on the liquid radwaste-the'xpression effluent line monitor becomes:

c < (1 x 10 ) f (uCf/ml) (Eq. 2)

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

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

F+f) ~A where F + f ) the minimum dilution factor f )m f ~Y iiPC where F + f - the setpoint dilution factor f )

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

F+

ff)

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

c X(A) < NPC F + 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/mi per cpm)

The setpoint for the dilution water flow (cooling tower blowdown) is 5000 gpm from both cooling tower basins. The setpoint for the LRW 1

discharge flow can then be determined from:

F +M - MM (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 Water System provides screened water from the cooling tower basin for cooling plant systems and equipment. The Residual Heat Removal (RHR) Service Water System provides water -from the 1 ~rrv

Engineered Safeguard Service Mater (ESSM) spray pond to the RHR heat exchangers. In post-accident conditions, RHR Service Water can supply water for vessel and containment floodfng. The Service Mate 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 (85%)

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

Hecause Service Water 5 RHR Service Mater are not normal release-pathways for liquid effluents, no credit should be taken for possible dilution scenarios. All 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 actfvity, the alarm setpoints for the Service Mater and RHR Service Water monitors are determined as follows:

OEC 11589

a. When monitor background< {2E-5)/Cal. Factor:

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

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

HI .RAD Setpoint = Background + 0. 5 (2E-5) /Ca 1. Factor DOWNSCALE 'r LOM 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 Mater).

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

(2E-5) = Cs-137 Maximum Permissible Concentration (uCi/ml).

Cal. Factor = Monitor response factor per unit Cs-137 concentration determined during most recent

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

The ALERT RAD setpoints for the RHR Service Water monitors are maintained at BOX of the applicable HI RAD setpoint (cpm).

2.2 AI BORN U T MO I ORS SPEC F C TION 3.3.7. - THE RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION CHANNELS SHOWN IN TABLE 3.3.7.11-1 SHALL BE OPERABLE WITH THEIR ALARM/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 WITH THE METHODOLOGY AND PARAMETERS IN THE ODCM.

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

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

Since the vent monitors are prograraned to calculate concentrations of iodine-131 and particulate being released based on the rate of accumulation of activity on the filters, setpoints can be established for the iodine and particulate channels.

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

1. An isotopic mixture is selected for the detector in question, if applicable. Noble gas and particulate detector setpoints are based on actual isotopic mixtures obtained from vent sample analysis or-the FSAR/FES expected release mixtures if actual samples do not contain sufficient detectable activity to accurately estimate the mixtures. The assumed isotopic mixtures are periodically reviewed to verify that they remain representative of plant effluents.

2. The selected noble gas or particulate mixture is used in the GASPAR program run to calculate the associated doses. The total source term (total curies used for the calculation) does not matter ass ion ong as the proper nuclides are present in the relative proportions indicated in sample analysis data or FSAR/FES tables.

For the iodine-131 setpoint, any release total for I-131 can be entered. The highest calculated annual average relative 10

P concentrations (X/gs) 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 Tota GA P R Source erm Limiting Re ease Rate 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 setpoint, 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 limit of 1500 mrem/yr.

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

11

Limiting Vent Concentration, uCi/cc imitino Release Rate Ci r 1 6uCi Ci (Eq. 6)

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

Sample calculations of waterborne and airborne effluent monitor 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 10K and 90X of the calibrated sensor ranges to provide indication of possibly abnormal flow rates.

SPECIFICATION 3.11.2 6 - THE CONCENTRATION OF HYDROGEN OR OXYGEN IN THE HAIN CONDENSER OFFGAS TREATMENT SYSTEH SHALL BE LIMITED TO LESS THAN OR EQUAL TO 4X BY VOLUHE.

Hydrogen recombiners are used 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 1X and 2X hydrogen.

'SPECIFICATION 3.11.2.7 - The radioactivity rate of the'noble gases Kr-85m, Kr-87, Kr-88, Xe-133, Xe-135 and Xe-138 measured at the motive steam jet condenser discharge shall be limited to less than or equal to 330 millicuries/second.

The main condenser offgas pre-treatment monitor provides indication of offgas activity prior to input to the holdup system. Alarm setpoints are based on the Tech. Spec. 3.11.2.7 noble gas release rate limit of 330 millicuries/second or less at the motive steam jet condenser discharge.

12

3.0 W S 3 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 ENTRAINED 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 Entrained Noble Gases Released From the Site to Unrestricted Areas in Liquid Waste":

gggj~de MPC uCi m Kr-85m 2E-4 Kr-85 5E-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

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 NPC 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

4.0 AIRBORN E U D S RATES SP RELEASED BE LIMITED C

IN 0 3.. THE DOSE RATE DUE TO RADIOACTIVE MATERIALS GASEOUS EFFLUENTS FROM THE SITE (SEE FIGURE 5.1.3-1)

TO THE FOLLOMING:

SHALL

a. FOR NOBLE GASES: LESS THAN OR EQUAL.TO 500 MREM/YR TO THE TOTAL BODY AND LESS THAN OR.EQUAL TO 3000 MREH/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 MREM/YR TO ANY ORGAN (INHALATION,PATHWAYONLY).

4.l ~IIO G II 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 equation for whole body dose:

Z' i) ( /4)v (4 iv) (Eq. 7) i and by the following equation for skin dose:

0 ~

1 Li+I'IMi)( ~ ~ i (Eq. 8)

where:

the whole-body dose factor due to gamma emissions for each iden)ffied noble gas radionuclide (i) (mrem/yr per uCi/m ) from Table 2.

Q'iv the release rate of radionuclide (i) from vent (v)

(uCi/sec).

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

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

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

the air dose factor due to ganma 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).

's the annual skin dose (mrem/yr).

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

4.2 RAD UC S OT ER A HOB GA 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 V 16 D opt

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

(Ri) (Wy) (0 iv) (Eq. 9) where:

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.

W- 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.

v the rel ease rate of radi onucl i de (i) from vent (v)

(uCi/sec).

Oc the annual organ dose (mr em/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

TABLE 2 1 z DOSE FACt'ORS FOR NOBLE GASES' Whole Body Ganma Air Beta Air Dose Factor Skin Dose Factor Dose Factor Dose"Factor K Li H N S

c e C r-83m 7.56E-02 1.93E+OI 2.88E+02 r-85m 1.17E+03 1.46E+03 1.23E+03 I.97B03 Kr-85 1.6IE%01 1.34E<03 I.72B.OI 1.95E+03 kr-87 5.92E+03 9.73E+03 6.17E+03 1.03E404 r-88 1.47E+04 2.37E+03 1.52E+04 2.93E+03 1.66E404 I.OIE+04 1.73E+04 1.06E+04 Kr-90 1.56E+04 7.29E+03 1.63E+04 7.83E+03 Xe-131m 9.15E+01 4.76E+02 1.56E+02 I.IIE+03 Xe-133m 2.51002 9.94B02 3.27E+02 1.48E+03 Xe-133 2.94B02 3.06402 3.53E+02 1.05B03 5 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 4.13E403 9.21E+03 4.75E+03 Ar-41 8.84E+03 2.69E+03 9.30E+03 3.28E+03 (he listed dose factors are for radionuclides that may be detected in airborne effluents and derIved from Table 0-1 io Reg. Golda'1;109.

7.565-02 7.56 x 10 A

DXT6~~

TABLE 3 l

SAMPLE ANNUAL AVERAGE RELATIVE CONCENTRATIONS AND DEPOSITION RATES t

I RELATIVE RELATIVE RELATIVE SITE CONCENTRATIONS CONCENTRATIONS DEPOSITION DOWNMIND BOUNDARY UNDECAYED/UNOEP EYED DECAYED, DEPLETED RATES

~SECTO ~ILES sec m D m NNE .78 4.7E-6 3.9E-6 1. 4E-8 NE .61 4.9E-6 4.5E-6 2.8E-8 ENE 3.3E-6 3.1E-6 2.7E-8 E .53 1.&E-6 1.4E-6 1.2E-&

ESE .51 2.1E-6 1.8E-6 1.4E-8 SE .42 2.&E-6 2.5E-6 2.3E-&

SSE .34 5.6E-6 4.7E-6 4.0E-8 S .34 &.OE-6 6.6E-6 3.6E-8 SSW .41 1.2E-5 1.0E-5 4. IE-8 SU ,.83 6.4E-6 5. 7E-6 1. 5E-8 WSM 1.03 1.3E-5 1.1E-5 1.9E-&

W 1.02 5.7E-6 5.2E-6 1.1E-&

WNW .62 7.0E-6 6.2E-6 1.6E-&

NW .65 6.6E-6 5.4E-6 1.7E-&

NNW .59 6.1E-6 5.&E-6 1. &E-8 N .59 6.3E-6 5.7E-6 2.1E-&

a From SSES 1992 Heteorological Summary, Haliburton NUS Corporation, 5/93.

Site Boundary distances are approximate, and current as of 5/93.

19

TABLE 4 DOSE FACTORS FOR INHALATION, INGESTION AND GROUND EXPOSURE PATHWAYS: RADIONUCLIDES OTHER THAN NOBLE GASES(l) (2)

(1)Reference letter R. K. Barclay to File R9-5: Technical Documentation of Lotus 1-2-3 ODCMTAB and TGTMSTR files: Gaseous Dose Factor Calcu'tation using NUREG-0133/Reg. Guide 1.109 Methodology, PLI 69605, ll/8/91.

(2)Reference letter R. K. Barclay to File R9-5: Technical Documentation:

ODCMTAB.MK1 Revision 1 Correction of Tritium in Vegetation Pathway Dose Calculations Factor Algorithms, PLI 72980, 11/24/92.

20 o~~

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

OPE: H-3 PATHWAY AGE GROUP BONE LIYER 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.oof+00 O.OOE+00 O.OOE+00 CHILD O.QOE+OO O.OOE+QO O.OOE+OO O.QOE+OQ O.OOE+OO O.OOE+00 O.OOE+00 O.OOE+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.'OOE+00 O.OOE+00 O.OOE+00 O.oof+00 GOAT ADULT 0.00E+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 Q.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 Q.OOE+00 8.82E+02 8.82E+02 8.82E+02 8.82E+02 8.82E+02 8.82E+02 N/A CHILD O.OOE+00 1.39E+03 1.39E+03 1.39E+03 1.39E+03 1.39E+03 1.39E+03 N/A INFANT O.oof+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 2.89BQZ 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.?2E+02 N/A CHILD Q.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+OO O.OOE+OO O.OOE+OO O.OOE+00 O.OOE+00 O.OOE+OO O.OOf+00 N/A BLE ADULT Q.OOE+00 1.82E+03 1.82E+Q3 1.82E+03 1.8ZE+03 1..82E+03 1.82E+03 N/A TEEN O.OOE+00 2.18E+03 2.18E+03 2.18E+03 2.18E+03 2.18E+03 2.18E+03 N/A CHILD Q.OOE+00 3.42E+03 3.42E+03 3.42E+03 3.42E+03 3.42E+03 3.42E+03 N/A INFANT 0.00f+00 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 0.00F+00 N/A TOTAL ADULT O.OOE+00 4.17E+03 4.17E+03 4.17E+03 4.17E+03 4.17E+03 4.17E+03 N/A INGEST. TEEN 0.00E+00 5.03E+03 5.03E+03 5.03E+03 5.03E+03 5.03E+03 5.03E+03 N/A CHILD O.OOE+00 7.86E+03 7.86E+03 7.86E+03 7.86E+03 7.86E+03 7.86E+03 N/A INFANT 0.00E+00 6.43E+03 6.43E+03 6.43E+03 6.43E+03 6.43E+03 6.43E+03 N/A INHAL. ADULT O.OOE+00 1.26E+03 1.26E+03 1.26E+03 1.26E+03 1.26E+03 1.26E+03 N/A TEEN Q.OOE+00 1.27E+03 1.27E+03 1.2?E+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.QOE+00 6.47E+02 6.47E+02 6.47E+02 6.47E+02 6.47E+02 6.47E+02 N/A BONE LIV R T.BODY THYROID KIDNEY LUNG G.l. SKI

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

• "*MAXIMUMVALUfS FOR PATHWAYS***

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

O.OOE+00 O.OOE+00 4.31f+03 2.11E+03 2.89E+02 3.42E+03 7.86E+03 1.27E+03 PAGE: 4-1 OAT

O.D.C.M.

ISOTOPE: C-14 MAXIMUM PATHWAY DOSE FACTORS-PATHWAY AGE GROUP BONE LIVER T.BODY RADIONUCLIDES OTHER THAN NOBLE GASES*

THYROID KIDNEY LUNG G.I. SKIN 0

GROUND ADULT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+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 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 INFANT O.OOE+00 O.OOF+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 1.69Et08 3.39E+07 3.39E+07 3.39E+07 3.39E+07 3.39E+07 3.39E+07 N/A MILK TEEN 3.12Et08 6.24E+07 6.24E+07 6.24E+07 6.24E+07- 6.24E+07 6.24E+07 N/A CHILD 7.6&E+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+08 3.21E+08 3.21E+08 3.21E+08 N/A COW ADULT 1.35Et08 2-71Ew07 2-71Et07 2-71B07 2.71E+07 2.71E+07 2.71E+07 N/A MILK TEEN 2.50E+08 4.99E+07 4.99E+07 4.99E+07 4.99E+07 4.99Ew07 4.99E+07 . N/A CHILD 6.14E+08 1.23E+08 1.23E+08 1.23E+08 1.23E+08 1.23E+08 1.23BO& N/A INFANT 1.20E+09 2.57E+08 2.57E+08 2.57E+08 2-57E+0& 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 2.30f+07 2.30E+07 2.30E+07 2.30E+07 2.30E+07 N/A CHILD 2.16E+08 4.'33Et07 4.33B07 4.33E+07 4.33E+07'.33E+07 4.33E+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 2.06B08 4.13Ei07 4.13E+07 4.13E+07 4.13B07'4.13E+07 4.13E+07 N/A =

TEEN 3.49Ew08 6.9&Et07 6.9&Et07 6.98E+07 6.9&B07 6.9&Ew07 6.9&E+07 N/A CHILD 8.53E+08 1.71E+08 1.71E+08 1.TIE&8 1.71E+08 1.71E+08 1.71E+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 6.47E+08 1.29E+08 1.29E+08 1.29Ei08 1.29E+08 1.29E+08 1.29E+08 N/A INGEST. TEEN 1.03B09 2.05E+08 2.05E+08 2.05E+08 2.05E+08 2.05E+08 2;05E+08 'CA CHILD 2..45Et09 4'.90E+08 4.90E+08 4.90E+08 4.90E+08 4.90E+08 4.90E+08 N/A INFANT 2.71E+09 5.7&E+08 5.7&E+08 5.7&E+08 5.7&E+08 5.7&E+08 5.7&E+08 N/A I

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.&7E+03 N/A CHILD 3.59E+04 6.73Et03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 N/A INFANT 2.65E+04 5.31E+03 5.31Ew03 5.31E+03 5.3IEw03 5.31E+03 5.31E+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 Deposition pathways: units are mrem-m2/yr/uCi/sec

~**MAXIMUMVALUES FOR PATHWAYS~*"

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

O.OOE+00 O.OOE+00 1.50E+09 1.20E+09 2.16E+08 8.53E+08 2.71E+09 3.59E+04 PAGE: 4-2 s 'v

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 'DULT 0.00E+00 0.00E+00 0.00E+00 0.00E+00.0.00E+00 0.00E+00 0.00E+00 O.OOE+00 TEEN 0:DOE+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 O.DOE+00 CHILD 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00.,0.00f+00 0.00E+00 0.DOE+00 INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.DOE+00 0.00E+00 0.00E+00 0.00E+00 GOAT MILK ~

ADULT CHILD 9.28E+09 5.77E+08 TEEN;-1.7IE+10 1.06E+09 4.22E+10 1.98E+09 3.59E+08 6.64E+08 1.63E+09 O.OOE+00 O.DOE+00 0.00E+00 1.04E+09 0.00E+00 0.00E+00 0.00E+00 1.44E+09 0.00E+00 0.00E+00 0.00E+00 1.17E+09

'/A N/A N/A INFANT 7.25E+10 5.12E+09 3.37E+09 0.00E+00 0.00E+00 0.00E+00 1.18E+09 N/A COW MILK ADULT TEEN 4.36E+09 8.'05E+09 2.71E+08 4.99E+08 1.69E+08 O.OOE+00 O.OOE+00 3.,12E+08 O.OOE+00 O.OOE+00 O.DOE+00 4.91E+08 O.OOE+00 6.77E+08

'/A N/A CHILD 1.99E+10 9.29E+08 7.65E+08 0.00f+00 O.DOE+00 0.00E+00 5.49E+08 .N/A INFANT 4.09E+10 2.41E+09 1.59E+09 0.00E+00 0.DOE+00 0.00E+00 5.54E+08 N/A MEAT ADULT 1.55E+09 9.63E+07 5.99E+07 0.00E+00 0.00E+00 0.00E+00 1.74E+08 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 0.00E+00 0.00E+00.,0.00E+00, 6.82E+07 N/A INFANT O.OOE+00 O.OOE+00 0.00E+00 0.00E+00, 0.00E+00,0.00E+00 O.OOE+00 N/A

~TBLE ADULT .7.09E+08 4.41E+07 2.74E+07 0.00E+00 0.00E+00 0.00E+00 7.98E+07 N/A TEEN 9.57E+08 5.93E+07 3.71E+07 0.00E+00 0.00E+00 0.00E+00 8.05E+07 N/A CHILD 2.16E+09 1.01E+08 8.34E+07 0.00E+00 0.00E+00 0.DOE+00 5.98E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00.0.00E+00- O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.59E+10 9.'89E+08 6.15f+08 0.00E+00 0.00E+00 0.00E+00 1.79E+09 'N/A INGEST. TEEN 2.74E+10 1.70E+09 1.06E+09 O.OOE+00.0.00E+00 O.OOE+00 2.31E+09 N/A CHILD 6.67E+10 3.12E+09 2.57E+09 0.00E+00 0.00E+00 0.00E+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 0.00E+00 0.00E+00 0.00E+00 8.64E+04 N/A TEEN 1.89E+06 1.10E+05 7.16E+04 0.00E+00 0.00E+00 0.00E+00 9.28E+04 N/A CHILD 2.60E+06 1.14E+05 9.88E+04 0.00E+00.0.00E+00 0.00E+00 4.22E+04 N/A INFANT 2.03E+06 1.12E+05 7.74E+04 0.00E+00.0.00E+00 0.00E+00 1. 61E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.l. SKIN 1

• 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 HILK: MILK: HEAT: VEGTBLE: INGEST: INHAL.

0.00E+00 0.00E+00 7.25E+10 4.09E+10 2.47E+09 2.16E+09 1.13E+11 2.60E+06 D.~T'AGE:

I 4-3

O.D.C.M. 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'ROUND ADULT 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+06 4.61E+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 O.OOE+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 0.00E+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 O.OOE+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 0.00E+00 1.39E+04 7.75E+03 3.06E+03 1.99E+04 2.34E+06 N/A CHILD 0.00E+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 0.00E+00 4.51E+04 2.94E+04 6.43E+03 5.72E+04 1.31E+06 N/A MEAT ADULT 0.00E+00 0.00E+00 2.50E+03 1.49E+03 5.50E+02 3.31E+03 6.28E+05 N/A TEEN '.'OOE+00 O.OOE+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 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0-OOE+00 0-00E+00 0.00E+00 N/A VEGTBLE ADULT 0.00E+00 O.OOE+00 3.35E+04 2.01E+04 7.39E+03 4.45E+04'8.44B06 N/A TEEN O.OOE+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 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ADULT O.OOE+00 0.00E+00 4.56E+04 2.73E+04 1.01E+04 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 0.00E+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 1.58Ew06 N/A INHAL. ADULT O.OOE+00 O.OOE+00 1.00E+02 5.95E+01 2.28E+01 1.44Ew04 3.32Et03 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+Ol 2. 43E+01 1.70Ei04 1.08E+03 N/A INFANT O.OOE+00 0.00E+00 8.95E+01 5.75E+Ql 1.32E+01 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 TOTAL PATHWAYS**~'ROUND'ROUND:

GOAT COW 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 DAT

O.D.C.M.

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

ISOTOPE:~ Mn-54 PATHWAY AGE GROUP BONE LIVER 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

'EEN 1.37E+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+05.0.00E+00 1.S3E+05 O.OOE+00 1.&BE+06 N/A MILK TEEN 0.00E+00 1.02E+06 2.03E+05 O.OOE+00 3.05E+05 O.OOE+00 2.10E+06 N/A CHILD 0: OOE+00 1.53E+06 4.07E+05 O.OOE+00 4'.29E+05 O.OOE+00 1.2&E+06 N/A INFANT O.OOE+00 2.84E+06 6.45E+05 0.00E+00 6.30E+05 0.00E+00 1.04E+06 N/A COW ADULT 0.00E+00 3.92E+06 7.'49E+05 O.OOE+00 1.17E+06 O.OOE+00 1.20E+07 N/A MILK TEEN O.OOE+00 6.54E+06 1.30E+06 0.00E+00 1.95E+06 O.OOE+00 1.34E+07 N/A CHILD O.OOE+00 9.7&E+06 2.61E+06 O.OOE+00 2.74E+06 O.OOE+00 8.21E+06 N/A INFANT O.OOE+00 1.82f+07 4.12E+06 O.OOE+00 4.03E+06 O.OOE+00 6.6&E+06 .N/A

, ADULT 0.00E+00 4.79E+06 9.14E+05 0.00E+00 1.43E+06 0.00E+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 0.00E+00 4.18E+06 1.11E+06 0.00E+00 1.17E+06 0.00E+00 3.51E+06 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00'.OOE+00 O.OOE+00 O.OOE+00 N/A uTBLE ADULT O.OOE+00 2.&OE+08 5.35E+07 O.OOE+00 8.34E+07 O.OOE+00 8.5SE+08 N/A TEEN O.OOE+00, 4.27E+08 8.46E+07 O.OOE+00 1.27E+0& O.OOE+00 8.75E+08 N/A CHILD O.OOE+00 6.34E+08 1.69E+08 O.OOE+00 1.7&f+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 0.00f+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 4.3&E+08 8.69E+07 0.00E+00 1.31E+08 O.OOE+00 8.9&E+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>> O.OOE+00 3.96E+04 6.30E+03 O.OOE+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 1.9&E+06 6.6&E+04 N/A CHILD 0.00E+00 4.29E+04 9.51E+03 0.00E+00 1.00E+04.1.5&E+06 2.29E+04 N/A INFANT .0.00E+00 2.53E+04 4.9&E+03 0.00E+00 4.9&E+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: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTB LE: INGEST: INHAL.

1.37E+09 1.61E+09 2.84E+06 1.S2E+07 1.47E+07 8.75E+08 8.9&E+08 1.9&E+06 PAGE: 4-5 DAT

O.D.C.M. 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 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+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 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 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 GOAT ADULT 2.06E+05 1.42B 05 3.32E+04,0.00E+00 0.00E+00 7.94E+04 8.16E+04 N/A MILK TEEN 3.65E+05 2.59E+05 6.04E+04 0.00E+00 O.OOE+00 1.64E+05 1.12E+05 N/A CHILD 9.17E+05 4:86f+05 1.51E+05 0.00E+00 0.00E+00 2.75E+05 9.0IE+04 N/A, INFANT 8.52E+07 7.16E+05 1.91E+05'.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 MILK TEEN 2".22E+07 1.57E+07 '3.67E+06 0.00E+00 O.OOE+00 9.97E+06 6.80E+06 N/A CHILD 5.56E+07 2.95E+07 9. 14E+06 0.00E+00 O.OOE+00 1.67E+07 5.47E+06 N/A INFANT 6.73E%07 4.34E+07 1.16E+07 '0.00E+00 0.00E+00 2-12E+07 5'52E+06 N/A MEAT ADULT l. 61E+08 1.11E+08 2.60E+07 O.OOE+00 O.OOE+00'.22E+07 6.39f+07 N/A TEEN 1.31E+08 9.29Ew07 2.17E+07 0.00E+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 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00f+00 0.00E+00 0.00E+00 N/A VEGTBLE ADULT 1.89E+08 1;31E+08 3.05E+07,0.00E+00 O.OOE+00 7.30E+07 7.50E+07 N/A TEEN 3.08E+08 2.18Ew08 5.09E+07 0.00E+00 O.OOE+00 1.38E+08 9.44E+07 N/A CHILD 7.67E+08 4.07E+08 1.26E+08 0.00E+00 0.00E+00 2.30E+08 7'.53E+07, N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 3.63E+08 2.51E+08 5.85E+07 O.OOE+00 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 0.00E+00 0.00E+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'.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 l. 11E+05 2.87E+03 N/A INFANT 1.97E+04 1. 17E+04 3.33E+03 0.00E+00 0.00E+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

• ~~MAXIMUM VALUES FOR PATHWAYS~~*

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

0.00E+00 0.00E+00 8.52E+07 6.73E+07 2.51E+08 7.67E+08 1.07E+09 1.24Ew05 PAGE: 4-6

.D.C.M.

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

ISOTOPE: Mn-56 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G. I,. SKIN GROUND ADULT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 TEEN O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 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 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 iGOAT ADULT O.OOE+00 7.17E-04 1.27E-04 O.OOE+00 9.11E-04 O.OOE+00 2.29E-02 N/A IMILK TEEN 0'.OOE+00 1.27E-03 2.26E-04 0.00E+00 1.61E-03 0.00E+00 8.37E-02 N/A CHILD 0.00E+00 2.22E-03 5.01E-04 0.00E+00 2.68E-03 0.00E+00 3.21E-01 N/A INFANT 0.00E+00 5.43E-03 9.36E-04 0.00E+00 4.67E-03 0.00E+00 4.93E-01 N/A ICOW ADULT 0.00E+00 1.05E-03 1.86E-04 0.00E+00 1.33E-03 0.00E+00 3.34E-02 N/A

)

MILK TEEN O.OOE+00 1.85E-03 3.30E-04 O.OOE+00 2.35E-03 O.OOE+00 1.22E-01 N/A CHILD 0.00E+00 3.23E-03 7.30E-04 0.00E+00 3.9IE-03 0.00E+00 4.69E-01 N/A INFANT 0.00E+00 7.92E-03 1.37E-03 0.00E+00 6.81E-03 0.00E+00 7.19E-01 N/A MEAT ADULT 0.00E+00 5.00E-54 8.86E-55 0.00E+00 6.34E-54 0.00E+00 1.59E-.52 N/A TEEN 0.00E+00 4.06E-54 7.21E-55 0.00E+00 5.14E-54 0.00E+00 2.67E-52 .N/A CHILD O.OOE+00 5.41E-54 1.22E-54 '.OOE+00 6.54E-54 O.OOE+00 7.84E-.52 N/A INFANT 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00. 0.00E+00 0.00E+00 N/A

.QTBLE ADULT 0.00E+00 5.25E+00 9.3IE-Ol 0.00E+00 6.66E+00 0.00E+00 1.67E+02 N/A TEEN 0.'OOE+00 4.73E+00 8.42E-01.0.00E+00 5.99E+00 0.00E+00 3.11E+02 N/A CHILD 0.00E+00 6.19E+00 1.40E+00 O.OOE+00 7.49E+00 0.00E+00 8.97E+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 TOTAL ADULT 0.00E+00 5.25E+00 9.31E-Ol 0.00E+00 6.66E+00 O.OOE+00 1.68E+02 N/A INGEST. TEEN 0.00E+00 4.73E+00 8.42E-Ol 0.00E+00 5.99E+00 0.00E+00 3..12E+02 N/A CHILD O.OOE+00 6.20E+00 1.40E+00 O.OOE+00 7.50E+00 O.OOE+00 8.98E+02 ,

N/A INFANT O.OOE+00 1.34E-02.2.30E-03 O.OOE+00 1.15E-02 O.OOE+00 1.21E+00 N/A INHAL. ADULT 0.00E+00 1.24E+00 1.83E-'01 0.00E+00 1.30E+00 9.44E+03 2.02E+04 N/A TEEN 0.00E+00 1.70E+00 2.52E-01 O.OOE+00 1.79E+00 1.52E+04 5.74E+04 N/A CHILD 0.00E+00 1.66E+00 3.12E-01 0.00E+00 1.67E+00 1.31E+04 1.23E+05 N/A INFANT 0.00E+00 1.54E+00 2.21E-Ol 0.00E+00, 1.10E+00 1.25E+04 7.17E+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

• ~MAXIMUM VALUES FOR PATHWAYS~**

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

0.00E+00 0.00E+00 4.93E-01 7.19E-Ol 7.84E-52.8.97E+02 8.98E+02 .1.23E+05 PAGE:

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

Co-58 PATHWAY AGE GROUP BONE LIVER T.BODY 'HYROID 'IDNEY LUNG G.I. SKIN GROUND ADULT 3.'75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08'3.75E+08 4.39E+08 TEEN 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 4.39E&8

'HILD 3.75E+0& 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 3.75E+08 4.39E+08 INFANT 3.75Ew08 3.75E+08 3.75E+08 3.75&08 3.75E+08 3.75BO& 3.75E+08 4.39E108 GOAT ADULT O.OOE+00,3.00E+05 6.72E+05 O.OOE+00 O.OODOO '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.OOEi00 6.96E+06 N/A CHILD 0.00E+00 7.71E+05 2.36E+06 0.00E+00 0.00E+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 0.00E+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 0;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 MEAT ADULT O.OOE+00 7.78E+06 1.74E+07 O.OOE+00 O.OOE+00 O.OOE+00 1.5&E+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 0'.OOE+00 O.OOE+00 O.OOE+00 4.09E+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 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 TEEN 0.00E+00 3.96E+07 9.14E+07 0.00E+00 0.00E+00 0.00E+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 0.'OOE+00 3.59E+07 8.05E+07 O.OOE+00 O.OOE+00 O.OOE+00 7,.2&E+08 N/A INGEST. TEEN O.OOE+00 4.90E+07 1.13E+08 O.OOE+00 O.OOE+00 0'.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 1.5&E+03 2.07E+03 O.OOE+00 0'.OOE+00 9.2&E+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 1.22E+03 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: MEAT: VEGTBLE: INGEST: INHAL.

3.75E+08 4.39E+08 6.96Et06 3.94E+07 1.58E+08 5;47E+08 7.2&E+08 1.34E+06 PAGE: 4-8

O.D.C.M. HAXIHUH

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

ISOTOPE:~ Fe-59 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY G.I. SKIN GROUND ADULT 2-70E+08 2.70E+08 2.70E+08 2.TOE+08 2.70E+08 2.70E+08 2.70E+08 3.17E+08 TEEN 2.70E+08 2.70E+08 2.70E+08 2.TOE+08 2.70E+08 2.70E+08'.70E+08 3;17E+08 CHILD 2.70E+08 2.70E+08 2.70E+08 2.TOE+08 2.70E+08'2.70E+08 2.70E+08 3.17E+08 INFANT 2.70E+08 2.70E+08 2.70E+08 2.TOE+08 2.70E+08 2.70E+08 2.70E+08 3.17E+08 GOAT ADULT 1.92E+05 4.52E+05 1.73E+05 0.00E+00 0.00E+00 1.26E+05 1. 51E+06 N/A HILK TEEN 3.35E+05 7.&3E+05 3.02E+05 0.00E+00.-0.00E+00 2.47E+05 1.85E+06 N/A CHILD 7.7&E+05 1.26E+06 6.27E+05 0.00E+00 0.00E+00 3.65E+05 1.3IE+06 N/A INFANT 1.12E+08 2.54E+06 9.99E+05 0.00E+00 0.00E+00 7.49E+05 1. 21E+06 N/A OW AOULT 9.41E+06 2.21ft07 8.47E+06 O.oof+00 0.00E+00 '6.1&E+06 7.37E+07 N/A ILK TEEN 1.64E+07 3.&3E+07 1.4&f+07 0.00E+00 0.00E+00 1.21E+07 9.06E+07 N/A CHILD 3.81E+07 6.16E+07 3.07E+07 0.00E+00 0.00E+00 1.79E+07 6.41E+07 N/A INFANT 7.11E+07 1.24E+0& 4.89E+07 0.00E+00 0.00E+00 3.67E+07 5.93E+07 N/A EAT ADULT ',1.03E+08 2.42E+08 9.27E+07 0.00E+00 0.00E+00 6.76E+07 8.06E+08 N/A TEEN 8.23E+07 1.92E+08 7.41E+07 0.00E+00 0.00E+00 6.05E+07 4.54E+08 N/A CHILD ,1.46E+08 2.36E+08 1.1&E+08 O.OOE+00 O.OOE+00 6.&4E+07 2.46E+08 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 3TBLE ADULT 1.02E+0& 2.39E+0& 9.17E+07 0.00E+00 0.00E+00 6.6&E+07 7.97E+08 N/A:

TEEN 1.5&E+08 3.6&E+0& 1.42E+08 0.00E+00 0.00E+00 1.16E+08 8.71E+08 N/A CHILD 3.60E+08 5.82E+0& 2.90E+08 0.00f+00 0.00E+00 1.69E+08 6.06E+08'.OOE+00 N/A INFANT ,0.00E+00 0.0OE+00 O.OQE+00 O.OOE+00 O.oof+00 O.oof+00 N/A TOTAL ADULT 2.14E+08 5.04E+0& 1.93E+08 0.00E+00 0.00E+00 1.41E+08 1.6&E+09 N/A INGEST. TEEN 2.57E+08 5.99E+08 2.31E+08 0.00E+00 0.00f+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 9.1&E+08 N/A INFANT 1.83E+OB 1.27E+0& 4.99E+O7 O.OOE+00 O.OOE+OO 3.74E+07 6.05E+07 N/A INHAL. ADULT 1.1&E+04 2.7&E+04 1.06E+04 0.00E+00 0.00E+00 1.02E+06 1.88E+05 N/A TEEN 1.59E+04 3.70E+04 1.43E+04 0.00E+00 0.00E+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 9.4&f+03 0.00E+00 0.00E+00 1.01E+06 2.4&E+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

• ~*NAXIHUMVALUES FOR PATHWAYS**~

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: MILK: HEAT: VfGTBLE: INGEST: INHAL-2.70E+08 3. 17E+08 1.12E+08 1.24E+08 8.06E+08 8.71E+08 1.6&E+09 1.53E+06 PAGE:

err

0-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 2.13E+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 0.00E+00 1.25E+06 2.76E+06 O.OOE+00 0.00E+00 0.00E+00 2.35E+07 N/A MILK TEEN 0.'OOE+00 2.12E+06 4.78E+06 O.OOE+00 O.OOE+00 O.OOE+00 2.77E007 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 0.00E+00 6.73E+06 1.59E+07 0.00E+00 0.00E+00 0.00E+00 1.60E+07 N/A COW ADULT O.OOE+00 8.29E+06 1,83Et07 O.OOE+00 O.OOE+00 O.OOE+00 1.56B08 N/A MILK TEEN O.OOE+00 1.41D07, 3.17E+07 O.OOE+00 O.OOE+00 O.OOE+00 '.83E+08 N/A CHILD O.OOE+00 2.18E+07 6.44E+07 0.00E+00 0.00E+00 0.00E+00 1. 21E+08 N/A INFANT 0.00E+00 4.46E+07 1.05&08 0.00E+00 0.00E+00 0.00E+00 1.06E+08 N/A MEAT ADULT 0.00E+00 4.19E+07 9.23E+07 0.00E+00 0.00E+00 0.00E+00 7.86E+08 N/A TEEN 0.00E+00 3.25E+07 7.32E+07 0.00E+00 O.OOE+00 0.00E+00 4.23E+08 N/A CHILD 0.00E+00 3.86E+07 1.14E+08 0.00E+00 0.00E+00 0.00E+00 2.14E+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 O.OOE+00 1.51E+08 3.34E+08 O.OOE+00'O.OOE+00 O.OOE+00 2.84E+09 N/A TEEN 0.00E+00 2.35E+08 5.29E+08 0.00E+00 0.00E+00 0.00E+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 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 0.00E+00 2.03E+08 4.47E+08 0.00E+00 0.00E+00 0.00E+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 0.00E+00 5.13E+07 1.21Et08 0.00E+00 0.00E+00 0.00E+00 1.22Ew08 N/A INHAL. ADULT O.OOE+00 1. 15Ew04-1.48E+04 O.OOE+00 O.OOE+00 5.97E+06 2.85B05 N/A TEEN O.OOE+00 1.51E+04 1.9BEt04 O.OOE+00 O.OOE+00 8.72E+06 2.59005 N/A CHILD O.OOE+00 1.31E+04 2.26Et04 O.OOE+00 O.OOE+00 7.07E+06 9.62E+04 N/A INFANT 0-OOE+00 8.02E+03 1. 18Et04 0.00E+00 0.00E+00 4.51E+06 3. 19E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKI

• 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. 'KIN MILK: MILK: MEAT: VEGTBLE-'NGEST: INHAL.

2.13E+10 2.51E+10 2.77E+07 1.83E+08 7.86E+08 3.06E+09. 3.81E+09 8.72E+06 PAGE: 4-10

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

ISOTOPE: ~ Hi-63 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID LUNG G.I. SKIN GROUND ADULT 0.00E+00 0.00E+00 0.00E+00 0.00E+00-0.00E+00 0.00E+00 0.00E+00 0.00E+00.

TEEN 0.00E+00 0.00E+00 0.00E+00 0.00E+00-.0.00E+00 0.00E+00 0.00E+00 O.OOE+00 CHILD 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 GOAT ADULT 5.19E+08 3.59E+07 1.74E+07 0.00E+00 0.00E+00 0.00E+00 7.50E+06 N/A HILK TEEN 9.11E+08 6.43E+07 3.09E+07 0.00E+00 0.00E+00 0.00E+00 1.02E+07 N/A CHILD 2.28E+09 1.22E+08 7.77E+07 0.00E+00 0.00E+00 0.00E+00 8.24E+06 N/A INFANT 2.24E+10 1.66E+08 9.34E+07 0.00E+00 0.00E+00 0.00E+00 8.28E+06 N/A COW ADULT 3.45E+09 2.39E+08 1.16E+08 0.00E+00 0.00E+00 0.00E+00 5.00E407 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 0,00E+00 0.00E+00 0.00E+00 5.49E+07 N/A INFANT 1.79E+10 1.11E+09 6.22E+08 0.00E+00 0.00E+00 0.00E+00 5.52E+07 N/A HEAT 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 0.00E+00 0.00E+00 0.00E+00 9.63E+07 N/A CHILD 1.64E+10 8.79E+08 5.59E+08 0.00E+00 0.00E+00 0.00E+00 5.92E+07 N/A INFANT O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A QTBLE ADULT 9-43E+09 6.54E+08 3.16E+08 0.00E+00 0.00E+00 0.00E+00 1.36E+08 N/A TEEN 1.52E+10 1.07E+09 5.15E+08 0.00E+00 0.00E+00 0.00E+00 1.71E+08 N/A CHILD 3.79E+10 2.03E+09 1.29E+09 O.OOE+00 O.OOE+00 0.00E+00 1.37E+08 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 2.40E+10 1.67E+09 8.07E+08 0.00E+00 0.00E+00 0.00E+00 3.48E+08 N/A INGEST. TEEN 3.07E+10 2.17E+09 1.04E+09 0.00E+00 0-OOE+00 0.00E+00 3.46E+08 N/A CHILD 7.18E+10 3.84E+09 2.44E+09 0.00E+00 0-OOE+00 0-OOE+00 2.59E+08 N/A INFANT 4.04E+10 1.28E+09 7.16E+08 0.00E+00 0.00E+00 0.00E+00 6.34E+07 N/A IHHAL. ADULT 4.32E+05 3.14E+04 1.45E+04 0.00E+00 0.00E+00 1.78E+05 1.34E+04 N/A TEEN 5.80E+05 4.34E+04 1.98E+04 0.00E+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 0.00E+00 O.OOE+00 2.09E+05 2.42E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. S I

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

• ""MAXIHUNVALUES FOR PATHWAYS*"~

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

0.00E+00 0.00E+00 2.24E+10 1.79E+10 1.64E+10 3.79E+10 7.18E+10 8.21E+05 PAGE: 4-11

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

ISOTOPE: Zn-65 PATHWAY AGE GROUP 80NE 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+08,7,40E+08 7.40E+08 7.40E+08 &.50E+08 CHILD 7.40E+0& 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 7.40E+08 8.50E+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.&7E+07 3. 14E+08 1.42E+08 O.OOE+00 2. 10E+0& O.OOE+00 1.98E+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 2.97fwO& 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+0& O.OOE+00 1.16E+09 N/A COW ADULT 6.24E+08 1.99E+09 8.97E+08 0.00E+00 1.33E+09 0.00E+00 1.25ft09 N/A MILK TEEN 9.5&E+08 3.33fw09 1.55E+09 O.OOE+00 2.13E+09 O.OOE+00 1.41E+09 N/A CHILD 1.&BE+09 5.01E+09 3.12E+09 O.OOE+00 3.16E+09 0.00f+00 8.&OE+08 N/A INFANT 2.53E+09 8.66E+09 3.99E+09 O.OOE+00 4.20E+09 O.OOE+00 7.31fw09 N/A ADULT 1.&2E+08 5.79E+08 2.62E+08 O.OOE+00 3.87E+08 O.OOE+00 3.65E+08 N/A TEEN 1.2&E+08 4.44E+08 2.07E+08 0.00E+00 2.84E+08 0.00E+00 1.88E+08 ,

N/A CHILD 1.92E+08 5.11E+08 3.18E+08 O.OOE+00 3.22E+08 O.OOE+00 8.9&E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00f+00 O.OOE+00 N/A ADULT 2.83E+08 9.01E+08 4.07E+08 O.OOE+00 6.03E+08 O.OOE+00 5.68E+08 N/A 'EGTBLE 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 2.06f+09 1.2&E+09 0.00E+00 1.30E+09 0.00E+00 3.62E+08 N/A INFANT . 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00'0.00ft00 N/A TOTAL ADULT . 1.19E+09 3.78E+09 1.71ft09 0.00E+00 2.53E+09 0.00E+00 2.3&fw09 N/A INGEST. TEEN 1.63E+09 5.68f+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.&SE+09 1.00E+10 4.63E+09 0.00f+00 4.86E+09 O.OOE+00 8.47E+09 N/A INHAL. ADULT 3.24E+04 1.03E+05 4.66E+04 0.00E+00 6.90E+04-8.64E+05 5.34E+04 N/A TEEN 3.&6E+04 1.34E+05 6.24E+04 0.00E+00 8.64E+04 1.24E+06 4.66E+04 N/A CHILD 4.25E+04 1.13E+05 7.03E+04 0.00E+00 7.14E+04 9.95E+05 1.63E+04 N/A INFANT 1.93E+04 6.26E+04 3.11E+04 0.00E+00 3.25E+04 6.47E+05 5.14E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. S I

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

• • • MAXIMUMVALUfS FOR PATHWAYS"~

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

7.40E+08 8.50E+08 3.33E+09 8.66E+09 5.79E+08 2.06E+09 1.00E+10 1.24fw06 PAGE: 4-12

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.

I:

SKIN'ROUND.

ADULT 8.89E+06 S.S9E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 S.S9E+06 1.02E+07 TEEN 8.89E+06 8.89E+06 8.89E+06 8.89E+06 8.89E+06 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 O.OOE+00 1.42E+08 6.63E+07 O.OOE+00 O.OOE+00 O.OOE+00 2.&OE+07 N/A MILK TEEN O.OOE+00 2.59E+0& 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 0.00E+00 1.22E+09 6.03E+08 0.00E+00 0.00E+00 0.00E+00 3. 12E+07 N/A COW ADULT 0.00E+00 6.7&E+08 3.16E+08 0.00E+00 0.00E+00 0.00E+00 1.34E+08 N/A MILK TEEN 0.00E+00 1.24E+09 5.&OE+08 0.00E+00 0.00E+00 0.00E+00 1.83E+08 N/A CHILD 0.00E+00 2.29E+09 1.41E+09 0.00E+00 0.00E+00 0.00E+00 1.47E+08 N/A INFANT 0.00E+00 5-81E+09 2.87E+09 0.00E+00 0.00E+00 0.00E+00 1.49E+08 N/A MEAT ADULT 0.00E+00 1.65E+OS 7.67E+07 0.00E+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 0.00E+00 O.OOE+00 2.03E+07 N/A CHILD O.OOE+00 1.95E+08 1.20E+08 O.OOE+00 0.00E+00 O.OOE+00 1.25E+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 uTBLE ADULT O.OOE+00 1.32E+08 6.17E+07 O.OOE+00 O.OOE+00 0.00E+00 2.61E+07 N/A TEEN 0.00E+00 1.93E+08 9.07E+07 O.OOE+00 0.00E+00 0.00E+00 2.86E+07 N/A

'HILD O.OOE+00 3.40E+08 2.09E+08 O.OOE+00 0.00E+00 O.OOE+00 2.19E+07 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ADULT 0.00E+00 1.12E+09 5.20E+08 0.00E+00 0.00E+00 0.00E+00 2.20E+08 N/A INGEST. TEEN 0.00E+00 1-83E+09 8.57E+08 0.00E+00 0.00E+00 0.00E+00 2.70E+08 N/A CHILD 0.00E+00 3.31E+09 2.03E+09 0.00E+00 0.00E+00 0.00E+00 2.13E+08 N/A INFANT 0.00E+00 7.03E+09 3.4&E+09 0.00f+00 0.00E+00 0.00E+00 1.&OE+08 N/A INHAL. ADULT 0.00E+00 1.35E+05 5.90E+04 0.00E+00 0.00E+00 0.00E+00 1.66E+04 N/A TEEN 0.00E+00 1.90E+05 8.40E+04 O.OOE+00 0.00E+00 0.00E+00'1.77E+04 N/A CHILD 0.00E+00 1.9&E+05 1.14E+05 0.00E+00 0.00E+00 0.00E+00 7.99E+03 N/A INFANT 0.00E+00 1.90E+05 8.82E+04 0.00E+00 0.00E+00 0.00E+00 3.04E+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 'OTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTB LE: INGEST: INHAL.

8.89E+06 1.02E+07 1.22E+09 5.81E+09 1.95E+08 3.40E+08 7.03E+09 1.9&E+05 PAGE: 4-13

O.D.C-M. HAXIHUM 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 2.14E+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 0.00E+00 4.43E+07 0.00E+00 0.00E+00 0.00E+00 2.47E+08 N/A HILK 'EEN 2.84E+09 0.00E+00 8.14E+07 0.00E+00 0.00E+00 0.00E+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 2.7SE+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 HILK TEEN &.7&E+08 0.00E+00 2.51E+07 0.00f+00 0.00E+00 0.00E+00 1.05E+08 N/A'/A CHILD 2.17E+09 O.OOE+00 6.20E+07 O.OOE+00 O.OOE+00 O.OOE+00 8. 41E+07 INFANT 4.13E+09 O.OOE+00 1.1&E+08 O.OOE+00 O.OOE+00 O.OOE+00 8.49E+07 N/A HEAT ADULT 1.20E+08 O.OOE+00 3.44006 O.OOE+00 O.OOE+00 O.OOE+00 1.92E+07 N/A TEEN 1.01E+08 O.OOE+00 2.90f+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 0.00E+00 0.00E+00.,0.00E+00 7.42E+06 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 I

VEGTBLE ADULT 8.19E+09 0.00E+00 2.35E+08 O.OOE+00 O.OOE+00 O.OOE+00 1.31E+09 N/A TEEN 1.35E+10 0.00f+00 3.86E+08 0.00E+00 0.00E+00 0.00E+00 1.60B09 N/A CHILD 3.29E+10 O.OOE+00 9.39E+08 0.00E+00 0.00E+00 0.00E+00 1.27E+09 N/A INFANT O.OOE+00 O.OOE+00 0.00E+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 N/A TOTAL ADULT 1.03E+10 0.00E+00 2.96E+08 0.00E+00 0.00E+00 0.00E+00 1. 66E+09 N/A INGEST. TEEN 1.73E+10 0.00E+00 4.95E+08 0.00E+00 0.00E+00 0.00E+00 2.06E+09 N/A CHILD 4.23E+10 0.00E+00 1.21E+09 0.00E+00 0.00E+00 0.00E+00 1.64E+09 N/A INFANT 1.05E+10 0.00E+00 5.02E+0& 0.00E+00 0.00E+00 0.00E+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 3.50E005 ~

N/A TEEN 4.34E+05 0.00E+00 1.25E+04 0.00E+00 0.00E+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 3.9&E+05 0.00E+00 1.14E+04 0.00E+00 0.00E+00 2.03E+06 6.40E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G. I.'KIN

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

• "~HAXINUN VALUES FOR PATHWAYS**~

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

2.14E+04 2.49E+04 7.04E+09 4.13ft09 1.92E+08 3.29E+10 4.23E+10 2.42E+06 PAGE: 4-14 DAT

O.D.C.H.

~ ~ ~ ~ MAXIHUH 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+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 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 0.00E+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,OOE+00 2.20E+10 O.OOE+00 O.OOE+00 O.OOE+00 2.50E+09 N/A CHILD 1.5IE+11 O.OOE+00 3.82E+10,0.00E+00 O.OOE+00 O.OOE+00 2.03E+09 N/A INFANT 7.80E+10 0.00E+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

'HILK TEEN 3.39E+10 O.OOE+00 8.37E+09 O.OOE+00 O.OOE+00 O.OOE+00 9.5IE+08 N/A CHILD 5.72E+10 O.OOE+00 1.45E+10 O.OOE+00 O.OOE+00 O.OOE+00 7.71E+08 N/A I

I INFANT 6.23E+10 O.OOE+00 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 7.88E+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 QTBLE ADULT, 5 48E+ll 0.00E+00 1.34E+ll 0".OOE+00 0.00E+00 0.00E+00 1.58E+10 N/A TEEN 7;IOE+ll 'O.OOE+00 1.75E+11 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+ll 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+11 O.OOE+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'NFANT 1.01E+08 O.OOE+00, 6.44E+06 O.OOE+00 O.OOE+00 1.48E+07 3 -43E+05 N/A 4.09E+07 0.00E+00 2.59E+06 0.00E+00 0.00E+00 1. 12E+07 1.31E+05 N/A I

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

• • "HAXIHUHVALUES 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+11 6.23E+10 7.00E+09 1.19E+12 1.41E+12 1.08E+08 PAGE: 4-15

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 0-OOE+00 O.OOE+00 O.OOE+00 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN 0.00E+00 O.OOE+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 CHILD 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 GOAT ADULT 3.83E+00 0.00E+00 1.03E-01 0.00E+00 0.00E+00 0.00E+00 4.06E+04 N/A MILK TEEN 7.03E+00 O.OOE+00 1.89E-Ol O.OOE+00 O.OOE+00 O.OOE+00 5.80fw04 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 0.00E+00 9.86E-Ol 0.00E+00 0.00E+00 0.00E+00 5.08E+04 N/A COW ADULT 1.79E+01 O.OOE+00 4.79E-Ol O.OOE+00 O.OOE+00 O.OOE+00 1.89E+05 N/A MILK TEEN 3.28E+01 O.OOE+00 8.84E-Ol 0.00f+00 O.OOE+00 O.OOE+00 2.71E>05 N/A CHILD 8.12E+Ol 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 2.37B.05 N/A HEAT ADULT 3.55E+01 O.OOE+00 9.52E-Ol O.OOE+00 O.OOE+00 O.OOE+00 3.76E+05 N/A TEEN 2.99E+01 O.OOE+00 8.04E-OI O.OOE+00 O.OOE+00 O.OOE+00 2.46E+05 N/A CHILD 5.65E+Ol O.OOE+00 1.51E+00 O.OOE+00 O.OOE+00 O.OOE+00 1.61ft05 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 VEGTBLE ADULT 4.39E+03 O.OOE+00 1.18E+02 0.00E+00 O.OOE+00 O.OOE+00 4.65007 N/A TEEN 4.10E+03 0.00E+00 1.10E+02 0.00E+00 0.00E+00 0.00E+00 3.38E007 N/A CHILD 7.61E+03 O.OOE+00 2.04E+02 O.OOE+00 O.OOE+00 0.00E+00 2.17E+07 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 4.44E+03 0.00E+00 1.19E+02 O.OOE+00 0.00E+00 0.00E+00 4.71E007 N/A INGEST. TEEN 4.17E+03 0.00E+00 1.12E+02 0.00E+00 0.00E+00 0.00E+00 3.44E+07 N/A CHILD 7.77E+03 0.00E+00 2.08E+02 O.OOE+00 O.OOE+00 O.OOE+00 2.21fw07 N/A INFANT 4.78E+02 0.00E+00 5.59E+00 O.OOE+00 0.00E+00 0.00E+00 2.88& 05 N/A INHAL. ADULT 2.09E+03 0.00E+00 5.61E+01 0.00E+00 0.00E+00 1.70E+05 ,5.06E+05 N/A TEEN 2.98E+03 0.00E+00 8.00E+01 0.00E+00 0.00f+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:

T.B./ORG. SKIN GOAT MILK:

COW MILK:

'OTAL MEAT: VEGTBLE: INGEST: INHAL.

0.00E+00 0.00E+00 5.80E+04 2.'71E+05 3.76E+05 4.65E+07 4.71E+07 5.59E+05 0 PAGE: 4-16 DAT

O.D.C.M. MAXIMUM PATHWAY

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

ISOTOPE: Sr-91 PATHWAY AGE GROUP BONE LIVER'.BODY 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 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 CHILD 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 GOAT ADULT 2.73E+04 0.00E+00 1. 10E+03 0.00E+00 0.00E+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 0.'OOE+00 O.OOE+00 O.OOE+00 2.72E+05 N/A INFANT 1.22E+05 0.00E+00 9.29E+03 0.00E+00 0.00E+00 0.00E+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 0.00E+00 5.3ZE+02 0.00E+00 0.00E+00 0.00E+00 6.07E+04 N/A CHILD 3.28E+04 O.OOE+00 1.24E+03 O.OOE+00 O.OOE+00 O.OOE+00 7".25E+04 N/A INFANT 6.84E+04 0.00E+00 2.48E+03 0.00E+00 0.00E+00 0.00E+00 8. 10E+04 N/A MEAT ADULT 5.01E-11 0.00E+00 2.02E-12 0.00E+00 0.00E+00 0.00E+00 2.38E-10 N/A TEEN 4.21E-ll O.OOE+00 1.68E-12 0".OOE+00 O.OOE+00 0-OOE+00 1.91E-10 N/A CHILD 7.90E-ll 0.00E+00 2.98E-12 "0.00E+00 0.00E+00 0.00E+00 1.74E-10 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

~TBLE 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 0.00E+00 3.74E+03 0.00E+00 0.00E+00 0.00E+00 4.26E+05 N/A CHILD 1.73E+05 0.00E+00 6.53E+03 0.00E+00 0.00E+00 0.00E+00 3.82E+05 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 0.00E+00 N/A TOTAL ADULT '.35E+05 0.00E+00 5.46E+03 0.00E+00 0.00E+00 O.OOE+00 6.44E+05 "

N/A INGEST. TEEN 1.58E+05 0.00E+00 6.27E+03 0.00E+00 0.00E+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 0.00E+00 1.18E+04 0.00E+00 0.00E+00 O.OOE+00 3.85E+05 N/A INHAL. ADULT ~, 6.19E+01 0.00E+00 2.50E+00 0.00E+00 0.00E+00 3.65E+04 1.91E+05 N/A

, TEEN 8.80E+01 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+04 1.74E+05 N/A INFANT 9.56E+01 0.00E+00 3.46E+00 0.00E+00 0.00E+00 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 TOTAL T.B./ORG- SKIN MILK: 'ILK:

COW MEAT: VEGTBLE: INGEST: INHAL-0.00E+00 0.00E+00 3.04E+05 8.10E+04 2.38E-10 4.79E+05 7.26E+05 2.59E+05 PAGE: 4-17

O.D.C.M. MAXIHUM 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 1.06f+06 1.06E+06 1.06E+06, 1.06E+06 1.2OE+06 TEEN 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.2OE+06 CHILD 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.2OE+06 INFANT 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.06E+06 1.20E+06 GOAT ADULT 5;32E+02 O.OOE+00 1.42E+Ol 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 0.00E+00 6.47E+01 0.00E+00 0.00E+00 0.00E+00 3.22E005 N/A INFANT 3.78E+04 0.00E+00 1,21E+02 0.00E+00 0.00E+00 0.00E+00 -'.25E+05 N/A COW ADULT 2.94E+03 O.OOE+00 7.85E+Ol O.OQE+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 2.22fw06 '/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 6.68E+02 O.OOE+00 O.OOE+00 O.OOE+00 1.80E+06 N/A HEAT 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 0.00f+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 1.98E+04 O.OOE+00 O.OOE+00 0.00E+00 9.85E+07 N/A INFANT O.OOE+00 0.00E+00 0.00E+00 '0.00E+00 0.00E+00 0.00f+00 0.00E+00 N/A VfGTBLE ADULT 4.27E+06.,0.00E+00 1.14E+05 O.OOE+00 O.OOE+00 O.OOE+00 2.35E+09 N/A TEEN 7.05E+06 O.OOE+00 1.89E+05 O.OOE+00 O.OOE+00 O.OOE+00 2.89E+09 '/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 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 4.74E+06 O.OOE+00 1.27E+05 O.OOE+00 O.OOE+00 O.OOE~OO 2.61E009 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 2.12fw06. N/A INHAL. ADULT 4.62f+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 0.00E+00 2.44E+04 0.00E+00 0.00E+00 2.63E+06 1.84E+05 N/A INFANT 5.88E+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 1

• ~MAXIHUH VALUfS FOR PATHWAYS*~~

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

1.06E+06 1.20fw06 4.01E+05 2.22E+06 2.56E+08 2.89E+09 3.05E+09 2.94E+06 PAGE: 4-18

O.D.C.M.

~ ~ ~ MAXIMUM PATHWAY DOSE FACTORS: RADIOHUCLIDES 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 0.00E+00 2.63E+03 0.00E+00 1.6IE+07 N/A MILK TEEN 8.15E+03 4.52E+03 2.49E+03 O.PPE+00 4.38E+03 0.00E+00 1.93E+07 N/A CHILD 1.84E+04 7.17E+03 5.12E+03 0.00E+00 6.73E+03 0.00E+00 1.33E+07 N/A INFANT 2.86E+05 1.42E+04 8.18E+03 0.00E+00 .1.01E+04 0.00E+00 1.19E+07 N/A .

COW ADULT 2.44E+04 1.36E+04 7.31E+03 O.PPE+00 1.34E+04 O.OOE+00 8.25E+07 N/A MILK TEEN 4.17E+04 2.31E+04 1.27f+04 0.00E+00 2.24E+04 0.00E+00 9.89E+07 N/A CHILD 9.41E+04 3-67E+04 2.62E+04 0.00E+00 3.44E+04 0.00E+00 6.78E+07 N/A INFANT 1.76E+05 7.24E+04 4.18E+04.0.0PE+00 5.19E+04 0.00E+00 6.11E+07 N/A MEAT ADULT 8.48E+05 4.72E+05 2.54E+05 0.00E+00 4.66E+05 0.00E+00 2.86E+09 N/A TEEN 6.62E+05 3.67E+05 2.02E+05 0.00E+00 3.56E+05 0.00E+00 1.57E+09 N/A CHILD 1.14E+06 4.45E+05 3.18E+05 0.00E+00 4.18E+05 0.00E+00 8.23E+08 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 '/A-3TBLE ADULT 1.10E+05 6.11E+04 3.28E+04 0.00E+00 6.04E+04 0-OOE+00 3.71E+08 N/A TEEN 1.64E+05 9.10E+04 5.01E+04 0.00E+00 8.82E+04 0.00E+00 3.89E+08 N/A CHILD 3.63E+05 1.41E+05 1.01E+05 P.OPE+00 1.33E+05 0.00E+00 2.61E+08 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 O.POE+00 N/A ~

TOTAL ADULT 9.87E+05 5.49E+05 2.95E+05 O.POE+00 5.43E+05 O.OOE+00 3.33E+09 N/A INGEST. TEEN 8.76E+05 ,4.86E+05 2.68E+05 0.00E+00 4.71E+05 O.OOE+00 2.08E+09 N/A CHILD 1.62E+06 6.30E+05 4.50E+05 O.POE+00 5.92E+05 0.00E+00 1.17E+09 N/A INFANT 4.62E+05 8.65E+04 5.00E+04 0.00E+00 6.20E+04-0.00E+00 7.30E+07 N/A INHAL. ADULT 1.41E+04 7.82E+03 4.21E+03 0.00E+00 7.74E+03 5.05E+05 1.04E+05

'/A TEEN 1.86E+04 1.03E+04 5.66E+03 0.00E+00 1.00E+04 7.5IE+05 9.68E+04 N/A

'HILD 2.35E+04 9.18E+03 6.55E+03 0.00E+00 8.62E+03 6.14E+05 3.70E+04 N/A INFANT, 1.57E+04 6.43E+03 3.78E+03 P.PPE+OP 4.72E+03, 4.79E+P5 1.27E+P4 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.

1.35E+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

O.O.C.H. MAXIMUM PATHWAY DOSE FACTORS: RAOIONUCLIDES 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 2.8IE+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 2.42f+08 2.42E+08 2.42E+08 2.8IE+08 GOAT ADULT 5.92E+01 1.90E+Ol" 1.28E+01 0.00E+00 2.98E+01 'O.OOE+00 6.01E+04 N/A MILK TEEN 1.03E+02 3.26E+01 2.25E+01 0.00E+00 4.80E+01 0.00E+00 7.53E+04 N/A CHILD 2.40E+02 5.28E+01 4.70E+01 0.00E+00 7.56E+Ol 0.00E+00 5.51E+04 N/A INFANT 3.56E+03 1.04E+02 7.38E+Ol 0.00E+00 1.12E+02 0.00E+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 HILK 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 0.00f+00 4.23E+02 0.00E+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 N/A HEAT ADULT 7.83E+05 2.51E+05 1.70E+05 0.00E+00 3.94E+05 0.00E+00 7.96E+08 N/A TEEN 6.27E+05 1.98E+05 1.36E+05 0.00E+00 2.91E+05 0.00E+00 4.57E+08 N/A CHILD 1.11E+06 2.45E+05 2.18E+05 0.00E+00 3.50E+05 0.00E+00 2.55E+08 N/A INFANT 0-00E+00 0-OOE+00 0.00E+00 0.00E+00 0-00E+00 0.00E+00 0.00E+00 N/A VEGTBLE ADULT 9.90E+05 3.17E+05 2.15E+05 0.00E+00 4.98E+05 0.00E+00 1.01E+09 N/A TEEN 1.56E+06 4.91E+05 3.38E+05 0.00f+00 7.22E+05 0.00E+00 1.13E+09 N/A CHILD 3.57E+06 '7.85E+05 6.99E+05 0.00E+00 1.12E+06 0.00E+00 8.19E+08 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 1.77E+06 5.69E+05 3.85E+05 0.00E+00 8.92E+05 0.00E+00 1.80E+09 N/A INGEST. TEEN 2.18E+06 6.89E+05 4.74E+05 0.00E+00 I.OIE+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 0.00E+00 7.39E+02 0.00E+00 3.41E+05 N/A INHAL. ADULT 1.07E+05 3.44E+04 2.33E+04 0.00E+00 5.42E+04 1.77E+06 1.50E+05 N/A TEEN 1.46E+05 4.58E+04 3.15E+04 0.00E+00 6.74E+04 2.69E+06 1.49E+05 N/A CHILD 1.90E+05 4.18E+04 3.70E+04 0.00E+00 5.96E+04 2.23E+06 6.11E+04 N/A INFANT 1.15E+05 2.79E+04 2.03E+04 0.00E+00 3.11E+04 1.75E+06 2.17E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKI

• 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. 42E+08 2.81E+08 7.53E+04 4. 21E+05 7.96E+08 1.13E+09 1.80E+09 2.69E+06 PAGE: 4-20

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 0.00E+00 O.OOE+00 O.OOE+00 0.00f+00 0.00E+00 O.OOE+00 0.00E+00 TEEN O.OOE+00 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 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 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 GOAT ADULT O.OOE+00 1.34E+06 2.55E+05 O.OOB.OO 3.03E+06 O.OOE+00 3.10E+06 N/A NILK TEEN 0.00E+00 2.42E+06 4.61E+05 O.OOE+00 5.53E+06 O.OOE+00 4.33E+06 N/A CHILD 0.00E+00 4.39E+06 1.09E+06 O.OOE+00 9.38E+06 O.OOE+00 3.63E+06 N/A INFANT 0.00E+00 1.12BOT 2.19E+06 0.00f+00 1.68E+07 O.OOBOO 3.70B06 N/A COW ADULT O.OOE+00 6.24f+06 1.19E+06 O.OOE+00 1.41E+07 O.OOE+00 1.45B.07 N/A HILK TEEN O.OOE+00 1.13E+07 2. 15E+06 0.00E+00 2.58E+07 O.OOE+00 2.02E+07 N/A CHILD O.OOE+00 2.05E+07 5.07E+06 O.OOE+00 4.38E+07 O.OOE+00 1.70B07 N/A INFANT O.OOE+00 5.24f+07 1.02E+07 O.OOE+00 7.83E+07 O.OOE+00 1.73E+07 N/A HEAT ADULT O.OOE+00 3.30E+04 6.27E+03 O.OOE+00 7.46E+04 O.OOE+00 7.64E+04 N/A TEEN 0'.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 0.00E+00 8. 10E+04 0.00E+00 3. 14E+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

. uTBLE ADULT 0.00E+00 2.03E+06 3.86E+05 0.00BOO 4.60E+06 0.00E+00 4.71E+06 N/A TEEN O.OOE+00 1.86B06 3.55E+05 O.OOE+00 4.27E+06 O.OOE+00 3.34E+06 N/A CHILD O.OOE+00 2.54E+06 6.30E+05 0.00E+00 5.43E+06 0.00E+00 2.10E+06

'/A INFANT O.OOE+00 O.OOBOO O.OOE+00 O.OOE+00 O.OOBOO O.OOE+00 O.OOE+00 N/A TOTAL ADULT O.OOE+00 9.64E+06 1.83E+06 O.OOE+00 2.18E+07 0.00E+00 2.24E+07 N/A INGEST. TEEN 0'.Oof+00 1.56E+07 2.9TB06 O.OOE+00 3.56E+07 O.OOE+00 2.79E+07 N/A CHILD 0. OOE+00 2.75E+07 6.80E+06 O.OOE+00 5.87E+07 O.OOE+00 2.27E+07 N/A INFANT 0.00E+00 6.37E+07 1.24f+07 O.OOE+00 9.51E+07 O.OOE+00 2.10E+07 N/A INHAL. ADULT Q.OOE+00 1.21E+02 2.30E+01 0.00E+00 2.91E+02 9.12E+04 2.48E+05 ,N/A TEEN O.OOE+00 1.69E+02 3.22E+Ol 0.00B00 4-.11E+02 1.54E+05 2.69E+05 N/A CHILD O.OOE+00 1.72E+02 4.26E+Ol 0.00BOO 3,.92E+02 1.35E+05 1.27E+05 N/A-INFANT O.OOE+00 1.65E+02 3.23E+Ol 0.00E+00 2.65E+02 1.35E+05 4.87E+04 N/A 80NE LIVER T.BODY THYROID KIDNEY LUNG G.l. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3 Deposition pathways: units are mrem-m2/yr/uCi/sec 1

"*"NAXIHUNVALUES FOR PATHWAYS**~

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

0.00E'+00 0.00E+00 1.68E+07 7.83E+07 8.10E+04 5.43E+06 9.51E+07 2.69E+05 PAGE: 4-21

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 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 TEEN O.OOE+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 O.OOE+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 1.79E-01 5.07E-01 6.46E+00 O.OOE+00 7.70E+00 2.48E-01 3.00E+02 N/A MILK TEEN 3.'llE-01 8.68E-Ol 1.12E+Ol O.OOE+00 1.29E+Ol 4.82E-01 5.70E+02 N/A CHILD 7.13E-01 1.40E+00 2.32E+01 0.00E+00 2.03E+01 7.10E-01 7.96E+02 N/A INFANT 1.24E+01 3.06E+00 3.94E+Ol O.OOE+00 3.29E+Ol 1.60E+00 8.89E+02, N/A COW ADULT 8.37E-Ol 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+01 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+01 3.31E+00 3. 71E+03 N/A INFANT 6.92E+00 1.43E+Ol 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 0.00E+00 0.00E+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 O.OOE+00 N/A VEGTBLE ADULT 1.02E+00 2.89E+00 3.68E+01 0.00E+00 4.39E+01 1.42E+00 1. 71E+03 N/A TEEN 9.03E-OI 2.52E+00 3.26E+Ol 0.00E+00 3.75E+01 1.40E+00 1.65E+03 N/A CHILD 1.55E+00 3.05E+00 5.05E+01 0.00E+00 4.43E+01 1.55E+00 1.73E+03 N/A INFANT O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 N/A TOTAL ADULT 2.04E+00 5.76E+00 7.34E+01 0.00E+00 8.75E+01 2.82E+00 3.41E+03 N/A INGEST. TEEN 2.67E+00 7.43E+00 9.63E+01 0.00E+00 1.11E+02 4.13E+00 4.88E+03 N/A CHILD 5.60E+00 1.10E+01 1.82E+02 0.00E+00 1.59E+02 5.57E+00 6.25E+03 N/A INFANT 1.93E+Ol 1.73E+01 2.23E+02. 0.00E+00 1.87E+02 9.07E+00 5.04E+03 N/A INHAL. ADULT 1.03E-03 2.91E-03 3.70E-02 0.00E+00 4.42E-02 7.64E+02 4. 16E+03 '.

N/A TEEN 1.38E-03 3.86E-03 4.99E-OZ 0.00f+00 5.76E-02 1.15E+03 13E+03 N/A CHILD: '.78E-03 3.48E-03 5.77E-02 0.00E+00 5.07E-02 9.5IE+02 4.81E+03 N/A INFANT 1.40E-03 2.88E-03 3.72E-OZ 0.00E+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

O.D.C.H.

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

ISOTOPE: Ru-106 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 4.18fw08 4.18008 4.18E+08 4.18E+08 4.18008 4.18E+08 4.18E+08 5.01E+08 TEEN 4.18fw08 4.18ft08 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 4.180.08 4.18E+08 4.18E+08 4;18E+08 5.01E&8 INFANT 4.18E+08 4.18E+08 4.18E+08 4.18E+08 4.18ft08 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 HILK TEEN 2.76E+03 0.00E+00 3.48E+02 0.00E+00 5.32E+03 0.00E+00 1.32ft05 N/A CHILD 6.79E+03 0.00E+00 8.47E+02 0.00E+00 9.17E+03 0.00E+00 1.06ft05 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.OOBOO 1.22E+03 O.OOE+00 1.86E+04 O.OOE+00 6.24E+05 N/A HILK TEEN 1.77E+04 O.OOE+00 2.24E+03 O.OOE+00 3.42f+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.OOBOO 1.12E+04 O.OOE+00 1.06E+05 O.OOE+00 6.83E+05 N/A ADULT 1.48E+09 0.00E+00 1.87E+08 0.00E+00 2,85E+09 0.00f+00 9. 56E+10 N/A TEEN 1.24E+09 0.00E+00 1.57E+08 0.00E+00 2.40E+09 0.00E+00 5.97E+10 N/A CHILD 2;34E+09 0.00E+00 2.92E+08 0.00E+00 3.16E+09 0.00E+00 3. 64E+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

~TBLE ADULT 1.73E+08 0.00E+00 2.19E+07 0.00f+00 3.34E+08 0.00E+00 1.12fwIO N/A TEEN 2.91E+08 0.00E+00 3.67E+07 0.00E+00 5.6lf+08 0.00E+00 1.40E+10 N/A CHILD 7.11E+08 0.00E+00 8.88E+07 0.00E+00 9.61E+08,0.00E+00 1. 11E+10 N/A INFANT O.OOE+00 0.00f+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00DOO N/A TOTAL ADULT 1.65E+09 0.00E+00 2.09E+08 0.00E+00 3.19E+09 0.00E+00 1.07E+ll 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 0.00E+00 3.81E+08 0.00E+00 4.12fw09 O.OOE+00 4.75E+10 N/A INFANT 2.07E+05 0.00E+00 1.30E+04 0.00f+00 1.23ft05 0.00E+00. 7.90E+05 N/A INHAL. , ADULT 6. 91E+04 0. 00f F00 8. 72E+03 0. OOE+00 1. 34E+05 9. 3 6E+06

- 9.12E>05 N/A TEEN 9.84E+04 0.00E+00 1.24E+04 0.00E+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 4.29E005 N/A INFANT 8.68E+04 0.00ft00 1.09E+04 0.00E+00 1.07ft05 1.16E+07 1.64E+05 N/A BONE LIVER T.BODY THYROID KIDNfY LUNG G.I. SKIN

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

• • • MAXIHUHVALUES FOR PATHWAYS*~"

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

4.18E+08 5.01E+08 1.32E+05 8.51E+05 9.56E+10 1.40E+10 1.07E+ll 1. 61ft07 PAGE: 4-23

O.D.C.M. 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 3.40E+09 3.40E+09 3.40E+09 3.40E+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 3.88E+06 2.30E+06 O.OOE+00 7.63E+06 O.OOE+00 1.58E+09 N/A MILK TEEN 6.93E+06 6.56E+06 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. OOE+10 N/A 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 9.52E+07 6.43E+07 5.14f+07 O.OOE+00 1.20E+08 O.OOE+00 7.65E+09 N/A INFANT 1.76E+08 1.28E+08 8.50E+07 O.OOE+00 1.84E+08 O.OOE+00 6.66E+09 N/A MEAT ADULT 3.42E+06 3.17E+06 1.88E+06 0.00E+00 6.23E+06 O.OOE+00 1. 29E+09 N/A TEEN 2.59E+06 2.45E+06 1.49E+06 0.00E+00 4.68E+06 0.00E+00 6.89E+08 N/A CHILD 4.30E+06 2.90E+06 2.32E+06 0.00E+00 5.41E+06 0.00E+00 3.45E+08 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 VEGTBLE ADULT 9.41E+06 8.70E+06 5.17E+06 0.00E+00 1.71E+07 0.00E+00 3.55E+09 N/A TEEN 1.42E+07 1.34E+07 8.18E+06 0.00E+00 2.56E+07 0.00E+00 3.78E+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+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 N/A TOTAL ADULT 4.36E+07 4.03E+07 2.39E+07 0.00E+00 7.92E+07 0.00E+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 1.80E+10 N/A CHILD 1.45E+08 9.80E+07 7.83E+07 O.OOE+00 1.83E+08 O.OOE+00 1.17E+10 N/A INFANT 4.07E+08 1.49E+08 9.84E+07 0.00E+00 2. 13E+08 0.00E+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 O.OOE+00 2.12E+04 5.48E+06 1.00E+05 N/A INFANT 9.98E+03 7.22E+03 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. SKI r

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: IHHAL.

3.40E+09 3.97E+09 1.84E+09 1.17E+10 1.29E+09 3.78E+09 1.80E+10 6.75E+06 PAGE: 4-24

O.O.C.M. MAXIMUM PATHWAY

~ ~ ~ DOSE FACTORS: RAOIOHUCLIDES OTHER THAN NOBLE GASES*

ISOTOPE:~ 1-131 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I.

GROUND ADULT 1.70Ej07 1.70Ej07 1.70E+07 1.70Ej07 l. 70E+07 1.70E+07 1.70E+07 2.07E+07 TEEN , 1.70Ej07 1.70E+07 1.70Ej07 1.70Ej07 1. 70E+07 1.70E+07 1.70E+07 2.07Ej07 CHILD 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 1.70E+07 2.'07Ej07 INFANT 1.70E+07 1.70Ej07 1.70E+07 1'.70Ej07 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.OOEj00 6.04E+07 N/A MILK TEEN 2.90E+08 4.06E+08 2.18E+08 1. 19E+ll G.99E+08 O.OOEj00 8.04E+07 N/A CHILD 7.04E+08 7.08E+08 4.02E+08 2.34E+ll 1. 16E+09 O.OOEj00 6.30E+07 N/A INFANT 1.22Ej09 1.73E+09 7.61E+08 5.69E+ll Z.OZE+09 O.OOE+00 6.18Ej07 N/A COM ADULT 7.46E+07 1.07E+08 6.12E+07 3.50E+10 1.83E+08 O.OOE j00 2.82Ej07 N/A MILK TEEN 1.35E+08 1.90E+08 1.02Ej08 5.53E+10 3.26E+08 0.00Ej00 3.75E+07 N/A CHILD '.29E+08 3.30E+08 1.SHE+08 1.09E+ll 5.42E+08 O.OOE+00 2.94E+07 N/A INFANT '.86E+08 8.08Ej08 3.55E+08 2.65E+ll 9.44E+08 0.00E+00 2.88E+07 N/A MEAT ADULT 3.54E+06 5.07Ej06 2.90Ej06 1.66E+09 8.68E+06 0.00E+00 1.34E+06 N/A TEEN 2.94E+06 4. 12E+06 2. 21E+06 1.ZOE+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.OOEj00 4.89E+05 N/A INFANT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOEj00 O.OOE+00 N/A

.GTBLE ADULT 2.86E+07 4. 10Ej07 2.35E+07 1.34E+10 7.02E+07 0.00E+00 1.08E+07 N/A TEEN 2.88E+07 4 '3E+07 2.16E+07 1. 18E+10 6.93E+07 0.00E+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.OOEj00 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 j00 1.01E+08 N/A INGEST. TEEN 4.57E+08 6.40Ej08 3.44E+08 1.87E+11 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 2.54Ej09 1.12E+09 8.34E+ll 2.97E+09 O.OOE+00 9.06E+07 N/A INHAL .. ADULT TEEN 2.52E+04 3.58E+04 2.05E+04 1. 19E+07

,3.54E+04 4.91E+04 2.64E+04 1.46E+07

6. 13E+04 8.40E+04 O.OOEj00 6.28Ej03 O.OOE+00 6.49E+03 N/A 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 3.79Ej04 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 COM TOTAL T.B./ORG. SKIN MILK: MILK: MEAT: VEGTBLE'NGEST: IHHAL.

1.70E+07 2.07E+07 5.69E+ll 2 '5E+ll 1.81E+09 1.84E+10 8.34E+1 1 1.62Ej07 PAGE; 4-25

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

ISOTOPE: i-132 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN GROUND 'DULT 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 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-OZ 2.37E-01 8.30E-02 8.30E+00 3.7&E-OI O.OOE+00 4.46E-02 N/A MILK TEEN 1.57E-01 4. 12E-01 1. 48E-01 1. 39E+O1 6.48E-01 O.OOE+00 1.79E-01 N/A CHILD 3.72E-01 6.84E-Ol 3.14E-01 3.17E+01 1.05E+00 O.OOE+00 8.05E-01 N/A INFANT 6.44E-01 1.57E+00 5.58E-01 7.35E+01 1.75E+00 O.OOE+00 1.27E+00 N/A COW ADULT 4.14E-OZ 1.11E-01 3.87E-02 3.'87E+00 1 76E-01 O.OOE+00 2.0&E-OZ

~

N/A MILK TEEN 7.34E-02 1.92E-01 6.89E-OZ 6.47E+00 3. 03E-Ol O.OOEOOO 8.37E-OZ N/A CHILD 1.74E-01 3.19E-01 1.47E-01 1.48Ew01 4.8&E-01 O.OOEi00 3.75E-Ol 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 4.8&E-59 1.75E-59 1.64E-57 7.69E-59 O.OOE+00 2.13E-59 N/A CHILD 3.37E-59 6.20E-59,2.85E-59 2.88E-57 9.49E-59 O.OOE+00 7.30E-59 N/A INFANT O.OOE+00 0. OOE+00 0. 000 00 0. OOE+00 0. OOE+00 O.OOE+00 0.00E+00 N/A VEGTBLE ADULT 1.90E+Ol 5.0&E+Ol 1.78E+Ol 1.78E+03 8.10E+01 O.OOE+00 9.55E+00 N/A TEEN 1.71E+01 4.48E+Ol 1.61E+Ol 1.51E+03 7.06E+Ol O.OOE+00 1.95E+Ol N/A CHILD 3.04E+01 5.59E+Ol 2.57E+Ol 2.59E+03 8.56E+Ol O.OOE+00 6.58E+Ol N/A INFANT O.OOE+00 O.OOE+00 O.OOEw00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 1.91E+Ol 5.12E+Ol 1. 79E+Ol 1.79E+03 8.15E+01 O.OOE+00 9.61E+00 N/A INGEST. TEEN 1.74E+01 4.54E+Ol 1.63E+01 1.53E+03 7.16f+01 O.OOE+00 1.98E+01 N/A CHILD 3.10E+01 5.69E+Ol 2.62E+01 2.64E+03 8.71E+Ol O.OOEw00 6.70E+Ol N/A INFANT 1.00E+00 2.30E+00 8. 19E-01 1.0&Ew02 2.57E+00 O.OOEt00 1.86E+00 N/A INHAL. ADULT 1. 16Et03 3.26E+03 1.16E+03 1.14D05 5.18003 0".OOEw00 4.06E+02 N/A TEEN >>1.59E+03 .4.38E+03 1.58E003 1.51E<05 6.92E+03 O.OOE+00 1.27E+03 N/A CHILD 2.,12E+03 4.07E+03 1.88E003 1.94E+05 6.25E+03 0.00E+00 3.20003 N/A INFANT 1.69E+03 3.54E+03 1.26Et03 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: INGEST: , INHAL.

0. OOE+00 0. OOE+00 7. 35E+0 1 3. 43E+0 1 2. 88E - 57 2. 59 f+03 2.64E+03 1. 94E+05 PAGE: 4-26

O.D.C.M.

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

ISOTOPE: ~ 1-133 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I.

SKIN'OUND 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 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+00,0.00E+00 OAT ADULT 2.09E+06 3.64E+06 1.11E+06 5.34E+08 6.34E+06 O.OOE+00 3. 27E+06 N/A ILK TEEN 3.82E+06 6.48E+06 1.98E+06 9.04f+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 2.85f+07 8.35E+06 5. 19E+09 3.35E+07 O.OOE+00 4.83E+06 N/A OW ADULT , 9.75E+05 1.70E+06 5. 17E+05 2.49f+08 2.96E+06 O.OOE+00 1.52E+06 N/A ILK 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 O.OOE+00 2.16f+06 N/A INFANT 9.14E+06 1.33E+07 3.90E+06 2.42E+09 1.56E+07. O.OOE+00 2.25E+06 N/A EAT ADULT 1.20E-01 2.09E-01 6.38E-OZ 3.08E+01 3.65E-01 0-OOE+00 1.88E-01 N/A TEEN 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 6.88E+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 INFANT 1.17E+06 1.44E+06 5.45E+05 2.68E+08 2.40E+06 O.OOE+00 5.81E+05 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00

'/A N/A OTAL ADULT 3.75E+06 6.53E+06 1.99E+06 9.59E+08 1. 14E+07 O.OOE+00 5.87E+06 N/A NGEST. 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 lHFANT 2.55E+07 4. 18E+07 1.22E+07 7.61E+09 4.9ZE+07 O.OOE+00 7.08E+06 N/A NHAL. ADULT 8.64E+03 1.48E+04 4.52E+03 2.15E+06 2.58E+04 O.OOE+00 8.88E+03 N/A TEEN 1.22E+04 2.05f+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 O.OOE+00 2.16E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKI "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: INGEST: INHAL.

O.OOE+00 5. 19E+09 2.42E+09 4.30E+Ol 2.68E+08 7.61E+09 3.85E+06 VEGTBLE-'.OOE+00 PAGE: 4-28

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

ISOTOPE: Te-132 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 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 CHILD O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 INFANT 0. OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 GOAT ADULT 1.30E+05 8.39E+04 7.88E+04 9.27E+04 8.08E+05 0.00E+00 3.97E+06 N/A HILK TEEN '.32E+05 1.47E+05 1.38E+05 1.55E+05 1.41E+06 0.00E+00 4.65E+06 N/A CHILD 5.53E+05 2.45E+05 2.96E+05 3.57E+05 2.27E+06 0.00E+00 2.47E+06 N/A INFANT 9.50E+06 5.64E+05 5.27E+05 8.33E+05 3.'53E+06 O.OOE+00 2.09E+06 N/A COW ADULT 6.05E+05 3.91E+05 3.67E+05 4.32E+05 3.77E+06 O.OOE+00 1.85E+07 N/A MILK TEEN 1.08E+06 6.85E+05 6.45E+05 7.22Et05 6.57E+06 O.OOE+00 2. 17E+07 N/A CHILD 2.58E+06 1.14E+06 1.38E+06 1.66E+06 1.06E+07 O.OOE+00 1.15Ew07 N/A

,INFANT 5.32E+06 2.63E+06 2.46E+06 3.89E+06 1.65E+07 O.OOE+00 9.74Et06 N/A HEAT ADULT 4. 68E+05 3.03E+05 2.84E+05 3.34E+05 2.92E+06 0.00E+00 1.43E+07 N/A

'EEN 3.83E+05 2.43E+05 2.28E+05 2.56E+05 2.33E+06 0.00E+00 7.68Ew06 N/A CHILD 6. 99E+05 3.09E+05 3.74E+05 4.51E+05'2.87E+06 O.OOE+00 3.11E+06 N/A INFANT O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A,

.~TBLE ADULT 1. 42E+06 9.18E+05 8.62Et05 1.01E+06 8.84E+06 0.00E+00 4.34E+07 N/A TEEN 1.29E+06 8.17E+05 7.69E+05 8.61Ew05 7.83E+06 0.00BOO 2.59E+07 '/A CHILD 2.31E+06 1.02E+06 1.24E+06 1.49E+06 9.49E+06 0.00E+00 1.03E+07 N/A INFANT O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ADULT 2.62E+06 1.70E+06 1.59E+06 1.87E+06 1.63E+07 0.00E+00 8.02E+07 N/A INGEST. TEEN 2.99E+06 1.89E+06 1.78E+06 1.99E+06 1.81E+07 0.00E+00 5.99E+07 N/A-CHILD 6. 15E+06 2.72E+06 3.29E+06 3.96E+06 2.53E+07 0.00E+00 2.74E+07 N/A INFANT 1.48E+07 3.20E+06 2.98E+06 4.72E+06 2.00E+07 O.OOE+00 1.18E+07 N/A INHAL. ADULT 2.60E+02 2.15E+02 1.62E+02 1.90E+02. 1.46E+03 2.88Ew05 5.10905 N/A TEEN 3.60E+02 2.90E+02 2.19E+02 2.46E+02 1.95E+03 4.49E+05 4.63905 N/A CHILD 4. 81Ew02 2.72E+02 2.63E+02 3.17Ew02 1.77E+03 3.77E+05 1.38Ew05 N/A INFANT 3.72E+02 2.37E+02 1.76E+02 2.79E+02 1.03E+03 3.40E+05 4.41E+04 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN 4

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

• ~*NAXIHUNVALUES FOR PATHWAYS*"~

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

O.OOE+00 O.OOE+00 9.50E+06 2.17E+07 1.43E+07 4.34E+07'.02E+07 5. 10E+05 PAGE: 4-27

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

OPE: I-134 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 TfEN 0.00E+00 O.OOE+00 O.OOE+00 0.00E+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+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.oof+00 O.OOE+00 O.OOE+00 0.00E+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 GOAT ADULT 1.09E-12 2.96E-12 1.06E-12 5.13E-11 4.71E-12 O.OOE+00 2.58E-15 N/A MILK l. 94E-12 5. 13E-12 1. 84E-12 8. 55E-11 8. 09E-12 0. OOE+00 6.76E-14 N/A CHILD 4.58E-12'8.51E-12 3.92E-12 1.96E-10 1.30E-ll O.OOE+00 5.64E-12 N/A INFANT 7.92E-12 1.95E-ll 6.92E-12 4.54E-10 2.18E-ll O.OOE+00 2.01E-11 N/A COW ADULT 5.08E-13 1.38E-12 4.94E-13 2.39E-ll 2.20E-12 O.OOE+00 1. 20E-15 N/A MILK TEEN 9.03E-13 2.39E-12 8.60E-13 3.99E-11 3.77E-12 O.OOE+00 3.15E-14 N/A CHILD 2.14E-12 3.97E-12 1.83E-12 9.13E-11 6.07E-12 O.OOE+00 2. 63E-12 ~

N/A INFANT 4.43E-12 9.08f-lZ 3.23E-12 2.12E-10 1.02E-ll O.OOE+00 9.39E-12 N/A HEAT ADULT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 N/A TEEN 0.00E+00 O.oof+00 O.OOE+00 0.00E+00 0.00E+00 O.OOE+00 O.OOE+00 N/A CHILD 0.00E+00 0.00f+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 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 LE ADULT 3.19E-05 8.65E-05 3.10E-05 1.50E-03 1.38E-04 0.00E+00 7.54E-08 N/A TEEN 2.88E-05 7.63E-05 2.74E-05 1.27E-03 1.20E-04 0.0OE+00 1.01E-06 N/A CHILD 5.12E-05 9.50E-05 4.37E-05 2.19E-03 1.45E-04 0.00E+00 6.30E-05 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00f+00 O.OOE+00 N/A TOTAL ADULT 3.19E-OS 8.65E-,05 3.10E-05 1.50E-03 1.38E-04 0.00f+00 7.54E-08 N/A INGEST. TEEN 2.88E-05 7.63E-05 2.74E-05 1.27E-03 1.20E-04 O.OOE+00 1.01E-06 N/A CHILD 5-12E-05 9.50E-05 4.37E-05 2.19E-03 1.45E-04 O.OOE+00 6;30E-05 N/A INFANT 1.24E-ll 2.85E-ll 1.02E-ll 6.66E-10 3. 19E-ll 0.00E+00 2.95E-ll N/A INHAL., ADULT 6.44E+02 1.73E+03 6.15E+02 2.98E+04 2.75E+03 0.00E+00 1.01E+00 N/A TEEN 8.88E+02 2.32E+03 8.40E+02 3.95E+04 3.66E+03 0.00E+00 2. 04E+01 N/A CHILD 1.17E+03 2.16E+03 9.95E+02 5.07E+04 3.30E+03 0.00E+00 9.55E+02 N/A INFANT 9.21E+02 1.88E+03 6.65E+02 4.45E+04 2.09E+03 0.00E+00 1.29E+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

"""MAXINUMVALUES FOR PATHWAYS**~

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

O.OOE+00 O.OOE+00 4.54E-10 2.12E-10 0.00E+00 2.19E-03 2.19E-03 5.07E+04 PAGE: 4-29 DAT

O.D.C.H. HAXIHUH 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 6.79009 6.79E+09 6.79E+09 6.79fw09 6.79f+09 6.79E+09 6.79E<09 7;92E+09

'EEN 6.79E+09 6.79ft09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 6.79E+09 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&9 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 1.06f+10 2.53E+10 2.07E+10 O.OOB.OO 8.19E+09 2.72E+09 4.43ft08 N/A MILK TEEN 1.85E+10 4.35E+10 2.02E+10 O.OOE+00'.38E+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+l1 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 5.28E+09 0.00B00 3.62E+09 1.38E+09 '.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 1.80E+10 3.35E+10 3.39E+09 0.00f+00 8.63E+09 3.54f+09 9. 11E+07 N/A NEAT "-

ADULT 3.59E+08 8.54E+08 6.98E+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.OOE+00 2.56E+08 9.18E+07 4.45fw06 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 O.OOE+00 N/A VEGTBLE. ADULT 4.21E+09 1.00E+10 8.19E+09 0.00E+00 3.24E+09 1.08E+09 1.75E+08 N/A TEEN, 6.70E+09 "l.'58E+10 7.3IE+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 0.00E+00 7.80E+09 2.80E+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 0.00f+00 N/A TOTAL ADULT 1.80E+10 4.28E+10 3.50E+10 0.00E+00 1.39E+10 4.60E+09 7.49E+08 N/A INGEST. TEEN 3.03E+10 7.13E+10 3.31E+10 0.00E+00 2.27E+10 8.65E+09 8.87E+08 N/A CHILD 6.96E+10 1.14E+ll 2.41E+10 O.OOE+00 3.54E+10 1.27E+10 6;.16E+D8 N/A INFANT 4.09E+10 1.62E+ll 1.63E+10 0.00fw00 4.16f+10 1.70E+10 4.39E+08 N/A INHAL. ADULT 3'.73fw05'.48E+05 7.28E+05 O.OOE+00 2.87E+05 9.76E+04 1.04B04 N/A TEEN 5.02ft05 1.13E+06 5.49E+05'0.00E+00 3.75E+05 1.46E+05 9.76E+03 N/A CHILD 6.51E+05 1.01E+06 2.25E+05 0.00E+00 3.30E+05 1.21E+05 3.85fw03 N/A INFANT 3.96E+05 7.03E+05 7.45E+04 0.00E+00 1.90E+05 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

• >>>>MAXIHUN VALUES FOR PATHWAYS"">>'ROUND:

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

TOTAL'NGEST:

INHAL.

6.79E+09 7.92fw09 1.28f+ll 3.35E+10 8.54E+08 2.52E+10 1.62E+11 1.13E+06 PAGE: 4-30

o D.C H- NAXINUN PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE GASES*

i iOTOP f: I -135 PATHWAY AGE GROUP BONE LIVER T. BODY THYROID KIDNEY LUNG G. I. SKIN GROUND ADULT O.OOE+00 O.OOBOO 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 0.00E+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 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 GOAT ADULT 6.93B03 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 H/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 5.05B04 1.21E+05 4.40E+04 1.08E+07 1.34E+05 0.00f+00 4.'37E+04 H/A COW ADULT 3.24E+03 8.47B.03 3.13E+03 5.59E+05 1.36E+04 O.OOE+00 9.57E+03 H/A MILK TEEN 5.75E+03 1.48B04 5.48E+03 9.52E+05 2.34E+04 0.00E+00 1.64E+04 H/A CHILD 1.36E+04 2.45E+04 1.16E+04 2.17E+06 3.75E+04 O.OOE+00 1.87E+04 " H/A INFANT 2.83E+04 5.63E+04 2.05E+04 5.05E+06 6.27E+04 O.OOE+00 2.04E+04, H/A-HEAT ADULT O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 H/A TEEN 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A CHILD O.OOE+00 O.OOE+00 O.OOE+00 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 H/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00f+00- N/A LE ADULT 1.29B.04 3.37E+04 1.24E+04 2.22E+06 5.40E+04 O.OOE+00 3.80E+04 H/A-TEEN 1. 16E+04 2.99E+04 1.11E+04 1.92E+06 4.73E+04 O.OOE+00 3.32E+04 H/A CHILD- ,2.06E+04 3.72B04 1.76f+04 3.29E+06 5.TOE+04 0.00E+00 2.83E+04 H/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00f+00 N/A TOTAL ADULT 2.30E+04 6.03f+04 2.23E+04 3.98E+06 9.67E+04 0.00E+00 6.81E+04- H/A INGEST. TEEN 2.97E+04 7.64E+04 2.83E+04 4.92E+06 1.21E+05 O.OOE+00'8.47E+04 H/A CHILD 6.34E+04 1.14E+05 5.40E+04 1.01E+07 1.75E+05 O.OOE+00 -8'70E+04 INFANT 7.88E+04 1.77E+05 6.45E+04 1.59E+07 1.97E+05 0. OOE+00 6.'40E+0'4 8/A IHHAL. ADULT 2.68E+03 6.98E+03 2.57E+03 4.48E+05 1.11E+04 O.OOE+00 5.25E+03 H/A TEEN 3.70E+03 9.44E+03 3.49E+03 6.21E+05 1.49B.04 O.OOE+00 6.95E+03 H/A CHILD 4.92E+03 8.73B03. 4.14E+03 7.92E+05 1.34B.04 0.00f+00 4.44E+03 H/A INFANT 3.86E+03 7.60E+03 2.77E+03 6.96E+05 8.47E+03 O.OOE+00 1.83E+03 H/A BONE LIVER T.BODY THYROID KIDNEY LU G G. I. SKIN

• Airborne pathways and tritium ingestion: units are mrem/yr/uCi/m3.

Deposition pathways: units are mrem-m2/yr/uCi/sec

• ~MAXINUN VALUES FOR PATHWAYS***

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

0-OOE+00 O.OOE+00 1.08E+07 5.05E+06 O.OOE+00 3.29E+06 1.59E+07 7.92E+05 PAGE: - 4-31 DATE, iJ/0 o//k

O.D.C.H. 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 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 1.49E+08 1.49E+08 1.49E+08 1.69E+08 CHILD 1.49fw08 1.49B08 1.49E+08 1.49B08 1.49E+08 1.49E+08 1.49&08 1.69E+08 INFANT 1.49E+08 1.49E+08 1.49E+08'.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 0.00E+00 7.84E+08 1.07E+08 1.60E+08 N/A MILK TEEN 6.07E+08 2.39E+09 1.61E+09 0.00f+00 1.30E+09 2.05E+08 1.92E+08 N/A CHILD 1. 37E+09 3. 77E+09 2. 44E+09 0. 00E+00 2. 01& 09 2.99E+08 1.32fw08 N/A INFANT 8.93E+08 7.88E+09 2.94E+09 O.OOE+00 3. 14E+09 6.42&08 1.20E+08 N/A COW ADULT 6.69E+07 2.64E+08 1.90E+08 0.00E+00 1.47E+08 2.02E+07 3.00E+07 N/A HILK TEEN 1.14E+08 4.48E+08 3.01E+08 O.OOE+00 2.44E+08 3.85E+07 3.61fw07 N/A CHILD 2.57E+08 7.07E+08 4.58E+08 0.00f+00 3.77E+08 5.62E+07 2.48B.07 N/A INFANT 5. 02E+08 1. 48E+09 5. 52 f+08 0. OOE+00 5. 89 f+08 1.20E+08 2.24E+07 N/A HEAT 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 0.00f+00 7.87E+06 1.17E+06 5.20E+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 2.03E+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 0.00E+00 5.21E+07 8.22E+06 7.. 71E+06 N/A CHILD 4.96E+07 1.36E+08 8.82E+07 0.00E+00 7.26E+07 1-08E+07 '.79E+06 N/A INFANT 0.00f+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 N/A TOTAL ADULT 4.48E+08 1.77E+09 I'.27fi09 0.00E+00 9.84E+08 1.35E+08 2. 01E+08 N/A INGEST. TEEN 7.4'9E+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 0.00E+00 3.73E+09 7.62E+08 1.42E+08 N/A INHAL. ADULT 3.90fi04 1.46E+05 1.10E+05 0.00E+00 8.56E+04 1.20E+04 1.17E+04 N/A TEEN 5.15E+04 1.94E+05 1.37E+05 0.00E+00 1.10E+05 1.78E+04 1. 09E+04 N/A CHILD 6.51E+04 1.7IE+05 1.16E+05 O.OOE+00 9.55E+04 1.45E+04 4.18&03 N/A INFANT 4.83E+04 1.35E+05 5.29f+04 0.00E+00 5-64E+04 1.18E+04 1.43&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

,*"*NAXINUHVALUfS FOR PATHWAYS*"~

GROUND:

T.B./ORG.

GROUND:

SKIN GOAT MILK:

COW HI LK:

TOTAL HEAT: VEGTBLE: INGEST: " INHAL.

1.49&08 1.69E+08 7.88E+09 1.48E+09 1.58E+07 1.36E+08 9.35E+09 1.94E+05 4 PAGE: 4-32 V

DAT

GASES*

O.D.C.N. NAXINUN PATHWAY DOSE FACTORS: RADIONUCLIDES OTHER THAN NOBLE ISO Pf: 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 1.02f+10 1.02E+10 1.02E+10 1.02E+10 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 N/A 4.53E+09 4.88E+08 3.76E+08'.17E+10 HILK TEEN 2.58E+10 3.43E+10 1.19E+10 O.OOE+00 N/A CHILD 6.20E+10 5.94E+10 8.77B09 O.OOE+00 1.94E+10 6.96f+09 3.72E+08 N/A INFANT 3.30E+10 1.16E+ll 8.22E+09 0.00E+00 3.11E+10 1.26E+10 3.62E+08 N/A COW ADULT 3.78E+09 5. 17E+09 3.39E+09 0.00f+00 1.76E+09 5.84E+08 1.00E+08 N/A HILK TEEN 6.86E+09 9.12B09 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. 15 B 09 1. 85E+09 9. 90E+07 '. N/A INFANT 2.64E+10 3.09E+10 2.19E+09 0.00E+00 8.28E+09 3.35E+09 9.65E+07 N/A HEAT ADULT 4;91E+08 6.71E+08 '4.40E+08 0.00f+00 2.28E+08 7.58E+07 1.30B07 N/A TEEN 4.08E+08 5.42E+08 1.89E+08 0.00E+00 1.85E+08 7. 17E+07 7.72E+06 N/A CHILD 7:51E+08 7.19E+08 1.06E+08 0.00E+00 2.34E+08 8.42E+07 4.50E+06 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

• LE ADULT 5.76E+09 7.88E+09 5.16E+09 0.00E+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 1.69B09 1.81B08 N/A CHILD 2.29f+10 2.19E+10 3.24E+09 0.00E+00 7.15E+09 2.57B09 1.37E+08 N/A INFANT O.OOE+00 O.OOE+00 0.00'E+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 N/A TOTAL ADULT 2.42E+10 3.32E+10 2.17E+10 0.00E+00 1.13E+10 3.74E+09 6.42E+08 N/A INGEST. TEEN 4.26E+10 5.67E+10 1.97E+10 0.00E+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:.13E408 N/A INFANT 5.94E+10 1.47E+ll 1.04E+10 0.00E+00 3.94E+10 1. 60E+10 4. 59E+08 N/A INHAL. ADULT 4.78E+05 6.21E+05 4.28B05 0.00E+00 2.'22f+05 7.52E+04 8.40B03 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 0.00E+00 2.82E+05 1.04E+05 3.62E+03 N/A INFANT 5.49B05 6.12B05 4.55B04 0.00E+00 '1.72E+05 7;13E+04 1.33E+03 N/A BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. S IN

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

"""MAXINUHVALUES FOR PATHWAYS~~~

GROUND: GROUND: GOAT COW TOTAL T.B./ORG. SKIN MILK: HILK: NEAT: VEGTBLE: INGEST: IHHAL. "

1.02f+10 1.19f+10 1.16E+ll 3.09E+10 7.51E+08 2.29E+10 1.47E+ll 9.07E+05 PAGE: 4-33

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

ISOTOPE: Sa-140 PATHWAY AGE GROUP BONE LIVER T. BODY THYROID KIDNEY LUNG G.I. SKIN GROUND ADULT 2.03E+07 2.03E+07 2.03E+07 2.03fw07 2.03E+07 2.03fw07 2.03007 2.32E+07 TEEN 2.03E+07 2.03E+07 2.03E+07 2.03E+07 2.03E+07 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 2.03fw07 2.03E+07 2.32E+07 INFANT 2.03E+07 2.03E+07 2.03f+07 2.03E+07 2.03E+07 2.03fw07 2.03fw07 2.32E+07 GOAT ADULT 1.46E+06 1.83E+03 9.54E+04 0.00E+00 6.22E+02 1.05E+03 3.00E+06 N/A MILK TEEN 2.63E+06 3.22E+03 1.69E+05.0.0OE+00 1.09E+03 2.17E+03 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 0.00E+00 3.10E+03 8.02E+03 3.21E+06 N/A COW ADULT 6.83ft06 8.58E+03, 4.47005 O.OOE+00 2.92f+03 4.9lf+03 1.410 07 N/A MILK TEEN 1.23fw07 1.51E+04 7.94E+05 0.00E+00 5.12E+03 1.02E+04 1.90E+07 N/A CHILD 2.97E+07 2.61E+04 1.74E+06 0.00f+00 8.4&E+03 1.55E+04 1.51E+07 N/A INFANT 6.12E+07 6.12E+04 3.15E+06 0.00E+00 1.45E+04 3.76B04 1.50E<07 N/A MEAT ADULT 9.52E+06 1.20E+04 6.24E+05 Q.OOE+00 4.07E+03 6.85E+03 '.96E+07 N/A TEEN 7.87E+06 9.65E+03 5.07E+05 0.00f+00 3.27E+03 6.49E+03 1. 21E+07 N/A CHILD 1.45E+07 1.27E+04 4.4&f+05 0.00E+00 4. 14E+03 7.59E+03 7.36E+06 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 VEGTBLE ADULT 5.98E+07 7.51E+04 3.92E+06 O.OOE+00 2.55E+04 4.30E+04 1.23fw08 N/A TEEN 7.50E+07 9.19E+04 4.83E&6 0.00E+00 3.12E+04 6.1&E+04 1.16f+08 N/A CHILD 1.62fw08 1.42E+05 9.4&E+06 O.OOE+00 4.63E+04 8.48E+04 8.23E+07 N/A" INFANT 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ADULT 7.76E+07 9.75E+04 5.0&E+06 0.00E+00 3.31E+04 5.58E+04 1.60E+0& N/A INGEST. TEEN 9.7&E+07 1.20E+05 6.31ft06 0.00E+00 4.07E+04 8.06E+04 1.51E+08 N/A CHILD 2.13E+08 1.87E+05 1.24E+07 0.00E+00 6.08E+04 1.11E+05 1 .08E+0& N/A INFANT 1.70E+08 7.43E+04 3.83E+06 0.00E+00 1.76E+04 '4.56E+04 1.82E+07 N/A INHAL. ADULT 3.90f+04 4.90E+Ol 2.57E+03 0.00E+00 1.67E+01 1.27E+06 2.1&E+05 N/A TEEN, 5.47B04 6.94E+Ol 3.52ft03 O.OOBOO Z.ZBE+Ol 2.03B06 2.29E+05 N/A CHILD 7.40f+04 6.4&E+01 4.33E+02 0 00fw00 2.11E+01 1.74E+06 1.02E+05 N/A INFANT 5.60E+04 5.60E+Ol 2.90f+03 0.00E+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: MEAT: VEGTBLE: INGfST: INHAL.

2.03E+07 2.32E+07 1.09E+08 6.12ft07 1.96E+07 1.62E+08 2.13E+08 2.03E+06 PAGE: 4-34 r

DAT

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

iSOTOPE: La-140 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN ROUND ADULT 0.00E+00 O.OOE+00 O.OOE+00 0.00000 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE<00 TEEN 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 CHILD O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0-OOE+00 0.00E+00 0.00E+00 INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 GOAT ADULT 2.44E-01 1.23E-01 3.25E-02 0.00E+00 0.00f+00 O.OOE+00 9.02E+03 N/A MILK TEEN 4.38E-01 2.15E-01 5.72E-02 0.00E+00 0.00E+00 0.00E+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 1.02fw04 N/A INFANT 1.82E+01 8.63E-01 2.22E-01 0.00E+00 0.00E+00 O.OOE+00 1.01E+04 N/A COW ADULT 1.14E+00 5.73E-Ol 1.51E-01 0.00E+00 0.00E+00 O.OOE+00 4.21&04 N/A ILK 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 0.00fw00 O.OOE+00 0.00E+00 4.76E+04 " N/A INFANT 1.02E+01 4.03E+00 1.04E+00 0.00E+00 0.00E+00 0.00E+00 4.73E+04 0/A EAT ADULT 1.22E-02 6.16E-03 1.63E-03 O.OOEWOO O.OOE+00 0.00E+00 4. 53ft02 N/A TEEN 1.01f-02 4.94E-03 1.32E-03 0.00fw00 0.00E+00 0.00&.00 2.84fw02 N/A CHILD 1.84E-OZ 6.44E-03 2.17E-03 0.00E+00 0.00E+00 0.00E+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

. TBLE ADULT 6.53E+02 3.29E+02 8.69E+Ol 0.00E+00 0.00E+00 O.OOQOO 2.41E+07 N/A TEEN 5.96E+02 2.93E+02 7.79E+01 0.00E+00 0.00E+00 0.00E+00 1.68ft07 N/A CHILD 1.07E+03 3.74E+02 1.26E+02 0.00f+00 0.00E+00 O.OOE+00 1.04E+07 N/A INFANT 0.00E+00 0.00E+00 0.00ft00 0.00E+00 0.00E+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 6.54E+02 3.30E+02 8.71E+01 0.00E+00 0.00E+00 0.00ft00 2.42E+07 N/A INGEST. TEEN 5.99E+02 2.94E+02 7.83E+01 0.00E+00 0.00E+00 O.OOE+00 1.69E+07 N/A CHILD 1.08E+03 3.76E+02 1.27E+02 0.00E+00 0.00E+00 0.00E+00" 1;05E+07 N/A INFANT 2. 85E+0 1 4. 89E+00 1. 26E+00 0; OOE+00 0. OOE+00 O.OOBOO 5:74E+04 N/A INHAL. ADULT 3.44E+02 1.74E+02 4.58E+Ol 0.00E+00 0.00E+00 1.36E+05 4.58E+05 N/A TEEN 4.79E+02 2.36E+02 6.26E+01 0.00E+00 0.00E+00 2.14E+05 4.87fw05 N/A CHILD 6.44E+02 2.25E+02 7.55E+01 0.00E+00 0.00E+00 1.83E105 2.26E+05 N/A INFANT 5.05E+02 2.00E+02 5.15E+Ol 0.00f+00 0.00E+00 1. 68E+05 8. 48& 04 N/A, BONE LIVfR 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: HEAT: VEGTBLE: INGEST: INHAL.

0.00E+00 0.00E+00 1.24E+04 5.76E+04 4.53E+02 2.41E+07 2.42f+07 4.87B05 PAGE: 4-35 DAT

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

ISOTOPE: Ce- l41 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 1.35E+07 1.35E+07 1.52E+07 TEEN 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+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 1.35E+07 1.35E+07 1.52E+07 INFANT 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.35E+07 1.52E+07 GOAT ADULT 2.78E+02 1.88E+02 2. 13E+01 0.00E+00 8.73E+01 0.00E+00 7. 19E+05 N/A MILK TEEN 5.10f+02 3.40E+02 3.91E+01 0.00E+00 1.60E+02 0.00E+00 9.74E+05 N/A CHILD 1.26E+03 6.26E+02 9.30E+Ol 0.00E+00 2.75E+02 0.00E+00 7.81E+05 H/A INFANT 2.07E+04 1.52E+03 1.79E+02 0.00E+00 4.68E+02 0.00E+00 7.84E+05 N/A COW ADULT 1.41E+03 9.51E+02 1.08E+02 0.00E+00 4.42E+02 0.00E+00 3.64E+06 N/A MILK TEEN CHILD INFANT

2. 58E+03 6.35E+03 1.26E+04

1. 72E+03 3.17E+03 7.68E+03

1. 98E+02 4.70E+02 9.04E+02

0. OOE+00 8. 11E+02 0.00E+00 1.39E+03 0.00E+00 2.37E+03

0. OOE+00 4. 93E+06 0.00E+00 3.95E+06 0.00E+00 3.97f+06

'/A N/A N/A MEAT ADULT 5.11E+03 3.92f+02 0.00E+00 1.61f+03 O.OOE+00 1.32E+07 N/A TEEN 4.29E+03 2.87E+03 3.29E+02 0.00E+00 1.35E+03 0.00E+00 8.20E+06 N/A CHILD 8.08E+03 4.03E+03 5.99E+02 0.00E+00 1.77E+03 0.00E+00 5.03E+06 N/A INFANT O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A OOE+00'.46E+03 VEGTBLE ADULT 1.49E+05 l. 01E+05 1.14E+04 0.00f+00 4.69E+04 0.00E+00 3.86E+08 N/A TEEN 2.38E+05 1.59E+05 1.83E+04 0.00f+00 7.49E+04 0.00E+00 4.55E+08 N/A:

CHILD 5.73E+05 2.86E+05 4.25E+04 0.00E+00 1.25E+05 0.00E+00 3.57E+08 N/A INFANT 0. 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ADULT 1.56E+05 1.06E+05 1.20E+04 0.00E+00 4.90E+04 0.00E+00 4.03E+08 N/A INGEST. TEEN 2.46E+05 1.64E+05 1.88E+04 0.00E+00 7.72E+04 0.00E+00 4.69E+08 N/A CHILD 5.89E+05 2.94E+05 4.36E+04 0.00E+00 1.29E+05 0.00E+00 3;67E+'08 Nj'A INFANT 3.33E+04 9.20E+03 1.08E+03 0.00f+00 2.84E+03 0.00E+00 4.75E+06 N/A INHAL. ADULT 1.99E+04 1.35E+04 1.53E+03 0.00E+00 6.26E+03 3.62E+05 1.20E+05 N/A TEEN 2.84E+04 1.90E+04 2.17E+03 0.00E+00 8.88f+03 6.14E+05 1.26E+05 N/A CHILD 3.92E+04 1.95E+04 2.90E+03 0.00E+00 8.55E+03 5.44E+05 5.66E+04 N/A INFANT 2.77E+04 1.67E+04 1.99E+03 0.00E+00 5.25E+03 5.17E+05 2.16E+04 H/A 80NE LIVER T. BODY THYROID K IDNEY LUNG G.l. 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-1.35E+07 1.52E+07 9.74E+05 4.93E+06 1.32E+07 4.55f+08 4.69E+08 6.14E+05 PAGE: 4-36 DAT

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

ISOTOPE: Pr-143 PATHWAY AGE GROUP BONE LIVER T. BODY THYROID KIDNEY i LUNG G. I. SKIN GROUND ADULT 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 TEEN O.OOE+00 0.00E+00 0.00E+00 0.00F+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 CHILD 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 0.00E+00 INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 GOAT ADULT 8.57E+00 3.44E+00 4.25E-Ol 0.00Et00 1.98E+00 O.OOE+00 3.75E+04 N/A MILK TEEN 1.57E+01 6.28E+00 7.83E-01 0.00E+00 3.65Et00 0.00f+00 5.18E+04 N/A CHILD 3.89E+01 1.17E+Ol 1.93E+00 0.00E+00 6.33ft00 O.OOE+00 4.20E+04 N/A INFANT 6.71E+02 3.01BOl 3.99E+00 0.00E+00 1.12E+Ol O.OOE+00 4.25E+04 N/A COW ADULT 4.02E+01 1.61E+01 1.99E+00 0.00E+00 9.31E+00 O.OOE+00 1.76E+05 N/A MILK TEEN 7.39E+Ol 2.95E+01 3.68f+00 0.00f+00 1.71E+Ol 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 1.97Et05- N/A INFANT 3.78E+02 1.4IE+02 1.87E+Ol 0.00E+00 5.26E+01 O.OOE+00 2.00E+05 N/A MEAT ADULT 6.96E+03 2.79E+03 3.45E+02 0.00B00 1.61B03 O.OOE+00 3.05E+07 N/A TEEN 5.86E+03 2.34E+03 2.92E+02 0.00Et00 1.36B03 O.OOE+00 1.93E+07 N/A CHILD 1.11Et04 3.33E+03 5.50E+02 0.00f+00 1.80B03 O.OOE+00 1.20E+07 N/A INFANT 0.00ft00 O.OOE+00 O.OOE+00 0.00f+00 O.OOE+00 0.00E+00 0.00E+00 N/A E ADULT 3.04E+04 1.22E+04 l.'51E+03 0.00E+00 7.04E+03 O.OOE+00 1.33E+08 N/A TEEN 4.00E+04 1.60E+04 1.99E+03 0.00E+00 9.27B03 O.OOE+00 1.3IE+08 N/A CHILD 8.98E+04 2.69E+04 4.45f+03 0.00Et00 1.46E+04 0.00E+00 9.68E+07 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 O.OOE+00 N/A TOTAL ADULT 3.74E+04 1.50E+04 1.86E+03 O.OOE+00 8.67B03 0.00E+00 1.64E+08 N/A INGEST. TEEN 4.59E+04 1.83E+04 2.28E+03 0.00ft00 1.07E+04 O.OOE+00 1.51B08 N/A CHILD 1.01E+05 3.03Et04 5.01E+03 0.00E+00 1.64E+04 O.OOE+00-1';09E+08 N/A INFANT 1.05E+03 1.72E+02 2.27E+Ol O.OOEt00 6.38Et01 O.OOE+00 2;42E+05 N/A INHAL. ADULT 9.36E+03 3.75E+03 4.64E+02 0.00BOO 2.16B03 2.81E+05 2.00E+05 N/A TEEN 1.34E+04 5.31E+03 6.62E+02 O.OOE+00 3.09E+03 4.83f+05 2.14E+05 N/A CHILD 1.85E+04 5.55E+03 9. 14E+02 O.OOE+00 3.00E+03 4,33E+05 9.73Et04 N/A INFANT 1.40E+04 5.24ftG3 6.99E+02 O.OOE+00 1.97E+03 4.33f+05 3.72E+04 N/A BONE LIVER T. BODY THYROID K IONEY 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: VEGTSLE: INGEST: INHAL.

0.00E+00 0.00E+00 5.18f+04 2.43E+05,3.05E+07 1.33E+08 1.64f+08 4.83ft05 PAGE: 4-37

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

ISOTOPE: Ce-144 PATHMAY 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 7.96B07 TEEN 6.88E+07 6.88f+07 6.88E+07 6.88E+07 6.88E+07 6.88B07 6.88B07 7.96E+07 CHILD 6.88E+07 6.88E+07 6.88B.07 6.88E+07 6.88B07 6.88E+07 6.88E+07 7.96B07 INFANT 6.88E+07 6:-SBE+07 6.88E+07 6.88B07 6.88E+07 6.88f+07 6.88E+07 7.96F+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 4.78E+04 1.98E+04 2.57E+03 0.00E+00 1. 18E+04 O.oof+00 1.20E+07 N/A CHILD 1. 18E+05 3.69E+04 6.28E+03 0.00E+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 COM 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 0.00E+00 7.52E+04 0.00B00 7.65E+07 N/A CHILD 7.50E+05 2.35E+05 4.00f+04 O.OOBOO 1.30E+05 O.OOE+00 6. 13E+07 N/A INFANT 1.07E+06 4.40E+05 6.02E+04 O.oof+00 1.78E+05 O.OOE+00 6.17E+07 N/A HEAT ADULT 7.55E+05 3.16E+05 4.05E+04 0.00E+00 1.87f+05 0.00E+00 2.55E+08 N/A TEEN 6.36E+05 2.63E+05 3.42E+04 0.00E+00 1.57E+05 0.00E+00 1.60E+08 N/A CHILD 1.20E+06 3.76E+05 6.40E+04 0.00E+00 2.08E+05 0.00E+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 0;OOE+00 N/A VEGTBLE ADULT 2.94E+07 1.23E+07 1.58E+06 0.00E+00 7.30E+06 O.OOE+00 9.95E+09 N/A TEEN 4.95E+07 2.05E+07 2.66E+06 0.00E+00 1.22E+07 0.00E+00 1. 24E+10 N/A CHILD 1. 21E+08 3'.BOE+O7 6.46E+O6 O'.OOE+OO 2.1OE+O7 O.OOE+OO 9.90E+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 3.04E+07 1'.27B07 1.63E+06 O.OOE+00 7.53E+06 O.oof+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 6.57E+06 O.OOE+00 2.14f+07 O.OOE+00 .I;Olf+lo N/A INFANT 2.48E+06 5.09f+05 6.97E+04 O.oof+00 2.06E+05 O.OOE+00 7. 14E+07 N/A INHAL. ADULT 3.43E+06 1.43E+06 1.84E+05 0.00E+00 8.48f+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 8.64f+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 I. SKIN

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

""*MAXIMUMVALUES FOR PATHMAYS*~

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

6.88E+07 7.96E+07 1.20E+07 7.65E+07 2.55B08 1.24E+10 1.27E+10 1.34E+07 PAGE: 4-38

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

OPE: Pr-144 PATHWAY AGE GROUP BONE LIVER T. BODY THYROID KIDNEY LUNG G. I. SKIN GROUND ADULT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 TEEN 0.00f+00 0.00ft00 O.OOE+00 O.OOE+00 O.OOE+00 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 O.OOE+00 0.00E+00 0.00600 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 N/A MILK TEEN O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+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 COW MILK ADULT TEEN O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

'/A N/A '.OOE+00 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 0.00E+00 0.00E+00 0.00E+00'.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A INFANT 0.00f+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A BLE ADULT 0.00E+00 0.00E+00 0.00E+00 0.00f+00 O.OOE+00 0.00E+00 0.00E+00 N/A TEEN O.OOE+00 0.00E+00 0.00E+00 0.00E+00 O.OOE+00 0.00E+00 0.00E+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 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 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 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A CHILD 0.00f+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00,0.00E+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-OZ 1.25E-OZ 1.53E-03 0.00E+00 7.05E-03 1. OZB 03 2. 15E-0& N/A TEEN 4.30E-02 1.76E-OZ 2.1&E-03 0.00fw00 1.01E-02 1.75603 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-OZ 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: MEAT: VEGTBLE: INGEST: INHAL.

O.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00f+00 0.00E+00 0.00fw00 4.2&E+03 PAGE: 4-39 OAT

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

ISOTOPE: Nd-147 PATHWAY AGE GROUP BONE , LIVER T. BODY -,THYROID KIDNEY LUNG G. I. , SKIN GROUND ADULT 8.31E+06 8.31ft06 8.31f+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06 TEEN 8.31E+06 8.31ft06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06

. CHILD 8.31E+06 8.31906 8.31E+06 8.31E+06 8.31E+06 8.31E+06 8.31E+06 9.97E+06 INFANT 8.31ft06 8.31E+06 8.31E+06 8.31E+06 8.3lf+06 8.31E+06 8.31E+06 9.97f+06 GOAT ADULT 5.09E+00 5.89E+00 3.SZE-Ol O.OOE+00 3.44E+00 0.00E+00 2.83E+04 N/A MILK 'TEEN, 9.80E+00'1.07E+01 6.38E-01 0.00E+00 6.26E+00 O.OOE+00 3.84E+04 N/A CHILD '.40E+Ol 1.95E+01 1.51E+00 O.OOE+00 1.07E+Ol 0.00E+00 3.09E+04 N/A

'NFANT 3.97E+02 4.90E+01 3.00E+00 0.00E+00 l.'89E+Ol 0.00E+00 3. 10E+04 N/A COW ADULT 2.38E+01 2.75fw01 1.65E+00 O.OOE+00 1.61E+Ol 0.00E+00 1.32E+05 N/A MILK TEEN 4.58E+Ol 4.98fw01 2.98E+00 O.OOE+00 2.93E+Ol O.OOE+00 1.80E+05 N/A CHILD 1.12E+02 9.11001 7.05E+00 O.OOE+00 5.00E+01 O.OOE+00 1.44E+05 N/A INFANT . 2.23E+02 2.29ft02 1.40E+01 0.00E+00 8.82E+01 O.OOE+00 1.45E+05 N/A HEAT ADULT 2.34E+03 2.70603 1.62E+02 0.00E+00 1.58E+03- O.OOE+00 1.30E+07 N/A TEEN 2.06E+03 2.24ft03 1.34E+02 0.00E+00 1.31E+03 0.00E+00 8.08E+06 N/A CHILD '3.86E+03 3.13ft03 2.42E+02-0.00E+00 1.72E+03 0.00E+00 4.96E+06 N/A INFANT 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00000 0.00E+00 0.00E+00 N/A VEGTBLE ADULT, 1.39E+04 1.61f+04 9.61E+02 0.00E+00 9.39E+03 0.00E+00 7.71E+07 N/A TEEN 1.72E+04 1.87ft04 1.12E103 O.OOE+00 1.10E+04 0.00f+00 6.74E+07 N/A CHILD 3.65E+04 2.95E+04,2.29E+03 0.00E+00.1.62E+04 0.00E+00 4.68E+07 N/A INFANT 0.00E+00 0.00ft00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A TOTAL ADULT 1.63E+04 1.88E+04 l. 12E+03 .O.OOE+00 l. 10E+04 0.00E+00 9.03E+07 N/A INGEST. TEEN 1.93E+04 2. 10f+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 0.00E+00 1.80E+04 O.OOE+00 5;19E+07 N/A INFANT 6.20E+02 2.78E+02 1.70E+01 0.00E+00 1.07E+02 0.00E+00 1.76E+05 N/A INHAL. ADULT 5.27E+03 6. 10f+03 3.65E+02 0.00E+00 3.56E+03 2.21fw05 1.73&05 N/A TEEN 7.86E+03 8.56E+03 5. 13E+02 0.00E+00 5.02f+03 3.72E+05 1.82E+05 N/A CHILD 1.08E+04 8.73fw03 6.81E+02 0.00E+00 4.8lft03 3.28E+05 8.2lfw04 N/A

'NFANT 7.94E+03 8.13003 5.00E+02 O.OOE+00" 3.15ft03 3. 22ft05, 3. 12fw04 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.

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: 4-40 DAT

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

OPE: Hp-239 PATHWAY AGE GROUP BONE LIVER T.BODY THYROID KIDNEY LUNG G. I. SKIN GROUND ADULT O.OOE+00 O.OOE+00 0.00f+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 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 1.98E-Ol 1.95E-02 1.08E-02 O.OOE+00 6.08E-02 O.OOE+00 4.00E+03 N/A MILK TEEN 3.79E-Ol 3.57E-02 1.98E-02 O.OOE+00 1.12f-01 O.OOE+00 5.74E+03 N/A CHILD 9.32E-01 6.69E-02 4.70E-02 0.00f+00 1.93E-Ol O.OOE+00 4.95E+03 N/A INFANT 1.64E+Ol 9.96E-02 9.96E-02 O.OOE+00 3.51E-Ol O.OOE+00 5.09E+03 N/A COW ADULT 9.26E-OI 9.10E-02 5.02E-02 O.OOE+00 2.84E-01 0.00E+00 1.87E+04 N/A MILK TEEN 1.77E+00 1.67E-01 9.25E-OZ O.OOE+00 5.23E-Ol 0.00E+00 2.68E+04 N/A CHILD 4 '5E+00 3.12E-01 2. 19E-01 0. 00E+00 9. 02E-01 0. OOE+00 2. 31 f+04 N/A INFANT 9.19E+00 8.22E-Ol 4. 64E-01 0.00E+00 1.64E+00 0.00fw00 2.38E+04 N/A MEAT ADULT 8.54E-02 8.40E-03 4.63E-03 O.OOE+00 2.62E-02 O.OOE+00 1.72&03 N/A

'EEN 7.47E-02 7.04E-03 3.91E-03 O.OOE+00 2.21E-02 0.00fw00 1.13ft03 N/A CHILD 1.41E-01 1.01E-OZ 7.09E-03 O.OOE+00 2.92E-02 O.OOE+00 7.47E+02 N/A

INFANT 0-OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 N/A ADULT 4.71E+02 4.63E+Ol 2.55E+Ol O.OOE+00 1.45E+02 O.OOE+00 9.50E+06 N/A TEEN 4.57f+02 4.31E+Ol 2.40E+01 0.00E+00 1.35E+02 0.00E+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 4.49&06 N/A INFANT 0.00fw00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOBOO N/A TOTAL ADULT 4.72ft02 4.64E+Ol 2.56E+Ol 0.00E+00 1.45E+02 0.00E+00 9.53E+06 N/A INGEST. TEEN 4.60fw02 4.33E+Ol 2.41E+Ol O.OOE+00 1.36E+02 O.OOE+00 6.97E+06 N/A CHILD 8.50E+02 6.10E+Ol 4.29E+01 O.OOE+00 1.76E+02 O.OOE+00 4.52E+06 N/A INFANT 2.56fw01 9.22E-01 5.64E-Ol O.OOE+00 1.99E+00 O.OOE+00 2.89E+04 N/A INHAL. ADULT 2.30E+02 2. 26E+01 1.24E+Ol 0.00E+00 7.00E+Ol 3.76E+04 1.19E+05 N/A TEEN 3.38E+02 3. 19E+01 1.77E+Ol 0.00E+00 1.00E+02 6.49E+04 1.32E+05 N/A CHILD 4.66E+02 3. 34E+Ol 2.35E+01 0.00f+00 9.73f+Ol 5.81E+04 6.40E+04 N/A INFANT 3.TIE+02 3.32E+O1 1.88E+01 O.OOE+00 6.62E+Ol 5.95f+04 2.49fw04 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: INGfST: INHAL.

0.00E+00 0.00E+00 5.74E+03 2.68f+04 1.72E+03 9.50E+06 9.53&06 1.32ft05 PAGE: 4-41 DAT

5.0 INDIVIDUAL DOSE DUE TO WATERBORNE FFLUENT SP I ICATION 3.11.1.2 - 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'HE 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 are based on ingestion of fish, drinking water and exposure on the shoreline. Drinking water is taken from the nearest public drinking water intake location (Danville Water Authority). Shoreline and fish ingestion are associated with the SSES river outfall (edge of initial mixing zone).

Methodology for calculating dose to the maximum hypothetical offsite individual has'een developed (l)(2) for separate (fish, drinking water--

and shoreline exposure) and composite liquid effluent pathways. This methodology incorporates usage, dilution, and transit parameters specific to the SSES site. V (1) PP&L Calculation OT-93-RKB-019 (2) PP&L Calculation OT-93-RKB-021 21

5. 1 Fish Pathway Liquid Effluent Dose Calculation Methodology The following expression is used to calculate the fish ingestion pathway dose contribution for the total release period from all radionuclides released in liquid effluent to unrestricted areas:

R sip' =Z~p+c K

v +k (Eq 10 where: Rj ~ Total fish ingestion dose during period to organ j to individuals of age group a from all radionuclides i in pathway p (mrem);

ajpj Fish ingestion dose conversion factor to organ j of individuals of age group a from all radionuclides i in pathway p (mrem-fthm/Ci-sec:

Tables S-la,b, and c);

c, Average concentration of radionuclide i in undiluted liquid effluent during batch release from radwaste (

L m2 UCi J

V) Total undiluted batch volume released from radwaste (gallons);

Conversion factor (3.785 e3 ml/gallon);

Minimum blowdown flow (ft /sec).

22.

.2 = taoie Hater Pathwav iffluent Dose Calculation Methodology

.he following exoression is used to calculate the fish ingestion pathway case cantrip t>on for the total release period from all radionucIides IeIeasea In liquia er'fluent to unrestricted areas:

4107 K~ exp(-X.ic DFy+

) ~

F C, ~ v'. + k]~ (Eq. !1)

~nere Total potable water ingestion dose during period to organ j to individuals of age group:a from all raaionuclides i in pathway p (mrem);

potable water ingestion Dose conversion factor to orgaa-j of individuals of age group a from a'll radionuclides i In pathway p (mrem-fthm/Ci-sec: Tables 5-2a,b,c, and d);

Radioactive decay constant (hr': Table 5-3);

River transit time (hr: Table 5-4);

OF~ - Dilution factor (unitless: Table 5-4);

~ther factors aescribed in Section 5.1.

5.3 Shoreline Exoosure Pathway The followino expression is used to calculate the shoreli'ne exposure pathway dose contribution for the total release period from all radionuclides released in liquid effluent to unrestricted areas:

'fpy, =Z~pK F

~ C *v <<k (Eq.12) where Ra

- Shoreline dose conversion factor to organ j of individuals of age group a from all radionuclides i in pathway p (mrem-fthm/Ci-sec: Table 5-5); other factors described in Section 5.1. 5.4 Projected Dose from Liquid Effluent The following expression is used to estimate the combined fish, water ingestion and shoreline exposure pathway dose contribution for the projected release period and volume from all radionuclides released in liquid effluent to unrestricted areas: ~alp/ Z t Kaipg + C'2 + vd + kj (Eq. 13) where R>> Total projected dose during period to organ j from fish, water ingestion and shoreline exposure to individuals of age group a from all radionuclides i in pathway p (mrem); fpj Compos i te dose conversi on factor (adul t, teen, chi 1 d) or water ingestion dose factor (infant) to organ j of individuals to age group a from all radionuclides i in pathway p (mrem/Ci released: Tables 5-6a, b, c, and d); other factors described in Section 5. 1. 1 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 (rolling 31-day) or quarterly composite analysis. I 25 DAZ The calculated dose contributions from these radionuclides shall be based on the actual composite analysis. The cumulative 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,II 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 II code. A discussion of the LADTAP II code as applied to SSES liquid effluent, is given in Section A.3.1 of Appendix A. 26 Table 5-la: Dose Factors for Fish Pathway: Maximum Hypothetical Adult (Page I of 2) Dose Factor Units: mrem-ft3/Ci-sec Locati on: Out fal 1 /FIXED DILUTION Usa e (Uao) (k / r)FISK) ~ 21 Dilution (1/No:FISK) ~ 15.9 Transit time (tf) hrs ~ 25 I sotop Liver T. Body Thyroid KIdney Luna QI-LLI K-3 0.00e+00 1.37e-04 1.37e-04 1.37e-04 1.37c-04 I.37e-04 1.37e-04 C-14 1.90tt01 3.80e+00 3.80e+00 3.80e+00 3.80e+00 3.80e+00 3.80c+00 Ma-24 7.78e-02 7.78e.02 7.78e-02 7.78e-02 7.78e-02 7.78e-02 7.78c-02 P-32 2.67e+04 1.66e+03 1.03m%3 0.00eHS 0.00e+00 0.00e+00 3.00cH)3 Cr-51 0.00e+00 0.00cHS 7.53e-04 4.50e-04 1.66e-04 9.99e-04 1.89e-01 Nn-54 0.00e+00 2.65eHS 5.06e-01 0.00e+M 7.89e-01 0.00e+00 8.12ct00 Nn-56 0.00e+00 8.06e-05 1.43e-05 0.00e+00 1.02e-04 0.00e+00 2.57e-03 Fe 55 3.99e-01 2.76e-01 6.43e-02 0.00e+00 0.00et(S 1.5Ce.01 1.58e-01 Fe-59 6.20e-01 1.46e+00 5.59e-01 0.00cHS 0.00eH)0 4.07e-01 4.86cKS Co-58 0.00c+00 5.36e-02 1.20e-01 0.00e+00 0.00e+00 0.00e+00 1.09eKS Co-60 0.00e+00 1.55e-01 3.43e-01 0.00e+00 0.00e+00 0.00e+00 2.92e+(S MI.63 1.89e+01 1.31c+00 6.33e-01 0 ~ 00e+00 0.00e+00 0.00c+00 2.?3e-01 MI.65 7.91c 05 1.03e-05 4.69e-06 0.00e+00 0.00eKS O.OOe+00 2.61e-04 Cu-64 0.00eHS 1.55e-03 7.26e 0.00e+00 3.90e-03 0.00e+00 1.32e-01 15 Zn-65 1.40e+01 4.46e+01 2.02etOI 0.00cH)0 2.98e+01 0.00e+00 2.Bless)1 16 Zn-69 2.35e-10 C.49e-10 3.13e- 1 1 0.00eKIO 2.92e.10 0.00e+00 6.?5e-l 1 17 Br-83 0.00e+00 0.00c+00 1.7Ce-05 0.00e+00 0 '0e+00 0.00e+00 2.51e-05 18 Br.84 0.00e+00 0.00cHS 2.14e 16 0.00e+00 0.00eHS 0.00e+00 1.68e-21 19 Br-85 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00cHS 0.00e+00 0.00a+00 20 0.00e+00 5.90etOI 2.?5etOI 0.00eHS 0.00e+00 0.00e+00 1.16e+01 21 0.00e+00 0.00cKS 0.00eKS 0.00e+00 0.00e+00 0.00e+00 0.00a+00 22 Rb 89 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00-23 Sr-89 1.32e+01 0.00e+00 3.80e-01 0.00e+00 0.00e+00 0.00c+00 2.12eHS 24 Sr-90 3.30e+02 0.00e+00 8.11et01 0.00cHS 0.00eHS 0.00e+00 9.5Ce+00 25 Sr-91 3.99e-02 0.00e+00 1.61e-03 0.00e+00 0.00e+00 0.00eH)0 1.90e&1 26 Sr.92 1.57e.04 O.OOcHS 6.77e-06 0.00cKS 0.00e+00 0.00c+00 3.10e-03 27 T-90 2.67e-04 0.00e+00 7.15e-06 0 ~ 00e+00 0.00e+00 0.00e+00 2.83e+00 28 Y-91m 2.84e-15 O.OOa+00 1.10e-16 0.00e+00 0.00cHIO 0.00e+00 8.34e-'15 29 Y 91 5.06e-03 O.OOe+00 1.35e-04 0.00eKS 0.00e+00 0.00et00 2.?Be+00. 30 T-92 2.30e-07 O.OOeHS 6.71e-09 0.00e+00 0.00eHS 0.00eKQ 4.02e-03 31 T.93 1.75e-05 0.00e+00 4.83e-07 0.00e+00 0.00eHS 0.00cHS 5.55e-01 32 Zr-95 1.44e-04 4.62e-05 3.13e-05 0.00e+00 7.25e-05 0.00e+00 1.46e<1 33 Zr.97 2.89e-06 5.83e-07 2.67e-07 0.00e+00 8.80e-07 0.00e+00 1.81e-01 34 2.66e-01 1.48c Ol 7.94e 02 0.00cHS 1.46e<1 0.00e+00 8.97e+02 35 No-99 0.00e+00 4.82e.02 9.16e.03 0.00e+00 1.09e-01 0.00e+00 1.12e-01 Table 5-1b: Dose Factors for Fish Pathway: Haximum Hypothetical Teen (Page 1 of*2) Dose Units: mrem-ft /Ci-sec Factor Outfall/FIXED ocation: DILUTION Usa e (Ua ) (k / r:fISH) e 16 Dilution (1/M:fISH) ~ 15.9 Transit=time (tf) hrs ~ 25 Isot Liver T. 8 Th roid GI-LLI, H.3 0.00e+00 1.06e.04 1.06e-04 '.06e-04. 1 ~ 06e.04 1.06e-04 = 1.06e-04-- C-14 2.07et01 C.13e+00 4.13e+00 4.13c+00 4.13eKS 4.13e+00 4.13eKS Na-24 8.02e-02 8.02e-02 8.02e-02 8.02e-02 8.02e-02 8.02e-02 8.02e-02 P-32 2.90e+04 1.80m%3 1.13~3 0.00e+M 0.00eHN 0.00et00 2.44')3 Cr>>51 0.00e+00 0.00e+00 7.76e-04 4.31e-04 1.70e-04 1.11c-03 1.30e 01 0.00e+00 2.61eKN 5.17e-01 0.00e+00 7.77e 01 0.00c+00 5.35eKN Hn-56 0.00e+00 8.44e.05 1.50e-05 0.00e+00 1.07e.04 0.00e+00 5.55e-03 Fe 55 4.18e-01 2.96e-01 6.91e-02 0.00e+00 0.00eKN 1.88e-01 1.~1 Fe 59 6.39e 01 1.49c+00 5.76e-01 0.00e+00 0.00cKN 4.71e-01 3.53e+00 10 Co-58 0.00e+00 5.33e-02 1.23e-01 0.00eKN 0.00e+00 0.00e+00 7.3Ca 01 Co-60 0.00e+00 1.55e-01 3.50c-01 0.00et00 0.00et00 '.00e+00 2.02eKN 12 Ni.63 1.96et01 1.38e+00 6.64e-01 0.00e+00 0.00e+00 0.00e+00 01 >'.20e 13 Mi 65 8.55e-05 1.09e-05 4 '8e 0.00e+00 0.00e+00. 0.00e+00 5.93a' 14 Cu-64 0.00e+00 1.63e-03 7.65e 0.00e+00 4.12e-03 0.00e+00 1.~1 15 Zn-65 1.27e+01 4.41e+01 2.06et01 ' 0.00e+00 2.83e+01 0.00e+00 1.87et01 16 Zn-69 4.87e-10 41e-11 0.00e+00 ~ 3.18e-10 0 ~ 00e+00 8.97i 10 2.55e-10'.00e+00 17 Br-83 0.00cHS 1.89e-05. 0.00e+00 " 0.00e+00 0.00e+00 0.00e+00 18 Br-84 0.00e+00 0.00 a+00 2.26e 16- 0.00eKS. 0.00e+00. 0.00e+00 0.00eKO 19 Br-85 0.00eKN 0.00e+00 0.00eKN 0.00e+00 0.00e+00 0.00e+00 '.00eKO. 20 Rb-86 0.00e+00 6.35+41 2.98+&1 0.00e+00 0.00eKN 0.00e+00 9.39eKS-21 Rb-88 0.00e+00 0.00et00 0.00e+00 0.00e+00 0.00cHN 0.00e+00 0.00eKO'.00aKO 22 Rb.89 0.00e+00 0.00eKN 0.00e+00 0.00e+00 0.00cHN 0.00e+00 Sr-89 1.44~1 0.00e+00 4.12e-01 0.00e+00 0.00e+00 0.00e+00 1 e72a400- 24 Sr-90 2.76e+02 0.00e+00 6.81et01 0.00e+00 0.00~0 0.00e+00 7.74eKS t 25 Sr-91 4.32e-02 0.00eKN 1.72e-03 0.00e+00 0.00cKN 0.00e+00 1.9~$ 26 Sr-92 1.69e-04 0.00e+00 7.21e-06 ~ 0.00e+00 0.00e+00 0.00e+00 4.31 ~ 03 27 Y 90 2.89e-04 0.00eKN 7.79e-06 . 0.00e+00 0.00cKN 0.00e+00 2.39eKO 28 Y-91m 3.07e-15 0.00c+00 1.17e-16 0.00+HR 0.00e+00 0.00ct00 '.45a-13 29 Y.9'I 5.49e-03 0.00cHN 1.47e-04 0.00e+00 0.00e+00 0.00e+00 2.25eKS-30 Y.92 2.51e.07 0.00c+00 ~ 7.25e 0.00e+00 0.00e+00 0.00e+00 31 Y-93 1.91e-05 0.00c+00 5.23e-07 0.00eKN 0.00e+00 0.00e+00 5.82e-01 32 Zr-95 1.C9e-04 4.70e.05 3.23c-05 0.00e+00 6.90e.05 0.00e+N 1.08e&1 33 Zr-97 3.11e-06 6.14e.07 2.83e-07 0.00c+00 9.32e-07 0.00e40 1.~1 '4 Mb.95 2.67e-01 1.48e-01 8.17e-02 0.00e+00 1.44e-01 0.00e+00 6.34~2 35 No 99 0.00e+00 5.13e.02 9.79e-03 0.00e+00 1.17e.01 0.00e+00 9.19~2 5-1b(1) OAT /o Table 5-la: Dose Factors f~r Fish Pathway: Haximum Hypothetical Adult (Page 2 of 2) Dose Factor Units: mrem-ft /Ci-sec Location: Outfall/FIXED DILUTION 36 Isoto Tc-99m 3.03e-07 Liver 8.55e.07 T. 8 1.09c-05 Th roid 0.00e+00 K i dna 1.30e-05 4 ~ 19e.07 0.00e+00 GI 5.06e-04 0.00e+00 LLI - 0 37 Tc-101 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 38 RU 103 2.64e-03 0.00e+00 1.14e-03 0.00e+00 1.01e-02 0.00e+00 3.08e-01 39 Ru-105 4.52e-06 0.00e+00 1.78e.06 0.00e+00 5.84e-05 0.00e+00 2.76e-03 40 Ru-106 - 3.99e-02 0.00e+00 5.05e.03 0.00e+00 7.70e-02 0.00e+00 2.58e+00 AB.110m 5.33e-04 4.93e-04 2.93e-04 0.00c+00 9.70e 04 0.00e+00 2.01e.01 42 Te-125m 1.54e+00 5.57e-01 2.06e.01 4.63e-01 6.26eHN 0.00e+00 6.14e+00 43 I'e-127m 3.91e+00 1 ~ 40e+00 C.?6c-01 9.99e-01 1.59e+Ol 0.00e+00 1.31e+Ol Te-127 1.00e-02 3.60e-03 2.17e.03 7.42e-03 C.OBe-02 0.00e+00 7.90e.01 Te. 129m 6.54+40 2.44e+00 1.04eHS 2.25e+00 2.73e+01 0.00e+00 3.29e+01 Te-129 1.79e-02 6.?le-03 4.35e-03 1.370-02 7.51e 02 0.00e+00 1.35e-02. 47 Te-131m 5.64e-01 2.?6e.01 2.30e-01 4.3?e-01 2.80e+00 0.00e+00 2.74e+Ol Te-131 1 ~ 08e-20 4.51e-21 3.Clc-21 8.87e-21 4.73e-20 0.00e+M 1.53e-21'.59~1" Te-132 1.17e+00 7.59e-01 7.12e-ol 8.38e-01 7.31 a+00 0.00e+00 50 I.130 4.05e-03 1.20e-02 4.72e.03 1.01e+00 1.8?e-02 0.00w00 1.03e.02 51 t.131 8.29e-02 1.19e.01 6.79e-02 3.88e+01 2.03e-ol 0.00e+00 3.13c.02; 52 I-132 2.36e 6.32e-06 2.21e-06 2.21e-04 1.01e.05 0.00e+00 1.19e-06 53 I -133 1.35e-02 2.34e.02 7.13e.03 3.44et00 4.08c-02 0.00e+00 2.10e.02'.48e-14>> I-134 6.26e-12 1.70e-ll 6.08e.12 2.94e-lO 2.70e-ll 0.00e+00 55 I-135 7.02e-04 1.84e-03 6.78e-04 1.21e-01 2.95e-03 0.00e+00 2.08e 03 564 Cs-134 1.Sic+02 ~ C.30e+02 3.51e+02 0.00e+00 1.39et02 4.62e+01 ,7.52e+00 57 Cs-136 1.79e+01 7.07e+01 5.09et01 0 00eKS 3 93e+01 5.39~00 8.03e+00= 58 Cs-137 2.32@42 3.17+42 2.0?+42 0.00eKS 1.08')2 3.5?F01 6.13c+00'-" - 59 Cs-138 1.62e-15 3.20e-15 1.59e 15 0.00e+00 2.35e-15 2.32e-16 1.37e 20 Ba-139 2.13e-09 1.52e-12 6.23e-ll 0.00cKO 1.42e-12 8.60e-13 3.7?e-09 61 Ba-140 1.11e.01 1.40e-04 7.30e-03 0.00e+00 4.76e 05 8.02e-05 -'.30e-01 '2 Ba-141 0.00e+00 . 0.00eKN 0.00+88 0.00e+00 0.00e+00 0.00e+00 0.00e+00.- Ba 142 0 ~ 00 a+00 0.00e+00 0.00c+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 La 1CO 5.90e.05 2.97e-05 7.86e-06 0.00e+00 0.00e+00" 0.00e+00 2.18eKS., 65 La-142 8.78e-ll 3.99e-ll 9.95e-12 0.00e+00 0.00e+00 0.00e+00 2.92e-07'.44e.02, Ce-141 1.33e-05 8.99e-06 1.02e.06 0.00eKR C.18e.06 0.00e+00 67 Cc.143 1.42e-06 1.05e 03 1.16e.07 0.00eKS 4.61e.07 0.00e+00 3.92e-02. Ce-144 7.07e-04 2.96e-04 3.80e.05 0.00eKS 1.75e 04 - 0.00e+00 2.39e-ol'9 Pr-143 3.17e.04.. 1.27e-04 1.57e.05 0.00e+00 734 e-05 0.00c+00 1.39e+M" 70 Pr-1C4 0.00et00 0.00e+00 0.00ekS 0.00e+00 0.00c+00 0.00e+00 0.00e+00'.19e+00 71 Md-147 2.14e-04 2.47e.04 1.CBe-05 0.00e+00 1 45e-04 ~ 0 00e+00 'M-187 8.68e-02 ,7.25e-02 2.5Cc-02 0.00e+00 0.00c+00 0.00e+00 2.38e+01'.57e-01 Rp 239 1.27e.05 1.25c.06 6.90e-07 0.00e+00 3.90e-06 0.00c+00 5-la(2) DAT Table 5-1c: Dose Factors for Fish Pathway: Maximum Hypothetical Child (Page 1 of 2) Dose Factor Units: mrem-ft /Ci-sec cati on: Outfall/FIXED DILUTION Usage (Ua ) (kg/ sFISH) N 6.9 Oilution (1/H:FISH) e 15.9 Transit time (tf) hrs ~ 25 Isotooe Bone Liver T. Body Thyroid Kidney GI LLI H.3 0.00e+00 8.72e-05 8.?2e-05 8.?2e-05 8.72e-05 8.72e-05 8.?2e.05 C.14 2.66e+01 5.31e+00 5.31e+M 5.31e+00 5.31e+M 5.31e+00 5.31e+00 Ma-24 8.72e-02 8.72e-02 8.?2e-02 8.72e-02 8.?Ze-02 8.72e-02 8.72e-02, P.32 3.'74e+04 1.?5et03 1.44et03 0.00e+00 0.00e+M 0.00e+00 1.03eKI3'.39e-02 Cr-51 0.00e+00 0.00e+00 8.28e-04 C.59e 04 1.26e-04 839e-04 0.00e+00 2.04eKIO 5A3e-01 0.00e+00 5.?2e-01 0.00e+00 1.71 AN 0.00e+00 7.69e-05 1.74e-05 0.00eHS 9.30e-05 0.00e+00 1.11e-02 Fe-55 5.49e 01 2.91e-01 9.02e-02 0.00e+00 0.00eKN 1.65e 01 5.39~2 Fe-59 7.75e-01 '.25e+00 6.25e-01 0.00~ 0.00~ 3.&4e-01 1.31ehS 10 Co 58 0.00e+00 4.25e-02 1.30e-01 0.00e+M 0.00eKS 0.00e+00 2ABe 01 Co-60 0.00e+00 1.26e-O'I 3.72e-01 0.00et00 0.00e+00 0.00e+00 6.99e-01 12 Mi.63 2.5?F01 1.37e+00 8.74e-01 0.00e+00 0.00e+00 0.00e+00 9.26e-02 13 Mi.65 1 '9e-04 1.03e-05 6.01e-06 0.00e+00 0.00e+00 0.00e+00 1.26e-03 14 Cu-64: 0.00et00 1.49e-03 9.03e-04 0.00et00 3.61e-03 0.00et00 7.01e.02 15 Zn-65 1.30e+01 3.47e+01 2.16e+01 0.00e4$ 2.19~1 0.00e+00 6.10eKS. 16 Zn-69 3.28e-'10 4.74e-10 4.38e 11 0.00cKN 2.88e-10 0.00e+00 2.99e 17 Br-83 0.00e+00 0.00e+00 2.43e-05 0.00eKN 0.00e+00 0.00e+00 0.00et00 Br-84. 0.00eKS 0.00e+00 2.68e-16 0.00e+00 0.00e+00 ~ 0.00et00 0.00e+00-19 Br-85 0.00e+00 0.00e+00 0.00eKS 0.00eKS 0.00e+00 ~ 0.00e+00 0.00eKN 20 0.00e+00 6.15e+01 3.78+%1 0.00e+00 0.00e+00 0.00e+00 3.9&eKS-21 0.00et00 0.00e+00 0.00eKIO 0.00e+00 0.00e+00 0.00eKO>> 22 Rb.89 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00eHN 0.00e+00 Sr-89 1.86e+01 0.00ekS 5.32e-01 0.00e+00 0.00e+00 0.00e+00 7.21e41-24 Sr-90 2.43e+02 0.00eKN 6.1?a+01 0.00e+O) 0.00e+00 0.00e+00 3.28eKO-Sr-91 5.55e-02 0.00eKS 2.09e-03 0.00e+00 0.00eKN 0.00e+00 1.22e-01 26 Sr-92 2.16e-04 ~ 0.00e+00 8.66e-06 0.00e+00 0.00e+00 0.00e+00 4.09e-03 = 27 Y.90 3.74e-04 0.00eKN 1.00e-05 0.00e+00 0.00e+00 0.00e+00 1.0?e+00-- 28 Y 91m 3.92e-15 0.00e+00 1.43e-16 0.00eKS 0.00e+00 0.00e+00 7.68e 12-29 Y.9'I 7.10e-03 0.00e+00 1.90e.04- 0.00et00 0.00eKS 0.00e+00 9.45e 01

• 30 Y-92 3.21e 07 0.00et00 9.20e-09 0.00e+00 0.00eKN - 0.00eKN 9.29e.03-31 Y-93 2.CSe-05 0.00e+00 6.72e-07 0.00e+00 0.00e+00 0.00cH40 3.65e.01-32 Zr-95 1.81e-04 3.9?e-05 3.54e.05 0.00e+00 5.69e-05 0.00e+00 4.14e-02 33 Zr-97 3.95e-06 5.71e-07 3.37e-07 0.00e+00 8.19e 07 '.00e+00 8.64e-02-.

34 Mb.95 3.16e-01 1.23e 01 8.78e-02 0.00e+00 1.15e 01 0.00et00 2e27~2-35 Ko-99 0.00e+00 4.88e-02 1.21e-02 0.00e+00 1.04e-01 0.00et00 4.04e 5-Ic(l) Table 5-lb: Dose Factors f~r Fish Pathway:., Maximum Hypothetical Teen (Page 2 of 2) Dose Factor Units: mrem-ft /Ci-sec Out fall /FIXED DILUTION 'ocation: Is otooe Liver T. 8 Th old K idn GI-LLI 36 Tc-99m 3.10e-07 8.64e-07 1.12e.05 0.00e+00 1.29e-05 4.80e-07 5.68e-04 37 Tc-101 0 '0e+00 0.00e+00 0.00e+00 0 ~ 00 a+00 0.00e+00 0.00e+00 0.00e+00 38 Ru.103 2.77e-03 O.DOe+00 1.18e.03 0.00e+00 '> 9.77e-03 0.00e+00 2.31e.01 39 Ru-105 4.87e-06 1.89e-06 0.00 a+00 6. 14e-05 0.00e+00 3.93e-03 40 Ru 106 4.33e-02 0.00e+00 5.46e.03 0.00e+00 8.35e.02 0.00e+00 2.08eKS 41 A .110m 5.20e-04 4.92e-04 3.00e-04 0.00e+00 9.39e 04 D.OOe+00 1.3Se-01 42 Te-125m 1.67e+00 6.03e-01 2.24e.01 4.68e.01 0.00e+00 0.00e+00 4.94e+00 43 Te-127m 4.25e+00 1.51e+00 5.06e-01 1.01e+00 '.72e+Ol 0.00e+00 1.'06et01 44 Te-127 1.10e.02 3.89e-03 2.36e-03 7.56e.03 4.44e-02 '.00e+00 8.47e.01 45 Te-129m 7.06e+00 2.62e+00 1.12e+00 2.28e+00 2.96e+01 0.00e+00 2.65e+01 46 Te-129 1.94e.02 7.24e-03 4.72e-03 1.39e 02 8.15e-02 0.00e+00 1.06e-01 47 Te-131m 6.06e.01 2.91e-01 2.43e-01 4.37e.ol 3.03+40 0.00+%0 2.33m%1 48 Te-131 1.16e.20 4.80e 21 3.64e-21 8.97e-21 5.09e-20 0.00&0 9.56e-22 49 Te-132 1.24e+00 7.84e-01 7.38e.01 8.27e.ol 7.63e+00 0.00e+00 2.48e+01 50 1-130 4.21e-03 1.22e-02 4.86e-03 9.93e.01 1.88e-02 0.00e+00 9.36e-03 51 I.131 8.88e-02 1.24e.01 6.68e-02 3.63w01 2.14e.ol 0 '0e+00 2.46e.02 52 I.132 2.48e.06 , 6.48e.06 2.33e.06 2.18e-04 1.02e-05 O.DDe+00 2.S2e 06 53 1-133 1.45e.02 2.46e.02 7.51e-03 3.44e+00 4.32e.02 0.00e+00 1.86e-02 54 I.134 6.56e-12 1.74e-ll 6.25e-12 2.90e-lo 2.74e-ll 0.00e+00 2.29e-'l3 55 I-135 7.36e-04 1.89e-03 7.02e-04 1.22e-01 2.99e-03 0.00e+00 2.10e.03 56 Cs 134 1.85e+02 4.36e+02 2.02e+02 0.00e+00 1.38e+02 5.29e+01 5.42e+00 57 Cs-136 1.80etOI 7.08e+01 4.76e+01 0.00e+00" 3.86e+0'I 6.08e 00 5.70~ 58 Cs-137 2.48e+02 3.30e+02 1.15e+02 0.00e+00 1.12e+02 4.36etOI 4.69e+00 59 Cs-138 1.74e-15 3.34e-15 1.67e-15 0.00e+00 2.46e-15 2.87e-16 1.5'Ie-18 60 Ba-139 2.32e.09 1.64e-12 6.77e-ll 0.00e+00 1.54e-12 1.13e-12 2.07e-08 61 Sa 140 1.19e.ol 1.46e-04 7.66e-03 0.00eKO '4.94e-05 9.79e.05 1.83e.01 62 Ba 141 0.00e+00 0.00e+00 0.00e+00 0.00e+8) 0.00e+00 0.00et00 0.00e+00 63 Ba-142 0.00e+00 0.00e+00 0.00et00 0.00~0 0.00e+00 0.00e+00 D.OOeHN 64 La-140 6.26e.05 3.08e.05 8.18e.06 0.00e+00 0.00e+00 0.00e+00 1.77e+00 65 La-142 9.36e-ll 4.16e-ll 1.04e-ll 0.00e+00 0.00e+00 0.00e+00 1.27e-06 66 Ce-141 1.44e-05 9.61e-06 1.10e-06 0.00e+00 4.53e.06 0.00e+00 2.75e-02 67 Ce-143 1.54e.06 1.12e-03 1 ~ 25e-07 0.00e+00 5.02e.07 0.00e+00 3.37e-02 68 Ce-144 7.68e 04 3.18e-04 4.13e-05 0.00e+00 1.90e-04 0.00e+00 1.93e 03. 69 Pr-143 3.44e 04 1.37e-04 1.71e-05 0.00eKS 7.98e-05 0.00e+00 1.13e+00 '0 Pr-144 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00 a+00 0.00e+00 71 Md-147 2.43e.04 2.64e-04 1.58e-05 0.00e+00 1.55e.04 0.00e+00 9.54e-01 72 M-187'.37e-02 7.64e-02 2.68e-02 0.00e+00 0.00et00 0.00e+00 2.07e401 1.43e.05 '.35e-06 7.51e-07 0.00eKS 4.24e-06 0.00e+00 2.18e 01 5-jb(2) OAT Table 5-lc: Dose Factors for Fish Pathway: Maximum Hypothetical Child (Page 2 of 2) Dose Factor Units: mrem-ft /Ci-sec ocati on: Outfall/FIXED DILUTION Isoto Liver T. B Th roid Xidne Gi LLI 36 Tc-99m 3.72c-07 7.29e-07 1.21e-05 0 ~ 00etoo 1.06e.05 3.70e-07 4.15e 04 37 Tc-101 lorn 0.00c+00 0 ~ Boa+00 O.ooe+00 0.00c+00 0.00e+00 ", 0.00e+00 0.00e+00 38 RU-103 3.43e.03 0.00e+00 1.32e.03 0.00woo O.Boa+00 8.86e-02"'.62e.03 39 RLI-105 6.21e.06 0.00e+00 2.25e.06 0.00e+00 5.46e-05 0.00e+00 4.06e.03 40 Ru 106 5.57e-02 0.00e+00 6.96e-03 0.00e+00 7.53e-02 O.Boa+00 8.67e-ol A 1 5.90e-04 3.98e-04 3.19e 04* 0.00e+00 7.42e-04 0.00e+00 4.74e-02 42 Te-125m 5.83e-ol 2.87e-ol 6.03e-ol 0.00et00 O.ooe+00 2.07e+00 43 Te-127'.15e+00 Te-127m 5.48e+00 1.48et00 6.51e.ol 1.31e+00 1.56e+ol 0.00e+00 4.44e+00-1.41e-02 3.80e 03 3.02e 03 9.76e-03 4.01e-02 - O.ooe+00 5.51e-ol-- 45 9.10eKS 2.54e+00 1.41e+00 2.93et00 2.67+41 O.ooe+00 1.11e+01-47'e-129m 46 Te-129 2.50e-02 6.99e-03 5.94e-03 1.79e-02 7.33e-02 0.00e+00 1.56e+00 Te-131m 7.72e.ol 2.67e-ol 2.84e-ol 5.49e-ol 2.58m%0 1.08etOI '.ooe+00 48 ~ Te-131 1.49e-20 4.55c-21 4 44e-ZI 1.14e-20 4.52e-20 0.00e OO 7.85e-ZO-. 49 '- Te-132 1.55c+00 6.84e-ol 8.26e-ol 9.96e-ol 6.35et00 0.00e+00 6.88eKS-50 I.130 . 5.15c-03 1.04e-02 5.36e-03 1.15e+00 1.55e-02 0.00e+00 4.86e-03 51 1-131 1.13e-ol 1.13c-ol 6.43e-02 3.74e+01 1.86e 01 0.00e+00 1.01e-02 " 52 I.132 3.06e.06 5.63e-06 2.59e 2.61e 8.61e 06 O.ooe+00 6.62e-ob" 53 1.133 1.84e-02 2.28e-02 8.62e 4.23eKS 3.80e-02 O.Boa+00 9.18e-03 54 1-134- 8.12e-l2 1.51e-ll 6.94e 3.47e-lo 231c-Il 0.00e+00 1.00e 11 55 I -135 9.11e-04 1.64e-03 7.76e 1.45e-ol 2.51e.03 O.Boa+00 1.25~3 56- Cs-134- 2 e 230+02 3.66e+02 7.73etOI- 0.00eKO 1.14et02 4.07e+01 1.97eKS'.64e+00 57 Cs-136 2.12+41 5.84e+01 3.78e+01 0.00eKN 3.11+%1 2.05eKN~ 58 Cs 137 3.12e42 2.99c+02 4.4'I a+01 0.00e+M 9.74+41 '.50e+01 1.87e40-59 Cs-138 Z.ZOc-15 3.06e 15 1.94e-l5 0.00e+00 2.15e-15 2.32e-16 1.41e-15 60 Be~ 139 2.99e-09 1.59e-12 8.65e-ll 0.00eKS 1.39e-l2 9.37e-'13 1.72e 07 61 Ba-140 1.50e-ol 1.31e-04 8.75e-03 0.00eKS 4.28e 05 7.83e-05 7.6~2 62 Ba-141 0.00eKS 0.00c+00 O.Boa+00 0.00e+00 0.00e+00 O.ooe+00 0.00et00'w 63 Ba-142 0.00eKS O.Boa+00 0.00e+00 O.Boa+00 0.00e+00 O.ooe+00 O.ooe+00" La-140 7.83e.05 2.74e-05 9.23e-06 0.00e+00- 0.00e+00 0.00e+00 7.63e&1-65 La-142 1.18e-lo 3.77e-ll 1.18e-ll 0.00e+00 0.00e+00 0 ~ Boa+00 7.46e-06 Ce-141 1.85e-05 9.24e-06 1.37e-06 0.00eHS . 4.05e-06 O.ooe+00 1.15e-02 . 67 Ce-143 1.97e-06 1.07e-03 1.55e-07 '.00eKN 4.49e-07 O.ooe+00 1.57e-oZ 68 ~ Ce-144 9.90e-04 3.10e 5.29e-05. 0.00e+00 1.72e O.ooet00 8.09e-02 69 Pr-143 4.45e-04 1.34e-04 2.21e.05 0.00e+00 7.23e-05 O.ooe+M 4.80e 01 70 Pr-144 0.00eKS 0.00c+00 0.00e+00 0.00e+00 0.00et00 O.ooe+00 0.00e+00. 71 Nd-147 3.12e.04 2.53e-04 1.96e.05 0.00et00 1.39e-04 O.ooe+M 4.00e-ol II-187 1.19e-ol 7.03e-02 3 ~ 16e-02 0.00e+00 0.00e+00 0.00e+00 9.88eKS Np-239 1.84e-05 1.32e-06 9.31e 07 0.00+40 3.83e-06 O.ooe+00 9.80e-02, 5-1c(2) Table 5-20: Dose Factors for potable Mater pathway: Haxisass Hypothetical Adult (PACE 1 OF 2) Dose Factor Units: mrem-ft /Ci-sec Location: Danvi lie Receiver/VARIABLE DILUTIDK Usage (Ua ) (kg/yr:WATER) ~ 730 Isoto Liver - T. Body Thyroid Kidney GI-LLI H-3 0.00e+00 8.43e-02 8.43e-02 8 430.02 8.43e-02 8.430.02 8.430-02 C-14 2.28e+00 4.56e-01 4.560-01 C.56e.01 C.56e.01 4.56e-01 4.560 01 Ka-2C 1.37@+00 1.37e+00 1.37e+M 1.37e+00 1.37e+00 1.37e+00 1.370+00 P-32 1.55e+02 9.64e+00 ~ 5.99ct00 0.00e+00 0 ~ 00 a+00 0.00e+00 1.74e+O'I Cr-51 0.000+00 0.00e+00 2.140 03 1.280.03 4.71e-04 2.83e.03 '.370-01 Hn-54 0.00e+00 3.67e+00 7.000-01 0.00e+00 1.09e+00 0.00et00 1.12et01 Hn-56 0.000+00 9.23e-02 1.64e-02 0.00e+00 1.170.01 0.00eKS 2.95 AS Fe-55 2.21e+00 1.53e+00 3.56e-01 0.00&00 0.00e+00 8.510.01 8.750-01 Fe-59 3.49eKN 8.19eKS 3.14eHR 0.00&00 0.00e+00 '.29e+00 2.73et01 10 Co-58 0.00e+00 5.98e-01 1.340+00 0.00e+00 0.00e+00 0.00e+00 1.21@%1 Co-60 0.00e+00 1.720+00 3.79e+00 0.00e+00 0.00eKN 0.00e+00 3.23etOl 12 K i-63 1.04e+02 7.240+00 3.50e+OO 0.00et00 0.00~ 0.00et00 1.51eKS .13 Ki-65 4.240-01 5.51e.02 2.51e.02 0.00~0 0.00e+00 0.000+00 1.C00+00 14 Cu-64 0.00e+00 6.69e-02 3.14e.02 0.00e+00 1.69e-01 0.00e+00 5.70eKS 15 Zn-65 3.89m%0 1.24etOI 5.59e+00 0.00e+00 8.27e+00 0.00e+00 7.79e+00 16 Zn-69 8.27e-03 1.58e.02 1.100-03 0.00e+00 1.030-02 0.00e+00 2.38e-03 17 Br-83 0.00e+00 0.00e+00 3.230-02 0.000+M 0.00w00 0.00et00 4.65e-02 'IB Br-84 0.000+00 0.000+M CD 18e-02 0.000+00 0.000+00 0.00e+00 3.280-07 19 Br-85 0.00eKO 0.00e+00 1.72e-03 0.000+00 0 ~ 00 a+00 0.000+00 0.000+00 20 Rb.86 0.00e+00 1.69~1 7.89e+00 0.00e+00 0.00e+00 0.00e+00 3.3Ce+00 21 Rb-88 0.00e+00 4.86e-02 2.580-02 0.000+00 0.00e+00 0.000+00 6.71e-13 22 Rb.89 0.00e+00 3.22e-02 2.260-02 0.00e+00 0 ~ 00e+00 0.00e+00 1.87e-15 Sr-89 2.47+42 0.00e+00 7.100+00 0.000+00 0 ~ 00e+00 0.00e+00 3.97et01 Sr-90 6.09et03 -0.00eKS 1.49~3 0.000+00 0.00e+00 0.000+00 1.76')2 25 Sr-91 4.55e+00 0.00cKS 1.840-01 0.00e+00 0.00ekS 0.00e+00 2.17et01 26 Sr-92 1.73e+00 0.00e+00 7.47e-02 0.000+00 0.00e+00 0.00et00 3.42et01 27 Y-90 7.720 03 0.00e+00 2.070-04 0.000+00 0.00e+00 0.00e+00 8.190+01 28 - Y-91$ 7.300.05 0.000+00 2.830-06 0.000+00 0.00e+00 0.000+00 2.1C0 04-29 Y.91 1.13e-01 0.000+00 3.03e-03 0.00e+00 0.00e+00 0.00e+00 6.23@%1 30 Y-92 6.790-04 0.00e+00 1.980-05 0.00e+00 0.00eKN 0.00e+00 1.19et01 31 Y-93 2.15e-03 0.00+AS 5.94e-05 0.000+00 0.00e+00 0.00e+00 6.83e+01 32 Zr-95 '3 2.440.02 7.83e-03 5.300-03 0.00et00 . 1.23e-02 0.000+00 2.48e401 Zr-97 1.35e-03 2.72e 1.240-04 0.000+00 C.11e.04 0.00e+00 8.43~1 4.99e-03 2.78e-03 1.490-03 0.000+00 2.75e-03 0.00et00 1.69')1 35 Ho-99 0.000+00 '.46eKS 6.58e-01 0.00etM 7.84e+00 0.00et00 8.02eKS 5-2a(1) / OAT Table 5-2a:. Dose Factors for potable Natcr pathways Haxlsua Hypothetical Adult (Page 2 of 2) Dose Factor Units: mrem-f t'/GI-sec Location: Danville Receiver/VARIABLE DILUTION Isoto Liver T. Body Thyroid GI LLI 36 Tc-99m 1.98e.04 5.60e-04 7.1Ce.03 0.00e+00 8.51c.03 2.75e.04 3.32e.01 I 37 Tc-IOI 2.04e-.04 2.94e-04 2.88e-03 0.00e+00 5.29e.03 1.50e-OC 8.83e-16 38 Ru-103 1.49e-01 0.00e+00 6.40e-02 0.00e+00 5.67e.01 0.00e+00 1.73e+01 39 Ru-105 1.24e.02 0.00e+00 4.88e-03 0.00e+00 1.60e-01 0.00et00 7.56eKS 40 Ru-106 2.21e+M 0.00e+00 2.79e-01 0.00e+00 4.26e+00 0.00e+00 1.43+42 C1 Ag-110m 1.28e-01 1.19e.01 7.06e-02 0.00e+00 2.34e-01 0.00e+00 4.85e+01 42 Tc-125m 2.15e+00 7.80e-01 2.88e-01 6.47e-01 8.75e+00 0.00e+00 8.59eKS C3 Te.127m 5.44e+00 1.94e+00 6.62e-01 1.39e+00 2.21 a+01 ~ 0.00e+00 1.82~1 44 Tc.127 8.83e-02 3.17c-02 1.91e.02 6.54e-02 3.60e-01 0.00et00 6.97e+00 45 Te-129m 9.23e+00 3.44e+00 1.46c+00 3.17e+00 3.85~1 0.00e+00 C.65e+01 46 Te-129 2.52e.02 9.48e-03 6.14e-03 1.94e-02 1.06e-01 0.00e+00 1.90e-02 47 Te-131m 1.39e+00 6.79e-01 5.66e-01 1.08e+00 6.88et00 0.00e+00 6.75+%1 48 Te.131 1.58e-02 6.61e-03 4.99e-03 1.30e-02 6.93e-02 0.00e+00 2.2Ce-03 49 Te-132 2.02e+00 1.31eKS 1.23e+00 1.C5e+00 1.26et01 0.00et00 6.19et01 50 I -130 6.07e-01 1.79e+00 7.07e-01 1.52e+02 2.79c+00 0.00e+00 1.5Ce+00 51 I.131 3.34e+00 4 ~ 78 a+00 2.74e+00 1.57e+03 8.19e+00 0.00e+00 1.26e+00 52 1.132 1.63e-01 4.36c-01 1.53e.01 1.53e+01 6.95e 01 0.00c+00 8.19e-02 53 1.133 1.14e+00 1.98e+00 6.05e-01 2.91e+02 3.46e+00 i 0.00e+00 1.78eKS 54 I-134 8.51c-02 2.31e-01 8.27e-02 4.01e+00 3.68e 01:, 0.00et00 2.02e-04 55 I -135 3.56e-01 9.31e-01 3.44e-01 6.14e+01 1.49c+00 0.00c+00 1.05e+00 . 56 Cs-134 4.99e+01 1.19@%2 9.72e+01 0.00e+00 3.85e+01 1.28etOI 2.08e+00 57 's-136 5.23e+00 2.06~1 1.49etOI 0.00e+00 1.15etOI 1.57et00 2.34e+00 Cs-137 '8 6.COe+01 8.75m%1 5.73e+01 0.00e+00 2.97e+01 9.88et00 1.69eHS 59 Cs.138 4.43e-02 8.75e-02 C.34e-02 0.00e+00 6.C3e-02 6.35e-03 3.73e-07 60 Ba-139 7.79e-02 5.55e-05 2.28e-03 0.00e+00 5.19e 05 3.15e.05 1.38e-01 61 Ba-140 1.63e+01 2.05e.02 1.07e+00 0.00e+M 6.96e-03 1.17c-02 3.3~1 62 Ba 141 3.78e-02 2.86e-05 1.28e-03 0.00et00 2.66e-05 1.62e-05 1.78e-11 63 Ba-142 1.71e.02 1.76e-05 1.08e-03 0.00cHS 1.C9e-05 9.96e-06 2.41e-20 64 La-140 2.01e.03 1.01e-03 2.67e-04 0.00eKS 0.00eHS 0.00e+00 '.43et01 65 La-142 1.03e-04 1.16e-05 0.00e+00 0.00et00 0.00e+00 3.C1e.01 4.67e.05'.08e-03 66 Ce-141 7.52e-03 5.77e-04 0.00e+00 2.36e-03 0.00e+00 1.94+%1 67 Ce-143 1.32e-03 9.80e.01 1.08e 0.00et00 C.31e-04 0 ~ 00ct00 3.66e+01 68 Cc-144 3.92e.o'I 1.64e-01 2.10c-02 0.00e+00 9.72e-02 0 '0e+00 1.32')2 69 Pr-143 7.39e-03 .2.96e-03 3.66e-OC- 0.00e+00 ~ 1.71e-03 0.00eHS 3.24~1 70 Pr-144 2.42e.05 1.00e-05 1.27e-06 0.00e+00 5.66e-06 0.00e+00 3.C8e-12 71 Xd.147 5.05e-03 5.84e-03 3.49e-04 0.00e+00 3.41e.03 0.Doe+00 2.80et01 72 U-187 8.27e-02 6.91e-02 2.42e-02 0.00c+00 0.00e+00 0.00e+00 2.26~1 73 Np-239 9.56e-04 9.40e.05 5.18e-05 0.00e+00 2.93e.04 0.00e+00 1.93~1 5-2a(2) Table 5-2b: Dose Factors for potable Nat'ar pathways Haxisssa Hypothetical Teen (Page 1 of 2) Dose Factor Units: mrea-ft3/Ci-sec Location! Danvi lie Receiver/VARlABLE DlLUTlOM J Usa e (Ua ) (k / r:MATER) ~ 510 tsotooe Bone Liver T. 8 Thvroid Kidne Lung Gl LLl H.3 0.00e+00 5.95e.02 5.95e.02 5.95e 02 5.95e-02 5.95e-02 5.95e-02 C-14 2.28e+00 C.56e.01 C ~ 56e 01 4.56e.01 C.56e-01 4.56e-01 4 '6e-01 Ma-24 1 ~ 29e+00 1.29e+00 1.29e+00 1.29e+00 1.29e+00 1.29e+00 1.29eKR P.32 1.55et02 9.59e+00 6.00e+00 0.00e+00 0.00e+00 '.00e+00 C.43e-04 2.88e-03 1.30et01'0 Cr-51 0.00e+00 0.00et00 2.02e-03 1.12e-03 3.39e-01 Hn-54 0.00e+00 3.31e+00 6.56e-01 " 0.00e+00 9.8?e-01 0.00e+00 6.?9eKO Hn-56 0.00e+00 8.86e-02 1.58e-02 0.00e+00 'l.12e.01 0.00e+00 5.83e+00 ~ Fe-55 2.12e+00 1.50a+00 3.51e 01 0.00e+00 0.00e+00 9.54e-01 6.51e-01 Fe-59 3.29e+00 7.69e+00 2.97e+00 0.00et00 0.00e+00 2.C2e+00 1.82+%1-Co-58 0.00eKS 5.45e-01 1.26e+00 0.00et00 0.00e+00 0.00e+00 7.52e+00 . Co-60 0.00e+00 1.58et00 3.55et00 0.00e+00 0.00e+00 0.00e+00 2.05e+01 12 Ni 63 9.93~1 7.01c+00 3.37e+00 0.00e+00 0.00e+00 0.00e+00 1.12e+00-13 Mi-65 C.20e.01 5.3?e-02 2.45e-02 0.00e+00 0.00&00. 0.00e+00 2.91e+00-14 Cu-64 0.00e+00 6.45e-02 3.04e-02 0.00e+00 1.63e-01 0.00e+00 5.00eHS 15 Zn-65 3.23e+00 1 ~ 12e+01 5.23e+M 0 ~ 00e+00 7.18e+00 0 '0e+00 4 ~ 75e+00-16 Zn.69 8.25e-03 1.5?e-02 1.10e-03 0.00e+00 1.03e-02 0.00e+00 2.89e 17 Br-83 0.00e+00 0 '0e+00 3.22e-02 0.00e+00 0.00et00 0.00e+00 0.00a+00-18 Br-84 ~ 0.00e+00 0.00e+M 4.05e-02 0 '0e+00 0.00e+M 0.00e+00 0.00e+00-19 Br-85 0.00e+00 0.00e+00 1.71e-03 0.00e+00 0.00e+00 0.00e+00 0.00+H)0 20 Rb.86 0.00e+00 1.67e+01 7.85e+00 0.00e+00 0.00~0 0.00e+00 2.47e+00-21 Rb.88 0.00e+00 C.78e-02 2.55e-02 0.00e+00 0.00a+00 0.00e+00 C.10~- 22 Rb.89 0.00e+00 3.09e-02 2.18e-02 0.00e+00 0.00e+00 0.00e+M 4.?3e-'l 1 'r-89 2.47a+02 0.00e+00 7.0?a+00 0.00e+00 0.00e+00 0.00e+00 2.94~1 Sr~90 " C.66e+03 0.00a+00 1.15e+03 0.00eKS 0.00e+00 0.Doe+00 1.31~2 Sr-91 4.53et00 0.00a+00 1.80e-01 0.00e+00 0.00e+00 0.00e+00 2.05~1 26 Sr-92 1.71 a+00 0.00e+00 7.29e-02 0.00e+00 0.00e+00 0.00e+00 4.36eKl1 27 T-90 7.69e-03 0.00eKN) 2.07e-04 0.00e+00 0.00a+00 0.00e+00 6 34~1 28 Y-'91m 7.2Ce-05 0.00cKN 2.?7e-06 0.00e+00 0.00eKS 0.00e+00 3.42e-03 29 Y.91 1.13e-01 0.00e+00 3.02e-03 0.00e+00 0.00e+00 0.00e+00 4.62~1 30 Y.92 6.79e-04 0.00e+00 1.96e-05 0.00e+00 0.00e+00 0.00e+00 1.~1-3'l T-93 2.15e.03 0 ~ 00et00 5.89e-05 0.00@+0) 0.00e+00 0.00e+00 6.56+%1 32 Zr-95 2.31e-02 7.29e-03 5.02e-03 0.00e+00 1.07e-02 0.00e+00 1.68et01 33 Zr-97 1.33e-03 2.63e.04 1.21e-04 0.00eKN 3.99e-04 0.00e+00 7.12e+01 34 Mb.95 4.61e-03 2.'56e-03 1.C1e-03 0.00e+00 2.48e.03 0.00e+00 1.09e+01 35 Ho.99 0.00e+00 3.38e+00 6.45e-01 0.00~0 7.74e+00 0.00et00 6.06eKS-5-2b(1) Bose factors for Potable Mater Pathmyt Maxisssa Hypothetical Teen (Page 2 of 2) Oose factors: mr~t'/Ci.sec Locatlont Oanviiie Receiver per BROL 'Table 5.2 23/VARIABLE OILUTIO)I Is otooe Liver I T. Body Thyroi d L'idney Luna Gl LLI 36 Tc-99m 1.86e-04 5.19e.04 '6.73e-03 O.aaeHN 7.74e-03 2.88e-04 3.41e-ol 37 tc-101 2.02e-aC 2.8?e-04 2.82e-03 O.aae+00 5.19e-03 1.75e-04 4.91e 11 38 Ro 103 1.C3e-al O.aae+00 6.11e.02 O.aae+00 5.04e-ol O.oae+00 1.19et01 39 RLI 105 1.22e-02 O. aaeHN 4.75e-03 O.aoe+00 1.5Ce 01 O.aae+00 9.8'?a+00 40 RU 106 2.2ae+00 O.aae+00 2.7?e 01 O.aae+00 4.2Ce+00 O.aaeHS 1.05et02 41 Ag-liam 1.15a-al 1.09e-al 6.&2e 02 O.oaeKN 2.08e-ol O.aaeHN 3.06eo01 42 Te 125m 2.15e+00 7.7Ce-a'I 2.8?e 01 6.00a-ol O.aae+00 O.aaa+00 6.34eHN 43 Te-127m, S.C2eHN 1.92e+00 6ASa 0'1 1.29e+00 2.20e401 O.aae+00 1.35et01 Te-127 8.86e-02 3.14e.02 1.91e 02 6.11e 02 3.59e 01 O.aaa+00 6.84eHS 4 45 Te-129m. 9.14a+00 3.39e+00 1.CSe+00 2.95eHN 3.83et01 O.aae+00 3.43et01 Te 129 2.51e-02 9.3?e 03 " 6.11e-03 1.8ae-02 1.05e-ol O.aaeHN 1.3?e-ol 47 Te-13lm- '.3?eHN 6.56e-ol 5.~1 ~ 9.8?e 01 '.84eHN O.aaa+00 5.2?et01 Te-131 1. 5'?a-02 6.45e-03 4.89e 03" 1.21e 02 6.84e 02" O.aaa+00 1.28')3 Te-132 1.96eHN 1.2Ce+00 1.1?eHN 1.3 1eHN 1.21 F01 O.aaeHN 3.93et01 sa 1.130 5.78e-ol 1.6?F00 6.~1 1.'36e+02 2.57eHN O.aaeHS 9.09~1 1.28eHN-'.34e+03 51 l-131 3.28e+00 4. 59e+00 Z.C7a+00 7.91e+00 O.oae+00 52 I -132 1. 57e-01 4. 10e 01 ~ 1.C7e 01 1.38e+01 6.45e-ol O.aae+00 1.78e-ol 53 1.133 1.13e+00 1.91e+00 5.83a-al 2.67e+02 3.35eHN O.oae+00 I 1.C5e+00 > 54 1.13C 8.190 02 2.17a-al I 7.8ae 02 3.62eKN 3.42e-ol O.aaa+00 2.B6e~ 55 1.135 3.C2e-ol 8.81e-al 3.2?e-01 1.39e+00 0. Boa+00 9.76~1 '.67e+Ol 56 Cs.134 C.70eH)1 1.11et02 5 13~1 O.oae+00 3.51~1 1.34e+01 1.3?a+00 I 57 Cs-136 1.9ae+01 '.27~1 O.aae+00 1.03et01 1.63e+00 1.53eHS . SB Cs.137 6.28~1 8.36a+01 2.91e+01 O.oae+00 2.84e+OI 1.11e+01 1.19eHN: 59 Cs-138 C.35e-02 8.36e-02 4.18e<2 O.oaeHN 6.1?e 02 7.18e 03 3.?9~ = Ba 139 7.Boa<2 S.C9e-05 2.2?e-03 O.aae+00 5.17e-os 3.78e-os 6.96e4$ 61 Ba 140 1.59e+01 1.95e 02 1.03eHN 6.62e&3 1.31e 02 2.~1 '.oaeHS 62 Ba-141 3.76e-02 2.81e-05 1.26~3 O.aae+00 2.61 a&5 1.92e~ 8.02')8-Be~142 1.68e&2 1.68e-os 1.03~3 O.oaeKN 1.42e<5 1.12e-05 5.15e 14 ~ La-140 1.95&3 9.59e-04 2.55e-04 O.oae+00 O.oaeHN O.aae+00 5.51e+Ol 65 La-142 l.aae 04 4.46e 05 1.11e-os O.oaeHN O.aaeHN O.oaaHN 1.36eHN t Ce-1C1 7.4~3 4.98e-03 5.72e.04 O.ooeHS 2.3Ce-03 O.aaeHS 1.42et01 67 C0-143 1.32e 03 9.59e 0'I 1.07e 04 4.30e~ O.oae+00 2.88e+01 " '.oaeHN Ce-144=. 3.90~1 1.62e-ol Z.lao&2 O.aae+00 9.65e&2 O.oaeHN 9.82e-o'1 69 Pr-143 7.35e-03 2.93e 03 3.66e44 O.aaeHN - 1.71e-03 O.aae+00 2.42efol " 70 Pr-144.: 2.Cle-os- 9.8?a-06 1.22e-06. O.aaeHN 5.6?e-06 O.aaeHN - 2.~-. 71 Rd 147 5.~3 5.72e-03 3A3e~- O.ooeKN 3.36e-03 O.oaeHN 2.06et01= M-187 8.19~2 6.68e-02 2.3Ce-02 O.aaeHN O.Oae+OO O.Oae+OO 1.81e+Ol Mp-239 9.8?e 04 9.31e.05 5.1?e 05 O.aaeKN 2.92e-04 O.aae+00 1.5ae+01 '- 5-2b(2) Tsbi ~ 5-2c: Dose Factors for Potable Water Pathwsyt Maximum Hypothaticei Ciuld IPAGE 1 OF 2I Doss Factors: mramft ICi.sec Locsoon: Dsnviiie RaceivarNARIABLE DILUTION Usage IUopl Ikgfyr:WATERI ~ 510 Bone T. Body Lung H.3 0.00e+ 00 1.14c 01 1.14e41 1.14e41 1.14e4'I 1.14e41 1.14e41 C-14 6.79a+00 1.36e+00 1.36e+00 1.36e+00 1.36e+00 1.36e+00 1.36e+00 ~ Na 24 3.25a+00 3.2Sa+00 3.2Sa+00 3.26e+00 3.26a+00 3.25s+00 3.26a+00 P-32 4.63a+02 2.17a+01 1.78e+01 0.00e+00 0.00e+00 0.00a+00 1.28e+01 Cr.61 0.00a+00 0.00a+00 4.99e43 2.77e43 7.S7e44 '.06e43 2.65e01 Mn-64 0.00a+00 6.00e+00 1.60o+00 0.00a+00 1.68e+00 0.00a+00 6.04o+00 ~ Mn-66 0.00a+00 1.87e41 4.23e02 0.00e+00 2.27a41 0.00o+00 2.72at01 Fa.66 6.46a+00 3.42e+00 i 1.08e+00 0.00a+00 0.00e+00 1.94e+00 6.34e4'I Fa.69 9.26a+00 1.SOa+01 7.46e+00 0.00a+00 0.00e+00 4.34e+00 1.66o+01 10 Co.68 0.00a+00 1.01 a+00 3.09e+00 0.00a+00 0.00e+00 0.00e+00 6.89o+00 0.00e+00 2.97o+00 8.76et00 0.00e+00 0.00e+00 0.00o+00 r'.64o+01 12 Ni-63 3.02a+02 1.62a+01 1.03e+01 0.00e+00 = 0.00a+00 0.00a+00 1.09e+00.'.44e+01 Ni-66 1.25a+00 1.17a41 6.84e42 0.00a+00 0.00e+00 0.00a+00 14 Cu.64 0.00a+00 1.37e41 8.30e42 0.00o+00 3.32c 01 0.00e+00 6.46e+00. 15 Zn.66 7.69e+00 2.06e+01 1.27a+01 0.00e+00 1.28a+01 0.00e+00 3.60e+00 16 2.46c 02 3.SSc 02 3.28o43 0.00e+00 2.16e42 0.00e+00 2.24e+00~ 17 Br-83 0.00a+00 0.00a+00 9.59e42 0.00 a+00 0.00 a+00 0.00a+00 0.00ot00>> 18 Br 84 0.00e+00 0.00e+00 1.11e41 0.00o+00 0.00o+00 0.00o+00 0.00e t00 ~ 19 Br.86 0.00e+00 0.00e+00 5.12a43 0.00o+00 0.00o+00 0.00o+00 0.00o+00 ~ Rb 86 0.00a+00 3.76a+01 2.31e+01 0.00e+00 '.00a+00 0.00e+00 2.42o+00 y 21 Rb.88 0.00e+00 1.07e41 7A1e42 0.00e+00 0.00o+00 0.00e+00 6.23e43 22 Rb 89 0.00a+00 6.68e42 5.83e42 0.00a+00 0.00e+00 0.00e+00 6.72e44 23 Sr-89 7.41o+02 0.00e+00 2.1'let01 0.00e+00 0.00o+00 0.00e+00 2.87e+01 " 24 Sr-90 9.S4o+03 0.00a+00 2.42e+03 0.00e+00 0.00e+00 0.00o+00 1.28e+02-25 Sr 91 1.35a+01 0.00e+00 5.08o41 0.00e+00 - 0.00e+00 0.00e+00 2.87o+01 26 5 82 S.07a+00 0.00e+00 2.03o41 0.00e+00 - '.00e+00 0.00e+00 9.69o+01" 2.31a42 6.56o+01 . 27 0.00a+00 6.17a44 0.00a+00 0.00e+00 0.00e+00 28 Y.91m 2.14e44 0.00 a+00 7.80e46 0.00e+00 0.00e+00 0.00o+00 4.20e41 Y-91 3.38e41 0.00 a+00 9.03e43 0.00e+00 0.00e+00 0.00e+00 4.60e+01 = Y.92 2.02e43 0.00e+00 5.78a46 0.00a+00 0.00a+00 0.00 a+00 6.83e+01 31 Y-93 6.40e43 0.00 a+00 1.76e44 0.00e+00 0.00a+00 0.00a+00 9.54e+01 . 32 Zr-96 6.61e42 1.43o42 1.27e42 0.00 a+00 2.05o42 0.00e+00 1.49e+01 33 Zr.97 3.92e43 5.67e04 '.34e44 0.00e+00 8.13e44 0.00e+00 8.58e+01 Nb.86 1.26a42 4.91e43 3.51e43 0.00a+00 4.62e43 0.00a+00 9.09e+00 35 Mo-99 0.00a+00 7.48a+00 1.85o+00 0.00a+00 1.69e+01 0.00o+00 6.17a+00 Table 5-2d: Dose Factors for potabl ~ Hater pathuayt Haxisus Hypothetical infant (Page 1 oF 2) Dose Factors: mrea-f t'/Ci-sec Location: Danville Receiver per EROL Table 5.2-23/VARlABLE D1LUT10N Usa e (Ueo) (kg/ rtHATER) e 330 1sotooe Bone Liver T. 8 Th old Ki Lung 01-LL1 1 H.3 O.ppe+00 < 1.12e-p'1 1.12e-pl 1.12e-pl 1.12e-pl 1.12e-pl 1.12e-pl 2 C-14 8.60e+00 1.8Ce+00 1.84e+00 1 ~ 84e+00 1.84e+00 1.84e+00 1.84eKN 3 Na 24 3.67et00 3.67e+00 ' 3.67e+00 3.67e+00 3.67e+00 3.67et00 3.67e+00 4 P-32 6.17e+02 3.63et01 2.39e+01 O.ppe+00 0 Opetpp O.ppetpp 8.35eKO 5 Cr.51 O.ppet00 O.ppe+00 5.12e.03 3.34e 03 7.30e-04 6.50e 03 1.49e-pl 6 Kn 54 O.ppe+00 7.22et00 ~ 1.64e+00 O.ppe+00, 1.60e+00 O.ppe+00 2.65eKS 7 Hn-56 O.ppe+00 2.97e-pl 5.12e-02 D.ppe+00 2.55e-pl O.ppe+00 2.70e401 8 Fe.55 5.05e+00 3.26et00 8.71e-pl '.ppe+00 O.ppe+00 1.59eKN 4.14~1 9 Fe.59 1.12e+01 '.95~1 7;70eKN p.pp~ ~ O.ppe+00 5.77e+00 9.33eKN 10 co-58 '.ppe+00 '.31e+00 3.26e+00 D.Ops+00 O.ppe+M O.ppe+00 3.26eKS 11 Co-60 O.ppe+00 3.92e+00 9.26e+00 0 ~ ppeKS - O.ppe+00 O.ppe+00 9.33eKS 12 Hi-63 2.30e+02 1.42et01 7.99e+00 O.ppe+00 O.ppe+00 O.ppe+00 7.~1 13 Ni.65 1.71 a+00 1.93e.pl 8.78e-02 O.ppe+00 i O.ppe+00 O.ppe+00 1.47m%1 14 Cu.64 D.ppe+00 2.21e-pl 1.02e-pl D.ppe+8) 3.74e.pl O.ppe+00 4.54e+00 15 Zn.65 6.68e+00 2.29e+01 1 ~ 06 a+01 D.ppe+00 1.11e+Ol 0.00~0 1.93+41 16 Zn-69 3.39e-02 6.10e.02 4.54e.03 D.ppe+00 2.53e.02 O.ppe+00 4.97cKN 17 Br.83 O.ppe+00 O.Oped 1.32e-pl O.ppet00 O.ppe+00 O.ppe+00 O.ppcKS 18 Br-84 ~ O.ppe+00 O.ppet00 1.39e-pl O.ppe+00 O.ppet00 O.ppet00 O.Oped% 19 Br-85 O.ppe+00 O.ppe+00 7;04e-03 O.ppeKS O.ppe+00 O.ppe+00 O.ppeKS 20 Rb-86 O.ppe+00 6.17e+01 3;05e+01- O.ppe+00'.ppe+00 O.ppe+M 1.58e+00 21 Rb.88 O.ppe+00 1.81e-pl 9;91e-02 O.ppe+OO( O.Oped% O.ppeKS 1.7~1 22 Rb.89 O.ppe+00 '.04e-pl 7.15e 02 '.Ops+00 O.ppe+00 O.ppe+00 3.54~2 23 Sr-89 9.11e+02 O.ppe+00 2.61e+01 D.ppe+00 O.ppe+00 O.ppe+00 1.87e401 2C Sr.90 6.72~3 O.ppe+00 1.71 a+03 0.00et00 0.00~0 O.ppe+00 8.39at01 25 Sr-91 1.82et01 O.Opere 6.57e.pl O.ppe+00 O.ppe+00 O.ppet00 2.15~1 26 Sr-92 6.97e+00 O.ppe+00 2.59e.pl O.ppe+00 O.Cpa+00 O.ppe+00 7.51~'I '7 Y.90 3.15e-02 O.ppe+00 8.46e-04 O.Ops+00'.ppe+00 O.ppe+00 4.36et01 28 Y-91a 2.94e-04 O.ppe+00 1.00e-05 O.ppeKS . O.ppe+00 O.ppe+00 9.8pe-pl 29 Y.91 '.'lpe.pl O.Oped)0 1.09e-02 O.ppet00 O.ppe+M O.ppe+00 2.94et01 30 Y-92 2.78e-03 O.ppe+00 7.80e.05 O.ppet00 O.ppe+00 O.ppe+00 5.30m%1 31 Y-93 8.82e-03 O.ppe+00 2.40e-04 O.ppe+00 - O.ppe+00 O.ppe+00 6.97et01 32 Zr-95 . 7.CBe-02 1.82e-02 1.29e.02 O.ppe+00 1.96e-02 O.ppe+00 9.08et00 33 Zr-97 5.37e-03 9.22e-04 4.21e O.ppe+00- 9.29e-04 ~ O.ppe+00 5.~1 3C Nb-95 1.52e-02 6.28e-03 3.63e.03 O.Doe+00 4.50e-03 O.ppe+00 5.30m%0 35 Ko 99 O.ppe+00 1.23e+01 2.41e+00 O.ppe+00 1.84e+01 O.ppet00 4 ~ 07cKS 5-2d(1) Table 5-2c: Dose Factors for potable Mater pathvayt Haxiaua Hypothetical child (Page 2 of 2) Dose Factors: mrem-ft /Ci-sec Location: Danville Receiver/VARIABLE DILUTIOH Isotooe Bone Liver T. Body Thyroid GI LLI 36 Tc-99m 5.18e-04 1.02e-03 1.68e-02 0.00e+00 1.C8c-02 5.16e-04 5.78e-01 37 Tc-101 6.00e.04 6.28e.04 7.97e-03 0.00e+00 1.07e-02 3.32e-04 2.00e.03 38 Ru.103 4.10e-01 0.00e+00 1.580.01 0.00e+00 1.03e+00 0.00e+00 1.06ct01 39 Ru-105 3.62e.02 0.00e+00 1.31e.02 0.00e+00 3.18e-ol 0.00e+00 2.36et01 40 Ru 106 6.56e+00 0.00e+00 8.19e.01 0.00e+00 8.86e+00 0.00e+00 1.02et02 41 A -110m 3.02e-ol 2.04e-ol 1.63e-01 0.00e+00 3.80e-01 0 '0etM 2.43@41 42 Te 125m 6.40e+00 1.73et00 8.53e-01 1.80e+00 0.00e+00 0.00e+00 6.17eKS 43 Te.127m 1.62e+01 4.36e+00 1.92e+00 3.88e+00 4.62e+01 0.00e+00 1.31+%1 44 Te.127 2.64e.01 7.12e-02 5.67e.02 1.83e.01 7.520-01 0.00e+00 1.03')1 45 To~129m 2.73e+01 7.63e+00 4.24e+00 8.81e+00 8.02e+01 0.00e+00 3.33et01 46 Te-129 7.52e-02 2.10e-02 1.78e-02 5.36e-02 2.20e-01 0.00e+00 4.68eKS 47 Te-131m C.DCe+00 1.40e+00 1.49eHS 2.87e+00 1.35e+01 0.00e+00 5.67+41 Te 131 C.66e.02 1.C2e-02 1.39e-02 3.56e-02 1.41e-ol 0.00~0 2.45e-01 49 T0.132 5.67e+00 2.51e+00 3.03e+00 3.65e+00 2.33e+01 0.00e+00 2.52~1 50 I-130 1.64e+00 3.31e+00 1.71e+00 3.65e+02 4.95e+00 0.00e+00 1.55e+00 51 I -131 9.65e+00 9.71e+00 5.51e+00 3.21 a+03 1.59e+01 0.00e+00 8.64e 01 52 1-132 4.C9e-01 8.25c-ol 3.79e-01 3.83e+01 1.26e+00 0 ~ 00c+00 9.71e.ol 53 I.133 3.32e+00 4.11e+00 1 ~ 55e+00 7.63et02 6.84e+00 0.00et00 1.65ekS I.13C 2.35c.ol 4.36e-ol 2.01e-01 1.00e+01 6.68e-01 0.00e+00 2.S9e-01 55 I.135 9.82e.ol 1.77e+00 8.36e-ol 1.57e+02 2.71 a+00 0.00e+00 1.35e4$ 56 Cs-134 1.31e+02 2.15e+02 4.5C a+0'I 0.00e+M 6.68e+01 2.40e+01 1.16eKN 57 Cs-136 1.32et01 3.62e+Ol 2.34e+01 0.00e+00 1.93e+01 2.88e+00 1.27eKS . 58 Cs-137 1.83e+02 1.76e+02 2.59c+01 0.00e+00 5.72e+01 2.06e+01 1.10eKO t 59 Cs 138 1.28e-ol 1.78e-01 1.13e.01 0.00e+00 1.25e-01 1.35e-02 '.19e-02 60 Ba-139 2.32e-01 1.2Ce-04 6.73e-03 0.00et00 1.08e-04 7. 29e-05 1.34eo01 61 Ba-140 4.66e+01 4.08e.02 2.72e+00 0.00e+00 1.33e-02 2.43e-02 2.36et01 62 Ba-141 1.12c-ol 6.28e-05 3.65e-03 0.00e+00 5.44e-05. 3.69e-04 6.40e-02 63 Ba-142 4.90e-02 3.53e-05 2.74e-03 0.00e+00 2.86e-05 2.08c.05 '.40e La.1CO 5.67e-03 1.98e-03 6.68e-04 0.00e+00 0.00e+00 0.00e+00 5.52et01 65 La-142 2.94e-04 9.37e-05 2.93e-05 0.00ekS 0.00e+00 0.00et00 1.86ef01 Ce-141 2.23e.02 1.11e-02 1.65e-03 0.00e+00 4.87e-03 0.00e+00 1.39et01 67 Ce 1C3 3.92e.03 2.13e+00 3.08e-04 0.00e+00 8.92e-04 0.00e+00 3.11+%1 Ce-144 1.17e+00 3.66e.01 6.23e.02 0.00e+00 2.03c-ol 0.00e+M 9.54et01 69 Pr-143 2.20e-02 6.62e-03 1.09e.03 0.00e+00 3.58e-03 0.00e+00 2.38e%'1 70 Pr-144 7.2C@-05 2.24e-05 3.64e-06 0.00e+00 1.18e-05 0.00e+00 4.82e-02 71 Nd.147 1.57e-02 1.27c-02 9.82e-04 0.00e+M 6.96e-03 0.00c+00 2.01+41 M-187 2.41c-01 1.42e-01 6.40e-02 0.00eHS 0.00e+00 0.00e+00 2.00et01 Np-239 2.95e-03 2 ~ 1 le.04 1.49e-04 0.00e+00 6.11e-04 0.00e+00 1.57~1 5-2c(2) DAT Table 5-3 Radioactive Decay Constants Isotope Hsf(mfa Par(od Oacey ~ Haihdfe- Period Oaoey (S,M.H.D.Y) Constant (S.M.H,D,YI Constant (Hre 1) (Hral) 1, H.3 12.28 Y B.44o48 38 Ru-103 39>5 7.34e44 2 C.14 5730. Y 1.38e48 39 ~ Ru-10S 1.5de41 3 4 Na.24 P-32 Cr-51 15:" 14.29 ' 27.704 H 4.62a42 2.02a03 1.04e03 -'1 40' R 106 Ag-110m 42 " Te-125m 368% 58. 7.84e45 1.1de44 4.98e44 6 Mn-54 312.7 9.24a46 43 Ta-127m 109.- 2.65e44 7 Mn-SB 2.5785 H 2.68o41 44. Ta.127 7Ala42 8 Fa-66 2.7 2.93o46 45 Ta-129m 33.6 8.60o44 9 Fa59 BA7o44 46 Ta-129 B.dds44 10 Co.58 70.8 4.08o04 47 Te-131m 30. 2.31a02 11 Co BO 5.271 1.50o45 48 Ta-131 25. M l.dds+00 12 Ni-63 100.1 7.90o47 49 Ta-132 78>., H 8.8do03 13 Nhdd 2.52 H 2.75a01 SO S.dle42 14 Cu.64 12.701 5.46e42 51 I-131 8.04. 3.59e03 15 Zn.BS 244.4 ~ 0 1.18a44 52 h132 3.01aO'I 16 Zn.69 55.6 M 7.47a01- 53 (-133 20% H- 3.33o42 17 Br-83 2.39 H 2.90a01 54 I.134 7.89e41 18 Br.84 31.8 M 1.3'1 a+00 55 I-135 8.61 H. 1.05e41 19 Br-86 172: 8 1ASe+Ol 56 ~ 34 2.062 3.84e46 20 ~6"'8.66- D" 1.56o43 57 Cs-1 Ce-13d 13.16 2.19e43 21 Rb-88 178 M 2.33s+00 68 Cs-137 30.17 Y" 2.62o46 22 Rb.89 15!44<< M ~ 2.68a+00 59 Cs.138 1.28e+00 23 24 'r Sr 89 90" Sr-91 50.55 28.6'5 9.5 '6 D Y H 5.7'l e44 2.77a46 7.30o42 60" 61 62, Ba.139 Bo 140 Be.141 83.1 12.789 18N7 M-0 4.99e41 2.26a03 2.27s+00 Sr-92 2.71 H 2.56a41 . 63 Be.1 42 10.7 3.88o+00 27 Y-90 54.1 H ~ 1.08o42 84 ' La 140 1.72e42 28 Y.91m 49.71 8.35e41 65" La.142 96.4 = 4.36e41 29 Y-91 58.51 0 4.8~- dd- Ce-141 32M 8.89o04 30 31 Y-92 Y-93 10.'1 3.54 H'.8de41 8.86o42 67 Ca-143 33. 2.10e42 '2 68 Ce-144. 284> 1.02o44 Zr-96 64.02 D 4.51o44 69- Pr-143 13.56 2.13a03 33 Zr-87 16.9 H 4.10a02 70 -'r-144- '7.28 2AOe+00 34 Nb 95 35.06 D 8.24e44. 71 Nd.147 10.98 2.63e03 35 Mo-99 56.02 1.0Sa02 72 W-187 23345 2.9'la02 36 Tc.99m 5.02 1.15e41 73 Np-239 2.355 1.23a42 37 Tc-101 14.2 2.92e+00 5-3 Table 5-Zd: Dose Factors ior potable ilater pathwyt Haxlsua ilypothetical Infant (Page 2 of 2) Dose Factors: mrem-ft'/CI-sec Location: Danville ReceiverIVARIABLB OILUTIOM " Isotope Bone Liver T. 8 Th id L GI LLI Tc-99m 6.9?e-OC 1.44e.03 1.85e-02 0.00e+00 1.55e-02 7-51e-04 C.17e-01 37 Tc-101 8.2Ce-QC 1.OCe-03 1.03e-02 0.00e+00 1.23e-02 5.66e-04 1.76e-01 38 Ru-103 5.37e-ol 0.Doe+00 '.80e-01 '.ooeKS 1.12e+00 0.00e+00 6.53e+00 39 Ru-105 C.94e-02 0.00e+00 1.66e-02 0.00~ 3.63e-01 O.ooe+00 1.9~1 40 RIJ 106 8.75e>>00 0.00e+00 1.09e+00 0.00e+00 1.03e+01 0.00e+00 6.64et01 41 Ag-110m 3.62e-01 2.64e 01 1.75e-01 O.ooe+00 3.78e 01 o-ooe+00 1.3?et01 42 Te-125m 2.83eHN 1.1Ce+00 2.85e+00 O.OOe+00 0.00e+00 4.03aKS-43 Te-127m 2.12m%1 7.0Ce+00 2.5?@AS 6.13e+00 5.23&01 0.00crHR 8.5?F00 Te-127 3.63e 01 1.22e-01 7.80e-02 2.95e-01 8.86e-01 0.00e+00 7.62itgg. 45 Te-129m 3.63e>>01 1.25e+01 5.59eKN 1.39e+01 9.08eKl1 0.00e+00 Te-129 1.03e-ol 3.55e 02 2.41e-02 8.64e-o2 2.5?e-01 O.ooe+00 8.24e+00 47 Te-131m 5.52e+00 2 22e+00 1.83e+00 C.50e+00 1.53e+01 O.ooeKS 3.74+%1>> 48 Te-131 6.39e-02 '2.36e-02 1.79e-02 5.70e-02 1.63e-01 O.Doe+00 2.58eKOi-49 Te-132 7.55e+00 3.7C a+00 3.49e+00 5.52e+00 2.34et01 O.ooe+00 1.38et01>> '0 I -130 2.lee+00 1.92e+00 5.3?F02 5.26e+00 O.Doe+00 1.03eNO< 51 I 131 1.30e>>OI 1.5Ce+01 6.75~ S.OS~3 O.Doe+00 5.~1 52 I 132 6.03e-ol 1.2ze+00 4.36e 01 5.?Ca+01 1.36e+00 O.ooeKS 9.91e 01 53 I -133 4.54eKS 6.61e+00 1.93eKS 1.20e+03 7.7?F00 O.ooe+00 1.12et00>>.. 54 1-134 3.15e-01 6.46e-01 2.30e-01 1.51et01 7.22e-01 O.ooe+00 6.~1i 55 I.135 1.3ze+00 2.63e+00 9.58e-01 2.36e+02 2.93eKS O.ooeHN 9.51e&1'6 Cs-134 1.3?eeZ 2.55~2 Z.see%1 0.'OOeKS 6.5?ee1 2.69~1 6.93~1 57 Cs-136 1.6?A<01 4.90et01 58 Cs-137 1.89et02 2.22ct02 1.5?et01 0.00et00 . 5.95et01 2.41et01 6.93~1 59 Cs 138 1.75~1 2.8Ce 01 1.38e&1 . 0.00e+00 1.C2e-01 2.21e-02 4.54w01 60 Ba 139 3.20~1 2.12e-04 9.26e-03 '0.00ehN 1.2?e-04 = 1.29e-04 2.03e41'1 Ba-140 6.21~1 6.21e-02 3.20e+00 O.Doe+00 1.C7e-02 3.81e-02 1.52at01'-. 62 Ba-141 1.54e-01 1.06e-04 4.86e-03 0.00eKO 6.35e-05 6.43e-os 1.88eo00>>>> 63 Ba-142 6.~2 5.55e-05 3.29e-03 O.ooe+00 3.20e-os 3 36e-05 2.7~1'" 64 La-140 7.~ 3.02e&3 7.7?e-04 O.ooe+00 O.OOa+00 O.ooe+00 3.55t+01 65 La-142 3.99~ 1.47e 3.51e-os 0.00e+00 0.00e+00 O.ooe+00 2.49~1 66 Ce.141 2.86e-02 1.74e 02 2.05e-03 0.00e+00 5.3?e-03 O.ooe+00 9.00eKS:t 67 C@-143 5.3?e-03 3.56eKS 4.07e-04 O.ooe+00 1.04e-03 O.ooeKO 2.08etP1 ~ Ce-144 1.08et00 4.43e-01 6.06e-02 0.00~ 1.79e-01 O.ooe+00 6.21at01~'.46e-03 69 Pr-143 2.95~2 1.10e-02 0.00ehN 4.10e-03 O.ooe+00 1.56e41-70 Pr-144 3.85e-os 5.01e-06 O.ooe+00 1.39e-os O.ooe+00 1.79eKO:= 71 Nd.147 2.01e-oz 2.06e-02 1.26e-03 0.00eKS 7.95e-03 0.00e+M 1.31')1-72 M.187 3.28e-01 2.28e 01  ?.eee-02 0.00eKS 0.00eKS O.ooeKN 1.34et01 ~ Np-239 4.03e-o3 3.60e-04 2.0Ce-04 O.ooe+00 7.19e-oC O.ooe+00 1.~$ " 5-2d(2) I DATE Table 5-4 (Page 1 of 2) Dilution Factors and Transit Times'for SSES Effluents to Danville, Pa RIVER DEPTH RIVER DEPTH RIVER LEADING, NEAS. AT ENV. LAB HEAS. 'AT HCR DISCHARGE EDGE ILUTION FEET) ( INCHES) (CFS) (HOURS) FACTOR 1.5 144 500 68.7 136.4 1.6 145 530 67.8 140.1 1.8 '48 600 '66.3 147.3 150 670 64.8 155.5 2.2 152 730 63.3 164. 5 2.4 155 780 61.8 173.9 2.5* 156* 825* 61.1* 179.1* 2.6 157 870 60.3 184.5 2.8 160 930 58.8 195.7 162 1000 57.2 208.3 3.2 164 1200 52.7 250.6 3.4 167 1400 48.2 291.5 3 5* 168* 1500* 45.9* 280.9* 3.6 169 1600 43.5 271.0 3.8 172 1800 39.0 250.6 4, 174 2000 35. 5 250.6 4.2 176 2280 35.2 254.5 179 2560 34.7 259.1 4 5* 180* 2730* 34 5* 261.4* 4.6 181 2900 '34.2 263.9 4.8 184 3300 33.7 270.3 186 3700 33.0 '77.8 5.2 - 188 4140 32.3 284.1 5.4 191 4580 31.7 292.4 . 192* 4820* 31.4* 297.2* 5.6 193 5060 31.0 302.1 5.8 196 5580 30.2 312.5 6 198 6100 29.5 323.6 6.2 200 6780 28.5 339.0 6.4 203 7460 27.5 354.6 5* 204* 7890* 26.9* 366.3* 6.6 205 8320 26.2 378.8

• Interpolated value 5-4(l)

Table 5-4 (Page 2 of 2) Dilution Factors and Transit Times for SSES Effluents to Danville, RIVER DEPTH RIVER DEPTH RIVER LEADING HEAS. AT ENV. LAB HEAS. AT HCR DISCHARGE EDGE DILUTION FEET ( INCHES) CFS HOURS) FACTOR 6.8 208 9360 24.7 413.2 '10 10400 23.0 456.6 7.5 216 12500 20.0 588.2 222 14900 16.5 869.6 8.5 228 17500 15.3 980.4 234 20700 14.7 1071.8 9.5 240 24000 14.2 1173.7 10 246 27000 13.5 1285.3 10.5 252 30100 13.0 1373.6 258 34570 12.2 1567.4 11.5 264 38730 11.3 1795.3 12 270 42530 10.7 2057.6 12.5 276 46490 10.0 2398.1 13 282 50630 10.0 2597.4 13.5 288 54940 10.0 2832.9 294 59430 9.8 3067.5 14.5 300 64090 9.8 3311.3 15 306 68930 9.8 3558.7 15.5* 312* 74030* 9 8* 3802.3* 16 318 79130 9.8 4081.6 16.5* 324* 84580* 9 8* 4347.8* 17 330 90030 9.7 4651.2 17.5* 336* 95830* 9 7* 4926.1* 18 342 101630 9.7 5235.6 18.5* 348* 107780* 9 7* 5540.2* 19 354 113930 9.7 5882.4 19.5* 360* 120430* 9.6* 6192.0* 20 366 126930 9.5 6535.9 20.5* 372* 133780* 9 5* 6872.9* 21 378 140630 9.5 7246.4 21.5* 384* 147830* 9 4* 7604.6* 22 390 155030 9.3 8000.0

• Interpolated value 5-4(2)

Table 5-5: Dose Factors for Shore Exposure Pathway, All Age Groups (Page I of 2) Dose Factor Units: mrem-ft /Ci-sec Location: Edge of Initial Mixing Zone/FIXED DILUTION Dilution (1/No:SHORE) ~ 15.9 Transit time (ts) hrs ~ Sediment deo. time (tb) hrs ~ 131400 ADULT TEEN CHILD Usage 12 67 (Uao)(hr/ r) ~ Isot T. B Skin T. B Skin T- 8 Skin 8-3 0.00eKS 0.000%0 0.00e+00 0.000+00 '.00e+00 C-14 '.00e+00 0.000+00 0.00e+00 0.00e+00 0.00et00 0.00e+00 0.00e+00 Na-24 2.480.04 2.87e-04 1.380-03 1.600-03 '.890-04 3.350-04 P-32 0.00e+00 0.00e+00 0.00eHS 0.00e+00 0.000+00 0.000+00 Cr-51 1.010-04 1.19e-04 '.640-04 6.67e-04 1.180.04 - 1.390-04 . '6 Hn-54 3.0le.02 3.53e.02 1.680 01 1.970.01 3.51e-02 4.12e-02 Mn 56 1.50e-05 1.77e-05 8.370-05 9.90e-05 1.75e-05 2.07e-05 Fe-55 0.00e+00 0.00e+00 ~ 0.000+00 0.00e+00 0.000+00 0.00e+00 Fe 59 5.92e-03 6.96e 03 3.31e-02 3.89e-02 6.91e-03 8.12e-03 10 Co-58 8.230-03 9.64e-03 4.59e.02 5.38e-02 9.600-03 1.12e-02 Co-60 4.680-01 5.500.01 2.61w00 3.07e+00 5.45e.01 6.C20-01 12 Ni.63 0.00e+00 0.00e+00 0.00e+00 O.OOMOO 0.00e+00 0.00eKO 13 Ni-65, 4.90e-06 5.69e-06 2.74e-05 3.18e-05 5.72e-06 6.640-06 14 Cu-64 1.25e-05 1.41e-05 6.970.05 7.900-05 1.460-05 1.65e-05 15 Zn-65 1.620-02 1.87e-02 9.060.02 1.0Ce-01 1.89e-02 2.18e-02 16 Zn-69 0.00e+00 0.00e+00 0.00eKS 0.00e+00 0.00e+00 0.000+00 17 Br-83 7.92e-08 1.150-07 4.420-07 '.420-07 9.2Ce-08 1.340-07 18 Br-84 1.200-06 1.39e-06 6.670-06 7.790-06 1.39e-06 1.63e-06 19 Br 85 0.000+00 0.00e+00 0.00e+00 0.00et00 0.00e+00 0.00et00 20 Rb-86 1.95e-04 2.23e.04 - 1.090 03 1.240-03 2.27e-04 ~ 2.600-04 21 Rb.88 6.99e-08 7.99e-08 3.90e<<07 4.460-07 8.16e-08 9.32e-08 22 Rb-89 1.82e.07 2.18e.07 1.020.06 1.22e.06 2.12e.07 2.55e-07 23 Sr-89 4.700-07 5.450.07 2.62e-06 3.040 06 5.480 07 6.36e.07 24 - Sr-91 C.34e-05 5.07e-05 2.420-04 2.83e-04 5.06e-05 5.92e-05 25 Sr-92 1.310.05 1.45e-05 7.290 05 8.11e-05 1.52e-05 1.690-05 26 Y-90 9.65e-08 1.14e-07 5.39e-07 6.370.07 1.130.07 1.33e.07 Y-91m 9 470-07 1.10e 06 5.29e-06 6.12e-06 1.10e-06 1.28e-06 28 29 Y.91 Y.92 '.330-05 3.22e-06 2.620 05 3.830-06 1.300-04 1.800-05 1.460-04 2.14e-05 - 2.72e-05 3.760-06 3.06e-05 4.46e-06 30 Y-93 3.72e-06 5.09e-06 2.080 05 2.84e-05 4.3C0-06 5.940-06 31 Zr-95 5.310.03 6.160-03 2.97e-02 3.C4e-02 '.200-03<<7.190-03 32 Zr-97 6.17e.05 7.180-05 3.45e-04 4.01e-04 7.20e-05 8.38e-05 33 Nb-95 2.97e-03 3.490-03 1.660-02 1.950-02 3.460-03 4.070.03 34 No-99 8.590.05 9.94e-05 4.79e.04 5.55e-04 1.00e-04 1.160-04 5-5(l) Table 5-5: Dose Factors for Shore Exposure Pathway, All Age Groups (Page 2 of 2) Dose Factor Units: mrem-ft /Ci-sec Location: Edge of Initial Mixing Zone/FIXED DILUTION ADULT TEEN CHlLD lsoto T. Body Skin T. Body Skin T. Body Skin 35 Tc-99m 3.56e-06 4.08e-06 1.99e-05 2.28e-05 4.16c-06 4.76e-06 36 Tc-101 '2.38e-08 2.65e-08 1.33e-07 1.48e-07 2.78c-08 3.09c-08 37 Ru-103 2.35e-03 2.74c-03 1.31c.02 1.53e-02 2.74e-03 3.20e-03 38 Ru.105 1.18e-05 1.34e-05 6.60c-05 7.48e-05 1.38e-05 1.56c.05 39 RU-106 9.17c 03 1.10e.02 5.12e.02 6.14e-02 1.07e-02 1.28c-02 40 A -110m 7.47e 02 8.71e-02 4.17e 01 4.86e-01 8.71c-02 1.02c-01 41 Tc-125(a 3.37e-05 4.62c.05 1.88e-04 2.58e-04 3.93e-05 5.39e.05 42 Tc-127m 1.99e-06 2.35e-06 1.11e 05 1.31e-05 2.32e-06 2.74e-06 43 Te-127 6.01e 08 6.61c-08 3.35e-07 3.69e-07 7.01e-08 7.71e-08 44 Tc-12%a 4.29c 5.02c 04 2.40e-03 .-'2.80e-03 5.01e 5.85e-04 45 T@-129 3.14e-07 3.72e-07 1.76e-06 2.08e-06 3.67e-07 4.34e-07 46 ~ Tc-131m 1.70e 2.01e-04 9.51e-04 -- 1.12e.03 1.99e-04 2.34e-04 ~ 47 Tc-131 1.21e 07 1.43c-04 6.74c-07 7.97e-04 1.41e-07 1.67c-04 48 Tc-132 9.12c.05 1.07e-04 5.'09e-04 - 5.99e-04 - '1.06c-04 1.25e-04 49 1.130 1.'l3e.04 1.37c.04 6.32e 04 7.67e.04 1.32e.04 = 1.60c-04 50 1-131 3.72c-04 4.52e-04 2.08c-03 . 2.53e-03 4.35e-04 5.28c-04 51 1.132 2.00e-05 2.35e.05 1.12e-04 1.31e-04 2.33e-05 2.75e-05 52 1.133 5.15e-05 6.26e.05 2.88e-04 - 3.50e-04 6.01e-05 7.31e-05 53 1.134 4.42e-06 5.25c-06 2 47e-05 2.93e-05 5.15e-06 6.12e-06 54 1-135. 4.94e 05 5.76e-05 2.76e-04. 3.22e 5.76e-05 6.73e-05 55 Cs-134 .. 1.49e-01 "'1.74e-01 8.32c-ol 9.70e-01 1.74e-01 2.03c-01 56 Cs-136 3.27e-03 3.71c-03 1.83e-02 2.07e-02 3.82e.03 4.32e.03 57 Cs-137 2 24c 01 2.61e-01 1.25 a+00 1.46e+00 2.61e-01 3.05e-01 58 Cs-138 2.15c-06 2.46e-06 1.20e-05 1.37e-05 2.51e-06 2.87c-06 59 Ba-139 1.40c 06 1.57e-06 7.81e-06 8.78e-06 1.63e-06 1.84e-06 4 45c-04 5.08c-04 ' 2.84e-03 5.19e-04 5.93e-04 60 Ba<<140 . 2.48e<3 61 Ba-141 9.36e.08 1.07e-07 5.23e-07 5.96e-07 1.09e-07 1.24e-07 62 63 Ba-142 La-140 2.02e-08 4.10e-04 2.30e-08 4.65e-04 - 1.13e-07 2.29c-03 1.28e-07 2.60e-03 '.2.36e-08, 79e 2.68e-08 5 '2e-04 64 La-142 1.07e-05 1.28e-05 5.97e.05 7.17e-05 1.25e-05 1.50e-05 65 Cc-141 2.97e-04 3.34e-04 ~ 1.66e.03 1.87e-03 3.46e 04 . 3.90e 04 66 Ce.143 4.92e-05 5.59r05 2.75c 04

• 3.12e-04 5.74e-05 6.52e.05 67 Ce-144 1.51e-03 1.75c-03 8.43e-03 9.75e-03 1.76e 03 2.04e-03 68 Pr-143 0.00e+00 0.00et00 0.00c+00 0.00e+00 0.00e+OO 0.00e+N 69 Pr-144 3.62e-09 4.16e.09 2.02e-08 2.32c-08 4.22e-09 4.85e-09 70 Nd-147 1.82e 04 2.18e.04 1.02e-03 1.22e-03 2.12e-04 2.55e-04 71 V-187 4.96e 05 5.76c-05 2.77e-04 3.22e-04 5.79e-05 6.73c-05 72 Np-239 3.67c 05 4.25e-05 2.05e-04 2.37e-04. 4.28e-05 4.96e-05 5-5(2)

Table 5-6a: Composite Dose Factors: Maximum Hypothetical Adult (Page I of 2) Dose Factor Units: mrem/Ci Released cation: Danville (Mater Ing.)/Outfall (Fish 5. Shoreline)/FIXED DILUTION Usage (Uao) (kg/ r:FISH) ~ 21 Usage (Ua ) (kg/ r:MATER) a 730 Usage (Uao) (hr/yr:SHORE) ~ 12 Oilution (1/HO(SHORE) ~ 15.9 Oiiution (1/N TFlSH) a 15.9 Oilution (1/N:MATER) ~ 321 Transit time (FlSH) hrs ~ 25 Transit time (MATER) hrs a 25.8 Transit time (SHORE) hrs ~ Transit time (SE01NENT) hrs ~ 131400 tsotope Liver T. Body Thyroid Kidney Gt-LLl Skin H-3 0.00e+00 3 ~ 59e-05. 3 '9e-05 3.59e.05 3.59e-05 3.59e-05 3.59e-05 0.00e+00 C.14 1.70e+00 3.C1e.01 3.Cle-01 3.41e.ol 3.Cle-01 3.C1e-ol 3.4'le-Ol 0.00@+00 Na-24 7.09e-03 7.09e-03 7.12e.03 7.09e-03 7.09e-03 7.09e-03 7.09e 03 2.5%@05 P.32 2.39~3 1.49e+02 9.24e+01 0.00e+00 0.00ct00 0.00e+00 2.69e+02 0.00e+00 Cr-51 0.00e+00 0.00e+00 7.72e-05 4.07e.05 1.50e 05 9.0Ce-05 1.71e-02 1.07e~ Hn-54 0.00e+00 2.39e-01 4.82e-02 0.00e+00 7.10e-02 0.00e+00 7.31e-01 3.17e-03 Kn-56 0.00eKS 7.25e-06 2.63e-06 0.00e+00 9.21e-06 0.00e+00 2.31e.04 1.59~ Fe-55 3.64e-02 2.52c-02 5.87e-03 0.00e+00 0.00e+00 1.40e-02 1.CCe-02 0.00eKN Fe-59 5.66e-02 1.33c-01 5.15e-02 0.00e+00 0.00et00 3.72e-02 4.43e-01 6.24e 04 " 10 Co-58 0.00e+00 4.97e-03 1. 19e.02 0.00et00 ~ 0. 00e+00 0.00e+00 1.01e-01 8.64e Co-60 0.00e+00 1.44e-02 7.37c.02 0.00e+00 0.00e+00 0.00e+00 2.71e.01 4.93e-02 12 Hi-63 1.72e+00 1.19e-01 5.78c.02 0.00e+00 0.00e+00 0.00e+00 2.49e-02 0.00e+00 13 Ni-65 7.20e.06 9.35e.07 8.66e.07 0.00e+00 0.00e+00 0.00e+00 2.37e.05 5.11e.07 14 Cu-64 0.00e+00 1.C3e-04 6.84e.05 0.00e+00 3.61e.04 ~ 0.00e+00 1.22e-02 1.27e-06 15 Zn-65 1.26e+00 4.00e+00 1.81e+00 0.00e+00 2.68et00 0.00e+00 2.52e+00 1.67e-03 16 Zn-69 2.11e-11 4.03c-11 2.80e-12 0.00e+00 2.62e-11 0.00e+00 6.06c-12 0.00e400 17 Br-83 0.00e+00 0.00e+00 1.57e-06 0.00e+00 0.00e+00 0.00e+00 2.26e.06 1.03e-08 18 Br 84 0.00e+00 0.00e+00 1 07 07 0 00e+00 0 00e+00 0 00e+00 1.51e-22 1.25K)7 19 Br-85 0.00ekR << 0.00e+00 0 ~ 00et00 0.00e+00 0.00e+00 0.00e+00 0.00e+00 0.00eKS 20 Rb-86 . 0.00e+00 '.29e+00 2.47e+00 0.00~ 0.00e+00 0.00e+M 1 ~ 04e+00 2.0~ 21 Rb-88 0.00e+00 0.00e+00 6.27e.09 0.00e+00 0.00e+00 0.00e+00 0.00e+M 7.17~ 22 Rb.89 0.00e+00 0.00eHS 1.63e-08 0.00eKS 0.00e+00 0.00e+00 0.00e+00 1.9~ Sr-89 1.25e+00 0.00c+00 3.60e.02 0.00e+00 0.00e+00 0.00e+00 2.01e-01 4.89~ 24 Sr-90 3.13e+01 0 ~ 00e+00 7.69wM 0.00e+00 0.00e+00 0.00e+00 9.05e.01 0.00a+00 25 Sr-91 3.77e-03 0.00e+00 1.56e.04 0.00e+00 0.00e+00 0.00e+00 1.80e.02 4.55e 06 26 Sr-92 1.47e.05 0.00e+00 1.81e 0.00e+00 0.00c+00 0.00~0 2.91c-04 . 1.30e-06 27 Y-90 2.55c.05 0.00e+00 6.94e-07 0 ~ 00 a+00 0.00et00 0.00e+00 2.71e.01 1.02e 08 28 Y-91m 2.64e-16 0.00et00 8.49e-08 0.00e+00 0.00e+00 0.00e+00 7.74e-16 9.83HS 29 Y.91 4.85e 04 0.00e+00 1. 51e.05 0.00e+00 0.00e+M 0. 00e+00 2.67e.01 2.35e~ 30 Y-92 2.18e.08 '.00e+00 2.90c-07 0.00e+00 0.00e+00 0.00e+00 3.82c 3 43e&7 31 Y.93 1.67e-06 0.00e+00 3.80e.07 0.00eKS 0.00e+00 0.00e+00 5.30e-02 4.5&@07 Zr-95 1.97e.05 6.31e-06 4.81e.04 9.90e-06 0.00e+00 2.00e-02 5.53e~ 32 33 Zr-97 3.90e-07 7.87c.08 5 '7e-06 0.00e+00 0.00e+00 1.19e 07 0.00e+00 2.C4e.02 6.~ 3.13e~- 34 Nb-95 2.38c 02 1.33c.02 '.39e-03 0.00e+00 1.31e.02 0.00e+00 8.04+41 5-6a(1) k'V OAT Ic Table 5-'6a: Composite Dose Factors: Haximum Hypothetical Adult (Page 2 of 2) Dose Factor Units: mrem/Ci Released Location: Danville (Water Ing.)/Outfall (Fish E Shoreline)/FIXED DILUTION tsoeo Bone Liver T~ B Th roid L'1 dneV Lune GI-LLI Skin 35 No-99 0.00e+00 5.06e.03 9.70e-04 0.00e+00 1.15c.02 0.00e+00 1.17e-02 8.92e-06 36 Tc-99m 3.00e-08 8.47e-08 1.40e.06 0.00w00 1.29e.06 4.15e-08 5.01e-05 3.~7 37 Tc-101 0.00e+00 0.00e+00 2.14e-09 0.00e+00 0.00e+00 0.00e+00 0.00eKS 2.37e-09 38 Ru.103 2.77e-04 0.00et00 3.30e.04 0.00et00 1.06e.03 0.00e+00 3.24e-02 2.46e-OC-39 Ru-105 C.67e-07 0.00e+00 1.24e-06 0.00eKN 6.03e-06 0.00e+00 2.85e-04 1.20e-06 40 RU-106 4.19e-03 0.00e+00 1.35e-03 0.00e+00 8.09e.03 0.00e+00 2.71e-01 9.87~- 41 A -110m 8.36e.05 7.73e-05 6.74e.03 0.00e+00 1.52e-04 0.00e+00 3.16e-02 42 Te-125m 1.39e-01 5.02e-02 1.86e-02 4.17c-02 5.63e-01 0.00e+00 5.53e-01 1.26e-ol 4.29c-02 9.00e-02 0.00e+00 1.18e+00 2.11~7 C3 44 Te-127m Te-127 3.52e-01 9.02e-04 3.24e-04 1.95e 6.68e-04 1.43e+00 3.67e-03 0.00e+00 7.12e-02 2.97e+00 5.~ C5 Te-129m 5.89e-01 2.20e-01 9.33e-02, 2.02e.ol 2.46e+00 0.00e+00 46 Te-129 1.61e-03 6.05e-04 4.27e-04 1.23e-03 6.76e.03 0.00e+00 1.21e-03 47 Te-131m 5.08e-02 2.C9e-02 2.07e.02 3.9Ce-02 2.52e-01 0.00e+00 2.47e+00 '.2$ 48 Te-131 9.69e-22 4.05e-22 1.08e.08 7.97c-22 '.24e-21 0.00et00 1.37e-22 H5 49 Te-132 1.06e.01 6.84e-02 6.42e-02 7.55e-02 6.58c.01 0.00e+00 3.23e+00 9.62~ . 50 1-130 4.04e-04 1.19e-03 4.80e-04 . 1.01e.ol 1.86e-03 0.00e+00 1.02e.03 51 1-131 8.28c-03 1.18e.02 6.82e-03 3.88e+00 2.03e-02 0.00e+00 3.13e-03 52 1.132 2.31e.07 6.18e-07 2.01e-06 2.16e.05 9.850.07 0.00e+00 1.16e 07 2.11e~ ~ I '3 1-133 1.34e.03 2.33e.03 7.16e.04 3.43c-ol 4.07e-03 0.00e+00 2.10e-03 54 1-134 5.95e-13 1.62e-12 3.96e 07 2.80e-11 2.57e-12 0.00e+00 1.41e-15 4.~7 55 1-135 6.96e-05 1.82e-04 '7.17e.05 1.20e-02 2.92e-04 0.00e+00 2.06e-04 5.17~ ~ 56 Cs 134 ~ 1.62e+Ol 3.86et01 3.15e+01 0.00e+00 1.25m%1 4.14e+00 6.75e-01 57 Cs 136 1.61 F00 6.35c+00 4.57e+00 0.00e+00 3.53e+00 4.84e-01 7.21e-01 3.32e44-58 Cs-137 2.~1 2.84e+01 1.86etO'l 0.00e+00 ~ 9.65e+00 3.21e+00 5.50e-01 59 Cs-138 1.46e-16 2.87e-16 1.93c-07 0.00e+00 2.11e-16 2.09e-17 1.23e-21 2.21~7 60 Ba 139 2.46e '10 1.75e-13 1.25e-07 0.00+%0 1.64e-13 9.94e-14 C.36e-10 1.41~7 61 Ba 140 1.43e-02 1.80e-05 9.77e-04 0.00eKN 6.11e.06 1.03e-05 2.94e-02 8.39e-09 0.00e+00 0.00e+00 62 63 Ba 141 Ba 142 0.00c+00 0.00e+00 0.00e+00 0.00ekS 1.81e-09 0.00e+00 0.00e+00 0.00e+00 0.00eHS 0.00e+00 0.00eHS 2.~ -* 64 La-'140 5.65e-06 2.85e-06, 3.75e-05 0.00e+00 0.00e+00 0.00e+00 2.09e-01 65 LG-142 8.26c-12 3.76e-12 9.60e-07 0.00e+00 0.00e+00 0.00e+00 2.74e-08 66 Ce-141 3.25e-06 2.19e-06 2.68e-05 0.00eHN 1.02e-06 0.00e+00 8.39e.03 67 Ce-143 3.42c.07 2.53e-04 4.44e-06 0.00e+00 1.11c-07 0.00e+00 9.46e-03 5.01~ i 68 Ce-144 1.73e-04 7.22e-05 1.45e.OCi 0.00e+00 4.28e-05 0.00e+00 5.84e-02 1.57~-- 69 Pr-143 3.04e-05 1.22e-05 1.51e 06 0.00e+00 7.03e-06 0.00e+00 1.33e-01 0.00eKO 70 Pr-144. 0.00eKO 0.00e+00 3.24e-10 0.00e+00 0.00e+00 0.00e+00 0.00e+00 3.73e-10 71 Nd.147 2.05e-05 2.37e-05 1.77e 05 0.00e+00 1.39e-05 0.00e+00 1.14e-01 1.9~- 72 ll-187 7.79e-03 6.52e.03 2.28e-03 0.00c+00 0.00e+00 0.00e+00 2.13e+00 73 Np-239 1.34e-06 1.31e-07 3.36e-06 0.00eKN 4.10e-07 0.00e+00 2.'69e-02 5-6a(2) Table 5-6b: Composite Dose Factors: Maximum Hypothetical Teen (Page 1 of 2) Dose Factor Units: mrem/Ci Released Location: Danville (Mater Ing.)/Outfall (Fish & Shoreline)/FIXED DILUTION Usage (Ua ) (kg/ r:FlSH) a 16 Usage (Ua ) (kg/ r:MATER) < 510 Usage (Ua ) (hr/ r:SHORE) > 67 Dilution (1/No:SHORE) ~ 15.9 Oilution (1/K:FISH) ~ 15.9" Oilution (1/No:MATER) ~ 321 Transit time (FlSH) hrs

• 25 Transit time (MATER) hrs e 25.8 Transit time (SHORE) hrs ~ Transit time (SEOlNENT) hrs ~ 131COO isotone Liver T. Sody Thyroid Gl-LLl Skin H-3 0.00+40 2.61e-05 2.61e.05 2.61e-05 2.61e-05 2.61e.05 2.61e-05 O.ooe+00 2 C-14 1.85e+00 3.71e-ol 3.71e-ol 3.7le-ol 3.71e-ol 3.71e-ol 3.71e-ol O.ooe+00 3 Na-24 7.30e-03 7.30e-03 7.43e-03 7.30e-03 7.30e-03 7.30e-03 7.30e-03 1.C4e 04 4 P-32 2.61et03 1.61e+02 1.01e+02 O.ooet00 O.ooe+00 O.ooe+00 2.19e+02 O.ooeKS 5 Cr-51 O.ooe+00 O.ooe+00 1.21e-04 3.90e-05 1.54c-05 1.00e-04 1 ~ 18e-02 5.98e 05 6 Nn-54 O.ooe+00 2.35e-ol 6.16e-02 O.ooc+00 7.00e-02 O.Goo+00 4.81e.ol 1.77e-02 7 Nn-56 O.ooe+00 7.59c-06 8.86e-06 O.ooe+00 9.61e-06 O.ooe+00 5.00e.04 8.88e-06 S Fe-55 3.81e-02 2.70e-02 6.30e-03 O.ooe+00 O.Goo+00 1.71e.02 1.17e-02 O.ooeKN 9 Fe-59 5.82e.02 1.36e-ol 5.55e-02 O.ooe+00 O.ooe+00 4.29e 02 3.21e-ol 3.49e 03 10 Co-58 O.ooe+00- C.93e-03 1.55e-02 O.Goo+00 O.ooe+00 0 ~ Ooe+00 6.79e-02 4.82e 03 11 Co-60 O.ooe+00 1.CCc-02 2.67e-ol O.ooe+00 O.ooe+00 O.ooe+00 1.87e.ol 2.75e 01 12 Ni.63 1.78et00 1.26e.ol 6.05e-02 O.ooetoo O.ooe+00 O.ooe+00 2.01e-02 O.MeKN 13 Ni.65 7.77e-06 9.93e-07 2.91e.06 O.ooet00 O.ooe+00 O.ooe+00 5.38e-05 2.85e 06 14 Cu.64 O.ooe+00 1.50e-04 7.69e-05 O.ooe+00 3.Soe-04 O.ooeHS 1.17e-02 7.08e 06 15 Zn-65 1.14e+00 3.96e+00 1.86e+00 O.ooc+00 2.5C a+00 O.ooe+00 1.68e+00 9.35e-03 16 Zn-69 2.29e-ll C.3Te-ll 3.06e-12 O.ooe+00 2.85e-ll O.Goo+00 8.05e 11 0.00eKS 17 Br-83 O.ooe+00 O.ooe+00 1.74e-06 O.ooe+00 O.ooe+00 O.ooe+00 O.ooe+00 5.76e-08 18 Br-84 O.ooe+00 O.ooe+00 5.99e-07 0 ~ Oo a+00 O.ooe+00 O.ooc+00 O.ooe+00 6.9~7 19 Sr-85 0 ~ Ooe+00 O.ooe+M O.ooet00 O.ooe+00 O.ooe+00 O.oocKS O.ooet00 O.Goer 20 Rb.86 O.ooe+00 5.70e+00 2.68eKS O.ooe+00 O.ooe+00 O.Goo+00 8.43e.ol 1.12e 04 21 Rb.88 O.ooe+M O.ooe+00 3.50e-08 O.ooeKN O.ooe+00 '.ooe+00 O.ooe+00 4.00e-08 22 Rb 89 O.ooe+00 O.ooe40 9.11e-08 O.ooe+00 O.ooe+00 O.ooe+M O.ooe+00 1.09e 07 23 Sr-89 1.36e+00 0.00e+00 3.89e-02 O.Go+40 O.ooeHS O.ooe+00 1.62e.ol 2.73e-'07 24 Sr-90 2.60e+Ol O.ooe+M 6.43e+00 O.ooe+00 O.ooe+00 O.ooe+00 7.30e.ol O.ooe+00 25 Sr-91 4.07e-03 0.00+AN 1.84e-04 O.ooe+00 O.ooe+00 O.ooe+00 1.85e-02 2.54e-05 26 Sr.92 1.58e 05 O.ooe+00 7.22e-06 O.ooetoo O.ooe+00 O.ooe+00 4.03e.04 .

7.27e-06 27 Y.90 2.76e.05 O.ooe+00 7.91e.07 0 ~ Ooe+00 O.ooe+00 O.ooe+00 2.27e-ol 5.71e-08 28 Y-91m 2.84e-16 O.ooe+00 4.74e-07 0.00&00 O.ooe+00 O.ooc+00 1.34e-14 5.49e-07 29 Y.91 5.24e-04 O.ooe+00 2.57e.05 O.ooe+00 O.ooe+00 O.ooeKN 2.15e.ol 1.31e-05 30 Y.92 2.37e-08 1.61c-06 O.ooetoo O.ooe+00 O.ooe+00 6.50e-04: 1.92e-06 '.ooe+00 - 31 Y-93 1.81e-O6 0.00~OO 1.9le-06 O.ooe+M 0.00mO 0.00eue 5.53e-02 2.55e-06 32 Zr.95 1.97e-05 6.23e.06 2.66e-03 O.Goo+00 9.15e.06 O.ooe+00 1.4Ce-02 3.09~ 33 Zr-97 4.07e-07 8.06e.08 3.09e-05 O.ooe+00 1 ~ 22e.07 O.ooe+00 2.18e-02 3.60e 05 34 Nb.95 2.40e-02 1.33e-02 8.81e-03 O.ooe+00 1.29e-02 O.ooe+00 5.69et01 1.75e-03 5-6b(1) Table 5-6b: Composite Dose Factors: Maximum Hypothetical Teen (Page 2 of 2) Oose Factor Units: mrem/Ci Released Location: Danville (Water Ing.)/Outfall (Fish 5 Shoreline)/FIXED DILUTION-Isotone Bone ~ Liver T. Body Th id K1dney Lmy GI-LL1 Bk1n 35 Ho-99 0.00e+00 5.33e-03 1.06e-03 0.00e+00 1.22e-02 0.00e+00 9.54c-03 4.98e-05 36 Tc-99m 3.05e-08 8.50e-08 2.89e-06 0.00e+M 1.27e-06 4.72c-08 5 '8e-05 2.04e-06 37 Tc.101 0.00e+00 0.00e+00 1.19e-08 0.00e+00 0.00e+00 0.00e+00 0.00c+00 1.33c-08 38 Ru-103 2.88e-04 0.00~0 1.30e.03 0.00e+00 1.01e-03 0.00e+00 2.40e-02 1.37e.03 39 Ru 105 4.98e-07 0.00e+00 6. 11e 0.00e+00 6.28e-06 0.00e+00 4.02e-04 6.71e-06 40 RU 106 4.50e-03 0.00c+00 5.16e-03 0.00e+00 = = 8.67e.03 0.00c+00 2.16e-01 5.51e-03 AB-110m 7.87e-05 7.CSe-05 3.74e-02 0.00e+00 1.42e-04.- 0.00+KN 2.09e 02 4.36e 02 42 Te-125m 1 ~ 51e.01 5.43e-02 2.02e-02 4.21e-02 0.00e+00 0.00e+00 4.45e-01 2.31e-05 43 Te.127m 3.83e-01 1.36e-01 4.55e-02 9.11e-02 1.55et00 0.00e+00 9.54e-01 Te-127 9.87e.04 3.50e.04 2.12e-04 6.81e-04.- 4.00e-03 0.00e+00 7.62e-02 3.31e-08 45 Tc-129m 6.36e-01 2.36e-01 1.01e-01 2.05e-01 2.66e+00 0.00a+00 2.51e 46 Te 129 1.75e-03 6.52e-04 6.23e-04 1.25e-03 7.3Ce-03 0.00e+00 9.56e-03 2.34e-04 47 Te-131m 5.46e-02 2.62e-02 2.19e-02 3.94e-02 2.73e-01 0.00e+00 2.10c+00 1.01e 48 Te-131 1.05e-21 4.31c-22 6.05e-08 8.05e-22 4.57e 21 0.00c+00 8.58e 23 7.15e-05 49 Te.132 1.11e.01 7.06e.02 6.65e-02 7.44e-02 6.87e-01 0.00e+0) 2.24e+00 5.37e'05 50 t.130 4.15e-04 1.20c-03 5.37e-04 9.80e-02 1.85e-03 '.00e+00 9.2Ce 6.88e 05 51 t.131 8.80e-03 1.23e.02 6.80e-03 3.59e+00 2.12e.02 0 ~ 00 a+00 2.44e-03 2.26e-04 52 1.132 2.40e-07 6.29e-07 1.02e-05 2.12c-05 9.91e-07 0.00e+00 2.74e-07 1.18e-05 53 1-133 1.43e 03 2.43e-03 7.68e.04 3.40e 01 4.27e-03 0.00e+00 '.84e-03 5C 1.134 6.22e-13 1.65e-12 2.21e-06 2.75c-11 2.60e-12 0.00e+00 2.17e 14 2.63e 06 55  ! .135 7.24e-05 1.86e-04 9.38e-OS 1.20e 02 2.94e-04 0.00e+00 2.07e-04 2.89~5 56 Cs-134 1.66et01 3.91~1 1.82+%1 0.00e+00 1.2Ce+01 C.74eHS 4.86e-01 8.~2 57 Cs-136 1.62e+00 6.36e+00 4.27c4$ 0.00eKN 3.C6e+00 5.45e-01 5.12e-01 1.~1 3.91eKS 4.21e 01 1.31e 01 58 59 Cs-137 Cs-138 2.23et01 1.56e-16 2.96+41 2.99e-16 1.08e-06 0.00e+00 0.00e+00-1.01e+01 2.21e-16 2.57e-17 1.36e 19-2.35e 1.~ 7.~7 60 Be-139 2.64e-10 1.85e-13 7.00e-07 0.00e+00 1.75e-13 1.28e-13 61 'a-140 1.49e-02 1.82e-05 1.18e 03 0.00e+00 6.17e.06 1.22e 05 2.29e-02 2.55~" 62 Ba 141 0.00e+00 0.00c+00 0.00e+00 0.00e+00 0 ~ 00 a+00 0.00eKS 5.3Ce 08 Ba-1C2 0.00e+00 0.00eKS 1.01e-08 0.00eKS 0.00e+00 0.00e+00 0.00e+00 ~ 1.15e-08 La-140 La-142 5.96e 06 8.77e-12 2.93e-06 3.89e-12 2.~ 5.36e-06 -~ 0.00+HER 0.00c+00 0.00e+00 0.00e+00 0.00c+00 0.00eHS 1.68e 01'.19e.07 233e-04 6 43e.06 65 C0-141 3.33e-06 2.22e-06 1.49e-04 0.00e+00 1.05e-06 0.00e+00 6.36e-03 1.67e-04 67 Ce-143 3.52e-07 2.56e.04 2.47e 0.00e+00- 1.15e-07 0.00e+00 7.70e-03 Ce-144 1.78e-04 7.35e-05 7.66e-04 0.00eKN 0.00e+00 4.47c 8.74~- 69 Pr-143 3.28e-05 1.31e 05 1.63e-06 0.00eKS 7.60e-06 0.00e+00 1.08e 01 0.00e4$ Pr-144 0.00eKN 0.00e+00 1.81e-09 0.00e+00 0.00e+00 0.00e+00 0.00eHQ 2.08e 09 70 Nd 147 2.32e-05 2.52e-05 9.26e 05 0.00e+00 1.48e-05 0.00e+00 9.09e-02 1.09e 04 71 72 ll.187 8.42e-03 6.86e-03 2.43e-03 " 0.00c+00 0.00c+00 0.00e+00 1.86eKN 2.89e 05 1.49e 06 1.40e.07 1.85e-05 0.00e+00 4.40e-07 0.00e+00 2.26e-02 5-6b(2) Table 5-6c: Composite Dose Factors: Haximum Hypothetical Child (Page 1 of 2) Dose Factor Units: mrem/Ci Released Location: Danville (Mater Ing.)/Outfall (Fish & Shoreline)/FIXED DILUTION Usa (U ) (k / .FISH) ~ 6.9 Us e (Ua ) (k / :iNtER) < 510 Usage (Uan) (hr/ TSHORE) ~ 14 Oflutfon (1/Ã )SHORE) ~ 15.9 Ollutfon (1:FlSH) > 15.9 Dilution (1/}f:MATER) a 321 Transit tisIe CFISH) hrs ~ 25 Trans i t t{Iae (MATER) hra 0 25.8 Transit tice (SH(NTE) hrs ~ 1 Transit tfIae (SEOlf(ENT) hra a 131COO l sotooe &one L iver T. Body Thyroid Kidney Gl-LLl Skin 1 H-3 0.00ee00 3.960 05 3.96e-05 3.960-05 3.960-05 3.960-05 3.960 05 0.00ee00 2 C-14 2.38eKS 4.77e-01 4.77e-01 4.770 01 4.77e-01 4.770 01 C.770-01 0.000K' Na-24 8.100M 8.100.03 8.120.03 8.100-03 8.100-03 8.100-03 8.100-03 3.010-05 4 P.32 3.36ee03 1.57eKQ 1.29')2 0.00ee00 0.00eKN 0.00eKN 9.2&et01 0.00eKS 5 Cr.51 0.00'(N 0.00eKS 8.62e-05 4.200-05 1.150-05 7.66e.05 C.O10-03 1.25e-05 6 Hn-54 0.00ee00- 1.840 01 5.23e-02 0.000+00 5.170-02 0.00tHOO 1.55e-01 3.690.03 7 Hn 56 0.000+00 6.950-06 3.140-06 0.00a+0) 8.410-06 0.000e00 1.01e-03 1.850 06 8 F e-55 5.100-02 2.710.02 8.380 03 0.000+00 0.000+00 1.53e-02 5.01e-03 0.0004$ 9 Fe.59 7.210 02 1 ~ 170-01 5.870-02 0.00eKS 0.000+00 3.380 02 1.21e 01 7.280 04 10 Co-58 0.00ee00 4.090-03 1.34e-02 0.000+00 0.000+00 0.000KN 2.390.02 1.010-03 11 Co-60 0.00eKM 1.210-02 8.470-02 0.000+00 0.000+00 0.000+00 6.73e-02 5.750-02 12 Nf.63 2.39eKO ~ 1.~1 8.12e.02 0.00e+00 0.000+00 0.000+00 8.61e-03 0.00ee00 " 13 N f -65 1.010-05 9.500-07 1.070.06 0.000@0 0.000+00 0.00e+00 1 ~ 160 04- 5.960 07 1C Cu-64 0.0004(O 1.430 04 8.790-05 0.00ee(N, 3A7e-04 = 0.00ee00 6.730 03 1A&e 06 15 Zn-65 1.17ee00 3.120+00 1.940+00 0.00e+00 1.97eKS 0.000e00 5.C&0-01 1.950-03 16 Zn-69 2.95e-11 4.260 11 3.940-12 0.00e+00 2.580-11 0.00088 2.680 09 '.00088 17 18 8r 8r 63 64 ~ 0.00'(N 0.00eeOO 0.00oKM 0.000@0 2.2'le-06 1 ~ 250-07 ~ 0.000+00 0.000@0 0.00e+00 0.000+00 0.00ee00 0.000+00 0.~ 0.00eKN 1.200-08 1.~7 19 20 21 Br 65 Rb.66 R~ 0.00ee00 0.000KO-0.(OaKO-0.00eKO 5.53ee(O 0.00ee00 0.00eKS 3AOee00 7.31~ 0.000+00 0.00eeOQ 0.00eeOQ, 0.00eKQ 0.00eeOQ 0.000+00 0.00eKS 0.00ee00 0.00ee00 0.00ee00 3.56e 01 0.00080 " 2~ 0.000KN 8.~ 22 23 Rb.89 Sr-69 0.00ee00 1.88ee00 0.00eKO 0.00ee00 1.90cHS 5.~2 0.000K% 0.00ee00 '.000+00 0.000@8 0.00eHR 0.000@0 0.00et00 7.260-02 " 2.~ 5.71e-08 24 Sr-90 2.45ee01 0.00ee00 6.21eKO 0.00ee(N 0.00a+00 0.000+00 3.30e.01 0.00ee(N 25 Sr-91 5.550-03 0.00eKS 2.14e-04 0.000@00 0.000+00 0.00e4$ 1.220-02 5.310-06 26 Sr-92 2.130~ 0.00eKS 2.220.06 0.000+00 0.000e00 0.000e00 4.030-04 ~ 1.52e-06 27 Y-90 3.84aH6 . 0.00eKO 1.04e-06 0.000+00 0.00e+00 0.000+00 1.090-01 1.1~ 2& Y.910 3.780 16 0.00ee00 9.91e-08 0.000e00 0.000KO- 1.15e-07 29 Y.9'1 7.~ 3.2~ ~ 0.00ee00 2.2~ 0.000+00 0.000+00 0.000+00 0.00ee00-7.COe-13 9.720.02 2.740 06 30 Y-92 0.00eKQ 3.3&e 07 0.000e00- 0.000+00 0.00eKS 9.37e-04-- 4.~7 31 Y.93 2.5~- 0.000K% 4.5Scr07 0.000eOQ 0.000+00 0.000+00 3.730-02 5.320.07 32 Zr-95 3.C20 05 7.51 ~ 06 5.630 04-~ Q QQ0+OQ ~ 0.000+00 7.&C0-03 6A50 33 Zr-97 7.340 07 1.060 07 6.520-06 ~ 0.00e+00 1 '20-07 0.00eKS 1.610-02 7.51e-06 34 NtH5 2.830 02 1.100~02 8.19e-03, 0.00e+00 1.040-02 0.00eKS 2.040101 3.650-04 5-6c(1) Table 5-6c: Composite Dose Factors: Maximum Hypothetical Child (Page 2 of 2) Dose Factor Units: mrem/Ci Released Location: Danville (Water Ing.)/Outfall (Fish 8 Shoreline)/FIXED DILUTION I sosooe Borw T. B Th old < Idnev GI-LLI Sk)n 35 0.00eKS 5.9?e&3 1.C9e-03 0.00e+00 1 ~ 27e 02 0.00e+00 4.94e-03 1.04e 05 36 I Tc-99m 4.07e.08 1.70e-06 0.00e+00 1.16e-06 C.06e-08 C.55c-05 4.2?e.07 37 I Tc.101 0.00eKS 0.00eKQ 2.49e-09 0.00e+00 0.00c+00 0.00e+00 0.00e+00 2.7?e.09 38 RQ 103 4.20e-04 0.00eKO 4.0?e-04 . 0.00eKO 1.06e-03 0.00eKO 1.09e-02 2.8?e-04 39 RU 105 7.37e 07 0.00eKO 1.50e-06 0.00eKR 6 48e-06 0.00e+00 4.81e-04 1 40e-06 40 Ru 106 6.83e&3 0.00eKQ I.81e.03 0.00e+0) 9.22c 03 0.00e+00 1.06e-01 1.15e 03 R 110m 1.3?e 7.89e-03 0.00e+00 1.?3e-04 0.00c+00 1.10c-02 9.11 ~ 03 Te-125m 1.95~1 5.2?e-02 2.S9e-02 5.46e 02 0.00e+00 0.00e+00 1.88e&T 4.83a 06 43 Te-12?m 4.9~1 1.~1 5.89c-02 1.19e 01 1.41e+8) 0.00e+00 4.02c.01 2.~7 Te-127 1.2?e-03 2.?3c-04 8.82e-04 3.63e-03 0.00e+00 4.98e 02 6.91e-09 CS 'e-129a 8.24e 01 2.30e 01 1.2~1 2.66a 01 2.C2e+00 0.00eKN 1.00eKS 5.25a.05 1 ~ 41c.01 46 48 Tc-129 Te 131a Te-131 6 ~t 2.2?e 03 1.3Ce 21 6.33e 04 2.41e&2 2.5?e-02 1.26e-08 1.62e-03 4.9?e-02 1.03e-21 6.63e.03 2.3Ce 01 C.06e-21 0.00eKN 0.00e+00 0.00eKS 9.79e-01 7.05e-21 4.90e 05 2 10e-05 1A~ 'Te 132 1.40e 01- 6.19~2  ?.CBe 02 9.01e.02 5.75e-01 0.00e+00 6.23e-01 50 I 130 5.69~ ~ 1. 15e.03 6.04e 04- 1.2?e 01 1.72e-03 0.00e+00 5.38e-04 'I.C4e-05 51 I 131 1.26e-02 1.26e&2 7.21e-03 C.18e+00 2.07c.02 0.00e+00 1.12e.03 . 4.73e-05 52 1.132 3.2?e&7 6.01aM? 2.3?e 2.?9e-05 9.20e-07 0.00e+00 7.08e-07 2A6e 06 53 I 133 2.05e&3 01 '.?oc C.22e-03 0.00eKN 1.02c-03" 6.$ 5a-06 1-134 8.23e 'l3 1.53e 12 4.62e 07 3.52e-11 2.34-12 0.00eKN 1.01c-12 SA~? SS 1.135, 9.03a-05 1.59~2 2.?6e 04 0.00eKS 1.3?e-04 6 03e-06 56 Ca.134 2.Oleic)1 3.29ee01 6.%5eKS 0.00eKN 1.02ctO'I 3.66eKS 1.7?e-01 1.~2 57 Ca-136 1.91eKO 5.25eKO 3.39eKS 0.00e+00 2.?9eKS 4.1?c 'I 1.84 1 58 Ca-137 2.80eK)1 2.6$ ee01 3.99eKO 0.00eKQ 8.75e+00 3.15e+00 1.~1 2.~2 '9 Ca-1M '1.98e 16 2.75e-16 2.25e&7 0.00eKQ 1.93e 16 2.08e 17 1.26e 16- 2.5?+47. 60 Ba 139 4.32a-10 2.31e-i3 '.~7 0.00eKR 2.01a-'l3 1.36a l3 1.~7 61 Be 140 2.5?e 02 2i 25~ 1.55~ " 0.00et00 7.3Ce 06 1.30c&2 Ba 141 0.00eKO 0.00eKO 0.00e+00 0.00at00 0.00eKO 0.00e+00 Ba 142 0.MeKN 0.00eKO 2.11e~ " 0.00eKN '.00eKN 0.00e+00 0.00cKO 2ATe 09 La-140 8.~- 2.81~. C.39e 05- 0.00et00 0.00eHS 0.00e+00 7.83e-02 65 La-142 1.1?e 11 3.?3e lt T.ltc~ 0.00eKS 0.00e+00 0.00e+00 7.38e-07 1.3Ca 06 66 Ce 141 7.?CHS- '.1~ 0.00e+00 1.&9~ . 0.00eKO '.82e-03 67 Ce-143 8.14~7 " ~ O.Me+00 1.85e-07 O.MeKO 6.4?e-03 5.85HS.r 1~ 3.3~2 " '.21e.06 Ce 144 4 ~ 1.30&%- 1.80M 0.00eKN 0.00e+00 1.37~ . 2.27~ . 0.00e+00 7.C3e 0.00eKS 4.93c 02 0.00HOO. 69 Pr 143 Pr -144 0.00eKO 0.00aKO 3.78e '10 0.00eKN .00eKO 0.00e+00 0.00e+00 4.35e 10 70 71 Md-147 3.~- 0.00e+00 .42e-05 0.00e+00 0 ~ 00eKN 4.11c 02 8.89e 01 6.03a 06 M-187 1 ~ 0?e<2 2.84e 03 0.00e+00 .00eKS Rp.239 1.~7 3.95e-06 0.00e+00 .68e 07 0.00e+00 1.20e&2 4ASe-06 5-6c(2) Table 5-6d: Water Ingestion Dose factors: maximum Hypothetical Infant (Page I of 2) Dose Factors: mrem/Ci Released Location: Danvi1 le Receiver/FIXED DILUTION Uso (Uao) (k / zMAMR) e 330 Oilution (1/N sMATER) ~ 321' sotooo Transit tia>> (MATER) hre a Bone L iver 25.8 T. Body Thyroid . I Lmy Gl LLI 1 R-3 0.00eKR 3.12e-o5 3.12e-05 3.12e-05 3.12e-05 3.12e-05 3.12e-05 2 C-14 2 ~ Cpe-03 5.13e-04 5.13e.p4 5.13e-04 ~ 5.13e 5.13e.04 5.13e 04 3 Ma 24 3.11e-04 3.11e-04 3.11e-04 3.11e.04 3.11e.04 3.11e.04 3.11e-04 P.32 1.~1 9.63e 03 6.34o-03 O.ooe+00 O.ooe+00 2.21e-03 4 5 Cr-51 p. Mes% 0.00eKO 1.39e-06 O.ooe+00 9.08e-07 1.98e-07 4.46e 1.77e-06 4.~ 7.4~ 6 Xn-54 0.00eKS 2.01e-03 4.56e-04 O.ooe+00 O.MeKS 7 I(n-56 0.00'&) 8.07e 0& 1.39e 08 0.00eKS 6.93e-08 0.00eKS - 7.33e 06 8 F0-55 1.41e-03 9.10e.04 2.43e-pC 0.00ahS . O.ooe+00 4.45e.04- 1.16e-04 Fe.59 3.07e 03 5.37e-03 2.11e-03 0.00eKN 0.00eKS 1.59e-03 2.56e-03 9 9.~ ~ 10 Co-58 0.00eKS 3.61e-04 9.01e-04 0.00eKS 0.00eHS 0.00eKS ll Co-60 0.00eKN 1.09e 03 2.5~ 0.00eKO 0.00eKS 0.00eKS 2.61e-03 12 Ri.63 6.43e-02 3.9&e 03- 2.23e-03. 0.00et00 0.00eKS 0.00eKS 1.98e-04 13 wi.65 3.95e-07 4.47o-o& 2.03o-08 O.ooe+00 0.5k+M . 0.00e+00 3.Coo 06 0.00eKS 7.0pe-06 2.56e-05 O.Me+00 3.10e 04 I 14 15 Cu 64 Zn-65 I. ~3 1.51e 05 6.3&e 03 2.94e-03 O.Goo+00 O.poe+00 3.09e 03 0.00eKS 0.00eKN 5.~ 6.00o 12 16 Zn-69 4.09e l4 7.36e 14 ~ 5.4&e 15 0.00eKS 3 06o 14 17 Sr-83 0.00eKQ 0.00eKO 2.07e-08 0.00e+00 O.ooo+00 0.00oKO 0.00aKS ~ 18 Sr-84 0.00oKR- 0.00eKO 9.19e 20 0.00eKS 0.00eKN O.ooe+00 0 00eKS -'.00eKS 0 00eKS '~ 19 Sr-85 0.00eKO", 0.00eKO 0.00eKS 0.00eKS 0.00eKS 20 Rb-86 0.00eKQ ~ 1.66e 02 8.19e 03 0.00e+00 0.00eKO 0.00eKR 4 21 Rb 88 0.00eKO 0.00eKN 0.00et00 0.00eKS O.ooe+00 0.00eKS 0.00eKO 22 Rb 89 0.00eHR '.00eKN 0.00e+00 0.00eKS 0.00eHQ 0.00eKO 0.00eKS 7.~ ~ 23 Sr-89 2.51~1 0.00eKO 0.00eKO 0.00et00 ~ 0.00eKO 4.~1 2~2 ~ ~ 90 1.88eKQ 0.00eKN 0.00et(N 0.00eKO. 0.00eKS 24 Sr 0.~ ~ 25 Sr -9'I 7.72e~ - 2.79e~ '.00et00 0.00e+00 .= 0.00eKN 9 26 Sr-92 2 '.00et00 9.85~ 0.00et00 0 00eKO O.ooe+00 - 2 27 T.90 6.67e 06 0.00eKN 1.79~7 O.ooo+00 0.00eKO '.00eKO 9.21e-03 28 T.910 3.62e-l7 O.OOe+OO ~ 1.23e-l & O.OOe+00 O.OOeKN O.OOe+N 1.21e-13 29 T.9'I 1.13e 04 0.00eKN. 3.01e-06 0.00eKO 0.00eKO ~ 0.00et00 8 11e-03 30 T-92 4.9&AH 0.00eNO 1. Coe-10 0.00eKO 0.00eKO " 0.00eKO -. 9A7o-05 4.~7 1.14~ '.ooe+00 3-31~ 0.00eKS>> ~ 31 T-93 0.00eKS 0.00eKS 32 Zr-95 2.07e 05 = 5.03e-06 3.57e-06 0.00eHR - 5A2e-06 0.00eKO 2.51e-03 33 Zr.97 5.21e-07 8.94o~ C.GBe-p& 0.00eKS . 9.01e-o& "- 0.00eKS 5 34 Nb 95 4.17e-06 - 1.72e-06 9.93e-07 0.00e+00 . 1.23e-06 . 0.00eKS 1A5e43 35 Ro-99 0.00e+00 2.63e-03 5.13e-04 O.NeKN 3.93e-03 0.00eHN 8.66o 04 5-6d(l) Table 5-6d: Water Ingestion Dose Factors: Maximum Hypothetical Infant (Page 2 of 2) Dose Factors: ."..rem/Ci Released Location: Danvllle Receiver/FIXED DILUTION Isotooe I I. Iver T. B Th id GT I.I.I 36 Tc-99m I 9.98e-09 2.06e-08 2.65e 07 0.00c+00 2.22e- 7 1.08e.08 5.98e 06 37 Tc 101 I 0.00c4% 0.00eKR 0.00c+00 0.00c+00 0.00e+00 0.00c+00 0.00eKS 38 Ru 103 I I.C7e-04 0.00eNN 4.93c-05 0.00c+00 0.00c+00 1.79c-03 3.07c-04'.81e-06 39 Ru-105 Z.C6e 07 0.00eKS 8.27c.08 0.00e+00 0.00c+00 9.7le-05 40 Ru-106 2.CCe-03 0.00eKM 3.05e.04 0.00e+00 2.me 03 0.00eKS 1.85~2 'Cl " 4 -Iles 1. Dle-04 7.35e-05 C.86e-05 0.00c+00 1.05e-04 0.00c+00 3.81e 03 42 Tc 125m 2.33e-03 7. SO&)4- 3.15e-04 7.SSe-04 0.00e+00 0.00e+00 1.11e-03 43 Tc 127m 5.89e-03 1.95e-03 7.13c 04 1.70c-03 1.45e-0 0.00c+00 C4 Tc 127 1.50e 05 5.02ei06 3.22e-06 1.22e.05 3.65e-0 0.00eKS 3.15~- 45 'Ic-129m 9.92e-03 3.COe 03 1.53c-03 3.81e 03 2.CSe-02 0.00eKN C6 Tc-129 2.82e 05 9.71e-06 6.58c-06 2.36c-05 7. 01e.05. 0.00eKS 47 Te-131a 8.49~ 3AZe 04 2.82a-04 6.93e-04 2.35e-03 0.00eKS 48 Tc 131 C.46e 24 1.65e-24 I.Z5e-2C 3.98e 24 1.14e-23 0.00e+00 1.80e 22-49 Tc 132 1.68e 03 8.31a-04 7.75e-04 1.23c-03 5.20c 03 0.00c+00 3.07e<3 50 I-130 1.43c 04 3.15e 04 1.26e-04 3.53c-02 3.46c 04 0.00e+00 51 I.131 3.32e 03 3.91e 03 1.72c.03 1.28et00 4.57e-03 0.00c+00 52 1.132 7.07e-08 I.C4e 07 5.11e-DS 6.73e-06. 1.60c-07 0.00c+00 1.1~7 53 I -133 5.37e 04 7.81e 04- 2+29~ 1 ~ C2e-01 9.19c 04 0.00cKN 5C 1.134 I'.27e~13 2.60e 13 9.25e-l4 6.06e-12 2.91e-13 O.MeKO 2.69e 13 55 1.135 2.47e 05 C.COe 03 5.47e 05 0.00c+00 56 Ca 134 3.82a-02 7.12e002 7.19c&3 0.00e+00 1.83e 02 7.52e 03 1.9Ca44 ~ 57 Ca-136 C.40e 03 I.~Z 4.83~3 0.00eKN 5.1~3 1.05a-03 1.9Ce44 SS Cs-137 5.29a-02 6.20e.02 C.39~3 0.00c+00 1.66e-02 6.73c 03 59 Cs-138 1.76e 19 2.86e 19 1.39c-19 0.00eKN 1.43e-19 2.23c-20 4.57e 19 Ba 139 2~10 1.50e 13 6.55e 12 0.00eKQ 9.02e 14 9.09e 14 1A3a48* 61 Ba 1CO Ba 'I41 1.~2 0.00eKO 0.00eKQ ~ 8.43e~ 0.00eKO ~ 0.00e+00 0.00eKN 3.~ 0.00eKN ~ 1.00e~05 0.00eKN 0 OoeO

63. Ba 'IC2 0.00eKO 0.00eKM 0.00et00 0.00eKQ 0.Doe+0. 0.00e+00 0.00eKS I.a-ICO 5.41e&7 1.39~7 0.00eKS 0.Doe+00 0.00e4$

65 I.8-142 Ce 141 1.C9e 12 5.47e 13 1.31e 5.60~7 13 0.00e+00 0.00e+00 0.Doe+00 1.47e 06~ ~ 0.00eKS 0.00e+00 9.~ >> 67 Cc-143 8.73i&7 5.79~- 6.61aM 0.00e+00. 1.69e 07 0.00e+00 3.~" Cc-144 3.01e-04 1. 23e-04 << 0.00eKS C.99c 05 0.00eKS 1.~2 " 69 Pr-1C3 3.87e<7 0.00e+00 I.me 06. 0.00aKO Pr-144 0.00eKS 0.00eNN 0.00a+00 0.00eKN 0.00eKN 0.00eKS 0.00eKO>> 71 Rd 1C7 5.24ei06 5.38e 06 3.30e-07 0.00eKN 2.08c-06 0.00e+00 3A1~ M.187 3.01 ~ 05 1.0Ce-05 0.00et00 0.00eKS = 0.00e+00 Ro 239 8.20e-07 . 7.34eo08 C.15e-08 '.00eKN 1.C6e 07 0.00eKN 2.12e 03 5-6d(2) 6.0 ~ INDIVIDUAL DOSE OUE TO AIRBORNE EFFLUENT 6.1 ~ ~NDBL G!'P CIFICATION 3.11.2.2 - 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 GAHN RADIATION AND LESS THAN OR EQUAL TO 10 HRAD FOR BETA RADIATION, AND

b. DURING ANY CALENDAR YEAR: LESS THAN OR EQUAL TO 10 MRAD FOR GANN 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 gamma radiation during any specific time period: D = 3.17 x 10 g H. (X/Q)v Q.v (Eq. 14) and by the following equation for beta radiation during any specified time period: Db = 3.17 x 10 $ N, (X/Q)v Q;v (Eq. 15) Where: the air dose factor due to gamma emissions for each identified noble g~s radionucl,ide (i) (mrad/yr per uCi/m ) from Table 2. N. the air dose factor due'o beta emissions for each 1 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 the total gamma air dose from gaseous effluents for specified time period (mrad). 27 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 ONUCLIDES OTHE THAN NOBL GASES SP C F CATION 3.1 ..3 THE DOSE TO A MEMBER OF THE PUBLIC FROM IODINE-131, TRITIUM, AND ALL RADIONUCLIDES'N PARTICULATE FORM WITH HALF-LIYES GREATER THAN 8 DAYS IN GASEOUS EFFLUENTS RELEASED, FROM-EACH REACTOR UNIT, TO AREAS AT AND BEYOND THE SITE BOUNDARY (SEE 5.1.3-1) SHALL BE LIMITED TO THE FOLLOWING: 'IGURE

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: D -3.17x10 Z (Ri) (W) (0' (Eq. 16), 1 28 where: 0C the total dose to a critical organ'rom radio-nuclides other than noble gases for a specified time period (mrem). R) = the dose parameter for each identified radionucli)e (i) for the inhalation pathway (mrem/yr per uCi/m ) and for food and ground plane pathways (ma mrem/yr per uCi/sec) from Table 4. W the highest annual average dispersion parameter for estimating the dose to the critical individual; relative concentration (X/Q) (sec/m ) for the inhalation pathway and relative deposition rate (D/Q) (m ~) for the food and ground pathways such as from Table 3. Qg= 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. 29 7.0 TOTAL DOSE SPEC ICATION 3.11.4 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, WHICH SHALL BE LIMITED TO LESS THAN OR EQUAL TO 75 MREMS. The cumulative dose to any member of the public due to radioactive releases from the SSES site is determined by summing the calculated doses to .critical organs from the previously'iscussed effluent sources. The-annual dose to critical organs of a maximally exposed individual for the liquid effluents is determined by using Equations 10, 11, and 12 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 14 'modified by replacing M.'1 with K. from Table 2 for the whole-1 body dose and by Equation 15 modified by replacing N. by (L, + 1.1 M.) from Table 2 for the skin dose of Section 6.0: D 3.17 x 10 Ki (X/Q) vQiv (Eq. 17) Db 3.17 x'10 (Li + 1.1Mi')(X/Q)vQiv (Eq. 18) 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 16 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 (TL'D) monitors. Since all other uranium fuel cy'cle sources are f greater than 20 miles 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 30 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. A discussion of the methods used to calculate the total dose to critical organs of a maximally exposed individual is given in Section A.4 of Appendix A. 31 8.0 OPERABI I Y OF WASTE TREATME T SYSTEMS 8.1 L U D ASTE TRE TM NT SP C FIC T ON 3.11.1.3 - THE LIQUID RADWASTE TREATMENT SYSTEM, AS DESCRIBED IN THE ODCM, SHALL BE OPERABLE. THE APPROPRIATE PORTIONS OF THE SYSTEM SHALL BE'USED TO REDUCE THE RADIOACTIVE MATERIALS IN LIQUID WASTE PRIOR TO THEIR DISCHARGE WHEN 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 MREM TO THE TOTAL BODY OR 0.2 MREM TO 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 normal flow. Liquid from the filters enter a mixed bed demineralizer with a volume of 140 ft and normal flow rate of 200 gpm. There are two chemical waste neutralization tanks with 28,000 gal capacity. Low conductivity liquid wastes are collected in three pairs of LRW 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 ODCM Policy Statement 10.6. In cases when a batch of liquid waste must be released with treatment less than that specified in Section 0 10.6, a dose assessment using LADTAP or the methodology of Section 5.4 shall be performed prior to release to ensure that the limits of Specification 3.11.1.3 are not exceeded. 8.2 GASEOUS ASTE TREA MENT SP CIFICA ION 3.11.2.4 THE GASEOUS RADWASTE TREATMENT SYSTEM SHALL BE IN OPERATION. RNNEICA" I T .I WHENEVER THE NAIII CONOENHER AIR EJECTOR TEIIACHATIIIII) SYSTEM IS IN OPERATION. S I ON 3.1 2.5 THE APPROPRIATE PORTIONS OF THE VENTILATION EXHAUST TREATMENT SYSTEM SHALL BE OPERABLE AND SHALL BE USED TO REDUCE RADIOACTIVE MATERIALS IN GASEOUS WASTE PRIOR TO THEIR DISCHARGE WHEN THE PROJECTED DOSES DUE TO GASEOUS EFFLUENT RELEASES FROM EACH REACTOR UNIT TO AREAS AT AND BEYOND THE SITE BOUNDARY (SEE 32 FIGURE 5.1.3-1) WHEN AVERAGED OVER 31 DAYS WOULD EXCEED 0.3 MREM 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 55K 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. h 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 33 DAT contaminated air from selected areas of the radwaste building. The system contains two 100X capacity fans and two 50X 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.'he 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. 83 SO WASTE REA M T SPECIFICATION 3..3 THE SOLID RADWASTE SYSTEM SHALL BE USED IN ACCORDANCE WITH A PROCESS CONTROL PROGRAM, FOR THE PROCESSING AND PACKAGING OF RADIOACTIVE WASTES TO ENSURE MEETING THE REQUIREMENTS'OF 10 CFR PART 20, 10 CFR PART 71, AND FEDERAL. REGULATIONS COVERING THE: DISPOSAL OF THE'WASTE. The SSES solid radwaste 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 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. Hixing 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 (DAW) monitoring system is used to segregate radioactive from non-radioactive solid waste. 35 FIGURE 1 LIQUID RAOWASTE SYSTEU FLQ'I'I'IAGRAM ~oo lC 0 0 1QW ~ I ~0~ <<44 I C gC 4EI g)5" -GH 0 Qg Qtl $ 0= C v gE4% C LIR) '- oah- jh- ~ I C 0 C 4 CC 4 LI ll <<o M cIII s oo E 5C Z C 5 ogle RR IL EI IO Z ad) oLII $ I 0<< +Em+ Z I 7 EI g4f C Cl C 4 Cl 5 $E v ~ gpss C 4 0 ~ J EI hajj 0 oR oa wo SC) ~t>> n Cr OE Ql h~k Pil: st~NR <~k +CR o No ho ~ eQ C gl ~ J g4 RN hl P C

i EEg C I

ISr(ljs rgg Pzila <<coo !ills 5g !j4sji Og ijijl'.i:-  ;$ 5 Cagmg SS NC IIE+~oo C CWOCE 'J t~ ,CL 36;, 'MBIENT MAIN 6 AUX STEAM FROM ~<NIT I STEAM JET AIR EJECTOR UNIT I Of FGAS BYPASS OFFGAS RECOMBINEA SYSTEM I EL HEAT TRACING 1 I IE 136 PRE HEATER L TURBINE BLDG EXHAUST UNIT I IF 302 OU I.ET HEPA F ILTE DELAY PIPE IT 310 IF TEMPERATURE CIIABCOAI OFFGAS SYSTEM UNIT 'I IT 309 IA HARCDAL ADSOBBEB BE 6 IT 308 $ 1E IA IE IT307 A 9 11 10 306 IT 303A Q MAIN IE 133 MOTIVE STEAM JET STEAM DILUTIONSTEAM I I 6 T CON. I STEAM 3 DEN. JET I I SEA IS 125 I INLET PRE CIIILlEA~~ GUARD AIR RECOMB ~~~+I: I IE 134 H2 HEPA 8 D UNIT COOI.EB au IstSTAGE EJEC. VESSEL MOTIVE TOA I STEAM ~ CON I 4l JET'OND DEN. Q~ 2nd STAG c. SER I IE I31 I RECOMB I = COND I COMMON OFFGAS RECOMBINEA SYSTEM STEAM JET AIA EJECTOA CONDENSER MAIII UNIT 2 DELAY PIPE STEAM CON. AMBIENT TEMPERATURE CHARCOAL OEN. OFFGASSYSTEM SEA UNIT 2 UNIT 2 OFFGAS RECOMBINEA SYSTEM 2 OFFGAS BYPASS MAlh 5 AUX TURBINE BLDG EXHAUST STEAV UNIT 2 FROM UNIT 2 FIGURE 2 I g. cl y OFFGAS AND RECOQBINER SYST@ GLOM DIAGRAM t.r)lt, I i'tif t tl t1!Iltli!>>lItit)tl'i~ tlit.ft'it DMXNSIIIE'ENIH. RPDVASTE COOENSAIE RECEN. HASTE REOEN. HASTE FLEL PIXL RNCU BACXN. INCU BACKH, RESIN OENItCRALI?ER (XHIH. RESIN 0/KK STIXIASE VES%L IX'-3O I STORAOE VESSEL ll 106TIVKS hes SLSIOE I TIVKS F/0 BACXH. RLCE I VIIO 'Thta RECEIV IIXI TIVK ll 225 RECE IVI'IWK LT ISS Sl ISB 2T OSAGES 2l 225 01 283 IP-IOSA.B ( )~~ () RECEIERAI ION 2P-IOSA 8 QS QS QS SPENT RESIN TAIK OT-32S SPENT RESS~ TRANS.PUNP 0 OP-320 I IO ANSS ~ PIO RNSS liight LIIXIIO RAOHASTE FILTERS OF 3Rlis 0 WISIE SLIOCE PHASE SEP. OT-331 PAPER i RAOSr PLASTIC SLKETIHO~ l5CU RNCU CLOTHINOifEPh AINT PHASE SEP. PHASE SEP. CARTRIDCE FILTERS O HhSTE SLlOCE OT 318h OT 3188 OISCHARCE HIXINO PINW'P-332 -~TO RNSS~PISP TO RNSS SINIQXKR PISP'12 EVAPORATOR OS-33S ORINI HASTE HIXINO CONCENTRATE COW'ACTOR TALKS STORACE TINK RNCU SLUOCE OISCNARCE COIN'ACTOR OS-313 OT 3OTA.B OP-328 HIXINC PUNP OS-338 CP 334 F VAPORA I OR IRON IXNICENTRAIE EVAPORAIOR 0$ 5 0IG STORAOE TAN( OISCWIROE PISIP OP-328 55 hhL LSA HSA CRISIS WISTE HASTE OR BOXES CONTAINER COHTAIHER l<200FT I ISO TO IOOFT I W-Il WASTE NANAdEllkN (.'}SIIli l! 'I [IGUPE il 3'GLIP SYSTEII FLOW DZAGSAII i/d f)g I; FIGURE 4 SSES DRY CONTI)(lINATED WASTE PROCESSING Paper, Plastic, Rags, Sheeting, Clothing Second-Sort Contaminated Dry Solid Waste , Dry Solid Waste Dry Active Waste (DAW) Monitoring System PP&L 'Vendor Shredder Yes Services Drum Radioactive? Box Compactor Supercompaction Compactor Incineration 55-gal. Drums or Boxes No Free Released 39

9. 0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 9.1 O~FINITI N 0

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 MONITORING PROGRAM SPECI ICATION 3.12.1 - 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. The charcoal sampler cartridges used in the airborne radioiodine sampling program (Science Applications, Inc., Model CP-100) are designed and tested 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. 40 OAT P I 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, and 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 next Annual Radioactive Effluent and Waste Disposal report. Reporting requirements for the radiological environmental surveillance program are given in Appendix B. 9.3 CENSUS PROGRAM SPECIFIC TION 3.12.2,- A LAND-USE CENSUS SHALL BE CONDUCTED AND SHALL IDENTIFY WITHIN A DISTANCE OF 8 KM (5 MILES) THE LOCATION IN EACH OF THE 16 METEOROLOGICAL SECTORS OF THE NEAREST MILK ANIMAL, THE NEAREST RESIDENCE AND THE, NEAREST GARDEN* OF GREATER THAN 50 M~ (500 FTi) PRODUCING BROAD LEAF VEGETATION.

• Broad leaf vegetation sampling of at least three different kinds of vegetation may be perfo'rmed at the site boundary in each of two direction sectors with the highest predicted D/9'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.

41 0AT If a land use census identifies a location(s) with a higher average annual deposition rate (0/g) than a current indicator location, the following shall apply:

1. If the 0/g is at least 20 percent greater than a previously high 0/g, the new location shall be added to the program within 30 days of documented identification of sampling'easibility. The indicator

'ocation having the lowest 0/g may be dropped from the program after October 31 of the year in which the land use census was conducted.

2. If the 0/9 is not 20 percent greater than the previously highest 0/g; direction, distance, and 0/g 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. I L B TORY COMPARISON ROGRA SP CIFIC TIO 3.12.3 - 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 Commission. This participation shall include some of the determinations (sample medium-radionuclide combination) that are offered by EPA and that are 42 also included in the monitoring program. The results of the analyses of these crosscheck 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 Annual Radiological Environmental Operating Report. DAT FIGURE 5 ENVIRONMENTAL MONITORING LOCATIONS WITHIN ONE MILE OF THE SSES G OULD I ISLAND I NORTH I I I I I I I I I I I 14-I I I p <<<<'<<m ~ ~aJ l T ~ ~T 15SX T I~rm LAKE ~TAX I 14SS ~ K /T 13 I I T ~ ~ ol:::g fg e ~ ToSS7 T SSC T I p<<<<aI @6NI Q.12S1 I I Dr T ~ ate. l I l r-> BONNY L mm<<<< 1 NILE. SUSQUEHANNA RIVER AIR g 'mIRmX rnER T TIIERMOLUMINESCENT INSIMEIRT FIGURE 6 ENVIRONMENTAL hiONITORING LOCATIONS GREATER TIIAN ONE MILE FROhi THE SSES I SUSQUEHANNA t ANTICOKE SF I RIVER T ~ 2FI GLEN LYON 3F1. T T SI IICKSHIiNNY ( IiOCANAQUA CQ, ~IZ. ~' POND HILL 14Ei ~ f T , ~ 12EI J,v 'APWALLOPEN SEI . BERVICK '1lEIe +~m T AESCOPECK g'~ MIFFLINVILLE 5 NIKR: /r CONYNGHAhi HAZLETON W scag LE, AIR MuX r oRexmc vnzR nsn o Sam ZNY mERM01UQIN oOSIMELRY ~ 4y idge I ui IABIL 6 OPI,RAI IONAL RAOIOI 061CAL ENVIRONHENIAI HONI ION ING PHOrkAH Exposure Path<<ays Number oi Siuples SaN'pl ing and lype and nd o 3 y~acaQ zxls<< ect on ~rbo ne Continual sampler operation <<Ith Radioiodine Canister: analyze Radioiodine and 1251 0.4 mi VSV - E.O.F. Building sample collection <<eekly for l-131 Particulates 981 1.3 ml 5 - Tranmslssion Line 554 0.8 ml E - Environmental Laboratory 12EI 4.1ml VSv Barwick Hospital i, f61 14 ml SE - PPSL Hazleton Complex'52 0.5 mi NE -'SES Backup Het. lo<<er 0 6 ml Nv - Transmission Corridor Piriic.<<lite sii OI e Analyze for gross bets ri Jibing t i I y 1554 <<eekly.'uarterly 3,9 mi N - Hocanaqua less thorn 2i hours follcwlng Illter 102 3DI 3.4 ml NE ~ Pond HIII/lily Like fire Co. 'change. Perlorm I otopic an~lysis uu 12GI 15 ml VSV - PPLL Bloomsburg Service Center'52 composite sample lby location) quarterly. rec Radia on Perimeter Fence - 0.2 mi N Gamna Dose: quarterly. 102 Nocanaqua - 4.0 ml N ~ I 253 Perimeter Fence - 0.2 ml NHE 283 Durabond Corporation - 1.3 ml NNE 2F1 St. Adalberts Cemetery - 5.9 ml~lIHE 354 Perimeter Fence - 0.3 ml NE 301 Pond Hill/Lily Lake Fire Co. - 3.4 ml NE 3F1 Valania Residence - 9.1 mi NE 3GS 'Vllkes-Barre-Parrish St. Substation-16 ml NE' 453 Perimeter Fence - 0.2 mi ENE 4E1 Ruckles Hill Road Pole (P) 46422/N35197 - 4.8 AI EHE 4GI Crest<<ood industrial Pork 14 mi Perimeter Fence - 0.3 mi E EHE'57 5E2 Bloss Farm - 4.5 mi E 654 Perimeter Fence - 0.2 ml ESE 6A4 Riverside Restaurant - 0.6 mi ESE Page 2 of N Exposure Pathways and or le ~dt Hmaber of Samples Co Sampling and ect on r uenc r Jypo and uenc o Anal s s 6El St. James Church - 4.7 ml ESE 659 Perimeter Fence - 0.2 ml ESE 756 Perimeter Fence - 0.2 ml SE 7El Harwood 1ransmission LInu Pole t2-4.2 mi SE 7Gl PPSL Hatleton Complex - 14 mi Perimeter Fence - 0.2 ml SSE SE'S2 882 LaMall Residence - 1.4 mi SSE 803 Houry Residence - 4.0 ml SSE 9S2 Security Fence - 0.2 ml 5 9D4 Country Folk Store - 3.6 mi S 1051 Post South of Switching Station - 0.4 ml SSM 10Dl Ross Ryman Farm - 3.0 mi SSM 11S3 Security Fence - 0.3 ml 5'M 11E1 Thomas Residence - 4.7 mi 5'M 1253 Perimeter Fence - 0.4 mi 'MSM 12E1 Berwick Hospital - 4.7 mi MSM lZGl PPLL Bloomsburg Service Center - 15 mi Perimeter Fence - 0.4 ml M-MSM'352 13E4 Kessier Farm - 4.1 ml M 1455 Beach Grove Rd. 6 Confer's Lane Intersection 0.5 mi MIN 14E1 Canouse Farm - 4.1 mi MIN 15F1 Zawatski Farm - 5.4 mi NM 1555 Perimeter Fence - 0.4 ml IN 1651 Perimeter Fence - 0.3 ml NIN 1652 Perimeter Fence - 0.3 ml NIN 16F1 Hldlay Residence - 7.8 NNM Malerborne Su< face 656 river water Intake line'57 Honthly composite Gamna isotopic analysis. cool'Ing tower blowifown discharge line Honth'ly conyosite Composite tritium analysis at least quarterly. 0< inking IZHZ Oanvllle Mater Co. Monthly conposite Gross beta and gamma Isotopic (Approximately 30 mlles downstream) analyses monthly. Composite for tritium analysis at least quarterly. Sediment from Shoreline 78 Bell Bend - 1.2 mi SE Semi-annually Gaxma Isotopic analysis semi-annually. 'I Page 3 of 3 Exposure Pathways Nmaber of Samp)es Samp) lng and Type and and 0 c y~oca~tonsw Uenc 5 Ni)k**~ 1283 Young Farm - 2.0 mi MSM Sam)anth)y when anima) s are on Gasma isotopic and 1-131 ana)ysis IOGI Oavis Farm - 14 mi. pasture, monthly otherwise of each sample. Ray Ryman Farm - 3.5 mi. SSM SSV'OD2 1001 RSC Ryman Farm - 3.0 ml. SSll Fish and Invertebrates Outfall area Semi-annua))y. One sample'rom Germs isotopic on edlb)e portions. 2H Falls, each of two reacreationa)ly PA'Approx)mate)y 30 mi NNE) important species from any of the fol)owing fern)) Ies: bullhead catfish, sunfish, pikes, or perches. Food Products 1101 lehner Farm - 3.3. mi SM At time of harvest Gamna Isotopic on edib)e portions. vegetable 12F7 ).upinl Farm - 8.3 ml llSM vegetable 'The )ocation of samp)es and equipment were designed using the guidance ln the Branch Technica) Position to NRC Rev. Guide 4.8, Rev. 1, Nov. 1979, Reg. Guide 48. 1975 and ORP/SIO 72-2 Environmenta) .Radioactivity Surveillance Guide. Therefore, the airborne sampler )ocatlons were based upon X/Q and/or 0/Q. CO ! "A dust )oading study (RHC-TR-81-01) conc)uded chat the assumption of I for the transmission correction factor for gross beta ana)ysis of air particu)ate samples is valid. Air particulate samples need not bc we)ghed to determine a transmission correction factor. '"If a I milk samp)e Is unaval)ab)e for r~io than two sampling periods from one or more of the )ocations, a vegetation sample shall be substituted unti) a su)tab)e mi)k )ocation Is evaluated. Such an or.urrence wi)) be documented in the RENP annual report. Control samp)e )ocatlon. h Two-week composite if c~.i.ulated doses due to cons~tlon of water exceed one mill)rem per year. In these cases, I-131 analyses wil) b>> performed. c The samp)e co) )ec'.or wi) ) determine the species based upon avai)abi) lty, which may vary seasons))y and year)y. TABLE 7 } DETECTION CAPABILITIES FOR ENVIRONMENTAL SAMPLE ANALYSIS ~ i I Lower Limit of Detection (LLD) Airborne Particulate " or'Gas' Mater Fish Hilk Food Products Sediment Ana s's 9~MCL1l laULkkl lakllll C d gross beta 1x10 H-3 2000 Hn-54 15 130 Fe-59 I 30 260 Co-58 15 130 Zn-65 30 260 V Zr-95 30 1-131 1b 7x10 1 60 Cs-134 15 5x10 130 15 60 150 Cs-137 18 6x10 150 18 80 180 Ba-140 60 60 La-140 15 15 TABLE 7 (Continued) 1 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 sb 2.22 EVY exp (-A 6 t) where: LLD is the "a priori" lower limit of detection as defined above (as pCi per unit 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 ~~o 'before the= fact) limit representing the capability of a measurement system and not as a posteriori (after the fact) limit for a particular measurement. LLD for drinking water. 50 OAT 10.0 DOSE ASSESSHENT POL Y STATB1E S 10.1 Selection of Anal sis Res ts for Dose Ca cu ations 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 ssi nment of Re eases to the eactor 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..'ffluents 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 divided between Unit 1 and Unit 2 release totals. -'qually d.. Waterborne effluents shall be equally divided between Unit 1 and Unit 2 release totals.

10.3 Eva a 'on and o 'torin Cr'te 'a fo f lue t Pat wa Potential.unmonitored effluent pathways will be evaluated on a case-by-case basis. Periodic sampling and/or realistic evaluation be performed in order to demonstrate the significance of a 'ill 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. ot an Efflue t Pat wa : Realistic evaluation (e.g.,

engineering design, system operation, radionuclide inventory) 51 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. t

b. Insi nificant Effluent 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 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 periodically.

c. Si nificant Ef uent Pat wa : 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 NPC 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 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 Annual Effluent and Waste Disposal Report. 10.4 Flow from the SGTS Vent whe the S stem 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, 52 '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, ~r v d'ed that

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.

10e5 OD Set 's are U t Va ue 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. a 10.6 Oe nitio of "A o riate Treatme t" for L u'd astes 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 Oe2 . 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. 53 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. 11.1. 1. 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 treating 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 OAT 10.7 Ho itor 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: CO R CTIO FAC ORS ROU INE E FLUENT HONITORS MIU EEUA JPPTCUI TEE Reactor Building Unit 1 1.5 3.2 Reactor Building Unit 2 1.5 3.2 Turbine Building'nit 1 1.6 3.6 Standby Gas Treatment 1.5 3.9 Turbine Building Unit 2 1.6 3.6 CORRECTION FACTORS POST ACCID NT VE T HO ITORS MIU JIK ~PAU ICU 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 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. 55 10.8 Selection of Data for Determination of Dose Rate Com liance 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. 56 10.9 Low-Level Radioactivit in the Sewa e Treatme t P a t 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 r adiopharmaceuticals for diagnostic or . therapeutic purposes. 'n 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. Hecause 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:

l. 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 57 p ~

OAT for radioactivity. This can be accomplished by drawing a sample from the chlorine contact chamber. 11.0 OOC R AND RE S ON CONTROL 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 ODCH '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 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. 58 DAT /o APPENDIX A SAHPL CALCU IONS OF OOC PARAH S A. 1 SEESO~ITS A. 1.1 Wate borne fflue t o ito A.1.1.1 Li uid Radwaste Dischar e ine Honitor For an unidentified mixture with an assumed HPC of 1E-7 uCi/ml, an actual activity concentration of 1E-,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 h'igh 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 Etpg ~*B 1.3 x 10 kg d Setpoint cpm 2.3E3 + Background The -LRW discharge flow setpoint is then determined as follows: A-1 f F+f = Y(A) HPC J F where Y is made equal to 10. 5000+f 10 (1E-5) f 1E-7 f 5 gpm For an identified mixture with an actual HPC of 7.22E-7 uCi/ml and the same activity concentration, blowdown. flow-and X and Y values as above, the LRM discharge monitor setpoint value and LRM discharge flow setpoint-become-. High radiation setpoint concentration (c) 3E-5 uCi/ml High radiation setpoint value 2.3E3 cpm + Background LRM discharge flow setpoint (f) 36 gpm A.1.1.2 Se ice Water Ho to 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 DOMNSCALE Setpoint. 0.5 Background (0.5)(300 cps) 150 cps 0 00 0 1400 0 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 OOMNSCALE Setpoint = Background - 0.5 (ZE-5)/Cal. Factor = 1400 cps - 0.5 (2E-5)/1.5E-S) = 1400 cps - 667 cps = 733 cps A.l.1.3 RHR Service Mater Monitor Samole Data A: Background = 160 cpm Calibration Factor = 3.9E-9 uCi/ml per cpm (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) + (ZE-5)/(3.9E-9) = BO cpm + 5128 cpm = 5208 cpm LOM RAD Setpoint = 0.5 Background = 0.5 ( 160 cpm} = 80 cpm ALERT Setpoint = 0.8 HI RAD Setpoint = 4166 cpm Samole Data B: Background = 6000 cpm Calibration Factor = 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)(ZE-5)/Cal. Factor = 6000 cpm-+ (lE-5)/(3.9E-9) = 6000 cpm + 2564 cpm = 8564 cpm LOM RAD Setpoint = Background - 0.5 (ZE<<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 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 GEC g g F89. 1 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 m~8 ZK 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 Rel ati ve Concentrati on 4.1E-5 sec/m 3 3

Decayed Depleted Rel ative Concentration 3.8E-5 sec/m 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:

Limiting Release Rate-8.95E4 Ci/yr per vent (36.6 mrem) (5 'vents)

DAT

This limiting release rate is then converted to limiting (setpoint) concentrations using Equation 6 of the ODCM and high limit vent flow rates.

Sample High Limit Vent flow Rates:

Unit 1 Reactor Building Vent 4.77E9 cc/min Unit 2 Reactor Building Vent 4.77E9 cc/min Standby Gas Treatment System Vent 5.05E8 cc/min Unit 1 Turbine Building Vent 8.64E9 cc/min Unit 2 Turbine Building Vent 6.52E9 cc/min Limiting Vent Concentration 8.95E4 Ci r vent lE6 uCi Ci 3.57E-5 uCi/cc (5.26E5 min/yr) (4.77E9 cc/min) for Reactor Buildings 152 U

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 2.61E-5 uCi/cc A.1.2.2 Iod' -13 onitor When 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 ODCN, the limiting I-131 release rate is calcu-lated as follows: I A-5 eppv OAT

Limiting Release Rate =

.24 Ci (1500 mrem = 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

.8 Ci r vent 1 6 uC Ci '.90E-9 uCi/cc for min/yr) (4.77E9 cc/min) Reactor Buildings '5.26E5 1&2 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 5.57E-B uCi/cc Unit 1 Turbine Building 3.26E-9 uCi/cc Unit 2 Turbine Building 4.32E-9 uCi/cc A. 1'.2.3 Particulate Monitor Following are the SSES Final Environmental Statement (FES) expected annual release quantities for particu-late radionuclides:

0 A-6

Cr-51 1.2E-4 Ci/yr per reactor Mn-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

's-136 1.3E-3 Cs-137 2.1E-4 Ba-140 4.2E-5

'Ce- 1 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 the inhalation pathway is 1.33E-2 mrem to the teen lung. Using Equation 5 of the ODCM, the limiting release rate of particulates can be calculated:

Limiting Release Rate 2 -3 Ci 1500 m em 8.12E1 Ci/yr/vent (2.66E-2 mrem) (5 vents)

Using Equation 6 of the ODCM, the limiting (setpoint) particulate concentrations can be calculated for each of the five plant vents.

Limiting Vent Concentration 8.12E1 Ci r vent lE6 uCi Ci 3.24E-8 uCi/cc for (5.26E5 min/yr) (4.77E9 cc/min) Reactor Buildings 152 A-7

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 2.37E-8 uCi/cc A.2 AIRBORNE EFFLUENT 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. 'or the SSES site, the critical downwind sector is the West sector with an annu'al dispersion factor of 2.6 x 10

-5 expected release rate of the principal noble gas 3

sec/m . The e 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 ODCN should be used. The whole-body dose factor (Ki) 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:

K (Ki (X/ v iv (Equation 7) wb 2

D>

= (2.94 x 10 ~re~lrrr) (2.6 x 10 sec) 3 uCi/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

the ODCH should be used. The skin dose factor (Li) from Table 2 for"xenon-133 is 3.06 x 10 mrem/yr per uCi/m . The air dose factor (H,.) from Table 2 for 3

xenon-133 is. 3.53 x 10 2 mrad/yr per uCi/m3 .

Substituting these values and the previous values for-.

release rate.and annual dispersion factor in Equation 8, the skin dose contribution from xenon-133 from the SSES would be 7.1 mrem/yr:

D (Li + 1.1 Mi) (X/Q) (Q i ) (Equation 8)

D (3.06 x 102 Smear S

uCi/m

+-1.1 (3.53 x 10- ~~)) (2.6 x 10 )

uCi/m m x (396 uCi/sec) - 7.1 mrem/year

A.2.2 Rad o u de Othe ha ob e Ga 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

-5 3 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 dose due to the release of radionuclides other than noble gases in the gaseous effluent, Equation 9 in the 00CM should be used. The inhalation pathway parameter (Ri) from Table 4 for iodine-131 is 1.62 x 10 7 mrem/yr per 3

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.

0, - (Ri) (Wv) (Q i ) (Equation 9) 0 (1.62.x 10 ~mr ~) (2.6 x 10 ~s uCi/m m X (3.8 x 10 uCi/sec) 1.6 mrem/year INHALATION PATHWAY, I-131 A-10 DAT

A.3 ~INOIOIOO I OO A.3.1 Waterborne Effluents The liquid effluent dose calculations are performed using the Liquid Annual Dose To All Persons (LADTAP II) computer program..

This program may be used to calculate the quarterly (or any other time period) doses to the maximum i'ndividual. The computer'ode LADTAP II, which was developed by the ttRC to perform dose calculations in accordance with Regulatory Guide 1.109, is used.

The User's Manual for the LADTAP II 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 progr am.

A.3.2 ~AO I The airborne effluent dose calculations are performed using the.--

GASPAR computer program. This program may be used to calculate the maximum individual and population doses due to radionuclides released in gaseous effluents from the SSES. The code 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.

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 .5the Mest 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. The total release.

6 in a calendar quarter would be 7.9 x 10 seconds times 9

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 ODCH should be used. The gamma air dose 2

factor (H ) from Table 2 for xenon-133 is 3.53 x 10 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:

D 3.17 x 10 yr Hi (X/g) gi (Equation 14) g sec D

g

.- (3.17 x 10 ~r(3.53 x 10 ~m~l~g(2.6 x 10 ~se )

3 3 sec uGi/m m X (3.13 x 10 uCi/qtr)

.9 mrad/quarter To calculate .the quarterly beta air dose due to the xenon-133 re'lease in the gaseous effluent, Equation 13 in the ODCH should be:used. The beta air dose factor (N ) from Table 2 for xenon-133 .is 1.05 x 10 mrad/yr per uGi/m . Substituting these values in Equation 13, the quarterly beta air dose contribution from--

xenon-133 releases from the SSES would be 2.7 mrad:

Db 3. 17 x 10 ~r -. N. (X/9) 9' (Equation 15) sec D> (3.17 x 10 xr )(1.05 x 10* meadr)(2.6 x 10 aaa) 3 sec uCi/m m 9

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 uid Effluents The cumulative dose to any member of the public due to liquid effluents from the SSES should be determined from the LADTAP II 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.

A-13 OAT

THIS PAGE INTENTIONALLYLEFT BLANK APPENDIX B REPORTING RE UIREHENTS 8.1 ANNUAL ENVIRONHENTAL OPERATING REPORT, PART B, RADIOLOGICAL A report on the radiological environmental surveil1ance 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 Hay of each year. The period of.

the first report shal1 begin with the date of inftfal critical,ity. The=-

reports shal1 include a suaxaary.(format. of Table B-l), interpretations, and an analysis of trends. from the results of the radiological environmental survei1lance actfvitfes for;the.report-perfod, including a comparfson with operational controls,,preoperatfonal. studies.(as.=

appropriate), and previous enviroeaental 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 shal1 be submitted noting and explainfng the reasons for the-missing results; The .-

missfng data shall be-submitted as soon as .possible in -a supplementary report.

QEG g t 1989'-

B-I

8.2 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 8-2; 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. 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 Radiological Environmental Operating Report.

When more than one of the radionuclides in Table 8-2 are detected in the medium, the reporting level will have been exceeded E

if:

concentration 1 + concentration 2 + ... - 1 reporting level (1) reporting level (2)

If radionuclides other than those in Table 8-2 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.

8-2 hr c"l D/iT~

TABLE B-1 I

SAMPLE ENVlRONHENTAL RADlOLOGICAL MONlTORlNG PROGRAM ANNUAL

SUMMARY

'eporting 'Period: 1/1/79 -'2/31/79 Medium or Pathway Sampled (Unit of Heasurement Air Particulates

( 10~

pCi/m )

~

'f Type and Total Number Analyses Performed Gross Beta 336 Lower of Limit Detection LLII ~

All indicator' Location with Nighest Locations Mean 26.6(234/234)

(7.7-71)

Name, DI 102 3.7 mi

'Annual Hean Distance N

8 29.9(52/52)

(11-71)

Control Locations Mean Ran e 28.2(102/102)

(9.8-64)

Number of Nonroutine Reported Measurements

'Be-'7 '1(20/20)

GattIIa 28 (37-130)'01 3.2 mi NE 82(4/4)

(54-'130) 85(8/8)

(51-140)

Cs-137 0.6 1.6(4/20) 1D2 5.7(2/4) 2.7(1/8)

(1.1-'1.8) 3.7 mi NE (2.3-9 0) (2.7)

Air iodine 1-131 160 1.5 - (0/109) N/A N/A -(0/51) 1 1 (10 pCi/m )

o e: e examp e fall S ~

)l g) L, f "(

J L I';

a a are provided for tl)ustrat)ve purposes only.

0 r,f} .i I 0 l)

AC ) k 689 L,

TABLE B-2 REPORTlNG LEVELS FOR NONROUTlNE OPERATlNG REPORTS Broad Leaf Water Airborne Particulate Fish Hilk Vegetation

~Ana'I sos QCh~l 'of Gases'i m~ Ci k wet ~Ci~/1 ~Ci/~k~~we t H-3 2 10 Hn-54 1x10 3 x 10 Fe-59 I

4 x 10 1x10 3

Co-58 1x10 3 x 10 2

Co-60 3 x 10 '.9 1 x 10 I '2 Zn-65 3x10 2 x 10 lr-Nb-95 4 10'( )

I-131 2 3 1x10 2 Cs-134 1

30 10 1 x 10 60 1x10 Cs-137 50 20 2 x 10 70 2x10 3

)

Ba-La-140 2 x 102(b) 3 x 102(b)

C) ffl a

For drinking water samples.

~ .' This is 40 CFR r(" l,l Part 141

>t>

value.

, 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 Oe60 (April-Nov.)

4) Fraction of crop from garden, 0.76 o) 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 67.65 if T is supplied.

7) Average temperature over growing season 60.2'F

5) Fraction of year goats are-an. pasture-0.60-

9) Fraction of daily intake of goat from pastu,re while on pasture.0.75

10) Fraction of year beef cattle a~n gesture 0.60

11) Fraction of-d.a.ily intake of beef. cattle derived from. pasture while on=

pasture 0.55

APPENDIX D SI E SPECIFIC INFORM TION USED BY L DTAP II CODE

1) Total discharge per unit: ll cubic feet per second

2) Total Annual Blowdown Volume: 6.94E8 cubic feet

3) Dose to Maximum Hypothetical Individual Shorewidth Factor: 0.2 Sediment exposure time: 131,400 hr.

USAGE FACTORS PATHWAY INFANT CHILD ADULT" Fish k r 6.9 16 21 Potable Mater 330 510 510 730 liter r Shoreline 67 12 hr/yr DILUTION FACTORS (DF)

PATHWAY LOCATION DF Fish Outfall 15.9 Potable Water Danville 321*

Shoreline Outfal 1 15.9

• For estimating purposes. Actual dilution factors at Danville, Pa., for=

various river levels located in Table 5-4.

TRANSIT TIMES (Tp)

PATHWAY LOCATION T hr Fish Outfall 25**

Potable Water Danville 25.8*

Shoreline Outfall

• For estimating purposes. Actual river transit times at Danville, Pa., for various river levels located in Table 5-.4.

• • Includes one hour transit from outfall plus 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> to consumption.

0-1

PROCEDURE REVISION

SUMMARY

TITLE: SOLID RADIOACTIVE WASTE PROCESS CONTROL PROGRAM Incorporated PCAF 1-90-0517, Standardized Waste Stream names to be consistent within plant procedures and reports to state and federal agencies. Rewrote Section 6.2, Radioactive Waste Analysis and Classification (formerly sampling section), to incorporate additional guidelines as described in BTP on Radioactive Waste Classification. Major emphasis on obtaining sample and performing analysis to ensure results are directly translated to final waste form.

Incorporated changes to records forms to summarize information required for Wastetrak (SOOR 1-90-172).

Responsibility Sections revised to provide accountability between organization for processes being performed. Added new Section 6.3 to address testing and treatment of waste generating gas as described in NRC Information Notice 90-50.

Hinor changes were performed throughout procedure to provide agreement to major changes described above.

Revised Section 6.4, to incorporate current methodology for solidification processing. Revised Attachment A to minimize redundant data tracking between the AD and lower-tier procedures.

Added new Section 6. 10 to address waste stream characteristic changes due to process or operation.

151

C NGES TO THE SOLID WASTE OCESS CONTROL ROGRA The SSES Solid Radioactive Waste Process Control Program, NDAP-gA-0646, was reviewed and found acceptable by the PORC (PORC Meetings93-055, 93-114 and 93-128) during the report period.

Revision 1 incorporated changes required to replace Scientific Ecology Group NRC-approved Topical Report STD-R-05-ll-P-A with Pacific Nuclear NRC-approved Topical Report TP-02-P-A for waste processing methods and verification of acceptable waste forms.

Specific changes that have been incorporated into revision 1 are:

1. Removed references applicable to Scientific Ecology Group and added references applicable to Pacific Nuclear.

2. Changed contracted vendor services to Pacific Nuclear for solidified radwaste processing services and referenced Topical Report TP-02-P-A.

3. Clarified mixing requirements prior to sampling to be limited to solidification liners/high integrity containers.

4. Added High Integrity Container to liner type specifically used for solidification to meet stability criteria.

5. Revised PCP surveillance specimens section due to using high integrity containers to meet stability criteria.

6. Incorporated requirements for use of Pacific Nuclear Containers.

7. Revised Solidification and Dewatering Record Sheets to incorporate implementing procedure changes.

8. Revised Implementing Procedure Matrix (Attachment D) to reflect Pacific Nuclear procedures.

9. Added new Attachment E for materials not compatible with polyethylene containers. This was previously part of Section 6.7.3.

152

Revision 2 incorporated changes for submittal of the Solid Radioactive Waste Process Control Program from the Semiannual to the, Annual Radioactive Effluent and Waste Disposal Report per Technical Specification amendment, and, to calculations performed on the Dewatering Record Sheet.

These changes did not reduce the overall conformance of the solidified waste product to existing criteria.

A copy of the SSES Radioactive Waste Process Control Program, NDAP-RA-0646, Revision 2, is attached.

The procedure revision summary on page 2 of the Process Control Program describes other previously approved changes that have been incorporated.

153

PROCEDURE CHANGE APPROVAL FORM 2.

PCAF NO. / PAGE 1 OF 3'.

PROCEDURE NO. g F' -P Qp REV. Z- 4. FORM NO

5. PROCEDURE TITLE 6. PROCEDURE TYPE Col,a gM!~4!v~ e~.W QA PROGRAM (

PLANT PROC (

) YES ( ) NO

) YES ( ) NO P;.C.e~~ C 'r O~ P gV~

7. REQUESTED CHANGE DELETE PCAFs (~) NO ( ) YES All~.& ~, <~~5~

Continued ( )

8. REASON FOR CHANGE P~, <<b~

fnm Nr..lag gcogrw rs fA sn Wv Fleas S gs v~ Vi~sl <s<s

?~( ~sC ay ~ vl

-nn'o/~~

yn <n/~7 m~??~ yS~ g~7 Vr/cr .: tW.~g -

.M4~ "-

We~7 f Z- <Z 58 r~s 7' ';.<y;Cont~.-.t~' -'.',-.

9 RECOMMENDED FOR PERMANEN ( ) YES

( ) NO, EXPIRATION DATE (60 DAY MAXIMUM FOR<<TEMPORARX..STIRPES " "" -" -':0 ~

gio~g)XF"&LANT~'PROCEDURE'LE I EHS 11 THRU 15 ON'PAGEI'"'2/0~..

16. 17 ~ MANAGEMENT".REVIElf--

3-Z INITIATOR:

k1'8"P.'AUTHORI ATION (F DATE:

LANT PROCEDURES) c. (

j

( ) QADR NOT REQUIRED:,"i.,"~..'

( ') {}ADR"PERFORMEDiwHO..'CXIQCESTS NQh".,QADR- REQUIRED~<PRIG'TO P ROV: PER" BI<QClV'g

'I SHIFT SUPERVISOR DATE MANAGEMENT,. E 19 NQA QADR 20 COMMITTEE 'EETIHO. i~ . j<~'~~ "3

a. ( ) NQA QADR NOT REQUIRED TYPE:

b ( vf NQA QADR PERFORMED, NO COMMENTS

c. ( ) N ADR ORHED, COHNFNTS ATTACHED HTG 4:

REVIE DATE: RECOMMENDED ( ~)'ES<. (

YES'*

HO-REVISED: ( NO

11. APPROV MAR 1019% 'C vs ~ .

(INI ALS ) C). Tr.

FORM NDAP-QA-0003-l. Rev. 0. DUPLEX. < a<>e l <

~gggI 1-M-1489 IQIIIllIIr~+4~~ i ~

p<<.'?

W h

I '

4*

b \

t pa4 W

p"~

k4 (r >

1 0

PROCEDURE COVER SHEET NUCLEAR DEPARTMENT PROCEDURE SOLID RADIOACTIVE WASTE NDAP-gA-0646 PROCESS CONTROL PROGRAM Revision 2 Page I of 60 EFFECTIVE DATE:

PERIODIC REVIEW FREQUENCY:

PERIODIC REVIEW DUE DATE:

REVISED PERIODIC REVIEW DUE DATE: 4 PROCEDURE TYPE: QA Program ( ) YE + (4 0 Plant Procedure~ ( ) NO REVIEW METHOD:

( ) Alternate ( ..: xpea())ted

( ) PORC 'P~~ ERC Prepared by Date Reviewed pervi tt t ~l/

Recommended Date Functional Unit M ager PORC Committee Meeting No.

Date ERC Co ittee M t No Approved by ISSSRllIEIE9$ llNQQM8!E NQRP-QR-8646 LIMSRMNMSN

NDAP-gA-0646 Revision 2 Page 2 of 60 PROCEDURE E SIO

SUMMARY

SOLID RADIOACTIVE MASTE PROCESS CONTROL PROGRAM

1) Incorporated PCAF 1-93-0873 which changes Semiannual Radioactive Effluent Release Report to Annual Release Report per Technical Specification Radioactive.'ffluent ammendments,

2) Incorporated PCAF 1-93-1065 which added calculations previously done in MM-PS-100 on Dewatering Record Sheet, NDAP-(A-0646-2.

NDAP-0A-0646 Revision 2 Page 3 of 60 ZNBEE OF C NTENTE

~SCTION . PAG 1.0 PURPOSE

2. 0 POLICY/DISCUSSION

3.0 REFERENCES

4.0 RESPONSIBILITIES 4.1 EFFLUENTS MANAGEMENT SUPERVISOR

4. 2 SUPERVISOR OPERATIONS TECHNOLOGY 4.3 POWER PRODUCTION ENGINEER EFFLUENTS HANAGEHENT 4.4 HEALTH PHYSICIST EFFLUENTS HANAGEHENT 9 4.5 RADWASTE SUPERVISOR 10 4.6 CHEMISTRY SUPERVISOR 4.7 HP FOREMAN - EFFLUENTS HANAGEHENT 12 4.8 NUCLEAR EQUALITY ASSURANCE 12 4.9 AUXILIARY SYSTEMS OPERATOR 13

4. 10 SOLIDIFICATION/DEWATERING/SERVICES VENDOR 13 4.11 MANAGER NUCLEAR PROCUREMENT 4.12 MANAGER NUCLEAR SYSTEMS ENGINEERING 14 4.13 MANAGER - NUCLEAR MAINTENANCE 14

.4:14 MANAGER - NUCLEAR REGULATORY AFFAIRS 4.15 MANAGER - NUCLEAR TRAINING 15 4.16 MANAGER NUCLEAR SECURITY 5.0 DEFINITIONS 15

NDAP-0A-0646 Revision 2 Page 4 of 60 TABLE OF CONTENTS Continued SECTION . ~AG 6.0 PROCEDURE 19

6. 1 CONTRACTED VENDOR SERVICES 19 6.2 WASTE TYPES 20 6.3 RADIOACTIVE WASTE ANALYSIS AND CLASSIFICATION 25 6.4 TESTING/TREATMENT OF SOLIDIFIED RADWASTE FOR 28 COMBUSTIBLE GASES

6. 5 RADIOACTIVE WASTE SOLIDIFICATION 28 6.6 . RADIOACTIVE WASTE DEWATERING 37 6.7 HIGH INTEGRITY CONTAINERS (HIC) 39 6.8 IRRADIATED HARDWARE PROCESSING AND DEWATERING 42'3 6.9 CONTAINER INSPECTIONS 6.10 WASTE CONTAINER SPACE UTILIZATION 43'5 6.11 STORAGE OF PACKAGED RADIOACTIVE WASTE 6.12 TRANSPORTATION, SHIPPING AND DISPOSAL REGULATIONS 6.13 SHIPPING OF RADIOACTIVE WASTE 6.14 SHIPMENT CONFIRMATION 6.15 CHANGES TO THE SOLID RADIOACTIVE WASTE PROCESS CONTROL PROGRAM 6;16 EVALUATION OF PROCESS OR OPERATIONAL CHANGES 6.17 REPORTING OF MISHAPS INVOLVING LOW LEVEL WASTE FORMS 6.18 PCP IMPLEMENTING PROCEDURES 50 7.0 RECORDS 50

NDAP-QA-0646 Revision 2 Page 5 of 60 ACHMENTS Qlj ~CHMENT ~AG A =

Solidification Record Sheet 52.

B Dewatering Record Sheet 53 C Susquehanna Guaranteed Solidified/Dewatered Waste 57 Volume Record D PCP Implementing Procedure Matrix 57 E - Materials not Compatible with Polyethylene Containers 60

NDAP-CA-0646 Revision 2 Page 6 of 60 1.0 PURPOSE Provide administrative control, guidance and records for the processing, packaging, transportation, and disposal of radioactive waste. This procedure is the Process Control Program required by SSES Technical Specifications.

2.0 POLICY DISCUSSION This procedure is applicable to Low Level Radwaste (LLRW) generated as a result of the operation of the Susquehanna Steam Electric Station (SSES). The waste streams include solid and liquid waste as defined in the FSAR, but do not include spent fuel or greater than Class C waste.

Efficient generation and processing of radioactive waste is very important to the overall operation of SSES. An important objective with respect to radioactive waste generation is to minimize the volume of-waste generated. The processing of large volumes of waste can result in the inability to dispose of or store all waste packaged, the significant .

increased costs associated with increased waste generation, and the potential to over-burden the processing system and degrade its long. ters reliability. The Process Control Program describes the envelope within which processing and packaging of radioactive waste is accomplished to provide reasonable assurance of compliance with Low-Level Waste regulations and requirements. This procedure is applicable to SSES installed systems, temporary systems and equipment provided by vendors for processing, packaging, transportation, and disposal of applicable waste forms.

3.0 REFERENCES

3.1 49CFR100 - 177, Transportation 3.2 10CFR20, Standards for Protection'Against Radiation 3.3 10CFR61, Licensing Requirement for Land Disposal of Radioactive Waste 3.4 10CFR71, Packaging and Transportation of Radioactive Material 3.5 40CFR261, Identification and Listing of Hazardous'Waste 3.6 SSES Technical Specifications Section 3/4.11.3, Solid Radwaste System 3.7 SSES Technical Specifications Section 6.1.3, Process Control Program (PCP)

NDAP-gA-0646 Revision 2 Page 7 of 60 3.8 NUREG 0800, Standard Review Plan 11.4 Solid Waste Management Systems 3.9 Technical Position on Maste Form Rev. 1, 1991 3.10 Technical Position on Radioactive Waste Classification, Rev. 0, 1983 3.11 Regulatory Guide 1.21, Measuring, Evaluating and. Reporting Radioactive Haterial in Solid Wastes and Release of Radioactive-Haterial in Liquid and Gaseous Effluents from Light Water Cooled Nuclear Power Plants 3.12 Regulatory Guide 1.143, Design Guidance of Solid Waste Management Systems

3. 13 Regulatory Guide 7.1, Administrative Guide for Packaging and Transporting Radioactive Material 3.14 ANSI/ANS 40.35, Volume Reduction of Low Level Radioactive Waste-3.15 ANSI/ANS 55.1, Solid Radioactive Waste Processing System for- Light Mater Cooled Reactor Plant 3.'16 Pacific Nuclear Dewatering System Topical Report No. TP-02-P-A, Revision 2 3;17 Pacific Nuclear Solidi'fication Process Control Procedure No.

PT-51-WS, Revision 20 3.18 Disposal Site Criteria for Barnwell, S.C.

3.19 Disposal Site Criteria for Richland, Washington 3.20 DHEC-HIC-PL-001 South Carolina Certificate of Compliance for CNSI High Integrity Containers 3.21 DHEC-HIC-P0-006, South Carolina Certificate of Compliance for CNSI Overpack High Integrity Containers 3.22 DHEC-HIC-PL-012, South Carolina Certificate of=Compliance for Pacific Nuclear Systems, Inc.,High Integrity Container 3.23 PLA-1237, Process Control Program, August 17, 1982 3.24 Review of Process Control Program for Susquehanna, Unit 1, Youngblood to Curtis, September 30, 1982 3.25 Safety Evaluation NL-93-008, Solid Radwaste Maste Processing Services Utilizing Pacific Nuclear Processing System

NDAP-QA-0646 Revision 2 Page 8 of 60 3.26 IE Bulletin 79-19, Packaging of Low Level Radioactive Waste for Transportation and Burial

(') 3.27 NRC Information Notice No. 90-50, Minimization of Methane Gas Generation in Plant Systems and Radwaste Shipping Containers

( ) 3.28 Generic Letter 91-02, Reporting Mishaps Involving LLM Forms Prepared for Disposal

( ) 3.29 SOOR-1-90-148, Barnwell Received Container Pressurized with Flammable Gas

( ) 3.30 SOOR 1-90-172, Incorrect Sampling Method Used on Resin Liner

( ) 3.31 SOOR 1-91-322, Dose Rates on Container Higher Than Expected 4.0 ~RP N IBILITIE 4.1 Effluents Management Supervisor responsibilities:

4;.l. 1 Developing and implementing programs and procedures for radioactive waste processing, packaging, transportation and disposal.

4.1.'2 Maintaining the overall radwaste program to ensure compliance with applicable radiological and shipping regulations.

4.1.3 Ensuring personnel who perform support activities such as processing, packing, and transportation of low level radioactive waste are available and meet all qualifications and training required by SSES procedures.'ollecting, 4.1.4 maintaining, reviewing and submitting accurate data/information related to waste stream quantity and nuclide composition for inclusion into Annual Radioactive Effluent Release Report and State DER-BRP Quarterly Report.

4.2 Supervisor - Operations Technology responsibilities:

4.2.1 Providing technical assistance to Effluents Management personnel. This includes interpretations of state, federal, and disposal facility regulations regarding new, imminent, or proposed regulatory changes governing processing, packaging, transportation, and disposal.

NDAP-gA-0646 Revision 2 Page 9 of 60 4.2.2 Haintaining a current copy of local, state, federal and disposal facility regulations pertaining to disposal and transportation of low level radioactive waste.

4.2.3 'oordinating the submittal of the Annual Radioactive Effluent Release Report as per the SSES Technical Specifications.

4.2.4 Haintaining non-process control computer software for.

main-frame based systems, including software vendor; initiating program changes, and proper operation of" the software.

4.3 Power Production Engineer-- Effluents Hanagement responsibilities:

4.3.1 Ensure procedures are adequate to provide for proper.

solidification and dewatering of waste.

4.3.2 Ensure test data or-rationale is available to justify applicable solidification and dewatering functions of each waste type, or- any combinations, to.address disposal and regulatory agencies~ requirements.

4.3.3 Evaluate services provided'y various vendors to ensure contracted solidification and dewatering operations are performed in the most efficient and economical method, as required by the applicable regulatory agencies.

4.3.4 Perform the duties of Radwaste Supervisor as specified in this procedure in his absence.

4.3.5 Define waste streams based on generator, filtration media and means of processing.

4.3.6 Collecting, reviewing and submitting data related to the reporting of.mishaps and results of PCP surveillance specimen examinations to applicable regulatory agencies.

4.4 Health Physicist-- Effluents Hanagement responsibilities:

4.4.1 Haintain a sampling;and analysis program to ensure 10CFR61 compliance.

4.4.2 Ensure procedures are-adequate to provide for proper packaging and shipment of waste to ensure compliance with all applicable regulations.

NDAP-QA-0646 Revision 2 Page 10 of 60 4.4.3 Evaluate services provided by various vendors to ensure contracted waste packaging, processing, and transportation services are performed in the most efficient and economical method, as required by applicable regulatory agencies.

4.4.4 Perform the duties of HP Foreman - Effluents Management as specified in this procedure in his absence.

4.4.5 Coordinate radioactive material evaluation of product acceptability for disposal at specific disposal facilities.

4.5 Radwaste Supervisor responsibilities:

4.5.1 Ensure Solidification/Dewatering Equipment is operated in accordance with approved operating procedure, including vendor supplied equipment.

4.5.2 Ensure appropriate waste solidification and dewatering records are generated.

4.5.3 Interface with station support groups to ensure proper implementation of process control programs.

4.5.4 Provide direction to contractor personnel involved in solid waste processing activities including:

a. Ensuring test data is available to justify specific processing techniques.

b. Ensuring applicable vendor procedures and revisions are incorporated into applicable plant procedure and approved by PORC.

c. Coordinating pre-processing and post-processing .

treatment activities.

d. Evaluating services provided to ensure efficient.

and economical methods are used.

4.5.5 Ensure Solidification and Dewatering operations are carried out in an ALARA manner.

4.5.6 Interface with HP Foreman -'ffluents management for-liner and cask selection for solid waste shipping activities.

NDAP-OA-0646 Revision 2 Page ll of 60 Ensure proper marking of containers prior to filling.

4.5.7'.5.8 Ensure solidification/dewatering personnel are

'dequately trained per NTP-gA-42.3 and NTP-(A-42.6.

4.5.9 Estiyate classification of waste for container selection and processing method.

4.5.10 Ensure that waste streams loaded into High Integrity Containers are sampled for radionuclide and evaluated for chemical compatibility applicable to the use of High Integrity Containers.

4.5.11 Ensure proper inspections and documentation are complete prior to use of a High Integrity Container and ensure that container is properly used up to the point of transfer to .HP Foreman Effluents Management.

4.5.12 Complete and process High Integrity Container User Certificatton Statement to ensure the container is used properly.

4.6 Chemistry Supervi sor responsibilities:

4.6.1 Perform required sampling preparation and analysis in accordance with approved chemistry procedures.

4.6.2 Perform test solidification if required. Store test solidification billet if required.

I 4.6.3 Store samples used for dewatered waste stream analysis until associated liner is disposed.

4.6.4 Provide density of initial and final waste form.

4.6.5 Provide the isotopic mix and concentration of isotopes detected in the material sampled for solidification or dewatering.

4.6.6 Complete Chemistry portion of the Solidification and Dewatering Records.

4.6.7 Ensure personnel are adequately trained per NTP-(A-41.2.

4.6.8 Provide chemical analysis and/or treatment support as necessary for use of High Integrity Containers and liners.

NDAP-0A-0646 Revision 2 Page 12 of 60 4.7 HP Foreman -'ffluents management responsibilities:

4;7.1 Interface with Radwaste Supervisor for liner and cask selection and scheduling for solid waste shipping activities.

4.7.2 Complete, process, and file radioactive waste shipping documentation.

4.'7.3 Storage of packaged radioactive waste within the radwaste facilities.

4.7.4 Determine waste classification and description of solidified, dewatered, and other packaged waste.

4..7. 5 Final disposition of solidified, dewatered and other 8

packaged waste.

4.7.6 Ensures SSES is a registered user of applicable High Integrity Containers at,.specific disposal facilities.

4.7.7 Ensures HP personnel involved with radioactive waste handling have received Radwaste Worker training per NTP-(A-42.3.

4.7.8 Evaluate vendor services provided to ensure efficient and economical methods are used.

4.7.9 Complete and process Certification Statement for Disposal of High Integrity Containers as required by applicable regulatory agencies.

4.7.10 Process and package Cartridge Filters, Dry Active Waste, solid sealed sources and other non process wastes.

4.7.11 Collection of DAW and non-process waste (10CFR61) samples.

4.8 Nuclear guality Assurance responsibilities:

4.8.1 Perform periodic audit of implementation of this program and review of radwaste service vendor's gA Programs.

4.8.2 Inspection of Radwaste Containers as required by applicable procedures.

NDAP-gA-0646 Revision 2 Page 13 of 60 4.8.3 Ensure process controls are adhered to by inspection of test solidification, waste volumes, solidification agent additions, product acceptability checks, dewatering process sequence/acceptance criteria and records review.

4.8.4 Inspection of packaging, storage, and shipping activities, as required by applicable procedures.

4.9 Auxiliary Systems Operator is responsible for operating the plant solid and liquid radwaste equipment. in accordance with approved operating procedures as directed by the Radwaste Supervisor and Assistant Unit Supervisor.

4.10 Solidification/Dewatering/Services Vendor responsibilities:

Provide solidification, dewatering and/or volume reduction services in accordance with a valid contract for said services.

4.10.2 Provide test data or make data 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.

4.10.3 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.

4.10.4 Provide procedures that are or can be placed into the SSES procedure format for the services being provided.

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.

4.10.6 Complete applicable sections of Solidification and Dewatering Records required for-each container processed.

4.10.7 Ensure pre-qualification test data for each waste form shall be submitted to the Nuclear Regulatory Commission.

4.10.8 Provide a description of the equipment/process that is used in processing waste.

NDAP-gA-0646 Revision 2 Page 14 of 60 4.10.9 Obtain waste samples from processing .equipment in accordance with approved operating procedures.

4.10.10 Perform all pre and post'reatment activities as determined by Radwaste Supervisor.

4.11 Manager Nuclear Procurement responsibilities:

4.-11.1 Ensure High Integrity Containers are not exposed to ultra violet light (sunl.ight).

4.11'.2 Ensure proper material certification is complete prior to .issuance of High Integrity Containers to plant for use.

4.11.3 Receipt inspection of High Integrity Containers and document review to ensure conformance.

4;11.4 Ensure Certificate of Compliance (C of C) is received with High Integrity Container.

4.12'anager Nuclear Systems Engineering is responsible for. providing engineering support as required for operation of assigned radwaste systems and equipment.

4.13 Manager Nuclear Maintenance responsibilities:

4.13.1 Calibration and maintenance of applicable plant equipment in Radwaste Processing Systems.

4.13.2 Provide maintenance personnel to support processing, packaging and transportation of low level radioactive waste.

4. 14 Manager - Nuclear Regulatory Affairs responsibilities:

4.14.1 Submitting transportation cask user registration requests to NRC per 10CFR71.12.

4.14.2 Submitting to the NRC the Annual Radioactive Effluent Release Report.

4.14.3 Coordinating and submitting to the NRC the reports required as a result of Significant Operating Occurrence Report (SOOR) events, investigations, and resolutions.

NDAP-QA-0646 Revision 2 Page 15 of 60 4.15 Manager Nuclear Training responsibilities:

4.15.1 Providing training and re-training in applicable regulatory requirements to personnel directly involved in transfer, processing-, packaging, storage, and transport of radioactive waste.

4.15.2 Maintaining a record of training, attendees, and subject material for all Low Level Radioactive Waste training.

4.16 Manager Nuclear Security is responsible for notifying appropriate law enforcement agencies in the event of lost radioactive material shipments.

5.0 ~EINITiG 5.1 APPROVED CONTAINERS: Approved means approval issued or recognized by the NRC for-use in shipment of-radioactive material.

5.2 BATCH

The total volume of waste contained in a liner, isolated-waste mixing tank - spent resin tank concentrates tank or phase separator that has been sampled for-solidification/dewatering.

5.3 BILLS OF LADING: Shipping papers or manifests serving a similar purpose and containing the information required by 49 CFR 172.202, 203, and 204.

5.4 CARRIER

Means a person engaged in the transportation of passengers or property. '10CFR71.4) 5.5 CERTIFICATE OF COMPLIANCE: License requirements established by the Nuclear Regulatory Commission-for the use of- approved Radioactive Material Shipping Containers.

5.6 CHELATING AGENT: A chemical which combines with a metal so as to form a ring structure held by coordination bonds.

5.7 CHEMICAL FORM: The chemical content of the Radioactive Material being shipped.

5.8 CLOSED TRANSPORT VEHICLE: A-vehicle equipped with a securely attached exterior enclosure, which during normal transport, restricts the access of unauthorized. persons to the cargo space.

(49 CFR 173-403[C])

NDAP-QA-0646 Revision 2 Page 16 of 60 5.9 COMPOSITE SAMPLE: A mixture of samples collected representing conditions at tim'e of sampling, from the same sampling point, at different times.

5.10 CONSIGNEE: The individual or organization to whom the shipment is consigned or intended.

5.11 CURING TIME: The time allowed for the solidified product to set prior to its evaluation for product acceptability.

5.12 DECAY HEAT: The heat produced by radioactive decay, usually expressed in Watts or BTU/hr, but can be related to Curie Content..

5. 13 DEWATERED: The removal of free liquid from solid material to a point where less than IX for HIC's and l,ess than 0.5X for steel liners by waste volume remains as required by the disposal facility license.

5.14 EXCLUSIVE USE VEHICLE (a/k/a: Sole Use or Full Load): Shipment from a single consignor having the exclusive use of a transport vehicle and for which all initial, intermediate, and final loading and unloading is carried out by, or under the direction of the consignor, consignee, or his designated agent. (49 CFR 173.403[i])

5.15 FREE LIQUID: Liquid which is still visible after solidification or dewatering is complete, or"is drainable from the low point of a punctured container .

5.16 HAZARDOUS WASTE: Waste which contains material listed in 40 CFR 261, Subpart D and/o} exhibits one or more of the four characteristics cited in 40 CFR 261, Subpart C, and is not excluded from regulation under 40 CFR 261, Subpart A.

5.17 HIGH INTEGRITY,CONTAINER (HIC): A disposal site approved container that has an expected life of 300 years and provides the structural stability to meet disposal requirements.

5.18 HIGHWAY ROUTE CONTROLLED QUANTITY: A quantity, the aggregate radioactivity of. which exceeds that specified in (49 CFR 173.403[1]).

5.19 ISOTOPIC ANALYSIS: The identification of the isotopic elements involved in a sample of Radioactive Material.

5.20 LABELING: Labels applied to a container denoting the contents of the container and degree 'of hazard associated with the containers.

The labels are identified as the White I label, the Yellow II, and Yellow III label. A label stating Radioactive - LSA can also be applied to a container when 'appropriate. (49 CFR 172, Subpart E)

NDAP-OA-0646 Revision 2 Page 17 of 60 5.21 LIMITED QUANTITY OF RADIOACTIVE MATERIAL: Means a quantity of radioactive material not exceeding the material package limits specified in 49 CFR 172.423, and which conforms with requirements specified in 49 CFR 173.421. (49 CFR 403[m])

5.22 LINER: Steel cogtainer in which dewatered or solidification product is deposited.

5.23 LOW SPECIFIC ACTIVITY: Haterial in which the activity is essentially uniformly distributed and in which the estimated average concentration per gram of contents does not exceed the specification as stated in 49 CFR 173.403 (n).

5.24 LOW -LEVEL RADIOACTIVE WASTE (LLRW): Radioactive waste generated as a result of operation of SSES, excluding spent fuel or by product material, is classified by the NRC as low-level radioactive waste. LLRW does not include "greater than class C" waste.

5 25 MIXING RATIO: The ratio of waste to cement and additives required for satisfactory solidification.

5.26 MIXING RECIPE: The amount of waste, cement and additives mixed to solidify waste.

5.27 MIXED 'WASTE:' mixture of low level radioactive and hazardous waste.

5. 28 NORMAL FORM RADIOACTIVE MATERIALS: Means radioactive materials which do not meet the requirements of Special Form Radioactive Materials.

5.29 PLACARDING: A label affixed to all four sides of the transport vehicle denoting the presence and level of Radioactive material on the vehicle. (49 CFR 172; Subpart'F) 5.30 PROCESS CONTROL PROGRAM (PCP): Program which contains the sampling, analysis, and formulation determination by which, solidification of radioactive wastes from liquid systems is assured.

5.31 RADIOACTIVE MATERIAL: For purposes of transportation only, material in which the activity is essentially uniformly distributed and the estimated specific activity exceeds 0.002 microcuries per gram of material. (49 CFR 173.403[y] and [aa])

5.32 RADWASTE WORKER: Any individual involved with the collection, packaging, and transportation of radioactive waste.

NDAP-QA-0646 Revision 2 Page 18 of 60 5.33 SEALED SOURCES: Any by-product material that is .encased in a

~

capsule designed to prevent leakage or escape of by-product material.

5.34 SOLIDIFICATION: A conversion of radioactive materials from liquid and solid systems to a homogeneous (uniformly distributed) monolithic, iamobilized solid with definite volume and shape;-

bounded by a stable surface of distinct outline on all sides (free-standing). I 5.35 SOLIDIFIED RADMASTE: Net waste which is solidified (e.g.

evaporator concentrates, sludge), meets'the free liquid criteria, and satisfies applicable transportation and disposal site requirements. Oewatered resins or filter sludge satisfying the-twa lattor cr$ tor$ o shall also bo dofinod ai aolidif)ad radwaito..

5.36 SPECIAL FORM RADIOACTIVE MATERIALS: Radioactive material that -is=.

either a single piece, or is contained in a,sealed capsule,'hat;=

can be opened only be destroying the capsule and meets the additional requirements specified in 49 CFR'art 173.403(z). z4'.-::,

5.37 STABLE AND UNSTABLE MASTE FORMS'; Shill be defined as stated,in 61 and other supporting regulatory 4oceaents. 'OCFRPart 5;38 ~

TEST SOLIDIFICATION: The mixing of waste(s) and solidificatioa':.

in the laboratory tq support selectipn'of mixing ratias."and 'gents provide insurance for final product acceptgility. s 5.39 INDEX (TI): The dimensionlesW nupber placed on thee.,'.

A'RANSPORT of a package to designate the.degmee "yf'control-to'be-.. :"~; 'abel exercised by the carrier during transportat)on. The. transport  ;

index will be determined in accordance with 49 CFR- 173.403(bb)'.-'-

5.40 TYPE "A" PACKAGING: Packaging. which is designed in accordance .

with the general packaging requirements of 49 CFR 173.24;. and'"-;.-"'hich is adequate to prevent the loss or dispersal. of the--

radioactive contents, and to:retain the efficiency ofits.:

radiation shielding properties- if- the package is sub)ected:;to"the'.

test described in 49 CFR 03.465 or 173.466< ys appropriate.'. '.;;.'49.CFR 173.403[ggj) 5.41 TYPE "A" QUANTITY RADIOACTIVE MATERIAL: That material which aiy~

be transported in Type 'A'ackaging. (173;431[aj) 5.42 TYPE "B" PACKAGING: Packaging which meets the standards for"Type "A" Packaging, and in addition, meets the standards for. the hypothetical accident conditions of transport.

(49 CFR 173.403[hhj)

NDAP-gA-0646 Revision 2 Page 19 of 60 5.43 TYPE "B" QUANTITY RADIOACTIVE NTERIAL: That material which may be transported in Type "8" packaging. (173.431tb))

5.44 WASTE STREN: A by-product of a process system or. component with unique characteristics and maintained separate from other waste streams.

5.45 WASTE TYPE: Specific contents of a liner or tank which may contain one or multiple waste streams, the category of waste suitable for a particular means of processing.

5.46 WASTE PRE-CONDITIONING: The physical or. chemical adjustment of the waste to bring solidification.

it within an established envelope to assure 6.0 Q~OC D~U 6.1 CONTRACTED VENDOR SERVICES

~;

6.1.1 Solidified radwaste processing, services=,are provided~~~

by , Inc. for=waste:types.,inc)uded=.in-V<~ s Pr ocess Control Program.

6.1..2 NRC,approved Topical Report'..TP.-02-'P-'A;.descrVbes ." ~'-

V <. I..:., -t -0 methods and verification of=-acceptable:.waste-:foims-fiie.-

-IW:W iP t.:.. '-

dewatering.

Ve. ro'rtrO-'

6.1.3 . S 1Mltl t% pV .C 1.';-.

Procedure PT-51-WS, describes;:waste -processing-..

equipment, methods and verifi'cation~f="acceptable:-

waste forms for solidification;-,

provide stability per.the-.Branch~iechnical-Th1s=pyocedurs=-does:.'ot Position-.on Waste Form; Revision":2; .-', 'M 6;1.4- Volume reduction services- are;provided by. Scientific Ecology Group (SEG) for waste types-.in@luded-.in'.the==;-

Process Control Program;-

PQ [

6.1.5 contracted vendor services which'-are,requiredx g'ther for solidification, dewatering-and'volume reduction'".

services= shall be evaluated.'to:the."requirements-stated in this Process Control Program on, a case by. case basis.

NDAP-gA-0646 Revision 2 Page 20 of 60 6.2 IIIASTE TYPES The following waste types shall be processed in accordance with this procedure or in combinations as defined. The waste should be-dewatered whenever possible to minimize disposal volume.

6.2.1 Evaporator Concentrates a ~ The following are concentrated with the Radwaste Evaporators and are considered Evaporator Concentrates waste stream:

(1) Condensate Demineralizer regeneration effluent (2) Decon Shop drains (3) Chemistry Laboratory sink drains (4) Auxiliary Boiler blowdown effluent

b. The constituents of this waste stream may include the following:

(1) Tri-Sodium Phosphate (2) Sodium Sul fate (3) Phosphoric Acid (4) Sulfuric Acid (5) Sodium Hydroxide (6) Decontamination solutions (7) Negligible amounts of reagent chemicals used for chemistry analysis c~ Evaporator Concentrates in the range of 0-24 weight percent sodium sulfate (equivalent) shall be-solidified for final disposal.

d. Evaporator Concentrates shall not be mixed with any other waste type in final processing.

0 NOAP-QA-0646 Revision 2 Page 21 of 60 Mixed Solids a ~- The following process waste streams are col.lected either in Waste Mix Tanks, Waste Sludge Phase Separator or transferred directly to a liner/High Integrity Container and are considered Mixed Solids:

(1) LRW Filter Media and drain liquid (2) Sump Sludge (3) Ultrasonic Resin Cleaner Waste (URC Waste)

b. The constituents of these waste streams may include the following:

(1) Diatomaceous Earth (2) Powdered Resins (3) Fibrous material (4) Carbon materi al =

(5) Corrosion products (6) Various solids and dirt in small concentrations c~ Mixed Solids may be solidified or dewatered for final disposal.

d. Each waste stream should be processed separately.

RWCU Filter Media

'a ~ The Reactor Water Cleanup System and Fuel Pool Cooling and Cleanup System filter/demineralizer waste are collected in the RWCU Phase Separator and should be allowed to decay for 60 days.

This waste stream is considered RWCU Filter Media.

b. The constituents of this waste stream may include anion and cation powdered resin, corrosion and contaminants removed from the primary coolant.

NDAP-QA-0646 Revision 2 Page 22 of 60 Co RWCU Filter Media shall be dewatered in High Integrity Containers. If this waste must be solidified, Technical Specification 3/4.11.3 action statement must be performed.

Condensate/Radwaste Demineralizer Bead Resin a ~ Resins from the Condensate Demineralizers, Liquid Radwaste Demineralizer and vendor provided demineralization are collected in the Spent Resin Tank or transferred directly to a liner/High Integrity Container. This is considered to be Condensate/Radwaste Demineralizer Bead Resin.

b. The constituents of this waste stream may include various types of anion, cation, mixed bead resin and corrosion and contaminates removed from liquid waste streams.

C. Bead Resin may be solidified or dewatered for final disposal.

d. Bead Resin may be used to demineralize Chemical Waste in either steel liners or High Integrity Containers. " The Bead Resin may be solidified or dewatered for final disposal.

e. Condensate demineralizer bead resin should be ultrasonically cleaned prior to collection in the Spent Resin Tank.

Bead Resin may be processed by volume reduction methods which include drying, incineration, compaction or use as fill materials.

Cartridge Filters

'a ~ Cartridge Filter waste type consists of the following waste streams and constituents:

(I) CRD Filters - CRD or other filters and small un-irradiated primary system equipment such as valves, CRD lift pump filters, Rinse Tank filters and other metal components.

(2) RMCU Septa Septa from RWCU Filter Demineralizer including septa from Fuel Pool Cleanup Filter Demineralizer.

NDAP-gA-0646 Revision 2 Page 23 of 60 (3) Radwaste Filters including degasifier filters and other fiber or paper filters other than primary system.

(4) Underwater Vacuum Filters - non-process filters generated from wet cleaning activities.

b. Cartridge Filters may be processed by the following methods:

(I) Emplacement in a cement matrix in a steel drum/liner or in a High Integrity Container.

(2) Dried to a point where no free liquid is visible. Absorbent material may be included to absorb unintentional and incidental amounts of liquids.

(3) Dewatered if drying is impractical.

c~ Cartridge Filters to be solidified for final disposal shall not be mixed with any other waste type.

d. Each cartridge filter waste stream should be packaged separately unless analyzed prior to packaging in accordance with the requirements of this procedure.

Irradiated Hardware a~ Irradiated hardware is neutron activated metal removed from the internal area of the reactor pressure vessel. This waste stream is considered Irradiated Hardware.

b. The constituents of this waste stream may include control rod blades, LPRMS~s, IRK>s, TIP's and components expended during hardware processing and packaging activities. Startup;.

sources may also be processed as part of this waste stream.

c~ Irradiated hardware is packaged in steel liners for disposal.

d. Liquid shall be drained to ensure free liquid Acceptance Criteria are met.

NDAP-gA-0646 Revision 2 Page 24 of 60

e. Irradiated'hardware shall not be mixed with any other waste type in final processing.

Dry Active Waste -(DAW) a ~ Dry Active Waste is a waste stream.

b. The constituents of this waste stream consist of contaminated paper, plastic, wood, metal and f

other discarded material.

c~ Dry Active Maste shall be processed by volume reduction methods which may include incineration, compaction, decontamination and metal melting.

d. At a minimum, DAM shall be packaged in strong-

'tight containers.

'Liquid Oil Maste or Petroleum Based Haterials a ~ The constituents of this waste stream may include turbine lubricating oil, EHC fluid and other petroleum based materials.

b. Contaminated Liquid Oil Maste generated at the facility should be processed by a decontamination system, solidified for final disposal, or volume reduced by incineration, or other acceptable methods.

c~ Liquid Oil Waste at concentrations 1X and greater may be solidified provided the following are adhered to:

'(I) An emulsification agent is added at required concentrations.

(2) 'he Liner is NOT SHIPPED to Barnwell S.C.

Disposal Facility.

Solid Sealed Sources

a. -

Solid Sealed Sources requiring disposal shall be packaged for disposal as requested by Health Physics Supervision.

b. Hethod of disposal is dependent on waste class of the Solid Sealed Source and disposal facility requirements.

NDAP-QA-0646 Revision 2 .

Page 25 of 60

c. Acceptable methods of disposal include:

Placement within a container consisting of another waste type provided:

(a) The source contains isotopics already in the waste.

(b) The "source activity is significantly less than the waste activity.

(2) Class B and C sources shall be stabilized within an approved solidification or encapsulation media.

6.2.10 A Waste Type that is combined with a known amount of hazardous waste or "Mixed Waste" shall be processed for final disposal pending approval obtained from the-disposal facilities, Environmental Protection Agency, and U.S. Nuclear Regulatory Commission.

6;2.11 Waste types containing chelating agents within the range of O.l to 8.0 percent by weight shall be processed to a stable waste form in accordance with and authorized by Barnwell, S.C. Disposal Facility requirements and approvals.

6:2.12 Various other materials not specifically identified as waste types will be evaluated for solidification,,

dewatering volume reduction or other processing on a case by case basis.

(") 6.3 RADIOACTIVE WASTE ANALYSIS AND CLASSIFICATION 6.3.1 Radionuclide concentrations of radioactive waste are used to classify waste for shipping and disposal.

Radionuclide concentrations should be determined based upon isotopic analysis, volume and weight of final waste form.

NDAP-gA-0646 Revision 2 Page 26 of 60 The 10CFR61 Compliance'Program establishes a methodology for characterizing radioactive waste through the use of correlation factors. This program shall require as a minimum that:

a0 Samples representative of Susquehanna's waste streams are collected and analyzed such that results are obtained from a designated laboratory at least every two years (Class A) for development of specific correlation factors.

Waste streams known or suspected to be classified Class B or Class C should be analyzed on an annual basis.

b. Technical basis documentation and justification of correlation factors are developed for each waste stream and are acceptable for use.

Periodic evaluations and necessary adjustmentc to established ratios are performed in a timely manner.

c~ Correlation factors are re-evaluated following significant changes (greater than a factor of

10) in plant operations (such as significant changes in fuel leakage, radwaste operations, or equipment).

Determination of waste classification shall be in accordance with 10CFR61.55, Waste Classification, and its supplementary Branch Technical Position on Radioactive Waste Classification as follows:

a 0 Class A - Usually segregated from other waste classes at the disposal facility. Physical form and

,characteristics shall meet the minimum requirements specified in 10CFR61.56(a). If the stability requirements in 10CFR61.56(b) are met, the waste does not have to be segregated for disposal.

b. Class 8 - Physical form and characteristics shall meet, both the minimum and stability requirements specified in 10CFR61.56.

c. Class C - Physical form and characteristics shall meet both the minimum and stability requirements specified in 10CFR61.56. In addition, measures shall be taken at the disposal facility to protect against inadvertent intrusion.

NDAP-OA-0646 Revision 2 Page 27 of,60 Isotopic analysis may be performed by:

a~ Gamma spectrometry of a sample and use of correlation factors.

b. Direct gamma spectrometry of waste and use of correlation factors.

C.. radionuclide analysis of waste sample.

d..'omplete Dose to Curie calculations.

e. Activation analysis.

Volume and weight of final waste may be determined by:

a~ Calculation using analytically derived sample densities.

b. Calculation using standard waste densities.

c~ Direct measurement of volume and weight.

If samples of waste are used for classification, sampling program shall include:

'a Samples shall be obtained and analyzed for each

~

batch of wet waste if practical and ALARA.

b. Preferentially, samples should be taken for analysis following processing into a final waste form.

c~ Samples taken prior to final processing should enable results of'sample analysis to be directly translated to final waste form.

d. Bead resin used for. chemical demineralization shall be sampled"after resin has been depleted in process.

e. Solidification/Dewatering Services Vendor or another qualified individual shall obtain required samples.

Preparation of waste for sampling or analysis a ~ Wet Waste Collection tanks shall be recirculated in accordance with approved operating procedures prior to sampling or analysis.

NDAP-QA-0646 Revision 2 Page 28 of 60

b. Waste processing in solidification liners/High Integrity Containers shall be mixed in accordance with approved procedures prior to sampling or analysis.

c. Wet waste to be processed may also be mixed, recirculated and sampled or analyzed from mobile processing equipment.

6.3.8 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 final 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.

6.3.9 Deviations from sampling and analysis requirements shall be approved by Chemistry Supervisor and Effluents Nanagement Supervision.

6.4 TESTING/TREATMENT OF SOLIDIFIED RADWASTE FOR COMBUSTIBLE GASES 6.4.1 Solidified waste shall be tested and/or treated to ensure it is not c'a'pable of generating quantities of flammable or toxic gases, vapors or fumes which may be harmful to persons transporting, handling, storing or disposing of the waste.

6.5. RADIOACTIVE WASTE SOLIDIFICATION 6.5.1 General Requirements.

1

a. Wet Waste Types which may be solidified in High Integrity Containers are Evaporator Concentrates, Mixed Solids, Condensate/Radwaste Demineralizer Bead Resin, RWCU Filter Media and Liquid Oil Waste or Petroleum Based Haterial, Cartridge Filters and Solid Sealed Sources.

b. High Integrity Containers shall be used to meet the stability criteria in accordance with federal and disposal facility regulations.

c. Solidification processing shall be conducted by qualified SSES or Solidification/Dewatering/

Services Vendor. personnel.

NDAP-gA-0646 Revision 2 Page 29 of 60

d. The solidification process shall be operated in accordance with approved procedures. Procedures shall specify waste stream, amounts of solidification agent and additives or method for determination.

Waste Preconditioning

a. Waste preconditioning requirements shall be determined by 'chemistry analysis.

b. Preconditioning of waste shall be performed if-required prior to determining mixing ratios.

C, Waste preconditioning is required when any of the following conditions exist:

(1) A high or low pH condition, as determined-by. chemical analysis.

(2) Liquid content of the batch is out of the acceptable envelope for solidification.

(3) Solids content of the batch is out of the acceptable envelope for solidification.

(4) Known potential problem chemicals and constituents within waste that may adversely affect setting and stability of cement-solidified waste form.

d. Waste preconditioning shall be performed in accordance with approved procedures to ensure waste is within the acceptable envelope for solidification.

e. Upon completion of waste preconditioning, additional samples, as required, shall be obtained in accordance with Radioactive Waste-Analysis and Classification section of this procedure.

Determination of.Nixing Ratios a ~ Determination of mixing ratios shall be performed for each waste batch to be processed.

b. Deviation from the recommended mixing ratios shall be reviewed by Plant Operations Review Committee (PORC).

NDAP-QA-0646 Revision 2 Page 30 of 60 c ~ Chemistry Group determines:

(1) Density of the waste samples.

(2) Specific gravity of Sodium Sulfate Solution in Evaporator Concentrates.

d. Solidification/Dewatering/Services Vendor determines if the final mixing ratios are within the acceptable envelope for solidification.

e. Chemistry Group shall perform test solidification of waste as required by Test Solidification section of this procedure.

Chemistry Group determines mixing ratios to ensure proper solidification.

Test Solidification a ~ Test solidification shall be performed to support waste mixing ratios as follows:

(1) At least every tenth (10th) batch of the same waste stream.

(2) When sample analysis fall outside the established range and criteria indicating a change in waste characteristics.

(3) When it is believed that some unexpected or abnormal contaminant may be present.

(4) When requested by Radwaste Supervisor.

(5) Mixing of materials shall be accomplished in a manner that duplicates, to the extent practical, mixing conditions that are obtained with full-scale mixing in container.

(6) Curing shall be performed under conditions similar to those used in laboratory qualification test program.

NDAP-OA-0646 Revision 2 Page 31 of 60

b. Upon failure of a test solidification, an LCO is entered, additional samples shall be obtained, alternative solidification parameters are determined and a subsequent test verifies solidification. Test solidification shall be performed on each subsequent batch of the same--

waste stream until at least three (3) consecutive initial test solidification demonstrate acceptability in accordance with Technical Specification 3/4.11.3.

c~ guality Control shall verify test solidification acceptability and indicate the acceptability on the surveillance documentation. The acceptability requirements are defined in the PCP Surveillance Specimen section of this procedure.

d. Extra sample volume for backup testing shall be of after container disposal. 'isposed

e. High Integrity Container test solidification billet should be disposed after container disposal.

Test solidification should be performed with waste from samples obtained as follows:

(1) In accordance with Radioactive Maste Analysis and Classification section of this procedure.

(2) Sampling of the solids in the container and the liquids used for hydration, then mixed to the ratios that exist in the container.

Test Solidification Procedures shall be developed for each specific waste type.

h. Cement, water type and additives to be used in actual solidification shall be used in preparation of test solidification.

PCP Surveillance Specimens

'a ~ High Integrity Container test solidification" billets shall'e examined and tested for acceptability after the specified cure time for:

(1) Liquid on surface of solidified product less that 1.0X by waste volume.

NDAP-QA-0646 Revision 2 Page 32 of 60 (2) Visible defects, such as cracking, spalling, or disintegration.

(3) Strength by physically poking the surface of solidified product with a rigid unyielding device. Nominal surface denting is acceptable.

b. If Pacific Nuclear cement solidification is NRC approved to provide stability, PCP surveillance specimen examination testing and reporting is required in accordance with the Branch Technical Position on Waste Form, Revision 2.

Curing'Time

a. A minimum of 30 hours3.472222e-4 days <br />0.00833 hours <br />4.960317e-5 weeks <br />1.1415e-5 months <br /> shall be allowed for curing prior to capping or transporting container.

b. The container may be moved during the first hour after solidification but must remain undisturbed for the remaining 29 hours.

c. Deviations from minimum required curing time shall be approved by Radwaste Supervisor and justifications documented in remarks section of Solidification Record.

Solidification Product Quality a 0 Solidification product quality is assured by use of predetermined mixing ratios of waste, cement and additive. Liquid to be used for solidification should be demineralized water.

b. Pre-qualification mixing ratios are based on laboratory testing using non-radioactive waste materials.

c, Hixing ratios are re-enforced by the following:

(I) Test solidification performed periodically as stated in Test Solidification section of this procedure.

(2) Visually and physically checking at least every fifth (5th) container of the same waste type.

NDAP-QA-0646 Revision 2 Page 33 of 60

d. Container checks shall consist of:

(I) A visual check of solidified product for liquid on surface of product not to exceed 1.0X by waste volume.

(2) Physically poking the surface of solidified product with a rigid unyielding device prior to capping (Nominal surface denting may occur and is acceptable),.

e. Quality Control shall verify acceptability of solidified product when containers are checked.

f. Deviation from the container checking requirement shall be approved by the Radwaste Supervisor.

Handling of Unacceptable Solidified Waste Containers.

a0 If a solidified waste container does not meet acceptability requirements, a Non-Conformance Report (NCR) shall be issued.

b. If the reason for unacceptability is free liquid:

()) The free liquid will be removed; or

)h (2) Extra cement/additive will be added to solidify free liquid.

c, If portions or=all of the product did not solidify after three days:

(I) The waste container will be capped and placed in a storage location and periodically checked until such a time .

product- is acceptable; or (2) Additional solidification agents may be added to achieve satisfactory solidification, as -determined by the Radwaste Supervisor.

NDAP-gA-0646 Revision 2 Page 34 of 60 If the product solidifies prematurely prior to completing the addition of required amount of-cement and additive, as calculated on the solidification calculation sheet for the specific procedure used, the following is required:

(1) Chemistry Group shall perform a test solidification at actual ratio of cement and waste in the container, provided sufficient sample volume remains to complete this item.

(2) guality Control shall check the product for acceptability in accordance with Container Checks section of this procedure.

(3) The container is considered to meet acceptable waste form criteria for shipping provided the subsequent test solidification and/or container checks are acceptable to guality Control and concurrence of the Radwaste Supervisor is obtained.

(4) The above apply only if the Effluents Management Supervisor determines that the product can be classified as "Class A Unstable" or is placed in a High Integrity Container or structure that provides stability in accordance with IOCFR61 and the disposal facility criteria.

If the product does not solidify properly in accordance with the specific solidification procedure, the following is required:

(1) An evaluation of the liner shall be made by the following personnel:

(a) Effluents Management Supervision (b) Solidification Vendor - Operations (c) Solidification Vendor - Engineering (2) Disposal facilities shall be contacted and requirements for receipt of the liner in question shall be defined.

NDAP-QA-0646 Revision 2 Page 35 of 60 (3) Alternative packaging/processing shall be evaluated.

(4) Recommendations for final disposition shall be made to the Power Production Engineer-Effluents management.

(5) Final disposition shall be reviewed by Plant Operations Review Committee (PORC).

(6) Records shall be kept and documentation supportive of final disposition attached to the solidification record package.

(7) The liner may be shipped after Q.C. review of documentation is complete and disposal facility concurrence is received in letter form.

Specific instructions shall be established for handling unacceptable solidified waste container-on a case by case basis.

g. Quality Control shall re-verify acceptability of solidified product by performance of Container Checks.

Capping of Solidified Waste Containers

a. The requirements of Solidification Product Quality section of this procedure .shall be met prior to capping the container.

b'. If the container is not equipped with a passive vent and its contents are within the requirements of Low Specific Activity (LSA) ensure one of the following:

(1) The container should be shipped within (10) ten days 'after capping; or (2) If a container has been capped for longer than (10) days, it shall be opened, vented, and re-capped within (10) ten days of shipment.

NDAP-gA-0646 Revision 2 Page 36 of 60 c~ If the container exceeds the limits for Low Specific Activity and contains water and/or organic substances which could radiolytically

'generate combustible gases, determination must be. made such that the following criteria are met over a period of time that is twice the expected shipment time:

(1) The hydrogen generated shall be limited to.

a molar quantity that would be no more than 5X by volume of the container gas void or" (2) The container and shipping cask cavity shall be inerted with a diluent to assure that oxygen is limited to less than 5X by volume in those portions of the package which could have hydrogen greater than $ X. ~

Solidification Agent Control

a. Portland Cement .ASTM C-150 Type I shall be used for the mobile solidification process.

b. Other solidification agents may be used only after acceptable testing of the agent has been completed that demonstrates acceptable solidification and disposal facility approval has been obtained.'

~ Documented Certification is not required for materials received in bags provided material verification can be obtained as follows:

(1) Cement is acceptable provided the bag containing the cement indicates that cement is Portland Type I.

(2) Sodium Silicate is acceptable provided the bag containing the additive indicates Anhydrous Sodium Hetasilicate.

(3) Other additives are acceptable provided the container is clearly marked indicating the type of additive.

d. Other additives may be used for enhancement of solidification process as specified in the solidification procedure and documented in the solidification records.

NDAP-gA-0646 Revision 2 Page 37 of 60 6.5.11 Radioactive Waste Solidification Records A Solidification Record Sheet (Form NDAP-gA-0646-1) shall be completed for each container filled with solidification products.

Completion of the Solidification Record Sheet and the required accompanying documentation shall be as follows:

a. The Radwaste Supervisor is responsible for initiating this form and completing Parts 1 and 2.

b. Effluents Hanagement Supervision, Chemistry and Solidification/Dewatering/Services Vendor personnel shall provide and check off the required documentation specified in Part 3.-

c. guality Control shall provide review as required-for the Solidification Records.

6.6 RADIOACTIVE WASTE DEWATERING 1 6.6.1 General Requirements Waste Streams which may be dewatered in either High Integrity Containers or steel liners are LRW Filter Hedia, Ultrasonic Resin Cleaner Waste, Sump Sludge, RWCU Filter Hedia, Condensate/Radwaste Demineralizer Bead Resin and Cartridge Filters. The type of container used shall be based ori the waste classification and stability criteria in accordance with federal and disposal facility regulations.

b. Dewatering of Radioactive Waste shall be performed by qualified SSES or Solidification/

Dewatering Services Vendor personnel.

c. Dewatering of Radioactive Waste shall be performed in accordance with approved procedures.

d. Dewatering procedures shall be based on documented test data that has demonstrated the ability to achieve free liquid limits as specified by disposal facilities and applicable regulatory agencies. Liquid volume and drainage calculations and actual drainage verification may also be used to meet free liquid limits.

NDAP-gA-0646 Revision 2 Page 38 of 60

'e. High Integrity Containers shall be used for disposal when the concentration of radionuclides with half-lives greater than 5 years exceeds 1 pCi/cc.

Each waste stream which may be dewatered should be characterized by the Solidification/

Dewatering Services Vendor to ensure the operating parameters and effectiveness of the dewatering system are in accordance with the parameters established in the Topical Report.

Dewatered Product Control a ~ The final dewatered product shall contain less than 1X non-corrosive free liquid for High Integrity Containers and 0.5X for steel liners.

guality Control checks shall be performed on-process steps.

b. If a dewatered waste container does not meet acceptability requirements, a Non-Conformance Report (NCR) shall be issued.

c. Specific instructions shall be established for handling unacceptable dewatered waste container on a case-by-case basis.

d. Deviation from the container checking requirement shall be approved by the Power Production Engineer-Effluents Management.

Radioactive Waste Dewatering Records A Dewatering Record Sheet (Form NDAP-gA-0646-2) 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~ Effluents Management Supervision, Chemistry and Solidification/Dewatering/Services Vendor personnel shall provide and check off the required documentation specified in Part 4.

NDAP-gA-0646 Revision 2 Page 39 of 60

d. guality Control shall provide review as required for the Dewatering Record Sheet.

6.7 HIGH INTEGRITY CONTAINERS (HIC) 6;7.1 ,, Storage of High Integrity Containers a~ Pacific Nuclear and CNSI High Integrity Containers (HIC) stored in direct sunlight or in areas where there is a strong source of ultraviolet radiation shall be filled and disposed of within one year of manufacturing date.

b. Once filled a High Integrity Container may be-stored for a period until a total of one (1) year of ultraviolet radiation is received.

C. Short exposures (i.e., several hours) to sunlight, such as occurring during shipment and on site"transfer need not be counted when determining total ultraviolet exposure.

6.7.2 Uses of High Integrity Containers

'a ~ High Integrity Containers may be used to package'the following waste materials for burial at Barnwell, South Carolina and Richland, Washington low*level waste disposal facility(ies):

Dewatered bead resin, powdered resin and diatomaceous earth.

Compressible and non-compressible solid wastes.

Filter elements and cartridges.

Solidified resins, sludges, and liquid wastes.

Incinerator ash, residuals, or equivalent waste which has been rendered non-dispensable in a binding matrix.

Other dewatered and dry material provided concurrence is received by container vendor and disposal facility.

NDAP-gA-0646 Revision 2 Page 40 of 60 b.' Prior to using a High Integrity Container for a specific waste material, procedures shall be established to define the specific requirement that shall be met during use of the container.

The procedures shall contain:

Documentation requirements that specific conditions have been met such as inspection and exposure to degrading conditions.

Instructions as to how to handle and properly close the container.

Instructions for on-site storage of loaded containers for ultimate shipment for disposal.

~ The procedures shall provide a method for documenting required information relevant to the container from initial receipt to shipping for.-.-

disposal.

d. Required information shall be based upon the container certificate of compliance and disposal facility requirements.

e. Retention and utilization of the documentation shall be defined in the procedures.

The procedures shall establish specific guality Control inspection requirements.

d. Prior to the first shipment of a specific type of High Integrity Container, authorization shall be requested from the applicable regulatory agency governing use of the container in question at the disposal facility of concern.

I

NDAP-gA-0646 Revision 2 Page 41 of 60 High Integrity Container Limitations a ~ High Integrity Containers are approved for use provided the following physical limitations of-the waste are met:

)

(1) Payload density g1.47 gms/cc (2) Loading temperature 5170 F (3) Nupac EL-50 N.S. loaded weight  : 64200 lb (4) Nupac EL-142 N.S. loaded weight  : 68250 lb (5) Nupac EL-142 S. loaded weight  : <11250 lb (6) Nupac EL-190 N.S. loaded weight 511950.lb (7) Nupac EL-190 S. loaded weight 514800 1 b (8) Nupac EL-210 N.S. loaded weight 513000 lb (9) Nupac EL-210 S loaded weight: g17300 1 (10) CNSI Small loaded .weight 52500 lb (ll) CNSI Medium loaded weight ~2500 lb (12) CNSI Large loaded weight 52500 lb

b. The maximum concentration of radionuclides with half lives greater than (5) five years that may be disposed.-of in a High Integrity Container. is 350 pCi/cc. Other waste forms shall not exceed 1.0 X 10 . rads maximum integrated dose to the container.

C. ~ The polyethylene High Integrity Containers shall not come into contact with materials listed in-Attachment E.

d. A passive vent design shall be incorporated into the container to relieve internal container pressure.

Closure of High Integrity Containers a~ Closure of High Integrity Containers shall be completed in accordance with approved procedures.

NDAP-QA-0646 Revision 2 Page 42 of 60

b. If the. container is not equipped with a passive vent and its contents are within the limits of Low Specific Activity ensure one of the following:

(1) The container is shipped within (10) ten days after closing; or (2) If the container has been closed forbe-longer than (10) ten days, it shall opened, vented, and re-closed within ten (10) days of shipment.

C~ If the container exceeds the limits for Low Specific Activity or contains water and/or organic substances which could radiolytically generate combustible gases, determination must, be. made such that the following criteria are met-over a period of time that is twice the expected shipment time:

(1) The hydrogen generated shall be limited.to a molar quantity that would be no more than 5X by volume of the container gas void; or" (2) The container and shipping cask cavity shall be inerted with a diluent to assure that oxygen is limited to g5X by volume in those portions of the package which could have hydrogen greater than 5X.

d. Step 6.7.4.b and 6.7.4.c shall also apply to dewatered waste, in steel liners.

6.8 IRRADIATED HARDWARE PROCESSING AND DEWATERING 6.8. 1 General Requirements a~ Processing and dewatering of Irradiated Hardware shall be performed by qualified SSES or vendor.

personnel.

b. Processing and dewatering of Irradiated Hardware shall be. performed in accordance with approved procedures.

c ~

NDAP-gA-0646 Revision Page Dewatering procedures shall be based on liquid 2

43.of 60 0 volume and drainage calculations and actual drainage verification to demonstrate the ability to achieve free liquid limits as specified by disposal facilities and applicable regulatory agencies.

6.8.2 Dewatered Product Control

a. The final dewatered product shall contain less than 0.5X free liquid for steel liners.

b. guality Control checks shall be performed on process steps.

6.8.3 Irradiated Hardware Processing and Dewatering Records

a. All records generated shall be completed and-filed in accordance with approved implementing procedures.

6.9 CONTAINER INSPECTIONS guality Control shall inspect containers to be used

'.9.1 for solidification, dewatering, and other packaging for disposal.

6.9.2 This inspection shall assure that prior to use, the containers to be used for solidification, dewatering, or other packaging are intact and their internals are free of any visual damage that would prevent them from performing their intended function.

6.9.3 Packages shall meet the general criteria for normal transport conditions in accordance with the requirements of 49 CFR. Type A packages shall meet the additional design requirements specified in 49 CFR.

6.10 WASTE CONTAINER SPACE UTILIZATION 6.10.1 Waste volume shall be maximized within the guidelines of specific procedures to minimize potential void space at the top of waste container after solidification or dewatering is complete.

NDAP-gA-0646 Revision 2 Page 44 of 60 6.10.2 Waste volumes shall meet or exceed disposal site criteria. If waste volume is less than disposal facility criteria, requirements for disposal of the container in question shall be defined by the disposal facility.

6.10.3 Specific waste volumes committed to by the vendor shall be met or otherwise justified as to why waste volumes were not achieved.

6.10.4 Susquehanna Guaranteed Solidified/Dewatered Waste Volume Record, Form NDAP-(A-0646-3, shall be completed by vendor personnel, approved by Radwaste Supervisor and shall be used to track solidified/dewatered waste volumes achieved in each individual container.

6.11 STORAGE'OF PACKAGED RADIOACTIVE WASTE 6.11.1 Radwaste Supervisor shall provide Solidification and/or Dewatering Record sheets that have been reviewed by guality Control personnel stating that processed waste has been solidified or de-watered in accordance with the Process Control Program and meets the applicable shipping and disposal criteria.

6.11.2 Solidification and Dewatering Records shall include the isotopic mix, isotopic concentration of the waste that was packaged, the total volume of the waste, and the amount of water, cement or other solidification agent used, as appropriate.

6.11;3 Solidification and Dewatering Records shall be part of the permanent shipping records and adhere to requirements of the Process Control Program.

6.11.4 For materials packaged in a high integrity container, documentation shall be maintained on HIC storage and pre-shipment. checklist information.

6;11.5 Packaged radioactive waste shall be stored in areas designated by HP Foreman Effluents management.

Storage of packaged radioactive waste in the Low Level Radwaste Holding Facility (LLRWHF) shall be in accordance with approved procedures.

6:11.6 An inventory of stored, packaged waste shall be maintained in accordance with approved procedures.,

NDAP-0A-0646 Revision 2 Page 45 of 60 6.12 TRANSPORTATION, SHIPPING AND DISPOSAL REGULATIONS 6.12.1 Specific regulatory documents shall be maintained on site in a status that is current. Specific regulations that shall be maintained include but are not limited to the following:

a. 10CFR71 Packaging of Radioactive Haterial for transport and transportation of"radioactive material under certain conditions.

b. 49CFR100 199 Transportation.

c. Chem-Nuclear Systems Inc. Barnwell S.C. disposal site operating license number 097 State of South Carolina.

d. Chem-Nuclear System Inc. NRC Haterial License 12-13536-01.

e.. Chem-Nuclear System Inc. Barnwell S.C. disposal site operating procedures and site criteria.

f. US Ecology NRC Material License 04-0376601.

g. US Ecology Richland Washington disposal site operating license WN-1019-2 State of Washington.

Scientific Ecology Group Licenses R-73008-E94, R-01052-A91.

i. Cask Hanuals for casks of which PPEL is an authorized user.

j. A copy of the license for each facility to which Radioactive Haterial is sent.

k. 10CFR61 Licensing requirements for land disposal of Radioactive Waste.

6.12.2 Procedures applicable to transportation, shipping and disposal shall be developed.

a~ Procedures shall be established and maintained to provide directions and assure regulatory compliance for manifesting, which include applicable federal, state, and disposal facility regulations, and NRC guidance.

NDAP-gA-0646 Revision 2 Page 46 of 60

b. Procedures shall contain check off lists where and when applicable to assure specific attention is paid to the critical function being controlled.

c. Procedures shall contain guality Control notifications or hold points.

6.12.3 Computer software used to implement "applicable portions of the Process Control Program shall be in accordance with NDAP-(A-0801.

6;13 SHIPPING OF RADIOACTIVE WASTE, 6.13.1 All radioactive waste shall be shipped by Effluents Hanagement.

6.13.2 All radioactive waste shipped from SSES shall only -be .

to facilities licensed to receive the waste and in accordance with 10CFR20, 10CFR71 and 49CFR100-199.

6.13.3 Dry Active Waste (DAW) should normally be shipped as Type A quantities and therefore do not require specific licensed containers.

6.13.4 Waste containers shall be placed in a USNRC approved licensed shipping container if it:

a. Exceeds Type A quantities

b. Exceeds 1000 mr/hr on contact

c. Exceeds 1000 dpm/100 cm~ loose surface contamination on the exterior of the container.

6.13.5 The specific conditions of the Certificate of Compliance for each approved shipping cask shall be strictly adhered to.

6.13.6 Packaged waste may be shipped unshielded if:

Contact dose rates are less than 200 mrem/hr and dose rates at 6 feet are less than 10mrem/hr.

b. Curie content of the package shall be a Type A quantity.

c~ Container shall. be a minimum of a strong tight container.'

0 NDAP-QA-0646 Revision 2 Page 47 of 60 6.13.7 Prior to the shipment of a package of radioactive waste, the HP Foreman Effluents Management shall assure the container is surveyed for contact dose rates and surface contamination. Decontamination, if required, shall be done under the direction of the HP Effluents Management. Decontamination may be 'oregan waived based upon'adiological conditions.

6.13.8 All vehicles used to transport radioactive waste requiring the vehicle to be placarded shall be checked for adequate operation and safety conditions.

6.13.9 All Radwaste shipments from SSES shall normally be=via "Exclusive Use" vehicles. Specific instructions given to the driver include:

a. Expected route of travel to his final destination.

b. ,Maintaining "Exclusive Use" status.

c. Specific actions to be taken in the event of an" accident.

6.13.10 No vehicle carrying radioactive waste that is overweight shall leave SSES without a Pennsylvania overweight permit.

a. A DAW shipment or other shipment capable of having its weight adjusted, shall not be allowed to leave SSES overloaded.

b. An overloaded condition for any vehicle is based on total weight and weight per axle.

6.13.11 In the event access is denied to SSES at all operating disposal facilities, PP&L will provide carrier with a letter stating that SSES will meet all applicable federal, state; and compact requirements for receipt back of the radioactive waste/material in carrier's possession.

6.14 SHIPMENT CONFIRMATION If disposal site shipment acknowledgement is not received within 18 days from departure from,SSES, Effluents Management Supervision shall conduct a trace investigation for shipment location. If-the" disposal facility shipment receipt can not be confirmed within 20 days, a Significant Operating Occurrence Report (SOOR) shall be, generated.

NDAP-QA-0646 Revision 2 Page 48 of 60 6.15 CHANGES TO THE SOLID RADIOACTIVE WASTE PROCESS CONTROL PROGRAM 6.15.1 Any changes as described in the Technical Specifications, to the Solid Radioactive Waste Process Control Program shall be provided in the Annual Radioactive Effluent Release Report filed with the NRC.

6.15.2 Any changes to the Solid Radioactive Waste Process Control Program shall be approved by Plant Operations

.- Review Committee (PORC) prior to implementation.

( ) 6.16 EVALUATION OF PROCESS OR OPERATIONAL CHANGES Changes in radioactive waste processing or operational changes shall be evaluated to determine any impacts. on 6.16.1'.16.2 waste characteristics and/or form.

Evaluation should include as a minimum:

a. Operational evaluation of processing impacts.

b. Chemistry evaluation of changes to sampling and analysis methodology.

c. Effluents Management evaluation of packaging and/or shipping impacts.

d. Management evaluation for 10CFR61 e.'ffluents compliance.

Solidification/Dewatering Services Vendor waste stream characteristic evaluation of the dewatering/solidification system operating parameters and effectiveness.

( ) 6.17 REPORTING OF MISHAPS INVOLVING LOW LEVEL WASTE FORMS 6.17.1 10CFR61 establishes the minimum and stability requirements for Low Level Waste (LLW) forms. 10CFR20 requires certification that the processed waste satisfies the requirements of 10CFR61. Mishaps which may impact the final waste form shall be reported to the NRC.

NDAP-gA-0646 Revision 2 Page 49 of 60 Types of mishaps which should be reported include:

a ~ Failure of high-integrity containers used to ensure a stable waste form. Container failure can be evidenced by changed container dimensions, cracking, or damage resulting from mishandling (e.g., dropping or impacting against another object).

b. Hisuse of high-integrity containers, evidenced by a quantity of free liquid greater than 1 percent of container volume, or by an excessive

(>15X) void space within the container.

C. Production of a cement solidified Class B or-C waste form that has any of the following characteristics:

(1) Contains free liquid in quantities exceeding 0.5 percent of the volume of the-waste.

(2) Contains waste with radionuclides in concentrations exceeding those considered during waste form qualification testing accepted by the regulatory agency, which could lead to errors in assessment of waste class.

(3) Contains a significantly different waste loading than that used in qualification .

testing accepted by the regulatory agency.

(4) Contains chemical ingredients not present in qualification testing accepted by the regulatory agency, and those quantities are sufficient to.unacceptably degrade the waste product.

(5) Shows instability evidenced by crumbling, cracking, spalling, voids, softening, disintegration, non-homogeneity, or dimensional changes.

(6) Evidence of processing phenomena that exceed the limiting processing conditions identified in applicable topical reports or process control plans, e.g., foaming, temperature extremes, premature or slow hardening, and production volatile material.

NDAP-QA-0646 Revision 2 Page 50 of 60

d. Failure to adhere to high integrity container limitations as required by container certificate of compliance.

e. Notification of violation by disposal facility regulatory authorities at time of container receipt for disposal.

f. Failure of cement-solidified stable waste form long term PCP surveillance specimens due to evidence of significant cracking, spalling, or-bulk disintegration, compression or penetrometer strength and immersion test results.

6.17.3 Requirements for reporting of mishaps shall apply only to processing liners a'nd high integrity containers,.

containing radioactive waste in its final product form.

6.17.4 A Significant Operating Occurrence Report (SOOR) shall .

be generated if one of the mishaps mentioned occurs.

6.18 PCP IHPLEHENTING PROCEDURES Procedures required for implementation of the Process Control Program're shown in Attachment D.

7.0 RECORDS 7.1 The Solidification Records or Dewatering Records and the attached documents shall be forwarded to Effluents Hanagement Supervision.

for retention until such. time as the container identified on Record is shipped for final disposition.

7.2 When the identified container is shipped the Solidification Records or Dewatering Records and other documents concerning the Shipment shall be filed with the shipping documentation and forwarded to DCS for retention.

7.3 . Documentation of Radioactive Waste Shipments shall be retained as.

required by SSES Technical Specifications.

7.4 Radioactive waste shipping documentation shall consist of, but not "

limited to, the following records:

7.4.1 Radioactive Haterial Shipping Hanifest 7.4.2 Evaluation of isotopic mix and concentration

NDAP-gA-0646 Revision 2 Page 51 of 60 7.4.3 Radiological surveys of:

a. Vehicle upon arrival

b. Package to be shipped

c. Loaded vehicle prior to shipment 7.'4.4 Vehicle Safety inspection 7.4.5 Check-off sheet for loading procedure 7.'4.6 Documentation of adherence to Process Control Program (if applicable) 7.4.7 Special instructions to driver

Attachment A NDAP-gA-0646 SOLIDIFICATION RECORD SH ET Revision 2 Page 52 of 60 PART 1: Container Identification Information

1. PPSL Liner Number 2. Container Vendor Serial Number

3. Waste Stream (RWCU Filter Media cannot be entered)

4. Test Solidification required7 YES NO (circle one)

PART 2: Container Selection (Refer to WM-PS-100)

l. Estimated Liner Contact Dose Rates mR/hr

t. P>>'PC I C t tl Ci/gm

3. Expected Waste Classification/Stability

4. Container Type to be Used 5. Empty Weight of Container . 1bs

6. Expected Cask Type to be Used PART 3 P

Documentation Checklist d

l. Form NDAP-gA-0646-1 (original)

2. Waste Form Documentation WM-RP- Forms (original)

SC-068-002 Forms (copy)

Waste Form: STABLE UNSTABLE (circle one) h85N Liner Volume Utilized: YES NO (circle one)

3. Qaste Activity Documentation CH-RC- Forms (copy)

Isotopic Analysis (copy)

Compost added/Log entry made on CH-TP-055-1 Physics Data 4'ealthShipment Liner Radiological Survey (original) 0 II t I Pilmrt W lgtt lb. (If available ALARA)

PART REMARKS:

/

DATE ~KVIK DATE FORM NDAP-gA-'0646-1, Rev. 1, Page 1 of 1 (File R69-I)

Attachment B NDAP-QA-0646 Revision 2 Page 53 of 60 DEWATERING RECORD SHE PART 1: Container Identification Information

1. PP8L Liner Number 2. Container Vendor Serial Number

3. Waste Stream PART 2: Container Se1ection (Refer to iiN-PS-100)

l. Estimated Liner Contact Dose Rates mR/hr

2. Projected Curie Concentration "

PC< /9

3. Expected Waste Classification/Stability

4. Liner Type to be Used 5. Empty Weight of Container lbs.

6. Expected Cask Type to be Used a waste upervisor ate >me FORN NDAP-QA-0646-2, Rev. 2, (DUPLEX), Page 1 of 3 (File R69-1)

Attachment B NDAP-gA-0646 Revision 2 Page 54 of 60 DEWATE ING ECORD SHEET PART 3: Sampling and Analysis

1. Tank/Container sampled

2. Sample Number

3. Waste Stream

4. Isotopic Analysis attached

5. Specific activity of Dewatered Sample pCi/gm

6. a. Dewatered Volume

b. Dewatered Weight

c. Sample density gm/cc x 62.43 lb/ft

7. Composite added/Log entry made on CH-TP-055-1 The above tank/container containing solids has been analyzed in accordance with CH-RC-075 and -found to contain the isotopes and specific activities as indicated on the attached data sheets.

em>stry upervision ate lme FORM NDAP-gA-0646-2, Rev. 2, (DUPLEX) Page. 2 of 3 (File R69-1)

Attachment B NDAP-gA-0646 Revision 2 Page 55 of 60 DEWATERING RECORD SHEET PART 4: Container Shipment Information Summary PP&L Liner Number 2. Waste Volume

3. Form NDAP-gA-0646-2 (original)

4. Waste Form Documentation Calculated Waste Weight lb/ft x ft lb.

Part~

Actual Filled Container Weight lb. (if available ALARA) 100 x (Dewatered Waste Volume) ft' ft Part~ 1Cvas~o1 erne

>85% Container Volume Utilized YES / NO (Circle one)

Waste Form: STABLE UNSTABLE (Circle one)

5. Waste Activity Documentation CH-RC- Forms (Copy)

Isotopic Analysis (Copy)

6. Shipment Number PART 5: REMARKS:

a waste upv ate evs ew llate oreman . gmt. Dane FORM NDAP-gA-0646-2, Rev. 2, (DUPLEX), Page 3 of 3 (File R69-1)

Attachment C NDAP-gA-0646 Revision 2 Page 56 of 60 SUS UE ANNA GUA NTE D SO IDIFIED D E D W S E VOLUME CO 0

l. Date Liner number

2. Waste Type

3. Container Type

4. Burial Volume

5. Useable Container Volume fts

6. Guaranteed Ninimum Waste Volume fts

7. Waste Volume Attained inches x fts /inch fts

8. Waste Volume Container Usage 100 x (Waste Vol. fts + Guaranteed Win. Waste Vol ft.s) -100 M Am ~~0 4 YClu~

P O.O/

s X fvnnnn4wC Min.n/nsL Vnf. ~t.

H<mmvrr() its f~ Mvvrvnvv~t) /

lv/ Begin mmm.v Assnes mme Qo/v mc

/) g).~ /t.~~ t i/v1 ~jsVin..t. VW. yr" =. pF.

II- Remarks:

IZ- Signature o s ica on en or epresen a ve Signature a was e upervisor I

FORM NDAP-QA-0646-3, Rev. g; Page 1 of 1 (File R69-1)

n

< 1<' ,t r+

hi 'R I

V

Attachment D NDAP-0A-0646 Revision 2 Page 57 of 60 PCP I LEMENTING PROCEDURE MA RI WASTE PROCESSING va orator Concentrates Solidified Pacific Nuclear PT-51-WS Pacific Nuclear OH-114-NS Pacific Nuclear OM-104 ixed Solids - Solidified Pacific Nuclear PT-51-WS Pacific Nuclear OH-104 Pacific Nuclear OH-114-NS LRW Filter Media URC Waste RWCU Filter Media Sum Slud e - Dewatered .

Pacific Nuclear OH-43-WS WM-RP-107 Condensate Radwaste Demineralizer Bead Resin - So idified Pacific Nuclear PT-51-WS Pacific Nuclear OH-114 Pacific Nuclear OH-104 Condensate Radwaste Demineralizer Bead Resin - Dewatered Pacific Nuclear OH-43-WS SEG STD-P-22-002 (Resin Express)

WH-RP-106 WH-RP-104 Cartrid e Filters CNSI FO-OP-019 (Overpack)

WM-PS-230 Pacific Nuclear OM-16-NS WH-RP-105 Page 1 of 3

Attachment D NDAP-gA-0646 Revision 2 Page 58 of 60 PCP IMPLEMENTING PROCEDURE ATRIX Irradiated Hardware - Dewatered Steel Liner None D Active Waste DAW Packa in WM-PS-210 Li uid Oi Waste - Solidified Li uid Oil Waste - Decontaminatio None None Solid Sealed Sources None WASTE ANALYSIS ND CLASSIFICATION - 10CFR61 Pacific Nuclear ON-45 NS WM-RP-008 CH-RC-075 WN-PS-155 CH-RC-076 WN-PS-160 CH-TP-055 WM-PS-170 TESTING TREATMENT COMBUSTIBLE GASES WM-RP-009 WM-RP-301 ADIOACTIVE AS E SOLIDIFICATION - GENERAL CEMENT Pacific Nuclear OM-114-NS SC-068-002 {Test Solidification)

Page 2 of 3

Attachment D NDAP-gA-0646 Revision 2 Page 59 of 60 PCP IMPLEHE TING PROCEDURE MATRI RADIOACTIV WASTE DEWATERING - GENERA Pacific Nuclear OM-60-WS WM-RP-010 WM-RP-Oll HIGH INTEGRITY CONTAINERS Pacific Nuclear OM-16-NS Pacific Nuclear H-18-NS WH-RP-012 DISPOSA FACILITY RE UIRE ENTS WM-PS-180 WM-PS-401 (LLRWF)

PACKAGING WM-PS-310 (HN-142) WM-PS-314 (HN-190-1)

WM-PS-311 (LN-142) WH-PS-353 (CNSI 14-170)

WM-PS-312 (HN-100-111) WM-PS-315 (HN-200)

WM-PS-350 (CNSI 14-195) WM-PS-354 {CNSI 14-215)

WM-PS-351 (CNSI 21-300) WM>>PS-316 (HN 215H)

WM-PS-352 {CNSI 8-120A) WM-PS-318 (Westinghouse TCT)

WM-PS-313 (HN-194) WM-PS-319 (WCS Cask Drum)

WM-PS-355 (CNS 14-170-III)

TRANSPORTATION 49CFR 10CFR71 WM-PS-100 WH-PS-120 WM-PS-140 WM-PS-180 WM-PS-240 Page 3 of 3

Attachment E NDAP-gA-0646 Revision 2 Page 60 of 60 ATERIALS NOT COMPATIBLE WITH PO ET YLENE CONTAINERS Aliphatic hydrocarbons (hexane, octane, Gasoline bexene, octane, etc.)

Acetone Iodine Amyl Acetate Amyl Chloride Methyl bromide Aniline Methyl Chloride Aqua Regia Methyl ethyl ketone (HEK)

Hethylene Chloride Benzene Hoist Chlorine gas Bromine liquid Butane Nitric Acid (50X weight concentration)

Camphor Oil Organ Peroxides Carbon Disulphide Octyl cresol Carbon Tetrachloride Oleic acid Chlorine liquid Oleum Chlorobenzene Chloroform Pentane Chlorosulfonic acid Petroleum ether Chromic/sulfuric acid Phenol Cyclohexanone Propane Propylene dichloride Dibutylphtalate Dimethylamine Sulfric acid (60X weight concentration)

Diesel fuel Tetrahydrofurance Ethyl acetate Titanium tetrachloride Ethyl butyrate Toulene Ethyl chloride Trichloroethylene Ethyl ether Turpentine Ethylene chloride Tetralin

- Ethylene chlorohydrin Ethylene dichloride Xylene Fluorine Furfural Furfuryl alcohol Fuel Oil Page I of I

SECTION 6 REPORTS OF EXCEPTIONS TO THE SSES EFFJ VENT MONITORING PROGRAM 188

REPORTS OF EXCEPTION TO THE SSES EF LUENT MONITORING PROGRAM On 12/24/93, preparations were underway to make a liquid radwaste release when the Unit 1 cooling tower blowdown flow recorder, FR-11503, was declared inoperable. Technical Specification Table 3.3.7. 10-1 Action Statement 102 was entered. The instrument was being validated in accordance with OP-069-050. With valve flow open 50X, indicated flow was 5400 gpm; the acceptance criterion for this valve position is )5500 gpm. The incident was investigated under Significant Operating Occurrence Report 1-93-476. Due to the date of occurrence, the instrument does not exceed thirty (30) day inoperability reporting requirements in 1993. Since this event is a repeat occurrence, however, and it is now known that the instrument remained inoperable for more than thirty (30) days (into 1994), it will be discussed herein.

An event investigation for the Unit 1 cooling tower blowdown flow recorder failure produced two root causes or causal factors. The first item noted was a ringing emanating from the neutral conductor of the power supply feeding the blowdown flow instrument. This ringing (approximately 50,000 Hz) appears to cause the flow instrument to read low. The ringing can be eliminated by installing a ground jumper to the neutral conductor, or by installing a capacitor between neutral and ground. On the Unit 1 flow recorder, the flow reading is consistently low. The ground jumper was installed on this instrument, which immediately led to a substantial increase in the flow reading.

A second factor in the blowdown flow recorder failure is believed to be the space heater in the flow transmitter cabinet. The heaters are located near the top of the circuit cards used in the flow meter. The heater may not be the actual cause of the failures, although evidence suggests the heater affects the way the meters operate. Typically, the flow meter failures occur in cold weather, when freeze protection is operating. A temperature recorder indicated the temperature cards reached 152, with an average temperature range of 135'o 140', which is excessive for these It is now believed that long term exposure to these conditions degrades the flow meter's operation, or at least makes it

'lectronics.

more susceptible to the noise disturbance noted on the neutral conductors. Actions taken to prevent recurrence include:

1. Modification of the power supply to the flow meters to eliminate noise observed on the neutral conductor;

2. Revision of the manner in which the flow meter cabinet is freeze-protected.

This occurrence is the only case where an instrument was inoperable for a duration subject to the reporting conditions of Technical Specifications 3.3.7. 10.b .or 3.3.7. ll.b.

189

SECTION 7 CORRECTION TO DOSE REPORTED IN PREVIOUS SEML4lVlNUALEFFLUENT AlN) WASTE DISPOSAL REPORT 190

CORRECTION TO DOSE REPORTED IN PREYIOUS (1982) SEMIANNUAL EFFLUENT AND WASTE DISPOSAL REPORT In the process of researching information to support PPEL Calculation OT-93-RKB-021 (discussed in Section 5), a typographical error for Adult total body dose from liquid effluent, for the year 1982, was noted. The value stated in the Semiannual Effluent and Waste Disposal Report for this receiver and pathway is g5.80e-08 mrem. It is recommended in the Conclusion section of the calculation that a correction to this reported dose be submitted as an appendix to the next Semiannual Effluent and Waste Disposal Report. The value for Adult total body dose from liquid effluent for 1982 is hereby corrected to be g5.80e-03 mrem. This corrected value is not significant with regard to the Technical Specification 3.11.1.2.b limit of 3 mrem.

191