ML20140D340

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Reissued Rev 1 to Offsite Dose Calculation Manual
ML20140D340
Person / Time
Site: Nine Mile Point Constellation icon.png
Issue date: 08/31/1985
From: Leach E, Roman T
NIAGARA MOHAWK POWER CORP.
To:
Shared Package
ML17058A533 List:
References
PROC-850831, NUDOCS 8603260065
Download: ML20140D340 (47)
v • d • e


Text

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NINE MILE POINT NUCLEAR STATION -

I NINE MILE POINT UNIT 1 OFF-SITE DOSE CALCULATION MANUAL (ODCM)

I DATE AND INITIALS APPROVALS SIGNATURES REVISION 1 REVISION 2 REVISION 3 l

Chemistry and Radiation Management Superintendent E. M. lasch ( t.)

j z_4 h/Ff tuf Station Superintende NMPNS Unit 1 T. k. Roman h y//h

// ll " ' ~

General Superintendent Nuclear Generation Chairman of S.O.R.C.

T. J. Perkins y/yM Summary of ages Revision 1 (Effective )

PAGE DATE 1-90 August 1985 - Reissue This reissue reflects change in placement of revision NIAGARA MOHAWK PM*C8bilATION THIS PROCEDURE NOT TO BE USED AFTER MARCH 1987 SUBJECT TO PERIODIC REVIEW.

8603260065 860228 PDR ADOCK 05000220 R PDR

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i ODCM - NINE M7LE POINT UNIT 1 4

2*E .

1.0 INTRODUCTICN 1 2.0 LIQUID EFFLUENTS 2 2.1 Setpoint Determinations 2 2.2 Dose Determinations 5 3.0 GASEOUS EFFLUENIS 12 3.1 Setpoint Determinations 12 3.2 Dose and Dose Rate Determinations 17 3.3 Critical Receptors 25

.4.0 40 CFR 190 REQUIREMENTS 26 4.1~ Evaluation of Doses From Liquid Effluents 28 1 4.2 Evaluation of Doses From Gaseous Effluents 28

, 4.3 Evaluat' ion of Doses ' Prom Direct Radiation 29 5.0 ENVIRONMENTAL MONITORING PROGRM , 33 5.1 Sampling Stations 33 l 5.2 Interlaboratory Comparison Program 33 5.3 Capabilities for Thermoluminescent Dosimeters Used for Environmental Measurements 34 l TABLES 38 APPEND 3X A- Dose Parameters for Iodine - 131 and 133, Particulates and Tritim 67 '

B- Diagrams of Liquids and Gaseous Radwaste Treatments Systems 80 C Dispersion Calculatiou Tables 87

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3.0 GASEOUS EFFLUENTS r

3.1 Setpoint Determinations 3.1.1 Basis Stack gas and off gas monitor setpoints will be established such that the instantaneous release rate of radioactive materials in gaseous effluents does not exceed the 10 CFR 20 limits for ant.ual release rate. The setpoints rill be activated if the instantaneous dose rate at or beyond the i

(land) site boundary would exceed 500 aren/yr to the whole body

. or 3000 arem/yr to the skin from the continuous release of radicactive noble' gas in the gaseous effluent.

Monitor setpoints will be determined once per quarter under normal release rate conditions and will be based on the isotopic composition of the release and/or a more conservative default compositiot specified in the pertinent procedure. If l the calculated setpoint is higher than the existing setpoint, 1

it is not mandatory that the setpoint be' changed'.

Under abnormal site release rate conditions, monitor setpoints will be recalculated and, if necessary, reset at more frequent intervals as deemed necessary by C&RP Supervision. In particular, the JAF contribution shall be assessed.

During outages and until steady state power operation is again realized, the last operating setpoint shall be used.

l The skin dose rate limit is not used in setpoint calculations because it is never limiting.

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, (2) To ensure that 10 CFR 20 and Technical Specification dose rate limits are not exceeded, the hi hi alarms on the stack monitors shall be set lower than or equal to (0.9)

(Q) . Ei alarms shall be set lower than or equal to (0.5) (Q) ,,.

(3) Based on the above conservatism, the dose contribution from JAF can usually be ignored. During Emergency Classifi-cations at JAF due 'to airborne effluent, the 500 ar/yr value must be reduced accordingly. 1 (4) To convert monitor gross count rates to pCi/sec release rates, the following general formula shr.11 be applied:

(C ,-B) K, =

Q =

DCi/sec release rate where:

1 C, ' = monitor gross count rate in cps or cpa B = monitor background count rate i

l l

=

K, stack monitor efficiency factor with units of l pCi/sec-cps or pCi/sec-cpm.

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,p-,_, p , - - - - - - - - - -,--,,,-,----e

(2) The hi alare points shall activate with recombiner discharge rates equal to or less than 500,000 uCf/sec

- Q) To convert monitor mR/hr readings to uC1/sec, the formula below shall be applied:

RK "

O uCi/sec recombiner discharge release R R rate where:

1 R = mR/hr moni;or indicator K = efficiency factor in units of uCi/sec mR/hr R

determined prior to setting monitor alarm points l (4) Monitor KRfactors shall be determined using the genertl l

I formula :

t Kg =

E41/R where:

l Q

=

individual radionuclide recombiner discharge release rate as aetermined by isotopic analysis and flow rate monitor.

K fact rs a re conservarive than those calculated by the R

above methodology may be assumed.

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3.2 Dose and Dose Rate Determinations i

In accordance with specification 4.6.15.b.(2) and 4.6.15.b.(3), dose and dose rate determinations will be made monthly in order to determines (1) Total body dose rates and gamma air doses at the =mv4== X/Q 1and sector site boundary interface and beyond.

(2) Skin dose rates and beta air doses at the mari== X/Q 1and sector site boundary interface and beyond.

(3) The critical organ dose and dose rate at the maximum X/Q 1and sector site boundary interface and at a critical receptor location beyond the site boundary.

1 Either maximum five year annual average or real time meteorological data shall be utilized for dose and dose rate calculations. Where

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==v4== five year average annual meteorological data is assumed, dose ,

, and dose rates due to noble gases at locations beyond the site boundary will be lower than equivalent site boundary dose and dose rates. Therefore, under these conditions, calculation of noble gas -

dose and dose rates beyond the maximum X/Q 1and sector site boundary L

locations can be neglected. '

1 l

l l

The frequency of dose rate calculations will be upgraded when elevated release rate conditions specified in subsequent sections I

l 3.2.1.1 ana 3.2.1.2 are realized.

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l Critical organ doses and dose rates may be conservatively calculated by assuming the existence of a so-called " moving" critical receptor.

At this " moving" critical receptor' location, it is assumed that all pathways are applicable and the highest X/A and/or D/Q value for actual pathways as noted in Table 3-1 are in effect. A person's dose at the " moving" critical receptor location is equal to the same dose that person would receive if they were simultaneously subjected to the highest pathway dose at each critical receptor identified for each pathway.

l If dose or dose rates calculated, using the assumptions noted above, i reach Technical Specification limits, actual pathways will be evaluated, and doses / dose rates shall be calculated at separate i

critical receptor locations and compared with applicable lini:s.  !

4 Not all pathways need be considered in dose and dose rate calculations at each critical receptor location. For example, when calculating land sector site boundary doses and dose rates for particulates, iodines and tritium, only the ground deposition and inhalation pathways apply.

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. 3.2.2.1 Noble Gas Air Dose i The air dose at the critical receptor due to noble gas releases is determined as follows:

For gamma radiation

-8 D = 3.17 x 10 gg i7jg g i For beta radiation D ( 3.17 x 10-8IN gI/Q Qg where Mg = air gamma dose factor in (ar/ year per uCi/m ) for each isotope 1 (Table 4-1) '

Ng =

air beta dose factor (nrad/ year per uCi/m3 ) for each isotope 1 (Table 4-1)

X/Q = the relative plume concentration (in units of sec/m ) at the land sector site boundary or beyond. Either maximum 5 year ,

average annual values (Table 3-1 or Appendix C), or real time values may be assumed. 1 Qg = the total quantity of isotope i released during the period, (uci)

-8 3.17 X 10 = the inverse of the number of seconds in a year

'^ -=--

3.2.2.2 Radioiodine, Tritium & Particulates The doses to an individual from I-131, I-133, tritium, and particulates with half lives greater than 8 days will be calculated as follows:

L Dose = 3.17 X 10-8 I I R 9 g ijak j1 Where W3 = dispersion parameter either X/Q (sec/a ) or 2

D/Q (1/m ) depending on pathway and receptor i location assumed. Either 5 year average annual values (Table 3-1, or Appendir c) or real time values may be assumed.

g= the total quantity of isotope i released during the period, (uci)

Rijak = the dose factor for each isotope i, pathway j, age group a, and organ k (Table 4-2, 1

through 4-20) 3.i7 x 10' = the inverse of the number of seconds in a year The R values contained in Tables 4-2 through 4-20 were 1 calculated using the methodology defined in NUREG-0133 and Regulatory Guide 1.109, Revision 1.

3.3 Critical Receptors For the meat consumption dose pathway, the critical receptor is the greatest D/Q meat animal location. This location has been determined in conjunction with the land use census (technical specification 3.6.22) and is subject to change. The vegetation (food crop) dose is based on the greatest D/Q garden location from which samples are taken. This location also may be modified as a result of vegetation i sampling surveys. ,

4.0 40 CFR 190 REQUIREMENTS The " Uranium Fuel Cycle" is defined in 40 CFR Part 190.02 (b) as follows:

" Uranium fuel cycle means the operations of milling of uranium ore, chemical conversion of uranium, isotopic enrichment of uranium, fabrication of uranium fuel, generation of electricity by a light-water-cooled nuclear power plant using uranium fuel, and reprocessing of spent uranium fuel, to the extent that these directly support the production of electrical power for public use utilizing nuclear energy, but excludes mining operations, operations at waste disposal sites; transportation of any radioactive material in support of these operations, and the reuse of recovered non-uranium special nuclear and by product materials from the cycle."

Section 3.6.15.d of the Technical Specifications requires than when the calculated doses associated with the effluent relerses exceed twice the limits of sections 3.6.15.a.(2)(b), 3.6.15.b.(2)(b) and 3.6.15.b.(3)(b),

then calculations shall be made including direct radiation contributions from the reactor units and outside storage tanks (as applicable) to determine whether the above 40 CFR 190 dose limits have been exceeded.

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The doses from Nine Mile Pcint Unit 1 will be added to the doses to the maximum exposed individual that are contributed from other uranium fuel cycle operations within 5 miles of the site.

For the purpose of calculating doses, the results of the Radiological Environmental Monitoring Program may be included for providing more refined estimates of doses to a real maximum exposed individual.

Estimated doses, as calculated from station effluents, may be replaced by doses calculated from actual environmental sample results.

4.1 Evaluation of Doses From Liquid Effluents

.f For the evaluation of doses to real members of the public from liquid effluents, the fish consumption and shoreline sediment ground dose will be considered. The dose associated with fish consumption may be calculated using the ODCH methodology or by calculating a dose to man .

based on actual fish sample analysis data. The dose associated with shoreline sediment is based on the assumption that the shoreline would be utilized as a recreational area. This dose may be derived from liquid effluent data or from actual shoreline sediment sample analysis data.

Doses to members of the public from the fish consumption and shoreline sediment pathways will be calculaten using Regulatory Guide 1.109 methodology or ODCM methodology. ~

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4.4 Doses to Members of the Public Within the Site Boundary.

Section 6.9.1.e of the Nine Mile Point Unit 1 Technical Specifications requires that the Sea;iannual Effluent Release Report include an assessment of the radiation doses from radioactive liquid and gaseous effluents to members of the public due to their activities inside the site boundary as defined by Figure 5.1-1 of the specifications. A member of the public, as defined by the Technical Specifications, would be represented by an individual who visits the sites' Energy Information Center for the purpose of observing the educational displays or for picnicing and associated activities. It is assumed that an individual would spend four hours per week for twelve weeks at the Energy Information Center. The time spent at the facility is assumed to occur from approximately July 1 to September 30 of each year. Thus, the first Semiannual Effluent. Release Report

will not. address this particular dose because the summer season is the period of concern. The second reoort will~ address this dose based on forty eight hours occupancy.
  • The pathways considered for the evaluation include the inhalation pathway with the resultant lung dose and the direct radiation dose pathway with the associated total body dose. The direct radiation dose pathway, in actuality, include several pathways. These include: the direct radiation gamma dose to an individual from on overhead plume, a submersion gamma plume dose, and a ground plane dose (deposition). Other pathways, such as the in8estion pathway, are not applicable. In addition, pathways associated with water related recreational activities are not applicable here. These inicude swimming and vading which are prohibited at the facility.

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..- L' . -.L .-- ---  :-- ----:L D-J.- The inhalation pathway is evaluated by identifying the applicable h

radionuclides (radiciodine, tritium and particulates) in the effluent ,

for the appropriate time period. The radionuclide concentrations are then multiplied by the appropriate X/Q value, inhalation dose factor, air intake rate, and the fractional portion of the year in question.

Thus, the inhalation pathway is evaluated using the fol?owing

equation adapted from Regulatory Guide 1.109.-

R =(g[C Fg X/Q DFA R, t)

)

I where :

R =

the dose for the period in question to the lung (j) for all radionuclides (1) for the adult age group (a) in area per time period.

C= The average concentration in the. stack release of radionuclide i in pCi/m3 for the period in question F =

Unit 1 average stack flowrate in a /sec.

X/Q = The plume dispersion parameter for a location O'.50 miles west of NMP-1 (The plume dispersion parameter is 1.176E-07 and was obtained from the C.T. Main five year average grazing season X/Q tables. A X/Q value based on real time meteorology may also be utilized L

for the period in question).

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DFA g3,

=

the inhalation dose factor for radionuclide 1, the lung j, and adult age group a in area per pCi found on Table E-10 of Regulatory Guide 1.109 R,

=

annual air intake for individuals in age group a in M per year (this value is 8,000 m 3per year and f

was obtained from Table E-5 of Regulatory Guide 1.109).

t =

fractional portion of the year for which radionuclide i was detected and for which a dose is to be 1

calculated (equals 0.23 years).

The direct radiation gamma dose pathway includes any gamma doses from an overhead plume, submersion in the plume and ground plane dose (deposition). This general pathway will be evaluated by everage 1

4 environmental TLD readings. At least two environmental TLD locations will be utilized and located in the approximate area of the Energy Information Center (EIC) and the facility picnic area. These TLDs will be placed in the field on approximately July 1 and removed on approximately September 30 of each year (this time interval is composed of one quarterly TLD collection period). The average TLD readings will be adjusted by the average control TLD readings. This l .is accomplished by subtracting the average quarterly control TLD

value from the average Elc TLD value. The applicable quarterly control TLD values will be utilized af ter adjusting for the appropriate time period (as applicable).

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5.0 ENVIRONMENTAL MONITORING PROGRAM 5.1 Sampling Stations The current sampling locations are specified in Table 5-1 and Figures 5.1-1, 5.1-2. . The Environmental Monitoring Program is a joint effort between the Niagara Mohawk Power Corporation and the New York Power Authority, the owners and operators of the Nine Mile Point Unit 1 and the James A. FitzPatrick Nuclear Power Plant, respectively. Sampling locations are ei sen on the basis of historical average dispersion or deposition parameters from both units.

The average dispersion and deposition parameters for the two units have been calculated for a 5 year period, 1978 through 1982. These dispersion calculations are attached as Appendix C. The calculated dispersion or deposition parameters will be compared to the results of the annual land use census. If it is determined that a milk sampling location exists at a location that yields a significantly higher (e.g. 50%) calculated D/Q rate, the new milk sampling location will be added to the monitoring program within 30 days. If a new location is added, the old location that yields the lowest calculated D/Q may be dropped from the program after October 31 of that year.

5.2 Interlaboratory. Comparison Program Analyses shall be performed on samples containing known quantitiu of radioactive materials that are supplied as part of a Commission approved or sponsored Interlaboratory Comparison Program, such as the

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TABLE 3-1 Critical Receptor Dispersion Parameters see i LOCATION DIR MILES X/Q D/Q m Residences

  • E 1.4 1.4 E-07 4.8 E-09 Dairy Cows ** ESE 1.6 4.3 E-08 1.5 E-09 Milk Goats ** SE 3.0 1.6 E-08 4.6 E-10 1 Heat An4==1s** SSE 1.8 2.1 E-08 7.7 E-10 Gardens ** E 1.5 1.2 E-07 3.9 E-09 Site Boundary *** ENE 0.4 1.5 E-06 3.5 E-08
  • Value based on 5 ye,' *m al meteorological data
    • Value based on 5 year average grazing seacon meteorological data
      • Site boundary value based on mest restrictive X/Q 1and-based sector (ENE) and 5 year annual average meteorological data.

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e TABLE 4-1 DOSE FACTORS FOR NOBLE GASES Gamma Air Beta Air Dose Factor Dose Factor Ni 3 Ni ar-a._ arad-sE_

Radionuclides DCi yr WCi-yr Kr-83m 1.93E+01 2.88E+02 Kr-85m 1.23E+03 1.97E+03 Kr-85 1.72E+01 1.95E+03 Kr-87 6.17E+03 1.03E+04 Kr-88 1.52E+04 2.93E+03 l1 Kr-89 1.73E+04 1.06E+04 Kr-90 1.63E+04 7.83E+03 Xe-131a 3.27E+02 1.48E+03 l1 Xe-133m 3.27E+02 1.48E+03 Xe-133 3.53E+02 1.05E+03 Xe-135m 3.36E+03 7.39E+02 Xe-135 1.92E+03 2.46E+03 Xe-137 1.51E+03 1.27E+04 Xe-138 9.21E+03 4.75E+03 Xe-139 5.28E+03 6.52E+04 Ar-41 9.30E+03 3.28E+03

n

Nine Mile Point Nuclear Station Unit 1 Radiological Environmental Monitoring Program Sampling Locations Table 5.1 Type of

  • Map Sample Location Collection Site Location Radioiodine and 1 Nine Mile Point Road 1.8 mi 6 88* E Particulates (air) north Radioiodine and 2 Co. Rt. 29 & Lake Road 1.1 mi G 104* ESE Particulates (air)

Radioiodine and 3 Co. Rt. 29 1.5 mi 9 132' SL Particulates (air)

Radioiodine and 4 Village of Lycoming, NY 1.8 mi 0 143' SE Particulates (air) 1

-Radioiodine and 5 Montario Point Road 16.4 mi 6 42' NE Particulates (air)

Direct Radiation (TLD) 6 North Shoreline Area 0.1 mi 8 5' N 1 Direct Radiation (TLD) 7 North Shoreline Area 0.1 mi 6 25' NNE Direct Radiation (TLD) 8 North Shoreline Area 0.2 mi 8 45' NE Direct Radiation (TLD) 9 North Shoreline Area 0.8 mi 6 70* ENE Direct Radiatich (TLD) 10 JAF east boundary 1.0 mi 8 90* E I

l Direct Radiation (TLD) 11 Rt. 29 1.1 mi 9 115* ESE ,

Direct Radiation (TLD) 12 Rt. 29 1.4 mi 6 133' SE' Direct Radiation (TLD) 13 Miner Road 1.6 mi @ 159' SSE Direct Radiation (TLD) 14 hiner Road 1.6 mi 6 181* S Direct Radiation (TLD) 15 Lakeview Road 1.2 mi 6 200* SSk l Direct Radiation (TLD) 16 Lakeview Road 1.1 mi @ 225' Sh Direct Radiation (TLD) 17 Site Meteorological Tower 0.7 mi G 250* WSW Direct Radiation (TLD) 18 Energy Information Center 0.4 mi 6 265* W

  • Map - See Figures 5.1-1 and 5.1-2

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Nine Mile Point Nuclear Station Unit 1 Radiological Environmental Monitoring Program Sampling Locations Table 5.1 (Continued)

Type of

  • Map Sample Location Collection Site Location Direct Radiation (TLD) 19 North Shoreline 0.2 mi 6 294* WhW Direct Radiation (TLD) 20 North Shoreline 0.1 mi 6 315' NW Direct Radiation (TLD) ~21 North Shoreline 0.1 mi 8 341' NNW Direct Radiation (TLD) 22 Demster Beach Road 4.8 mi @ 97* E Direct Radiation (TLD) 23 Leavitt Road 4.1 mi 6 111* ESE Direct Radiation (TLD) 24 Rt. 104 4.2 mi 0 135
  • S E 1

Direct Radiation (TLD) 25 Rt. 51A 4.8 mi 9 156* SSE Direct Radiation (TLD) 26 Maiden Lane Road 4.4 mi G 183* S Direct Radiation (TLD) 27 Co. Rt. 53 4.4 mi 8 205* SSk Direct Radiation (TLD) 28 Co. Rt. 1 4.7 mi 8 223' SW 4

Direct Radiation (TLD) 29 Lake shoreline 4.1 mi 9 237' WSW Direct Radiation (TLD) 30 Phoenix, NY Control 19.8 mi G 170' S-SSE j Direct Radiation (TLD) 31 S.W. Oswego, control 12.6 mi 6 226' Sk 1

i Direct Radiation (TLD) 32 Scriba, NY 3.6 mi 0199* SSW Direct Radiation (TLD) 33 Alcan Aluminum, Rt. lA 3.1.mi 0 220' Sk l Dircet Radiation (TLD) 34 Lycoming, NY 1.8 mi 6143' SE

[- Direct Radiation (TLD) 35 New Haven, NY 5.3 mi 6 123' ESE Direct Radiation (TLD) 36 W. Boundary, Bible Camp 0.9 al 3 237' SW-WSW I

Direct Radiation (TLD) 37 Lake Road 1.2 mi 8 101' E-ESE Surface Water- 38 OSS Inlet Canal 7.6 mi 0 235' SW-WSW Surface Water 39 JAFNPP Inlet Canal 0.5 mi 0 70' ENE

  • Map - See Figures 5.1-1 and 5.1-2 l

l

Nine Mile Point Nuclear Station Unit 1 Radiological Environmental Menitoring Program Sampling Locations Table 5.1 l (Continued)

Type of

  • Map Sample Location Collection Site Location Shoreline Sediment 40 Sunset Bay Shoreline 1.5 mi 8 80' E Fish 41 NMP Site Discharge Area 0.3 mi G 315' NW and/or Fish 42 NMP Site Discharge Area 0.6 mi 9 55' NE Fish , 43 Oswego Herbor Area 6.2 mi 0 235' WSk Milk 44 Milk Location #50 9.3 mi 8 93* SE Milk 45 Milk Location #7 5.5 mi 0 107' ESE 1

Milk 46 Milk Location #16 5.9 mi @ 190' S Milk 47 hilk Location #40 15.0 mi @ 223* SW Food Product 48 Produce Location #1** 1.3 mi 8 98* E (O'Connor)

Food Product 49 Produce location #2** 1.8 mi @ 96

  • ES E (J. Parkhurst)

Food Product 50 Produce Location #3** 1.9 mi 8 101' ES E (Fox)

Food Product 51 Produce Location #4** 1.5 mi 8 114' Sk (C. Parkhurst)

Food Product 52 Produce Location #5** 2.1 mi G lil' S (C. R. Parkhurst)

Food Product 53 Produce Location #6** 2.2 mi @ 123' SE (J. Lawton)

Food Product' 54 Produce Location #7** 15.0 mi 9 223' ESE (Mc Millen)' -

Food Product 55 Produce Location #8** 12.6 mi @ 225* Sh (Denman)

  • Map - See Figures 5.1-1 and 5.1-2
    • Food Product samples need not necessarily be collected from all listed locations. Collected samples will be of the highest calculated site average D/Q.

o .

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TABLE C-1 D/Q TABLE, I

(ANNUAL METEOROLOGICAL DATA) 1NMP UNIT St STACK CORRECTED FOR OPEN TERRAIN RECIRCULATION 4

seesesseestessessesse RELATIVE DEPOSITION PER UNIT AREA (Neo-2) AT FIXED POINTS BY DOWNNIND SECTORS eseessessessessessee DIRECTION DISTANCES IN HILES FROH SITE .50 1.00 1.50 2.00 2.59 3.45 3.50 4.00 4.58 5.00 5.59 S 9.974E-09 2.980E-09 1.178E-09 6.345E-10 3.907E-19 2.74tE-te 1.999E-10 1.52tE-19 1.196E-SS 9.636E-it 7.927E-11 SSN SH 1.02tE-08 3.332E-99 1.331E-09 7.271E-19 4.590E-10 3.162E-10 2.388E-19 1.756E-19 1.37?E-10 1.119E-19 9.113E-11 4.038E-99 2.898E-99 8.846E-10 4.984E-19 3.206E-18 2.234E-10 1.64tE-te 1.252E-18 9.042E-11 7.914E-11 6.486E-11 HSH W

1.584E-09 6.278E-19 2.776E-19 1.612E-19 1.056E-19 7.443E-11 5.558E-11 4.223E-11 3.320E-11 2.68tE-11 2.198E-11  :

t.703E-99 6.908E-10 3.SS3E-19 1.703E-SE 1.172E-It 0.273E-11 6.127E-11 4 699E-it 3.702E-11 2.980E-ti 2.442E-11 NHH 3.909E-09 1.495E-99 6.589E-te 3.797E-10 2.478E-19 1.74tE-10 1.286E-10 9.84tE-11 7.742E-St 6.227E-11 5.190E NH MMW 1.32SE-08 4.15tE-99 1.695E-09 9.242E-SS 5.845E-19 4.026E-19 2.936E-10 2.229E-99 1.746E-19 1.401E-10 1.147E-19 1.277E-05 3.954E-99 1.566E-09 8.470E-39 5.31tE-19 3.641E-te 2.647E-10 2.998E-te 1.573E-19 1.264E-18 1.036E-19 N 1.222E-08 4.922E-99 1.647E-09 9.109E-te 5.794E-18 4.000E-10 2.932E-te 2.232E-te 1.75tE-tS 1.408E-te 1.954E-19 NNE 4.999E-99 1.730E-99 7.53?E-10 4.395E-tt 2.792E-18 1.954E-10 1.430E-18 1.999E-te 0.632E-ti 4.936E-11 5.677E-tt

HE ENE 6.613E-09 2.112E-99 8.916E-19 4.984E-10 3.199E-18 2.212E-10 1.619E-19 1.230E-10 9.432E-11 7.719E-11 6.395E-11

, i 2.386E-00 7.345E-99 2.96tE-99 1.6tSE-09 1.918E-09 6.993E-19 5.090E-10 3.06tE-10 3.922E-19 2.424E-39 1.904E-10 .

E 3.463E-99 1.036E-05 4.12SE-ST 2.225E-09 1.393E-09 9.533E-te 6.989E-te 5.23ef-80 4.095E-10 3.282E-10 2.485E-te li ESE 2.344E-08 6.998E-09 2.753E-99 1.479E-99 9.230E-10 6.303E-te 4.579E-te 3.459E-tO 2.704E-10 2.160E-10 1.775E-10 i SE SSE 1.827E-08 5.691E-09 2.242E-Of 1.212E-99 7.595E-IS 5.20SE-10 3.705E-10 2.072E-10 2.250E-99 1.800E-19 1.403E-10 9.394E-99 3.032E-99 1.105E-09 6.404E-10 4.914E-18 2.754E-10 2.006E-10 1.525E-10 1.19sE-te 9.649E-11 7.935E-11 i l

SPIRECTION DISTANCES IN N1LES FROM SSTE 6.00 6.50 7.00 7.58 0.99 8.50 9.00 9.50 10.99 15.00 29.00 I

SCW 5 6.633E-11 5.714E-ti 5.099E-11 4.542E-it 4.675E-11 3.68tE-it 3.343E-ti 3.OSPE-il 2.000E-11 1.484E-tt 9.391E-12 0$ 7.410E-St 6.623E-11 5.047E-11 5.206E-il 4.669E-11 4.214E-fl 3.826E-11 3.491E-ti 3.200E-St 1.604E-ti 1.069E-it I SH 5.400E-11 4.72tE-11 4.166E-11 3.787E-ti 3.322E-11 2.997E-11 2.719E-it 2.479E-ti 2.27tE-11 1.106E-St 7.417E-12 i ! ,

t NSM H

1.030E-11 1.618E-it 1.420E-11 1.264E-11 1.133E-11 1.922E-11 9.276E-12 9.460E-12 7.75tE-82 4.962E-82 2.540E-12 e 2.83tE-11 1.787E-ti 1.577E-11 8.403E-11 1.257E-il 1.134E-ti 1.029E-11 9.379E-92 0.59tE-12 4.490E-12 2.000E-12 HHW 4.241E-11 3.721E-11 3.203E-18 2.92tE-11 2.617E-11 2.360E-11 2.14tE-11 1.95tE-11 1.787E-11 9.314E-12 5.st4E-12  !

f.W 9.540E-11 0.292E-11 7.317E-11 6.509E-St 5.833E-11 5.260E-11 4.779E-11 4.347E-St 3.901E-it 2.969E-11 1.200E-11 NNH 0.630E-St 7.490E-11 6.6ttE-11 5.083E-11 5.274E-11 4.758E-St 4.317E-11 3.937E-11 3.607E-it 1.096E-St 1.179E-SS N 9.617E-11 S.370E-11 7.394E-11 6.500E-11 5.098E-11 5.328E-tt 4.027E-11 4.482E-11 4.032E-11 2.tOSE-11 1.319E-11 NNE 4.718E-11 4.130E-11 3.643E-11 3.24tE-11 2.984E-it 2.688E-11 2.374E-St 2.964E-11 1.901E-11 1.029E-11 6.498E-12 I

4 NE 5.232E-SS 4.552E-11 4.014E-11 3.569E-11 3.196E-11 2,000E-11 2.6 tee-11 2.377E-11 2.174E-11 1.120E-ti 6.914E-12 ,

ENE t.659E-19 1.43tE-19 1.263E-19 1.123E-19 1.086E-is 9.974E-St 0.220E-11 7.499E-11 6.065E-11 3.563E-St 2.214E-ti '

, E 2.234E-19 1.932E-10 1.705E-10 1.517E-te 1.359E-18 1.225E-19 1.11sE-10 1.012E-te 9.264E-St 4.000E-11 2.975E-11 ESE SE 1.470E-19 1.279E-18 1 128E-10 1.003E-10 9.909E-11 S.196E-11 7.35tt-it 6.700E-11 6.135E-SS 3.800E-11 1.fe2E-11 l I.237E-te 1.073E-18 7.473E-tt 9.432E-ti 7.559E-it 6.02tE-st 6.190E-fl 5.645E-st 5.t?3E-il 2.710E-ti 1.697E-il l

SSE 6.638E-11 5.770E-11 5.Of6E-11 4.539E-11 4.972E-11 3,677E-11 3.349E-18 3.949E-11 2.796E-18 1.488E-11 9.359E-12 O ,

I i

h f

1 TABLE C-2

! D/Q TABLE (GRAZING SEASCN METEOROLOGICAL DATA)*

I

! i 1NNP UNIT 01 STACK

' CORRECTED FOR OPEN TERRAIN RECIRCULATION i' esesseessessetteseets RELATIVE DEPOSITION FER UNIT AREA IHee-2) AT FIXED POINTS BY DONNNIND SECTORS

! DIRECTION DISTANCFS IN HIIES seessessessessessese l FRON SITE .50 1.00 1.50 2.00 2.50 3.00 3.55 4.00 5 4.50 5.00 5.50 l SSW 9.43tE-99 3.Sa6E-99 1.172E-99 6.292E-It 3.92RE-19 2.689E-20 1.956E-10 1.407E-tg 1.169E-te 9.417E-11 7.752E-11 SH 8.830E-09 2.91YE-09 1.160E-09 6.334E-10 3.997E-10 2.754E-10 2.011E-88 1.53tE-10 1.283E-15 9.69tE-t! 7.966E-11 4.996E-09 1.724E-09 7.228E-10 4.067E-10 2 6tSE-19 1.822E-18 1.339E-18 1.023E-te 0.044E-st 6.475E-tS 5.312E-11

, HSH W 1.17tE-89 4.783E-13 2.118E-10 1.233E-10 9.094E-11 5.712E-11 4.23tE-St 3.248E-11 2.56tE-11 2.864E-11 1.694E-11 j' WNH t.257E-ST 5.273E-te 2.395E-19 1.418E-te 9.315E-It 6.595E-11 4.894E-81 3.758E-it 2.963E-11 2.357E-11 1.957E-11

NW 3.639E-09 1.351E-09 5.990E-te 3.383E-10 2.292E-10 1.545E-10 1.140E-te 8.724E-11 6.564E-11 5.522E-st 4.524E-11 I NNu t.270E-98 4.854E-09 1.655E-09 9.IttE-te 3.777E-10 3.987E-19 2.911E-10 2.212E-19 1.734E-10 1.392E-te 1.149E-10 I N 1.272E-88 4.SetE-09 1.589E-99 9.621E-18 5.417E-te 3.719E-18 2.709E-10 2.056E-19 1.612E-18 1.295E-10 1.063E-10 i e

NNF 1.324E-08 4.369E-09 1.785E-99 9.067E-SS 6.274E-10 4.340E-18 3.174E-te 2.487E-te 1.897E-10 1.525E-te 1.251E-19 I

NE 4.8tSE-09.1.709E-09 7.382E-10 4.209E-19 2.727E-19 1.900E-te 1.484E-te 1.873E-te 5.43tE-11 6.776E-11 5.547E-11

, , ENE 5.252E-99 1.747E-09 7.496E-18 4.229E-te 2.724E-10 1.997E-10 1.792E-10 1.040E-te 0.312E-11 6.667E-st 5.448E-ti E 2.359E-00 7.495E-89 3.956E-89 1.60tE-09 1.065E-09 7.349E-10 5.364E-te 4.076E-10 3.194E-10 2.564E-te 2.tOGE-10 E8E 3.28tE-08 9.920E-89 3.937E-99 2.14tE-99 1.347E-99 9.242E-19 6.723E-te 5.990E-te 3.990E-10 3.20tE-10 2.620E-10 SE t.984E-80 5.790E-09 2.294E-09 1.239E-09 7.757E-10 5.380E-3s 3.857E-10 2.923E-19 2.207E-te 1.036E-te 1.503E-te SSE 1.628E-08 5.968E-89 1.983E-09 1.068E-49 6.673E-19 4.567E-10 3.319E-10 2.518E-10 1.974E-te 1.507E-18 1.303E-18 SDIRECTION 9.833E-09 3.087E-09 1.103E-09 6.389E=stDISTANCES 3.92tE-te 2.67bE-19 IN HIEES 1.942E-10 1.474E-18 1.157E-te 9.3t?E-11 7.668E-11 FRDM StiL 6.08 6.59 7.00 7.50 8.88 8.50 9.00 9.58 19.99 S 15.00 28.08 i em g

854 6.493E-St 5.642E-St 4.994E-it 4.449E-11 3.985E-ti 3.599E-it 3.27tE-11 2.996E-11 2.748E-11 1.456E-11 9.23tE-12 i g3 SH 6.658E-11 5.799E-11.5.121E-11 4.56tE-11 4.99tE-11 3.694E-11 3.354E-11 3.06tE-11 2.907E-11 1.403E-11 9.36tE-12 l j g MSN 4.428E-11 3.874E-11 3.419E-t!.3.043E-St 2.72SE-11 2.462E-ti 2.234F-11 2.030E-11 1.067E-11 9.797E-12 6.149E-12 N 1.412E-11 1.243E-11 1.8??E-11 9.762E-12 8.753E-12 7.898E-12 7.168E-12 6.539E-12 5.993E-12 3.150E-12 1.990E-12 7

WNW 1.628E-11 1<434F-11 1.266E-11 1.126E-St 1.909E-tt 9.105E-12 8.26tE-12 7.533E-12 6.901E-12 3.6ttE-12 2.263C-12 NW 3.764E-11 3.302E-tt 2.913E-11 2.592E-st 2.323E-11 2.095E-11 1.95tE-11 1.733E-11 1.597E-11 S.285E-12 5.879E-12 NNM 9.492E-11 8.253E-11 7.202E-11 6.479E-tt 5.886E-11 5.236E-it 4.749E-11 4.329E-11 3.964E-81 2.064E-11 1.286E-11 N 8.863E-fl 7.694E-tt 6.79tE-18 6.045E-tt 5.420E-St 4.890E-it 4.438E-11 4.047E-ti 3.709E-it 1.943E-ti 1.217E-11 i NNE 1.043E-10 9.004E-11 8.017E-11 7.135E-St 4.396E-11 5.771E-St 5.236E-38 4.775E-ti 4.375E-11 2.290E-st 1.434E-ti HE 4.612E-11 4.037E-fl 3.562E-11 3.160E-st 2.839E-t! 2.560E-11 2.322E-11 2.116E-18 1.930E-11 8.000E-11 6.203E-12 }

ENE 4.522E-11 3.94%E-11 *. 479E-11 3.994E-11 2.77tE-11 2.497E-St 2.263E-S$ 2.062E-11 1.006E-11 9.739E-12 6.02SE-12 E 1.748E-10 1.St9E-18 1.349E-10 1.192E-18 1.969E-10 9.637E-11 8.740E-St 7.966E-11 7.295E-it 3.795E-11 2.364E-11 ESE 2.181E-te 1.898E-10 1.66SE-18 1.484E-10 1.330E-19 1.199E-te 1.087E-10 9.918E-11 9.074E-11 4.714E-11 2.932E-11 '

SE 1.252E-10 1.084E-10 9.578E-11 0.515E-11 7.632E-11 6.053E-fl 6.243E-18 5.691E-SS 5.212E-11 2.715E-11 1.692E-11 SSE 1.SSSE-SS 9.435E-11 S.33SE-11 7.416E-tt 6.65tE-St 6.092E-St 5.448E-it 4.97tE-fl 4.556E-11 2.394E-18 1.594E-11 6.421E-tt 5.568E-11 4.910E-St 4.301E-11 3.93tE-11 3.551E-11 3.226E-18 2.945E-11 2.702E-11 1.433E-18 9.067E-1R L

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APF 2NDIX - A T

DOSE PARAMETERS FOR IODINE 131 AND 133 f PARTICULATES AND TRITIUM l

1 l

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, , , APPENDIX A DOSE PARAMETERS FOR IODINE - 131 AND - 133, PARTICULATES AND TRITIUM i This appendix contains the methodology which was used to calculate the dose 1 parameters for I-131, I-133, particulates, and tritium. The dose parameter, ,

Rg , was calculated using the methodology outlined in NUREG-0133 and Regulatory Guide 1.109, Revision 1. The radiciodine and particulate Technical Specification (Section 3.6.15) is applicable to the location in the unrestricted area where the combination of existing pathways and receptor age groups indicates the maximum potential exposure occurs, i.e. , the critical receptor. The inhalation and ground plane exposure pathways are considered to 4

cxist at all locations but the critical location will be used for dose purposes. The grass-goat-milk, the grass-cow-milk, grass-cow-meat, and vegetation pathways are considered to exist at specific locations. R g values have been calculated for the adult, teen, child and infant age groups for all pathways. The methodology used to calculate these values follows:

A.1 Inhalation Pathway j R = K(BR), (DFg),

where:

R = dose factor for each identified radionuclide i of the organ of interest (units = area /hr per uCi/m3);

K' = a constant of unit conversion:

6

= 10 pCi/uci; (BR), = Breathing rate of the receptor of age group a, (units = M /yr);

( DFg ), , = organ inhalation dose factor for radionuclide i for the receptor of age group a, (units = area /pCi). ,

1 ._ _ _ _ , ._

I

(

The breathing rates (BR), for the various age groups, as given in Table E-5 of Regulatory Guide 1.109 Revision 1, are tabulated below.

Age Group (a) Breathing Rate (m3/yr)-

Infant 1400 Child 3700 Teen 8000 Adult 8000 inhalation dose factors (DFA;), for the various age groups are given in Tables E-7 through E-10 of Regulatory Guide 1.109 Revision 1.

A.2 Ground Plane Pathway

~

t RG g

=

K'K"(SF)DFG; ( l-e i

)

A l

where:

C R = dose factor for the ground plane pathway for each identified radionuclide i fcr the organ of interest -(units = mrem /yr per uCi/sec per m 2)

K' = a constant.of unit conversion;

= 6 10 pCi/uCl; K" =~ a constant of unit conversion;

= 8760 hr/ year; i

.-11h3

hhwg -- -ee apa ==M*4-* +mw-'Mg** aN'==&M*8n J

A g

= the radiological decay. constant for radionuclide i, (units = sec~I) t = the exposure time, see:

= 8 4.73 x 10 sec (15 years):

DFG; = the ground plane dose conversion factor for radionuclide 1; (units = mrem /hr per pCI/m2) .

SF = the shielding factor -(dimensionless);

t A shielding factor of 0.7 is discussed in Table E-15 of Regulatory Guide

( 1.109 Revision 1. A tabulation of DFG; values is presented in Table E-6 of Regulatory Guide 1.109 Revision 1.

A.3 Grass-Cow or Goat-Milk Pathway

-1 t E; te -

At gb) g i f r(1-e ) + B, (1-e _ +

R; = K'Q p U,p , (DFL ), F g e fpf, Yy A E -

"A l

1

-A - -Agh t

E' t _x (1-fpsf ) "II-* ) + B gy (I-e ib) ,

Y A 5

E P I i

~

where:

M R; = dose factor for the cow milk or goat milk pathway, for each

( Identified radionuclide i for the organ of Interest, (units =

mrem /yr per uCI/sec per m-2) i i

. .O

/ K' = . a constant of unit conversion; 6

=' 10 pCl/uCI

~

Qp = The cow's or goat's feed consumption rate, (units = Kg/ day-wet weight)

U,p = the receptor's milk consumption rate for age group a, (units =

liters /yr);

Yy = the agricultural productivity by unit area of pasture feed grass, (units = kg/m2);

Y, = the agricultural productivity by unit area of stored feed, (units I

= kg/m2);

F, = the stable element transfer coefficients, (units = pCl/ liter per pCi/ day);

r = fraction of deposited activity retained on cow's feed grass:

=

( DFL;), the organ ingestion dose factor for radionuclide i for the receptor in age group a, (units = mrem /pCl):

1 =

A; + A ,;

1; = the radiological decay constant for radionuclide i, l (units = sec ~I);

! A, = the decay constant for removal of activity on leaf and plant.

! surfaces by weathering

= 5.73 x 10 ~7 sec ~I (corresponding to a 14 day half-life):

--73 ?

t

_- _ . _ _ . . _ __ _ _ _ _ . ._ ._ _ _ . ~

l l

l b

'[ ,

t g

= the transport time- from feed to cow or goat to milk, to receptor, (units = sec);

t = the transport time from harvest, to cow or goat, to consumption, h

(units = sec);

t b

  • period of time that soil is exposed to gaseous effluents, (units =

sec);

B gy = concentration factor for uptake of radionuclide i from the soil by the edible parts of crops, (units = pCi/Kg (wet weight) per-pCi/Kg (dry soil);

P = effective surface density for soil, (units = Kg (dry soll)/m2);

f p

= fraction cd the year that the cow or goat is on pasture *:

[

\-

f, = fraction of the cow feed that is pasture grass while the cow is on pasture *;

t, = period of pasture grass and crop exposure during tha growing season, (units = sec);

  • Milk cattle and goats are considered to be fed from two potential sources, pasture g.rass and stored feeds. Following the' development in Regulatory.

Culde 1.109 Revision 1, the value of f, was considered unity in lieu of site-specific information. The value of f was 0.667 based upon an p

8-month grazing period.

Table A-1 contains the appropriate' values and their source in Regulatory

, - Guide 1.109 Revision 1.

The concentration of tritium in milk is based on the airborne concentration rather than the deposition. Therefore, the R. is based on X/Q:

k '

M '

R =

K'K'"F,Op u,pm ;) , 0. m o. W )

~ .

_7p, .

w -- -.-.,-w. - ,,, 6-r-

t

'Where:

M =

R .g. dose factor for the cow or goat milk pathway for tritium for the organ of interest, (units = mrem /yr per uCi/m3):

K'" =

a ecnstant of unit conversion:

103 gm/kg; H

absolute humidity of the atmosphere, (units = gm/m3); , '

O.75 =

the fraction of total feed that is water:

0.5 = the ratio of the specific activity of 'he feed grass water to the atmospheric water.

.( Other values are given above. A value of H of 8 grams / meter 3, was used in lieu of site-specific information.

A.4 Grass-Cow-Meat Pathway

~

-A *e

-A gf t - p(g E

I ), , Bg(1-e

-AhJ +

R = K'Q p U,pF,p (DFL), e ff ps Y

v

~

I g E; _

-1 E

t -

-A t -A't

  • + B gy (I-e gb) *

(1-fp f,) r(1-e )

Y A r s Py E

, i I -

l I

l R Bg =

dose factor for the meat ingestion pathway for radionuclide i for any organ of interest, (units = mrem /yr per uCi/sec per m-2) l

(

F, =

the stable element transfer coefficients, (units = days (Kg):

1

--75 '

n.n ,. .-- .-, --

w -

l_

( U,p = the receptor's meat consumption rate for age group a, (units =

kg/ year; t, =

the transport time from slaughter to consumption, (units = sec);

th = the transport time from harvest to animal consumption, (units = sec);

t, =

period of pasture grass and crop exposure during the growing season, (units = sec)

All other terms remain the same as defined for the milk pathway. Table A-2 contains the values which were used in calculating RB, The concentration of tritium in meat is based on airborne concentration rather than deposition. Therefore, the R is based on X/Q.

g B =

R .g. K'K'"Ffp Q U,p (DFL,), [0.75(0.5/H)]

where:

B RT =

dose factor for the meat ingestion ' pathway for tritium for l any organ of interest, (units = mrem /yr per uCi/m3).

All terms are denned above. -

~A.5 Vegetation Pathway The integrated concentration in vegetation consumed by man follows the i

l expression developed for milk. Man is considered to consume two types of vegetation (fresh and stored) that differ only in the time period between harvest and consumption, therefore:

1 o

-. . . - . . . _ - - . .. . -_. _ _ _ =. . ___ -  : .

J e

( r i e

[ -Ai tb R = Uf L

-Alg t f -A E

t g (;_,

K'(DFLg ), *

"I' ' Y v AE

'v ai i s

-A '

Eg t -Agb t

8 (I-e j s -Alth r(I-e .) IV U,fe g +

Y AE g P i s where: '

V Rg =

dose factor for vegetable pathway for radionuclide i for the organ of interest, (units = mrem /yr per uCi/sec per m-2)

K' =

a constant 6

of unit conversion:

= 10 Ci/uCI:

f s~ L U, =

the consumption rate of fresh leafy vegetation by the receptor in age group a, (units = kg/yr) f =

L the fraction of the annual intake of fresh leafy vegetation grown locally; f =

g the fraction of the annual intake of stored vegetation g rown locally; t =

g the average time between harvest of leafy vegetztion and its consumption, (units = sec);

t =

the average time between harvest of stored vegetation and its consumption, (units = sec);

Yy =

the . vegetation area density, (units = kg/m2) k' =

t, period of leafy vegetable exposure . during growing season (units = sec);

'A77L e

( .

f All other factors are defined above.

Table A-3 presents the appropriate parameter values and their source in Regulatory Guide 1.109 Revision 1.

In lieu of site-specific data, values for f and f o f, 1.0 and 0. M .

L g respectively, were used in the calculation. These values were obtained from Table E-15 of Regulatory Guide 1.109 Revision 1.

The concentration of tritium in vegetation is based on the airborne concentration rather than the deposition. Therefore, the Rg is based on X/Q:

7 R = K'K" U f +

T L Uffg (DFL;), 0. 75 (0.5 / H) a where:

i 8.,

Y RT =

dose factor for the vegetable pathway for tritium for any organ of interest, (units = mrem /yr per uCi/m3).

All other terms are defined in preceeding sections.

e-

- - - - ^

^

f

(

[ TABLE A-1 Parameters for Cim and Coat Milk Pathways Parameter Value Reference (Reg. Culde 1.109 Rev.1)

Qp (kg/ day) 50 (cow) Table E-3 6 (goat) Table E-3 I

-Y y (kg/m2) 0.7 Table E-15 tg (seconds) 1.73 x 105 (2 days) Table E-15 r 1.0 (radiolodines) Table E-15 0.2 (particulates) Table E-15 (DFLg ), (mrem /pCI) Each radionuclide Tables E-11 to E-14 F, (pCi/ day per pCilliter) Each stable element Table E-1 (cow)

Table E-2 (goat)

'~

tb (seconds) 4.73 x 108 (15 yr) Table E-15 Y,(kg/m2) ,

2.0 Table E-15 , .

Yy (kg/m2) 0.7 Table E-15 '

th (seconds) 7.78 x 10I (90 days) Table E-15 U

ap (liters /yr) 330 infant Table E 330 child Table E-5 400 teen Table E-5 310 adult Table E-5 t, (seconds) 2.59 x 106 ( asture) Table E-15 5.18 x 10 (stored feed)

B gy (pCl/Kg (wet weight) Each stable element Table E-1 per pCi/Kg (dry soil))

P (Kg dry soll/m2) 240 Table E-15 e

_ -, _ .~ _ _

j

(

\ \

l TABLE A-2

{

Parameters for the Meat Pathway Parameter Value . Reference (Reg. Guide 1.109 Rev. Il r 1.0 (radioiodines) Table E-15 0.2 (particulates) Table E-15 Ff (pCi/Kg per pCi/ day) Each stable element Table E-1 U8p (Kglyr) 0 infant Table E-5 41 child Table E-5 65 teen Table E-5 110 adult Table E-5 (DFL;), (mrem /pCl) Each radionuclide Tables E-11 to E-14' Yy (kg/m2) 0.7 Table E-15 f Y,(kg/m2) 2.0 Table E-15 s

tb (seconds) 4.73 x 108 (15 yr) Table E-15 t, (seconds) 1.73 x 106 (20 days) . Table E-15 th (seconds) 7.78 x 106 (90 days) Table E-15

, t, (seconds) 2.59 x 106 (pasture) Table E-15 l-l 5.18 x 10 (stored feed)

Op (kg/ day). 50 Table E-3 I

B;y (pCl/Kg (wet weight Each stable element Table E-1 per pCi/Kg (dry soil))

P (Kg (dry soil)/m2) 240 Table E-15 L

I

4

. - , . . . , . . . . . - - - . . . . - , . --w.=

l j TABLE A-3 l Parameters for the Vegetable Pathway Parameter Value Reference (Reg. Guide 1.109 Rev.1)

. r (dimensionless) 1.0 - (radioiodines) Table E-1 0.2 (particulates) Table E-1 -

(DFL;), (mrem /CI) Each radionuclide Tatsles E-11 to E-14 U (kglyr) - infant 0 Table E-5

- child 26 Table E-5

- teen 42 Table E-5

- adult 64 Table E-5 Uf (kg/yr) - infant 0 Table E-5

- child 520 Table E-5

- teen 630 Table E-5

- adult 520 Table E-5 tg (seconds) 8.6 x 10" (1 day) Table E-15 th (seconds) 5.18 x 106 (60 days) . Table E-15 Yy (kg/m2) .2.0 . Table E-15 t, (seconds) 5.18 x 106 (60 days) Table E-15 tb.(seconds) 4.73 x 108 (15 yr) Table E-15 P(Kg(dry soil)/m2) 240 Table E-15 togy(pCl/Kg (wet weight) Each stable element . Table E-1 per pCi/kg (dry soil)) .

I i

l

'{

sa-

. _ . . - . . _ . . . _ . _ . .. _ . . . . . _ , . ~ _

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D/Q TABLE t

! (CRAZING SEASON METEOROLOGICAL DATA) l

! NMP UNITM ST ACK j CORRECTED FOR OPEH TERRAIN RECIRCULATION *e***o**eceeeeeeeese

eeoeooooooseeeeeeeees RELATIVE DEPOSITION PER UNIT AREA iMee-ti AT FIRED POINTS SY 00WNUINO SECTORS i OIRECTION DISTANCES IN MILES FROM SITE .54 1.00 9.50 2.40 2.50 3.00 3.50 4.00 4.50 5.00 5.50 S l.079E-00 3.324E-99 1.270E-99 6.748E-10 4.18tE-It 2.840E-10 2.064E-10 1.565E-10 1.227E-19 9.076E-fl 3.120E-II SSW 3.03eE-88 3.242E-09 f.tT9E-09 6.049E-10 4.207E-80 2.936E-19 2.136E-19 1.68tE-te 1.272E-10 1.023E-10 8.40lE-fl SW 5.999E-89 8.974E-09 8.074E-10 4.464E-10 2.839E-10 1.964E-19 8.436E-10 l.093E-10 0.509E-fl 6.890E-Il 5.655E-fl .

l.658E-09 5.939E-19 2.526E-10 1.43tE-19 9.253E-fl 6.463E-fl 4.757E-fl 4.24,E-fl 3.635 3.806E-ll E-fl 2.059E-fl 3.340E-fl 2.300E-fl l WSW W l.87eE-09 6.736E-ie 2.90eE-10 i.66tE-te 1.07eE-ie 7.548E-n 5.56eE-fl 2.6 6E-fl 2.te.E-It UNW 4.629E-99 1.579E-09 6.677E-10 3.760E-10 2.410E-19 1.683E-10 9.236E-te 9.423E-ll 7.398E-fl 5.945E-fl 4.867E-Il .

NW l.586E-08 4.78tE-49 1.906E-09 1.032E-99 6.468E-10 4.43eE-19 3.287E-10 2,437E-19 1.906E-10 1.520E-10 8.25tE-10 -

NNW I.556E-98 4.650E-99 l.8ISE-09 9.780E-19 6.055E-10 4.129E-10 2.993E-10 2.265E-80 1.77tE-10 1.4ttE-10 1.165E-10  ;

t N 1.635E-08 5.076E-09 2.93tE-09 8.lt5E-09 6.953E-10 4.776E-10 3.477E-10 2.639E-10 2.967E-10 l.459E-19 1.36eE-10 NNE 6.522E-09 2.ll3E-09 e.8etE-te 4.899E-te 3.127E-10 2.967E-10 9.595E-19 1.206E-10 9.45tE-fl 7.585E-fl 6.295E-fl <-

NE 7.276E-99 2.222E-99 9.14tE-te 5.928E-10 3.185E-te 2.194E-10 1.590E-10 f.tl2E-te 9.478E-fl 7.591E-fl 6.199E-fl ENE t.955E-98 8.799E-99 3.409E-09 1.000E-09 1.176E-99 8.036E-10 5.829E-10 4.412E-40 3.440E-10 2.764E-10 2.24tE-10 E 3.97tE-88 8.143E-08 4.46tE-09 2.375E-99 1.473E-99 1.000E-09 7.236E-10 5.463E-10 4.263E-10 3.414E-te 2.79tE-10

, ESE 2.305E-00 6.595E-09 2.553E-09 9.353E-49 8.36tE-19 5.672E-10 4.994E-10 3.089E-10 2.410E-10 1.930E-19 1.579E-10 SE l .88tE-98 5.557E-09 2.143E-09 1.138E-09 7.045E-t e 4.789E-10 3.464E-10 2.619E- 19 2.040E-19 1.644E-10 1.347E-10  :!

SSE I.120E-08 3.361E-09 1.277E-09 6.743E-10 4.16tE-le 2.824E-te 2.042E-10 1.545E-10 1. TIDE-10 9.728E-fl 7.993E-Il DIRECileN DISTANCES IN MILES ,

,' FROM s 1E 6.00 6.50 7.90 7.59 8.00 0.50 9.00 9.55 10.00 15.96 29.99 lt

S 6.796E-St 5.884E-ll 5.197E-ll 4.620E-Il 4.853E-fl 3.75eE-fl 3.406E-Il 3.199E-91 2.85tE-fl 1.50SE-Il 9.5tlE-12 I!

SSW 7.el8E-Il 6.090E-fl 5.377E-fl 4.707E-II 4.294E-It 3.876E-fl 3.518E-fl 3.280E-II 2.943E-fl f.549E-fl 9.74tE-82 l l SW 4.7 tee-fl 4.105E-fl 3.623E-fl 3.224E-11 2.899E-fl 2.607E-ll 2.366E-fl 2.tS7E-ll f.976E-fl f.034E-Il 6.467E-It '

t WSW l.57tE-Il 1.375E-ll 1.tl4E-ll t.SSSE-fl 9.682E-la 8.734E-te 7.925E-It 7.et7E-It 6.6tlE-It 3.445E-It 2.179E-It W l.830E-Il I.603E-fl f.414E-fl 1.tSSE-ll 3.127E-11 1.917E-fl 9.229E-12 8.405E-It 7.690E-It 4.9 tee-12 2.504E-12 WNW 4.049E-fl 3.536E-fl 3.It9E-11 2.776E-il f.487E-Il 2.243E-fl 2.034E-li f.854E-ll 9.690E-Il 8.830E-It 5.509E-It NW t.04tE-19 9.097E-Il 7.947E-fl 7.969E-Il 6.334E-Il 5.7tlE-fl 5.878E-fl 4.799E-fl 4.3 tee-fl 2.24fE-fl 1.392E-St j NNW 9.714E-It 8.397E-fl 7.4ffE-fl 6.595E-It 5.99fE-fl 5.33tE-fl 4.837E-fl 4.4tlE-fl 4.040E-fl 2.198E-It 9.315E-fl N l.133E-10 9.820E-Il 8.673E-Il 7.787E-fl 6.917E-fl 6.239E-Il 5.659E-Il 5.189E-fl 4.726E-fl 2.465E-ll 1.538E-fl d

NNE 5.158E-fl 4.491E-fl 3.96tE-fl 3.524E-Il 3.I$7E-St 2.846E-fl 2.58tE-fl 2.35tE-Il 2.15tE-Il I.fl6E-fl 6.930E-It NI 5.846E-fl 4.462E-Il 3.935E-fl 3.499E-fl 3.333E-St 2.823E-fl 2.558E-ll 2.330E-ll 2.83tE-fl I.997E-fl 6.766E-SE ENE I 802E-50 1.627E-10 9.435E-10 8.271E-10 1.544E-te 1.03tE-19 9.350E-Il 8 SteE-fl 7.799E-Il 4.04tE-fl 2.50SE-fl E 2.323E-19 2.901E-14 1.745E-80 9.570E-80 9.407E-10 9.26SE-19 1.150E-10 9.847E-10 9.587E-Il 4.957E-II.3.969E-St ESE I.314E-18 1.131E-te 9.98tE-ll G.879E-ll 7.955E-fl 7.172E-fl 6.502E-It 5.925E-Il 5.424E-Il 2.800E-Il I.740E-fl i SE l.t24E-te 9.702E-ll 8.564E-fl 7.622E-fl 6.833E-fl 6.865E-Il 5.593E-fl 5. tele-fl 4.673E-11 E.44tE-Il 1.525E-fl l . SSE 6.604E-ll 5.774E-Il 5.999E-fl 4.540E-It 4.073E-lt 3.677E-fl 3.330E-Il 3. 647E-f l 2.793E-I l f .473E-f l 9.268E-St i.

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