Text

Radwaste & Environ Monitoring Annual Rept 1983
	ML20087P396
Person / Time
Site:	Quad Cities
Issue date:	03/31/1984
From:	; TELEDYNE ISOTOPES
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QUAD CITIES STATION 1 RADI0 ACTIVE WASTE AND ENVIRONMENTAL MONITORING ANNUAL REPORT 1983 ww 2

i TELEDYNE ISOTOPES MIDWEST LABORATORY.

Northbrook, Illinois.

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P*2&Yaggg MARCH 1984 4(

PDR

QUAD CITIES NUCLEAR POWER STATION RADIOACTIVE WASTE AND ENVIRONMENTAL MONITORING ANNUAL REPORT 1983

-l MARCH 1984 i

TABLE OF CONTENTS Page

- INTRODUCTION 1

SUMMARY

2 1.0 EFFLUENTS 1.1 Gaseous 3 1.2 Liquid 3 2.0 SOLID RADI0 ACTIVE WASTE 3 3.0 DOSE TO MAN i

3.1 Gaseous Effluent Pathways 3 3.2 Liquid Effluent Pathways 5 4.0 SITE METEOROLOGY 5 5.0 ENVIRONMENTAL MONITORING 5 5.1 Gamma Radiation ~

6 5.2 Airborne I-131 and Particulate Radioactivity 6 5.3 Aquatic Radioactivity 6 5.4 Milk 7 5.5 Special Collection 7 6.0 ANALYTICAL PROCEDURES 7 7.0 MILCH ANIMAL CENSUS 7 8.0 NEAREST RESIDENT CENSUS 7 APPENDIX 1 - DATA TABLES AND FIGURES 8 Station Releases Table 1.1-1 Gaseous Effluents 9 Table 1.2-1 Liquid Effluents 19 Table 2.0-1 Solid Waste Shipments 24~

Figure 3.1 3.1-4~ Isodose and Concentration Contours 36 Table 3.1-1. Maximum Doses Resulting from Airborne Releases 40 Table 3.2-1 Maximum Doses Resulting from Liquid Discharges 42.

Environmental Monitoring Figure 5.0-1 Locations of Fixed Environmental Radiological Stations 44 Table 5.0-1 Standard Radiological Monitoring Program 46 Table 5.0 5.0-5 Environmental Summary Tables 48 Table 5.1-1 ~ Gamma Radiation Measurements (TLD) ~ 52.

-APPENDIX II - METEOROLOGICAL DATA 55

' APPENDIX III - ANALYTICAL PROCEDURES 84 iii F

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e INTRODUCTION

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Units 1 and 2 of the Quad Cities Station located near Cordova, Illinois next to _ the Mississippi River, are 800 MWe boiling water reactors, similar in design to Dresden Units 2 and 3. The plant has been designed to keep releases to the environment at levels below those specified in the regulations.

Liquid . effluents from Quad Cities are released to the Mississippi ~ River in controlled batches after radioassay of each batch. ' Gaseous effluents are 4 released to the atmosphere after delay 'to pemit decay of short half-life gases. Releases to the atmosphere are calculated on the basis of analyses of daily grab samples of noble gases and continuously collected composite samples of iodine and. particulate matter. The results of effluent analyses are r summarized on a monthly basis ~ and reported to' the Nuclear Regulatory Commis-sion - as required per Technical Specifications. Airborne concentrations of noble gases, I-131 and particulate radioactivity in off-site areas are calcu-lated using effluent and meteorological data on-isotopic composition ~ of' effluents..

Environmental monitoring is conducted by sampling at indicator and. reference '

(background) -locations in' the vicinity of thel Quad Cities plant to measure changes in radiation or radioactivity levels that may be attributable to plant-operations. If significant changes attributable to Quad Cities are ' measured, these changes are' correlated with effluent releases. External gama radiation exposure from noble gases and I-131 in milk are the most critical pathways at-this Esite; however, an' environmental monitoring program is conducted which includes other pathways of less importance.

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G _ - . . , _ g __ , , _ _ _ _

SUMMARY

Gaseous and liquid effluents for the period remained at a fraction of the Technical Specification limits. Calculations of environmental concentrations based on effluent, Mississippi River flow, and meteorological data for the period indicate that consumption by the public of radionuclides attributable to the plant are unlikely to exceed the regulatory limits. Gansna radiation exposure from noble gases released to the atmosphere represented the critical pathway for the period with a maximum individual ' dose estimated to be 0.18 mrem for the year, when a shielding' and occupancy factor of 0.7 is assumed.-

Environmental monitoring results confirm that dose via other pathways was not significant.

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1.0 EFELUENTS; ,

- ,1.1 Gaseous Effluents'to the Atmosphere Measured concentrations and isotopic composition of noble gases, radiciodine,- and particulate radioactivity released to the atmos-phere during the year, are listed in Table 1.1-1. A total of 1.20

'. ~

E+04 curies of fission and activation gases was released with an average release rate of 3.82E+02 pCi/sec.

A total of 0.18 curies of I-131 was released during the years with an' average release rate of 2.94E-01 pCi/sec:

A total of 0.25 curies of beta-gamma emitters and 3.74E-05 curies

,0f alpha emitters was released as airborne particulate matter, with a'n average release rate of 8.04E-03 pCi/sec.

A total .of 5.04E+02 curies of tritium was released, with an average release rate of 1.59E+01 pCi/sec.

~1.2 Liquids Released to the Mississippi A total of' 2.69E+06 liters of radioactive liquid waste (prior to dilution) containing- 0.14 curies- (excluding tritium, gases, and alpha) were discharged after dilution _ with a - total of 1.94E+09 liters of-water.

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These wastes were released at a quarterly average concentration of 3.51E-07 pCi/ml during the first and second quar-ters, dicharged on an unidentified nuclide _ basis; and 5.39E-08 pCi/ml dur,ing the third and fourth -quarters, which is 4.0% of: the Technical Specification release -limits for unidentified radioac-tivity. A total o'f 2.80E-05 curies of alpha radioactivity and 3.88 curies of tritium were released. . Quarterly release estimates and

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principal radio-nuclides in liquid effluents are given- in Table

, 1.2-1. 7 2.0 SOLID RADI0 ACTIVE WASTE r

Solid radioactiv5 wastes were shipped to Richland, Washington;

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Beatty, Nevada; and Barnwell . Nuclear _ Center, South Carolina. The-record of waste shipments is summarized in Table 2.0-1.

4 3.0 DOSE-TO' MAN

,3.1. Gasequs Effluent Pathways

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.'Gama Dose Rates- j

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' Gamma air and 'whole body dose rates off-site -were.' calculated based on measured release rates, isotopic composition of the: noble gases,

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and _ meteorological - data forf the period - (Table 3.1-1). Isodose-contours.of whole body dose are-shown in Figure 3.1-1 for the. !

year. Based .on - measured- effluents and meteorological data, the l

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< maximum dose to an individual would be 0.18 mrem for the year, with

an occupancy or _ shielding factor of 0.7 included. The maximum J gamma air dose was 0.30 mrad.

[ Beta Air and Skin Rates i The range of beta particles in air is relatively small (on the order i- of a few meters or less): consequently, plumes of gaseous effluents may .be considered " infinite" for purpose of calculating the dose i

from beta radiation incident on the skin. However, the actual dose to sensitive skin tissues is difficult to calculate because this depends on the beta particle energies, thickness of inert skin, and clothing covering sensitive tissues. For-purposes of this report the skin is taken to have a thickness of 7 mg/cm2 and an occupancy

- factor of 1.0 is used. The. skin dose from_ beta- and gamma radiation for the year was 0.27' mrem.

The air concentrations of: radioactive noble gases at the off-site receptor locations are given in Figure 3.1-2. The maximum off-site i beta air dose for the year was 0.08 mrad.

E Radioactive Iodine 1 The human thyroid exhibits a significant capacity to concentrate

ingested . or inhaled iodine, and the radioiodine, I-131, released during routine operation of the plant, may be made available to man

thus-resulting in a: dose to the thyroid. -The principal pathway of-l interest ~ for this radionuclide_ is ingestion of radioiodine in milk

by an- infant. Calculation _made in previous ' years indicate .that contributions to doses from inhalation of I-131. and I-133, and I-133 in' milk ar'e negligible.-

l l Iodine-131' Concentrations in Air L The calculated concentration contours for I-131 in air are shown-in

Figure 3.1-3. -Included . in ' these calculations is an iodine cloud ,

depletion factor which accounts -for the phenomenon of elemental iodine deposition .'on . the ground. The maximum 1 gff-site . average concentration -is estimated to ~ be 1.58E-01 pCi/m3 .for theyyear.

Dose to Infant's Thyroid

[ The hypothetical thyroid dose _ to an infant living near. the plant via' L -

! ingestion of- milk was calculated. ' The. radionuclide' considered was

' I-1311and the source of milk was taken to belthe. nearest dairy farm

with the. cowsipastured from May to 0ctober. .The: maximum inf ant's?

th'yroid dose ~ was :0.05 mrem 'during the_ year '(Table 13(1-1)_.,

Concentrations of~Particulates in Air. <

Concentration contours of ' radioactiva 'airborneD particulatesR are -

Tshow'nj:in Figure D3.1-4. : fThe maximum off sit'e' average -level is_ J estimated to be.8.98E-01;pCi/m3 , .

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Summary of Doses Table 3.1-1 summarizes the doses resulting from releases of airborne radioactivity via the different exposure pathways.

3.2 Liquid Effluent Pathways l

The three principal pathways through the aquatic environment for potential doses to man from liquid waste are ingestion of potable water, eating aquatic foods, and tuposure while walking on the shoreline. Not all of these pathways are applicable at a given time or station but a reasonable approximation of the dose can be made by adjusting the dose formula for season of the year or type and degree of use of the aquatic environment. NRC* developed equations were used to calculate the doses to the whole body, lower GI tract, thyroid, bone and skin; specific parameters for use in the equations are given in tha Commonwealth Edison Off-site Dose Calcu-lation Manual. The maxin.um whole body dose for the year was 0.01 mrem and no organ dose exceeded 0.02 mrem.

4.0 SITE METEOROLOGY A summary of the site meteorological measurements taken during each quarter of the year is given in Appendix II. The data are pres-ented as cumulative joint frequency distributions of 296' level wind direction and wind speed class by atmospheric stability class determined from the temperature difference between the 296' and 33' levels. Data recovery for all measurements on the tower was about 98.4%.

5.0 ENVIRONMENTAL MONITORING Table 5.0-1 provides an outline of the radiological environmental monitoring program as required in current Technical Specifications.

This program went into effect in November 1977 and differs from previous programs in the number and types of analyses performed.

r Tables 5.0-2 to 5.0-5 summarize data for the year.

Except for tables of special interest, tables listing all data are no longer included in the annual report. All data tables are available for inspection at the Station or in the Corporate offices.

. Specific findings for various environmental media are discussed below.

Nuclear Regulatory Commission, Regulatory Guide 1.109 (Rev. 1).

5

5.1 Gama Radiation External radiation dose from on-site sources and noble gases re-leased to the atmosphere was measured at six indicator and ten reference (background) locations using solid lithium fluoride thermoluminescent dosimeters (TLD). A comparison of the TLD results for reference stations with on-site and off-site indicator stations is included in Table 5.1-1. Additional TLDs, a total of 61 were [

installed on June 1, 1980 such that each sector was covered at both \

five miles and the site boundary.

5.2 Airborne I-131 and Particulate Radioactivity Concentrations of airborne I-131 and particulate radioactivity at monitoring locations are sumarized in Tables 5.0-2 through 5.0-5.

Locations of the samplers are shown in figure 5.0-1. Airborne I-131 remained below the LLD of 0.1 pCi/m3 throughout the year.

Gross beta concentrations ranged from 0.010 to 0.118 pCi/m3 at indicator locations with an average concentration of 0.031 pCi/m3 for the year. No radioactivity attributable to station operation was detected in any sample.

5.3 Aquatic Radioactivity Surf ace water samples were collected daily and composited for analwis weekly from the Inlet Canal, Blowdown Diffuser Pipe, Spray Canal Blowdown Pipe, East Moline Water Works, and Davenport Water Works. The cooling water samples were analyzed weekly for gross beta concentrations. A composite sample from each quarter from the blowdown diffuser pipe did not indicate measurable radioactivity attributable to station operation. Exclusive of one sample, annual mean gross beta concentration in the blowdown diffuser pipe water sample measured 4,6 pCi/l while annual mean beta concentration in water collected at inlet canal measured 4.2 pCi/1 indicating that there was no measurable amount of radioactivity attributable to the station releases, except in one sample.

i The sample collected on 28 October 1983 from Spray Canal Blowdown yielded 1586i28 pCi/l of gross beta activity. Gama scanning of the sample yielded the following results: Mn-54 48til pCi/1; Co-58 36til pCi/1; Co-60 1160i26 pCi/1; Nb-95 28110 pCi/l and Ru-106 430i94 pCi/1. Presence of these isotopes in the sample is station related.

Samples from the two water works were composited monthly and ana-lyzed for gamma emmiters. All samples analyzed were below the limits of detection for the program indicating that there was no measurable amount of radM. :tivity due to station operation present.

Levels of gamma radioactivity in fish collected were measured and found in all cases to be below the lower limits of detection for the program.

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A sediment sample was analyzed by gamma spectrometry. Gamma-emitters!were either below the limits of detection or at the level usually/ encountered in the environment (Cs-137, 0.35 pCi/g dry weight)' indicating the presence of no -radioactivity due to station operation.

5.4 Milk Milk samples were collected monthly from November through April and weekly from May through. 0ctober and analyzed - for iodine-131.

Sampled locations were the Hansen Dairy Farm located about 5.5 miles northeast of ~ the Station, and Musal Dairy Farm ' located 5.5 miles southwest of the Station. Radiciodine was ' below the limits of detection -of 0.5 pC1/1 during the grazing period (May to October)-

and 5.0 pCi/l during the non-grazing period -(November to April).

5.5 Special Collection No special collections were made during the period.

6.0 ANALYTICAL PROCEDURES A description of the procedures used for analyzing radioactivity in environmental samples is given in Appendix.III.

7.0 MILCH ANIMAL- CENSUS A census of- milch . animals ' was conducted :within five miles of the Station and-the finding is presented below. -The survey was conduc-

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~ ted by " door-to-door" canvas and by information from Illinois and Iowa Agricultural. Agents. The census was conducted by G. Kreuder on

~ August.2, 1983.

There- were no dairy farms within ' a' five mile. radius !of- the Quad Cities Nuclear Power Station.

8.0 NEAREST RESIDENT CENSUS A . census of- the - rearest residents was conducted by- G. Kreuder on

. August 2,'1983. . The location of: residences remained unchanged from the previous census.

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APPENDIX I DATA TABLES AND FIGURES i

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Table 1.1-1 1

1 QUAD CITIES NUCLEAR POWER STATION i

. t I

1

! ;QCP 100-525 IBevision 1 ID/138 EFFI.UENT AND WASTE DISPOSAI. Ilay 1983 SENI-ANNUAL REPORT (%1.b 19(3 l.

GASEQUS EFFI,UENTS - SUttiA l ION M ALL REI.EASIS 1

. Quarter Quarter Est.. Total' Unit 1st 2nd Erro'r. %

A. TISSION & ACTIVATION GASES i 1. Total Release

Ci 2.25E03 4.02E03

2. Aversae release rate for period pCi/see 2 90E 02 5.11E02

3. a. Percent of Tech Spec 7.7E-02 9.42E-02 limit ch4--y 1

b. Percent of Tech Spec 3 0E-01 3 16E-01 limit Stack 1 B. IODINES 9 02 l6.42E-02

1. Total Iodine-131 Ci ,

2. Averane release rate for period WCi/sec 3.46E-01 8.17E-01

3. a. Percent of Tech Spec limit station. 1 2.98E-01 14.53E ot C. PARTICUIATES '

2. Particulates with half-lives-

> 8 days Ci 3.66E-02 1.77E-01 ,

I pCi/sec 4.71E-03 2.25E-02

2. Averste release rate for period 3.43E-05 1.16E-06

3. Gross alpha radioactivity D. TRITIIRf

1. Total Release Ci 1.1)E00 8.75E00 l j

2. Averste release rate for period WCi/see 1.43E-01 1.11E00 t 9 I

1 i

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Table 1.1-1 (continued)

QUAD CITIES NUCLEAR POWER STATION ;

ID/138 EFFI.UDIT AND WASTE DISPOSAI, SEMI-ANNUAI. REPORT Ju1y - December.1983 GASEOUS EFFI.UENTS - SIRfMATION OF ALI. REIZASES Quarter Quarter Est. Total' Unit Third Fo~urth Error. %

A. FISSION & ACTIVATION GASES ,

i 3

1. Total Release

Ci 3 58E03 2.20E03 j

2. Averste release rate for period WCi/sec 4.51E02 2. 77E02

3. a. Percent of Tech Spec limit Chimney 1 9.28E-02 5.56E-02 i

b. Percent of Tech Spec limit Stack

1 3.78E-01 2.14E-01 B. I0 DINES l

1. Total Iodine-131 Ci 5.77E-02 l3.41E-02 8 I t I 2. Averste release rate for period WCi/sec 7.26E-03 4.28E-03

3. a. Percent of Tech Spec limit station'. % 4.07E-01 -l1.84E-01 C. PARTICUIATES ,

i 1. Particulates with half-lives

> 8' days Ci 3 11E-02' 8.15E-03 4

2. Averste release rate for period UCi/sec 3 9fE-03 1.03E-03~ ,

3. Gross alpha radioactivity 5.80E-07 1.40E-06 D. TRITIIRf

1. -Total Release Ci 6.61E00 '4.88E02- l

2. Averase release rate for period WCi/sec 8.32E-01 6.14E01 1

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Table 1.1-1 (continued)

QUAD CITIES NUCLEAR POWER STATION i

j GASEOUS EITI.UENTs 1983 '

Elevated Release

' Continuous Mode Batch Mod, Quarter Quarter Quarter Quarter i Nuclides Released Unit 1st 2nd i 1

1. Tission*Sases .

i

<LLD Er-85 Ci <LLD Er-8Se Ci 8.20EC! 1.88E02 Er-87 C1 2.24E01 2.22E02

.g Er-88 C1 4.59E01 2.64E02 Ze-133 Ci 2.69E02 1.06E03 4.36E02 6.80E02 Xe-135 Ci Ze-135m eg 2 93E02 3.36E02 5.87E02 7.01E02 Ee-138 Ci Ci C1 Ci Unidentified Ci <LLD <LLD ,

1 Total for Period Ci 1.73E03 3.45E03 l

2. Iodines eg 2.25E-02 4.87E-02 I-131 eg 1.01 E-01 2.72E-01 I-133 1 50E-01 1.46E-01 ,

I-135 eg 74E-01 4,67E-01 Total for Period Ci O

11

.- --- v. 4 -..c-- 7 -.w, , , , , - , c - w

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Table 1.1-1 (continued) e i QUAD CITIES NUCLEAR POWER STATION l l

l GASEOUS EFFI,UENTS - E1evated Re1 ease ,1983 Continuous Mode Batch Mode Quarter Quarter Quarter Quarter Third Fourth Nuclides Released Unit 4

1. Fission gases .

Ci <LLD <LLD Ir-85 Ir-S5e ci 2.59E02. 2.69E02 1.25E02 5 08E01 Er-87 C1 Ci 3.81E02 3.80E02 Kr-88 9.84E02 9 09E02 Ze-133 Ci 1.88E02 1.43E02 Ze-135 C1 1.72E02 6.5E00 l I,-135s C1 8.71E02 1.88E01 Ie-138' Ci s

Ci CL 4

. .l Ci Ci (LLD <LLD

). ,

Unidentified .

,l Ci 2.98E03 1.78E03 Total for Period i

2. Iodines 4.48E-02 <

.E-02 1-131 C1 Ci 2.5c '. 9 38E-02 f I-133 ,

1.53E00 '1.21E-01 I-135 Ci j

1.83E00 2.47E-01l T. cal for e.rt.d C1 I

i 12

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l Table 1.1-1 (continued) l I QUAD CITIES NUCLEAR POWER STATION GASEWS EFFMIENTS,1983 Costinuous Mode Batch Mode gst rter ynd rter Quarter Quarter .

Nuclides Released Unit g Particulates 3.

1.01E-03 4.2$6 04 !

Sr-89 Ci 1.52E-04 5 50 & o.5

! Sr-90 -

C1 D--->

Cs-134 Ci

. -04 2.53E-04 l Cs-137 Ci gg 1.43E-02 1.75E-02 l ge.lso less than 8 day La-140 ha t f-li fe Ci <LLD <LLD l Cr-51 Ci i

Mn-54 Ci v v

':o-58 Ci J l l Ci 9.45E-03 2.14E-04 Co-60 l

Ci 2. 85E-03 2.06E-03 -

l I-131 i

< LLD<----->

l An-110e Ci Ce 141 5.0E-05 2.77E-05 '

Ci l

C1 Ci

! Ci Unidentified C1 1 13 -

I i

Table 1.1-1 (continued)

QUAD CITIES NUCLEAR POWER STATION r GASE0US EFFI,UENTS- Elevated Release ,1983 Continuous Mode Batch Mode

M**

Nuclides Released- Unit urY j

3. Particulates ,

6.52E-04 5 74E-04 l gr-89 Ci St-90 Ci 3.8E-05 1 50E-05 Ci 3 35E-05 2.00E-05 Cs-134 Ci 3 6BE-d4 3.30E-04 Cs-137 eg 7 91E-03 '2.31E-03 j Ba-140- '

Less than 8 Day <LLD <LLD j La-140 wai f t i f, Ci i

<LLD <LLD Cr-51 Ci

< D <LLD l Hn-54 Ci D CD Co-58 Ci l'

Ce-60 Ci 4.17E-04 6.17E-04 ..J ,

, I-131 Ci 7 72E-04 f.76E-03 ,

"i

<LLD <LLD g An-110m Ci Ce-141 Ci <LLD 2.58E-05 l

i ci Ci i

' CL Ci Unidentified 'Ci <LLD ' <LLD ,

'14 4

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Table 1.1-1 (continued) ;

i

QUAD CITIES NUCLEAR POWER STATION GASEQUS TJTLUENTS,1983 '

Continuous Mode Batch Mode '

Quarter ,

Quarter Quarter

!NuclidesReleased Unit 1st 2nd e

1. Tission Gases Er-85 Ci 'LLD utr-85e ! Ci ! 'tL h I

' 1.20E01 Er-87 ! Ci l Er-88 Ci V )

Xe-133 ! Ci 1 5.86E01 2.84E02 ,

Xe-135 C1 1.20E02 l 1.12E02 l ]

i Xe-135m Ci 3.40E02 {1.56E02 I.

Xe-138 Ci .

<LLD ----y > !

Ci ; i i

! ! Unidentified <LLD <LLD' ' I, CL I

Total for Period Ci 5.18E02 i 5.63E02

2. Iodines i f

~

I-131 Ci 4.25E-03 1 55E-02 I-133 Ci 2.13E-02 4.72E-02 ,

n e

I-135 Ci 3.66E-02 1.14E-01 f 6.22E-02 !

Total for Period Ci , , 1.77E-01 l 15

I Table 1.1-1 (continued) 4 QUAD CITIES NUCLEAR POWER STATION QCP 100-525 Revision 1 l

' GASEOUS EITI,UENTS - Ground Release ,1983 i

Continuous Mode Batch Mode

.g Quarter Quarter Quarter Quarter

.Nuclides Released Unit Third Fourth -

1. Fission Gases ,

CD CD Er-85 Ci l 'l.!Er -85s Ci ! 9.50E00 <LLO Ir-87 ! Ci <LLD <LLD Er-88 -

Ci . 1.30E01 l <. LLD Ie-133 ! Ci 1.94E02 2.06E02 ,

2.02E02 2.2iE02- l !

Ie-135 Ci f Ci 1.86E02 l <LLD Ie-135s

~i

<LLD <LLD

,,Ie-138 Ci .

I

' Ci f :

I

!Unidentified Ci

<LLD <LLD I

6.04E02 4.27E02 Total for Period Ci .

i 2. Iodiaes I-131 Ci 1.28E-02 2.18E-03' I-133 Ci 3 36E-02 7.14E-03, l I-135 Ci 8. 38 E-01 2.64E-02 I

i' L

Total for Period Ci a 8.85E-0t ,

3.57E-03*

l O

16 l

-. _u . _ _ _

l Table 1.1-1 (continued) l

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l QUAD CITIES NUCLEAR POWER STATION 6 32TLUENTS ,1983 Continuous Mode Ratch Mode Quarter Quarter Quarter ,

Quarter Nuclides Released 13mit 1st 2nd l

3. Partiemiates Sr-89 C1 2.42E-05 l93E-oS Sr-90 Ci 2.35E-06 8 89f-M Cs-134 : Ci 5 90E-05 3.71E-05

Cs-137 Ci 3.96E-04 l304E-04 ,

I Ba-140 C1 4.81E-03 , 2.59E-03 La-1401ess than 8 day half-Il faci < LLD ----;-o l i i

!- :.2.10E-04 , 1.01E-03 Cr-51 C1-1.38E-04 l1.19E-04 Ha-54 C1 7 30E-06 l Co-58 Ci l~ 1.58E-04 1

Co-60 Ci 4.49E-03 2.42E-03 I-131 Ci l 1.43E-03 2.50E-03 An-110e Ci 7.10E-06 < LLD . .

Tc99m Ci I 3.63E-04 1. 37E-03 .

I Zn65 ci < LLD' 4.62E-04 Ce 141 Ci

/ 9.02E-06 l 8

l Ci Ci l Ci 'g Unidentified , ,

4 17

Table 1.1-1 (continued)

QUAD CITIES NUCLEAR POWER STATION QCP 100-S25 Revision 1 GASEOUS EFFLUENTS - Ground Release ,1983 J

Continuous Mode Batch Mode Quarter Quarter .l, Quarter

, Quarter Nuclides Released Unit Third Fourth l

3. Particulates ,

6.59E-05 6.0E-05 St-89 Ci 5.12E-06 1.35E-05 Sr-90 Ci 5 26E-05 8.38E-05 Cs-134 ) ci i

Ca-137 ci 4.77E-04 l 5.54E-04 ,

~

Ba-140 Ci 2.30E-03 3.54E-04 Less Than O Uay

<LLD i <LLD l La-140 Half Li fe Ci

' I Cr-51 Ci 5.69E00 9 12E-05 fin-54 Ci _

1.99E-04 g'- 2 56E-04

+ .

' 2.44E-05 Co-58 Ci 7.92E-05-l. -

Ci 4.98E-03 5 53E-03 Co-60 1.68E-03 5.13E-04 I-131 Ci

-i i 2.11E-05 l 1.93E-05 An-110e Ci f '

D

_l Tc 99m Ci 3 00E-05 <LLD l Cs 136 Ci-l Ci 6.41E-04 1.47E-05 l

' <LLD t.4E-05

" Ci i

Ci !

Ci <LLD :<LLD i Unidentified- , ,

~ 18 ~

_ _ - - -. . . _ _- , . - - - - _ _ _ - - - . _ = _ -

k Table 1.2-1 r

4 QUAD CITIES NUCLEAR POWER STATION LIQUID EFTLUDITS - SUMMATION OF ALL RELEASES ,1983

. Unit l nY ,

A. , FISSION AND ACTIVATION F20 DUCTS

.1. Total release (not including tritium, asses, alpha) Ci 6.79E-02 224Gd

2. Average diluted concentration f.9M 07 durina period uCi/e1.5.07E-07

3. Percent of soolicable limit 1 .61E00 6,%@O

4. Maximum diluted concentration 2 3E-06 i durina piriod UCi/n1 2.70E-07 B. TRITIUM

1. Total release Ci 1.77E00 4.69E-01

2. Average diluted concentration durina period WCi/nl 1.34E-05 4.08E-06

.3 Percent of applicable limit 1 4.46E-01 1.36E-01 C. DISSOLVED AND ENTRAINED GASES I 2.25E-03 !7.51E-04

1. Total release Ci

2. Average diluted concentration durina period UCi/a1 1.70E-08 6.53E-09 .

Percent of applicable limit 1 5.68E-04 2.18E-04 3

t D. GROSS ALFEA RADICACTIVITT 1.52E-13 1.08E-14

1. Total release ci

~

2. Averste concentration released WCi/a1 l

E.

VOLUME OF.IdASTE RELEASED (Prior to dilution) Liters l7.10E05 l3.31E05 ,

F. VOLUME OF DILUTION WATER USED 1 DURING PERIOD Liters . [ 1.'32E08 s1.15E08 19

f f

i Table 1.2-1 (continued) t i QCP 100-S25 QUAD CITIES NUCLEAR POWER STATION Revision 1

' LIQUID EFFLUENTS - SUMMATION OF ALL RELEASES,1983

! i Est. Totar

! , Unit l Quarter Third l Quarter Fourth Error, %

1 A. - FISSION AND ACTIVATION PRODUCTS .

.1. Total release (not including -

tritium. mases, alpha) C1 2.40E-02 2.27E-02

2. Average diluted concentration 9 1E-08 durina period pCi/mi + 1.67E-08 Percent of applicable limit g 4.40E-01 1.30E00 3

4. Maximum diluted concentration 4.4E-05 1.5E-05 durina period WCi/mi 1

B. TRITI121 8.08E-01 8.35E-01

1. Total release Ci

2. Average diluted concentration 3.35E-06 pCi/a1 5.65E-07

, durina period i

?

1.88E-02 1.12E-01

, .3 Percent of applicable limit g.

i -

C. DISSOLVED AND ENTRAINED GASES

1. Total release -Ci 1.40E-02 1.67E-03

, 2. Average diluted concentration durina period pCi/a1 9 7E-09 6.71E-09 Percent of applicable limit 3 24E-04 2.24E-04 3 %

1, D. GROSS ALPHA RADIOACTIVITY l 5.90E-07 5 75E-06 ]

1. Total release Ci.

f' g

~ ~

WCi/al .10E-13 , 2.31E-11

2. Average concentration released l

' E. VOLUME OF WASTE RELEASED (prior l

{ I to dilution) Liters 6.72E+ 05 - l .9.74E05 .

l aF. VOLUME OF DILUTION WATER USED :

Liters .l'1.44E09 l '

2.49E08

! I DURING PERIOD s

20'

QCP 100-S25 Table 1.2-1 (continued) Revision 1 QUAD CITIES NUCLEAR POWER STATION LIQUID EFFLUENTS, 1983 Continuous Mode Batch Mode }

Quarter Quarter j Quarter Quarter i ;

Nuclides Released Unit 1st 2nd i

[$$(.M l

Sr-89 Ci 1.98E-02 .

f i sr-90 Ci 7.02E-03 8.E6-c6 :

Tc .

3.6E-04 7.7E-04 i

Cs99m134 Ci 2 . 0 E-04 9.1E-04 i Ce 141 2. 8E-05 c7.7E-06 i Cs-137 Ci 1. 7E-0 3 2.3E-03 l-133 5 3E-04 1 9E-03 I-131 Ci 4.8E-04 6. 34E-04 -

Sr-91 .. 1.3E-03 7.7E-04 Co-58 Ci 3.1E-04 2.8E-04 '

1-135 2.5E-04 9 5E-04

,- Co-60 C1 2.7E-02 4.2 E-0 3 Sr-92 1.2E-04 - Lt.:

Fe-59 Ci <LLD tt Na 24 2.ZL-04 0.It-94 '

Zn-65 Ci 5.7E-05 6.4E-05 __

eg 5.4-04 4.6E-04 j fin-54

. -04 9.0E-04 ,

Cr-51 Ci f Zr-95 Ci <LLD < gi) l

~

6 Ci <LLD -LLT)

Nb-95 ! ;

Mo-99 Ci 5.0E-04 6.0E-04 l l 1 5E-05 3 7E-05 Aa-110m -C1 Ba-140 eg 3 1E-03 ' 9 7E-04

<LLD 5.5E-05 .

Cs-136 C1 Less than 8 day l La-140 ha I f- 1i fe Ci I l Ci ,

Unidentified Ci 6.7E-02 .2;1P(.02 l Total for Period (above) Ci l

! 1

.cg 1.7E-03 1.8E-04 Ze-133 I Xe-135 - f Ci 5. 3E-04 , 5.7E-04, !

Prepared by / Approved by i / ein Supervisor

1 QCP 100-525 Table 1.2-1 (continued) Revision 1 l QUA0 CITIES NUCLEAR POWER STATION LIQUID EFFL"E.!TS, 1933 ;

., Continuous Mode Batch Mode Quarter Quarter

Quarter Quarter i t ,

Nuclides Released Unit Third Fourth y i Sr-59 C1 1.02E-03 1.43E-04 , f Sr-90 Ci 2.93E-05 6.9E-05 j Ce 141 2.9E-05 7.34E-05 !

Cs-134 C1 2.61E-04 4.01E-04 i Cs-137 Ci 2.24E-03 3.65E-03 ,

I-131 .Ci 4.13E-03 1 35E-03 1-333 . 2 92E-03 2.27E-04 i Co Ci 5.47E-04 3 25E-04 i

Sr 91 5.30E-04 7 75E-05 Co-60 Ci 5.88E-03 1.20E-03 3-i35 c.2E-04 1.95E-04

Fe-59 Ci <LLD <LLD ha-i4 3.og-oa i,sig-og Zn-65 Ci 4.53E-04 6.20E-04 _

l h' o) 1.ost us Ptn-54 Ci '7.21E-04 8.00E-04 j nu tu)

Cr-51 Ci 4.7E-04 k*dkE! Oh f l Ce 144 3.45E-05 *I Zr-95 Ci <LLD 2.26E-04 Sr 92 2.96E-05 8 l Nb-95 Ci <LLD 5 72E-05 ! I i t 1 Mo-99 Ci 1.4E-03 3 96E-04 I I

' 1. -04 2.42E-04 An-110m Ci

'~ ~ ~'

i Ba-140

Ci i 5 -5 D Cs-136 Ci Less Than o Day tialf La-140 Li fe Ci (LLO <LLD Tc 99m C1 1.28E-03 1.28E-04

<LLD <LLD .

Unidentified Ci l 2.40E 7 13E-02 f Total for Period-(above) Ci 6.6E-04 1.16 E-03 '! l Xe-133 Ci 6.5E-04 1.24E-04 [

Xe-135 . Ci , ,

- re ared by / d A b ) pyroved d / ' p d- ellii Supervisor n

i l

l Table 1.2-1 (continued)

QUAD CITIES NUCLEAR POWER STATION ERRATA FOR LIQUID ALPHA RADICACTIVITY 1983 1st Qtr 1983 2nd Qtr. 1983 l TOTAL RELEASE IN CURIES 2.08E-05 , 8.39E-07 AVERAGE CONCENTRATION IN uct/mi- 1.58E-10 7.29E-12

- l i-6 9 '

s h

I t

g-O i.

23 ,

b. . . . .. - . . .

Table 2.0-1 QUAD CITIES NUCLEAR POWER STATION

. . . e. a 4 .. s. i s . t. .ic :.- , .i

+,e 48. & / c.

. . . s a , 4 ;. a . . e s ..

. JANUARY 1983

., . ,. ' t. i .. . . . . . , , ..u.. ' e. 4 - 4 . . , ,. .

. s n.

vsr.2/e. s s.: su..a .s. .os

,,/sa,.a . u 6.4 ....t. 2,. ....

ese.,,. s. s.. ...... .s...,.

..,,i.s s. ..c 4...s. ..,....

rar. <a s. . .. s s.:.rt seou.o.

.. . / s . / . a u. s.. s.~., s .:.o.

.. a # . *. # - . b L. ,..t.. . 6. L . . , J e a / a , a

s' '

bL Iv..b. # !' = . . L .

se s / s ., s ; 4 . . ea os ui .f.... . * .Ja

.* s J , *. s .* 9 s*. s u s . .' . ,ss . e r-t 4sa/s.. . 4. s . ". . * . ***a*.Ps "s/e8e . 4 * *. . b s.'.w. 4 .**

s s' t s ", .' . .u

s ' .' . J . .'.. ..t s

../ is . 8 4 ed * * . e a. se *

.#. a..a4

, /was s t ..b a.L..w #ee4.1

.4s..,

. , w . w.L s . *. . . . . . * . .'

i' s # . s .. * .L s...be e. . . . -

. s a. a s .. 6 as ..- . e .* 4 ..a.

- s,L s. . .8 s . . *. . .n.e . s .

sae%e, . e.. . . s e. e.. seu .#. . ..: .

- a / e e / . w .. s*..#4 e,a* . ..'.

sea /6 as . .. a .~.- seee ..

. 4 / a. a . ., . e.L 8..... *ej.J

.. s i i s . .. .. s.... < ...o.

Readable copies of these data points will follow as soon.as they are received from Quad Cities Station, as per discussion between C. Bennett, L. Duchek of CECO and M.C. Schumacher of NRC, Region III, on March _28, 1984.-

i I

I

-24.

l i

Table 2.0 1 (continued)

QUAD CITIES NUCLEAR POWER STATION

. . . . , a .siste . .. s e t . . . - ..i

s. .. s s .s 41 s . . . s. s i s i. :. c a .. e 4 ., ..

FEBRUARY 1983 o r. - .. . . . . . 6 r . .. . . s i. . *4 4 . . . 4 .:

. . i .:.

..us .ei e a '.. sas s . :. . . aa::..o t v.: / . c i . : . . . .: s. - ....6., s. e . . :.

s i so . s. . ... s :... .s....s u.i.ro. u .au s.:.u. sss....

i. ,.si s u. u .- c 1..... os.:. .

sei . o i. : 6 .au a.. . . s. . . u . .. . : .

s us.so . u u.s os...u .~.a.

s.i.a.o . .

. . . s. s.:.. . , s . :. .,

../..,.. ., i. ...s, . ...

.ein.,.. s. . u ..c i..... .,. .4 s s s .. . ; .. . s. .s e , . . s .,

.. s . o ., s. . s.- ....sa.

.o...

l i ia e : i. . ... . .... .iv..i

s. i,.... s. .. . u ..:... ...: .,.

s o f . 3, i. i. .. . . . . . . , ..,,.,,

e s i s. a . s s . . . ,...:. . :. . ..s.

..su..: .

t.u . . . . . . e.,.: .

eur e so . u ..u s.. . . . . . o : . . u ..

s a. i . . : . . . .n.a... .<.:.. .,

Readable. copies of these data points will follow as soon as they are received from Quad Cities Station, as per discussion between C.- Bennett, L. Duchek' of CECO and M.C. Schumacher of NRC, Region III, on March 28, 1984.-

'25 .

-6 ,- . . _ .

Table 2.0-1 (continued)

QUAD CITIES NUCLEAR POWER STATION J.64,. ansat..t.sa.a. . cic s e. . . .e. i .

we AIw als ww.w.6JIJLt J s o s 46:

MARCH 1983

4. l t b 4.... s, 9J W s,L w e' L e&kbJts..ALa weet

........ ......... ...... ...... .........t..

te .3 / w s' /

4 6. t. w b 4v' . v t, .e a e . s, .

4. J / v o s . 3 Ls bwL svs.ww =ce2.Js uJ/ v4s , l e. a a s,a6 4. t 4 L -. . # s 2;...

L. 3 / w & # . ; t. - e . s. 4 . .'. 4 si A s.

i . t. w est s ne r s s s.L s.5.ss sL.I.t.

" a / a t s e ., u. e . s. b..te s . . ..s i.J/elte s G LL s...tt a s . 4 . I .' '

sa/ w"/

s 4. Lw s.k.aw sets.cf

,1 # 4 t # . J w- 4.4 J U *, . . . s6e i.J.

v a l s S / ., s. . t. . e. se . er o s. s a . e s.

t.s/s-s* b. t . .: . s t J.t t . . = . = . . ,

l' a # 6 ** s ., b. e.L s . . g .- s. '# n i . ** =

14 / s e*#

s. ..w 2 ..t* w *. e e . 6 s.

d s / a :'s . , .. .. e .. g a s.,. ; a s s . 3, L. J / a f # e ? L ..b As.. 6w 4 .* , # . , .

tJ/s.1 4 L s . :. . s v ..s.....

us/ l s 's 6 6. ....t.. ., i g . .

u.o/s.So J u- e . s. s s . . .' s . ....:.

48 J / c. .S s .' s t. . i. st .bw L..=. e bJs64#*s L. e.b s . d . *J . JLea.a.

si .,4 s. . o - ., %< ..s s....- it. .cn

" J / a. . p a e, t . :. s . ,; . 6 s.

g , ; e,. .

v J /a.* # J L 4.A s s . 4. *

ti4L.c.

Us/s*4 J L. . ..b si..tt 314 a .6 e v a / s s s ., b. bor 3 ,, e . :. g , ; . 5 c.

us/sie s t t. s,...,. .

4.-..

va/s s r < . t *.s .s...r. ~s.s.n.

Readable copies of these data points will follow as soon as they are received from Quad Cities Station, as per discussion between C. Bennett, L. Duchek of Ceco and M.C. Schumacher of NRC, Region III, on March 28, 1984.

26

n Table 2.0-1 (continued)

QUAD CITIES NUCLEAR POWER STATION

=$ 8. S a t.. AL*Li4eL e. .IL C .,r . . s e. I

b. 40.s e/m

..s*bilJks Joee16 .

APRIL 1983 w e. i t bw l'... .. i t 4. 6 *. L . .* *,4La.4w. As.

weeb

s., / w e / s 2 L.

t.b awJ.v. 46.i. 6 U /dua s a %. . s. b i n. a . % . *

%.se.Ge w=/ wur ? s b. 8. 6 sw3..w . ** ..t.

a.%/utse 6 s. s a. s.y.s. a *:..

U*s vis

a w w... as'.i. .*se.c.

c a. Je t .. L . *

.b i . ~. . v . L.=v..ia w=p..i .i t- 3 .4 4,. 4w . . i s . a. .

s* /8A# .; g e.,w .......

e g s a c / ., ..w.. L. *

.. a . . t t =... .

b=#43s.. L ..b a e *. . te k , *=l.*. J go , / 4*j,a 8

. . , g ,ig g,sa 3....

e ,, asp , w ..L , s . v g- 3 ...

b / A"*/ s 4 s.= 1e..t t ofa'..s

(**#40#- s L. bL as..s. ,fe.4 u%/A /L w L.L 3 . . . b *. . s s e .e %

s/at t. o s. *.L ss..t. . ss J..,

se ! g t o . - l'S e . e s. ss' ' s e. . *. . t e .e.se v s e s. s / J e.* / g t p . ,

E~*. J . . % s. .b ~..:.

w . .6 3..... .s>.s,

: % f s e t - 2 4 .s i.a.ss s'as..w.

v./,p ; a . . . a. 6. ..s 4.*.

t%s63#s s b .sb J..et . .8,r...

4 -e / 3 d . J b. .wb 4 s.se a . . * . . .

t m / . .s / 5. ..L . e%s S. o e. 0 e* *> .l

b / .1 # . 0 w. sb ag a

.s . g .be ,

i as # a. i t

J b - ..b a * * . 6. u J .- J . s .

... .s. ~s.o.u r

s <. , / . s. . .. s ..w. -r...,..

a s_e e *

_a_. .. . *_..t.= * * * .s_=...-

a ? * *_ a ' * * * * * * * * * - *

s Readable copies of these data points will follow as'soon as they are received-

.from Quad Cities Station, as per discussion between C. Bennett, L. Duchek of CECO and M.C. Schumacher of NRC, Region III, on March 28, 1984.

e 27;

l l

I 4

Table 2.,-1 (continued) l 4

QUAD CITIES NUCLEAR POWER STATION e

. L 4 ., 9*LAt#LI&et .eC1L C t. .- ...I 6 AIs &/t

..etas 19 44 e D i e e A s e.

t MAY 1983 e.

L 4L** L. . 4 .'. e . 4.L Ja.

A t 4 6 . s' e .

8 4 L a. a .

i 6. .

8

-JIL t# 3 / w f./ t la L. . .L s .. ; e 4. w

.e

e, a . a e t* ,/ J e # ) b- tv4 4 v . t. w e s t s i . e. g

i. J / . .% # . . r e L. L L.6 ar.',.t. .8...e u #w=#a . .

..b e . . . . t. C . D a # . . ..

tof.%e 2 .. LL se: . v '. she'.s.

u s t . ** # . u. s.: tw

. s s.

8 % 's . s s

' I w .. t . .e b sr as..sw s. s '. . * .

s. s / we#- s 4 s. . *. a . . . s. . s. . . ,

t* : o e* * . % 6L e ..u e. 4 .e s.i..i . s ..L af s # 6 / .e b .. . L 48 -,.....t 4 e... .i s8.. .a?

JJ/4* # s b 6 *

.a. #w.60 .s .

t . / a .. s O s. 4 . *. as..t w , a 3 . ** .

IJ#a./ s i a*....

m's t a e. / . , 8 t .. k s..s

. ... 3 ..t6- . . a . ., s

../.3# *- w. 8 .. w e . .i. 4 . . s. .

4* s t s e s , t t.L 4...n. ...t. ,

s t 4 * # . 6. 6 wi 4 s . . .. # *. . e . s . .

valaioe .% . . t .. s .....s a...g

. . / 4 * / . ? be ..L e .. *. e. ,a#....

e ts ) / a . d . s *.'L t.8 s8e e.% *

. .2 w Ji a ## s L .* .b 4...t w 1, s . ..as l' .t / 4 *. s . ,

, s. n . *. 3,*,.. ,s,a.g 4 s / a. * * # $ L f. . 4....s. *: .6 ., a

%8J/e.24 '

b- .L 1t s.6 *e * * . . , .*

. Ed J # .) # . O l. Lwb jes.t.

e. , p g . p' . ;, Lf.v.e4

n. s. L j.J.. .,

v o t e. .o i b % i" .* w *

. .. . e' .. .t..

6s .9 / 0 / 0 b . twb & t *. . 6 . 's , e 's . c t M e / e.e. # . J .L L.

4 .c e e . .* l *. 0 0 0:/asi a u. s.. s.s..s ...eo

. ......,.... ,,. a , , . , , , . - . . . . . . . . . . . . .

Readable copies of these data points will follow as soon as they are received -

from Quad Cities Station, as per discussion between C. Bennett, L. Duchek of CECO and M.C. Schumacher of NRC, Region III, on March 28, 1984.

-28

Table 2.0-1 (continued)

QUAD CITIES NUCLEAR POWER STATION ns . . s . .. t. 8 s . e .. a s t. :. .s b e l i =. & / a, ow e = =c) e a s a Seetiu JUNE 1983 t, l g'. L t- e .* e .. t6* a .a b o s 4. t 8' 6 8*.4 L k a 6 e .ALw salb O 9 / .71 # L s 1. . .4 s . La b f.sh ..ww ww/wrsts b. b w *. A.,. u a ...v est sse, b. c o s: a... 6. 3 1=;.s.

96/43#s* e. .. w b a.%.w, J .* . . J .,

u / w 9 / * .a b . ..b 3...L= 1 'e e. * .6*

U./Jo.#*. L b4* 8h*.Uw *&.**...A v . / .# r s t. . b . E. a...sv s. e. 4 *,

b6/.ss*a L Lww a 4 4 . = .. .t .ae bk/ w ## 8 . b . .w 6 J.- # JL 49.4 .

b b / V ** #

A b. **w $ej... w 8 7 d .8 b es . s & se d . . L .b l ..ge j e, ' e. s .4e tt/J #s. m. ..b a .: . 6 s s.. . t .e w 4/ 4*#*, 6- b*4 I .s . * . e.

. . a *.

t . / 4 .9 # a s. t . :: 4 , *.a . w e 1 6 i ..*. . w ,

kw/a.St s b. =b . *sess 46 4*...

4 . / J ' g a .*, e *

4 . . s. L '..t, ., 7 .,

La w / 4 ## . * -.b~ l * . U s. I a = = * * . t '.

es . / & I # * .a i. * .L 8i * . . . 4s* .4**

.V se b s f . s s-. so . . l '. e.' l*'..n*

u s' / C u / J 6 ..m S . .e . s e a s e et .ss s- e. / a # . .a b.

.. ...s 86 4* ..N g . / ., 4 s ' L. 6. . . e * * . .* 6 .. . 4

w w / b 6 p ..; t I-b' 46... .. 48. .

e./Lft a b .

w . 8. as.. *- 6*

8# .4*

bw/cle.. b. Lw. A t % . v '. f*i.fo

g. .s / ,,, . / ? .;, L. 6 b- ss... = . . ' " . ....

s s / a..g e a % 6 wt $saeds a.L*.se ta s,. / .*, .' 4 t .o b+ t= w L . .s *... *

.*

e s

Readable

copies of these data points will follow as soon as they are received from Quad Cities Station, as per discussion between C. Bennett, L'. Duchek of CECO and M.C. Schumacher of NRC, Region III, on March 28, 1984.

'29' .

Table 2.0-1 (continutd)

SULII) h Ali10 ACTIVE WASTE SU%t RY utITS 1/2 mal)-Ci1 IFS ST AT10N 7 /1 $r 63 DATE Ch TWANL Hl!RI AL VOLUME HILLICllRIES dITE

~

07/06/63 CN tSC 85.00 40540.00 07/07/63 Ch PSC 105.00 94o9.77 07/06/63 CK est 105.00 10411.79 07/06/63 Ch r' 8 C 105.00 10685.20

~ ~~~07/11/63 CN 6SC 105.00 10553.30 07/11/83 C r. HSC 105.00 108d5.30

^

07/12/63 -

CN RSC 65.00 40540.00

~07/14/63^ dAChE USE 1210.50 42,50 07/15/83 C c. PSC 105.00 11184.40 07/16/83 CN 6SC 105.00 10785.66 07/16/83. Ca uSE 105.00 6115.00 07/19/83 C r. It hC 65.00 40540.00 07/21/83 Ct v8C 105.00 10361.44

~~ 07/22/63 L t: b5r 105.00 10204.04 07/25/n3 Cd est 105.00 66u6.20

~~

07/25/E3 C r- osC 105.00 1804.04 07/26/83 CN HSC 85.00 40540.00 07/28/83 CN USE 105.00 7280.26 07/29 /B3 _

Cn I:SE 105.00 12401.38 MONTHLY TOTALS 3020.50 293130.60 l .

l USE - ti.S. ECOLOGY

' BSC - HARNhELL S0llTH CAROLINA

.__.. _CH_ ,.CHEN NUCLEAR CO. , ,, .

30

-f

^

Tab 1e 2.0-1 (continued) 4 FOLID NAD104CTIVE WASTC 'iUMMARY UNITS 1/2-s

, r:tlAD-CIllES STAT 10Y

. . . . ;'r .

h/14H3 DATE f C0 TRANS Bl'RI AL -, V O LilM E- ri!LLICURIES SITE

........ n ......... ......

08/01/h3 C- OSE 105.00 ,,. 8672.27

. Oo/01/b3 CN t SE 105.00 9a53.52

. _ .... 08/.02/63 CH PSC 65.00 39628.04

, 08/04/P3 HACKE USE 1203.00 26.03 06/05/83 Cr4 GSC 105.00 2401.70

. 08/08/83 CA BSC 105.00 5615.58 08/0H/83 D USE ~

105.00 6909.55

. 06/09/t3 CN RSC b5.00 104331.43

~

08/11/P3 C, USE t' 105.00 1668.54 J'08/15/83' Cd bSE ,195.00 718.29 "08/12/e3 C:. RSC 105.00 423H.25

~

'06/15/03 C e- USE 105.00 5574.13

, 08/16/83 C i< fi SC 65.00 109331.43 36.38 08/18/63 NArKE LISE '1101.25 06/19/63 C ri d5C ,- 105.00 5197.20 06/22/83 Cx Psc- "

105.00 2997.05 06/22/63 to- Hbc -

105.00 3049.34

~ ~ ~ ~

08/23/83 '

Cw BSC , 85.00 109331.43 08/25/P3 CN tiSE '

,. 105.00 330.37 08/2h/83 CN USE 105.00 M908.03 08/29/63 C r. R3C .. 105.00 5305.03 08/29/63

~

CN .

65C e 105.00 5507.74 08/30/h3 Cu j~ , P,3 C 85.00 109331.43 l . . .

[ ****[f,,*'**********'********************

MOF'THLY TudLS e 4409.25 553764.76

~

fT llSE - 11.S. t! color.i ?

8SC - (I ARNWtiLL SHUTH LapnLINA '

CN. - CHEM htiCLE A 4.LO'. ,

p, c O-ag 4 g a T r

x .

/ r,- -v, 31

Table 2.0-1 (continued)

SOLID RADIDACTIVF WASTE Sur4HARY llN I TS 1/2 UUhs-CITIE' SIA110N 4/19hb DATE- Cu TRANS BliRI AL VDLUME MILLICURIES i SITE 09/d1/63 CN USE 105.0u 74d1.27 09/07/83 CN tis C e5.00 109331.43 09/06/83 C t. USE 105.00 9852.80 09/08/83 CN L'S E 105.00 13765.81 09/09/83 CN USE 105.00 15691.25 09/12/B3 CN HSC 105.00 15246.M0 09/12/83 Ch HSC 105.00 15436.96 09/13/83 Cl. HSC 85.00 14010.16 09/15/83 Ct: IlSE 105.00 10220.77 09/16/83 CN bSC 105.00 14398.70 09/19/83 CA hbC 105.00 14338.01

_ _09/19/83 C r. ASC 105.00 14884.70 09/21/83 HAChE lihF s1264.75 212.94

_ 09/22/83 CD bbt 105.00 471.93

_ __09/23/83 CN Phc 105.00 14676.40 -

09/26/63 CF BSC 105.00 15613.88

~

09/26/63 C6 abC 105.00 141GS.60 09/29/63 Cu tfSE 105.00 7645.82 09/30/83 CN FSC 105.00 518.70 a* e * * * .* * * * * * * * *.* * * *w* ***** * = a a ee s a e a n

, l'. __. . . .

_ MUNIHLY TOTALS 3139.75 307955.95 f

USE - ti.S. ECOLOGY a JSC - B ARNHt.LL SGilTb C AkHLIN A ,

CN - CHEh NUCLEAh Co.

l- .______._L-l

~

32

~

l l

Table 2.0-1 (continued) l f

SOLID RADIDACITVF WASTE SbnkAPY I Istv 1 T E 1/2 ObAO-CITTEb S1AITUA 10/1983 DATE CD TRANS SUPIAL VOLUME MILLICUNIES SITE 10/03/83 Cp USF 105.00 10521.45 10/05/83 CN 6SC 105.00 23543.64

, . . 10/06/83 HACKE OSE 1789.75 356.11

. 10/07/83 CN BSC 105.00 29934.80

. 10/07/83 CN !!SE 105.00 1619.06

_._ 10/11/63 CN BSC 85.00 32100.59 10/11/83 C r. 183F ts5.00 153800.00 10/12/63 Ce ESC 105.00 570.50

. 10/13/83 HACKE USE 1105.50 59.73 10/13/83 CN PSC 65.00 32100.59 10/14/P3 Cs BsC 105.00 :22409.29.

_ . _ . .._10 /14 / 8* 3 C es inSE 105.00 '

7 5935.63 10/17/63 CN ict 105.00 22009.93

-l

10/18/83 CN "sc 65.00 32100.59

_ 10/19/83 CN USE 105.00 6041.79 10/20/83 CN i:SC 105.00 21050.61

. 10/21/F3 CH HSC 105.00 .21023.70.

._10/21/03 CN EMC 105.00 _

21823;,79

_ 10/24/63 CN HSC 105.00 19407.00 10/24/M3- C: MSC 105.00 2nn47.69 10/25/83._ _ Cn adC 85.00 32100.59

_. 10/26/83 CN hSC 105.00 22533.60

= 10/26/83 CN USE 105.00 2809.92

r. 1012 7 / 8 3_. .. _._ _ HACKE 06F 1289.75 239.48

_- 10/28/83 Cu 6SC 105.00 22569.10 11 10/28/83 Cu 65C 105.00 576.60 x 1_Q/31/B3 CN USE 105.00 1776.56-

.- 10/31/83 CN llLE. 105.00 621.51

~ ~ ' ~

'* n'.* * * . * ' * *..* n * *

~

**g

~

u **-***********n* .4 .

^~ ~

nnNTHLY TOT AL S b210.001 561864.25 USE - U.S. ECDL0r,y

.BSC = liARNhELL SOUTH CAPOLINA CN . CMEM NUCLEAR CO.

, a

. . . _ ' ~ ~ ' ~

( 33

, . x

Table 2.0-1 (continued)

SOL]n RAD 104CTivF. H ASTE SUMARY lit:I T S 1/2 ouAb-C))TEF STATTON 11/1963 DATE CO TRANS RUP1AL VOLilME MILLICURIES SITE 11/01/83 Ca aSC B5.00 32100.59 11/o2/P3 C t. RSC 105.0u 8162.77 11'/04/83 H Acne. t*SF '510.00 71.53 11/04/P3 CN liSE 105.00 1763.00 11/07/83 Cn ESC 105.00 21025.36

- ~

11/07/03 C.. PSC 105.00 21699.S9 11~/ 0 8 / 0 3 ~ ^ -~ CN -6SC 85.00 30057.62 11/09/b3 CN BSC 105.00 22069.91 11/09/63 CN ESC 105.00 20121.13

-'~ ~~11/10/63" ~' HAChE USE 1289.75 179.35 11/141/B3 CN Pbt 1u5.00 14844.20

~

11/15/83 CN USF 141,MO 2763.00

~

11~/14/F3 - - ~~ C+ A.s c 105.00 14765.32 e 11/16/03 CN 05C 105.00 1452o.10 7- 11/17/83 ~ HACnE ilSF .1629.50 92.69

~~11/18/63 CF BbC 105.00 1699.80 5 11/18/63 CA BSC 105.00 1674.20 i -

11/21/83 ~~~

Cu h8C 105.00 2752.80 f D 22 /E 3~~~~ 'H AC K E usE .1214.en 63.56 11/23/83 C6 bSC 105.00 cc74.70 11/23/83 CN ESC 105.00 5133.50

. fT/28'/63-" ~CN BSC 105.00 5387.06 T. ~

11/28/83 CN BSC 105.00 5220.80 11/29/83 ~

Ca ~

USE 141.8u 1197.77 J '11'/307B3 ~~ ' CF ' BSC 105.00 4374.01 11/30/83 CN USE 105.00 304e.24

~

s

0HT4LY TOTALS 6387.85 243327.M0

.T

~

U.SE-- U_.S _ECULOGY ,

BSC = BARNWELL SOUTH CAROLIHA ,

.f Ch CHEM NUCLEAR CO. .l 1

34

l Table 2.0-1 (continued)

SOLID PADIH ACTIVF WASTE SilMM ARY l' NITS 1/2 001.0-CITIfS STATION e_- _ ._

12/1903

, DATE CU TRANS FURIAL VOLitNE MILLICURIES STTE 12/01/83 HACnE USE 1240.50 125.96 12/02/63 CN USE 105.00 4177.39 12/02/e3 C:4 8SC 105.00 3327.55 12/05/63 C r: USE 105.00 'S004.35 12/05/83 CN USE 105.00 5356.50 12/0o/83 Ch llS F 144.96 437.98 12/u7/e3 C r' nst 105.00 2167.36 12/06/83 NACKE USE 1210.50 103.39

._. . 12/09/63 C i. r' S C 105.00 2109.24 12/12/63 - C *-t usE 105.00 9524.34 12/14/63 Cia BSC 105.00 6743.Su 12/14/H3 C r. BSC 105.00 1967.43

. __ _ __ 12/16/83 HACnE udE 1289.75 122.47

12/19/P3 Ch SSC 105.00 5767.42

, 12/20/H3 Cf. PSC 105.00 1118.40 12/20/83 CS 6dC 105.00 6114.50 12/21/83 Ces HSC 105.00 4527.70 r 12/21/83 Ch HSC 105.00 2698.60 12/28/63 " Acne USE 1269.75 74.97 12/30/63 C h. PSC 105.00 5804.06

.s 12/_3_0/83 _ _ Cri HSC 105.00 5223.30 i.

e

[ ___ MONTHL.Y_ TOTALS .

6855.48 77642.49 e.i.

USF - li.S. ECOLOGY i

BSC - BARHNELL SOUTH CAROLINA CN -

CHEM HUCLtAR CO.

9 emime me sme me-emM em e 4 ed= e-es nia- e<a e m. meg .

-*9.

g I MhweE W B4hh eI mi-mA*n wm ee9et my h 4 e e- e 35

Figure 3.1-1

/n

i

=t, N a l . ,,

Estimated Cumulative Gamma Dose (mrem) from the Quad Cities Station for the l o

period January-December 1983. . p Isopleth Labels 20 Smallfigure-multiplyby10*f Large figure - multiply by 10" RELEASE-POINT

'k d[*'

~T I 10

[ I .J

~ r

~,

5 e,,,

SCALE ,

'.,a.

/,

~ . o i e 10 * ""

~

Q .

~

g' 4

,E ' -

C L I N T O N I 8 i

, 10 .

. . . as,-

~ f uston'.

.x

. ci. neon

) .- . tp e

,,,,," 25 Q +

f '7 .

s.% X %

ui x /

y.

7 %c.-

1

~~- 50 ,

( ,

1 O he W i oI L L I N O I S ,f

, g3fe... I C K 7 i

Ee'; g E"'

d -

, S C O T T !

R O E.' s '

. . . - t . ... -

' iSLA -

v . . . . .@ p D

/ *l gi .g <

- d itt er

,th 'ud . . /.' /

w--N ',_7..... -

3

'**[gesA= =

1...

[w -

d i

SCALE O S c is to esatts 5- so aS 90 29 30 mm O. . - -

36

l l

Figure 3.1-2 ,

t.

Estimated Total Concentration (pCi/m3 ) of . i , ,. l Iodine from the Quad Cities Station for 25 .

o p the period January-December 1983. ,

Isopleth Labels 15,0* fhI Smallfigure-multiplyby10-j RELEASE' "P'*'

Large figure - multiply by 10' POJNP 'Mt'

'$ 10W ff s

\

i

.j, SCALE

! I 4 . o e a :

mitts

, . . . La.

. ? 4,

=?",

~ . s C L I N T O N N OE' -

4 1 i

'o

's<, e 4 y*

, oitons -

f %

[5 De win j cnnten

p,y?

p.->

y

)

u s so * , '

ci n sa w % 48 F ' / us so w , ,

. Morrison k

( comonew .i , 1

" s nos ,,*'r e,

,,~~10

~

i.

SITE

?

. , lY ,~

I O I

e ? L L l N O S f

*, WH ITESI D E e

s . ( ordova -3,s -

. any.= s., ,

s , x.,

f T L

S C O T T f R O C K N, " Er

[jj l

..,, .7,.

.i....s'..*" ' . . ' 2.5 i . ....

} i st, o.- - . -_

'e

. t" H E N R Y

.'hOx gf g me w .

...o

. us.

SCALE 9 e io is to mitts 9 _..e io is to as so um 37

Figure 3.1-3

-. v y N a l . ,e Estimated Total Concentration (pCi/m3 ) of a

Noble Gases from the Quad Cities Station for l

the period January-December 1983. ,

5 **- . Me Isopleth Labels 2g9 Small figure - multiply by 10 RELEASE [

Large figure - multiply by 10 0 POJNT

( f. 2.5

-z.5 3 1

) e se SCALE 9 ! I mitts

/

, ,, r=

. j ' '

- ?:, q; in C L I N T O N

{E' -

- ~

ac ' ,

,, 10 7 K+ K ,

w witen chaton

5 9, /n u s so , De Win ; hhf '

8 so y ,

g ,, , w gy - x -s u s so M . 8, ,

O Morrison 25 con,ons .,

\ ,

^ '

I O e W A 50'h' gst ITE , ( LL I N O I S ,f

. - i

=

e c u ovo t'g W H ITESI D E -

.y. , y, 4

.+-

C O T'T W l R-Ol C K ds E"

, S .

N _ w.u ... .

)t1e.,,,,,* ,,7 - .* 7* ' .'

. ,, i . .o r

I SLA D-d5 /1 iu of

h / m*"

f.# /

'ity- m &

l

, ! H E N R Y

[ 3

- n e..., 5 nuca w .

SCALE 9 s 'o se to miles l.

l 0 S so iS to 2.s so um 38

l 1

t Figure 3.1-4

// * ,

n, Estimated Total Concentration (pCi/m3) of N . ,e Particulate Matter from the Quad Cities to ,

, Station for the period January-December 1983. * ,

R Iso leth labels 10 ***

(

2f[ Ashs- h*

I Sma 1 figure - multiply by 10-2 s ,

j Large figure - multiply by 10-3 SN RELEASE gBh4/ g 3

1 .s -

l ,

I Er SCALE O e :

/ ,p

^ '

^ utLis

) 0 Geese g s 2 3 un

, .. tm . l 2 -

C L I N T O N

$'s

2 *' ' 3+h:! h '

5 i 1 i '

1 10 I t/ -

< .e .. **

e, ,

: ulfen I y

f'g ---

/*

u , ,o

o. w,,,

25 t .

Ctenton

,o , .

$g v e

x 9

3 .

c... ,

,k Morrison lJ

% eo. ,,***., ,,,

~.. p ,' 't W A;30 SITE / / -

1 O m g P I L L I N O El S ,f h,,, % j W H/

ITESI 0E,' '

, *T~

f ,

S C O T%

p_.

, M ....

d , . Erie 3....

, . !=90 Port 8,ren

,' - ISLAN0Ip jy W; { M or

># /. 40

~,

l l

J liP" H E N R Y ma 'casop ,

e

- k I.00

' N' l ,

SCALE O S po is go uitgg O 4 M 29 M au

{ S m

Table 3.1-1 -

QUAD CITIES STATIDW = UNIT 1

, MANINtiM DnSES RF.5DI.TINC FROM AfRRORNE RELEASES PERIDD nr RFl. EASE DCTHRF.R 1, 1991 - DECEMBER 31, 1993 DATE OF CALCULATION 03/15/04 TYPE CupHFNT PFP10D CHRRENT OHARTEP THIRD OtlARTEM SECOND QUARTER- FIRST GUARTER ANNUAL CANNA Alp (NRAn) 0.197E=01( w) 0.197E=0lt W ) 0.760E=0lt N ) 0.480E=01(NNE) 0.345E=0lt W ) 0.152E 00( # )

RETA AIR (MPAD) 0.140F=02(WNW) 0.74eE=02(WNW) 0.lR8E=01(WNW) 0.760E=02(WNW) 0.517E=02( SW) 0.383E=01(WNW)

WHOLF RnDY (MREM) n.104E=01( N ) 0.104E=01( N ) 0. 4 5 67.= 01 ( N 3 0.lSPE=01(NNE) 0.178E=01( N ) 0.916E=01( N )

EKIN (WHEM) 0.I53F=01( N ) 0.153E=01( N ) -0.656E=0lg N ) 0.256E=01(NNE) 0.273E=0l( N I 0.133E 00( N )

ORCAN (MeEMI 0.R05E=u)(WNW) 0.An5E=01(WNW) 0.192E=01(WNW) 0.474E=02(MNW) 0.131E=02(WNW) 0.260E=01(WNW)

CRITICAT. ORC =PERS TH-IN TH-IN TH-IN TH-IN TM-IN TH-IN COMPL1 ANCE ST ATt15

~ [$

10 CFP 50 APP. I 10 CFR 50 APP.!

TYPE QUARTEPl.Y nBJECTIVE % or APP. I YEARLY ORJECTIVE % OF APP. I CAMN4 AIR (MEAD) 5.0 0.39 10.0 1.52 RETA AIR (MR Att) 10.0 0.07 20.0 0.19 WMOLE RODY (NRFM) 2.5 0.42 5.0 1.83 SKIN ( NR F.M ) 7.5 0.20 15.0 0.99 ORGAN (MREN) - . 7.4 0.01 15.0 0.17 CRITICAL HRCAN= PERSON (TH-IN) (TH-IN)

CRITICAL 0* CAMS: RN=RONE, I.V LIVFR, TMsTOTA1. Rn0T-TMsTHYpnin, KnsFIDNFf, LNrLHNC, GIsCI=LLI CRITICAL PER50Wt ADsADHLT, INsTNFAMT

Table 3.1-1 (continued)

OUAD CITTFS STATION - UNIT 2 MARTMUM onAES RF.Sur. TING FROM AIRRORNE PEl. EASES PERIDO OF DFLEASF nCTopER 1,19RI - DECEMBER 31, 1993 DATE OF CALCULATION 03/15/94 TYPF fitf RENT PEP 30D CUNPENT OttAR1ER THlWD 00APTEM SECOND OUAPTER FIRST GUARTER ANNUAL CANNA AIR (MPAD) 0.197E-Of( N1 0.197E-Ol( W) 0.760E-Ott N ) 0.419E-Ol(NNE) 0.345E-Ott W ) 0.152E 00( N )

BETA AIR (NBAD) 0.740E-07(WNW) - 0.740E-07(WNW) 0.18PE-01(WNW) 0.760E-02(WNW) 0.517E-07( SW) 0.383E-01(WNW)

WHOLF PODY (NREM) 9.104E-01( N ) 0.104E-01( N ) 0.456E-01( N ) 0.180E=01(NNE) 0.179E-Ol( N ) 0.916E-01( N 1 SMIN (wpFN) 0.151E-01( N 3- 0.15)L-0$( N ) 0.656E-Ott N ) 0.256E-Ol(MNE). 0.773E-01( N ) 0.133E 00( N )

ORCAN (MPEu). . 0.p05E-01(NNW) 0.805E-03(WNW) 0.19?E-01(WNW) 0.474E-02(WNW) 0.13tE-02(WNW) 0.260E-01(WNW)

.CRI?! CAL nPG-PERS TH-IN TH=lN TH-IN TH=lN TH=lN TH-IN

(( CnMPLTANCE STATUS to CFR 50 APP. I 10 CFP 50 APP.!

TYPF QUARTFRLY OBJFCTIVE % OF APP. I TEARI.Y OBJECTIVE % OF APP. I CANNA AIR (MRAD) 5.0 0.39 10.0 1.52 RETA' AIR (4HAD) 10.0 0.07 70.0 0.19 WHOLE Pn0Y (MPFN) 2.% 0.42 5.0 1.0)

SKIN (MNEpi 7.5 0.20 15.0 0.99 ORGAN (wpFN) 1.5 0.01 15.0 0.17 CPITICAs. nacAN-PENSON (TH-IN) (TH-TN)

CPITICAL ORGANMt'RNsPUNE, I.Vzt.TVFP, TMsTnTAL PODY THsTHYP010, EDsFinNFV, I.Nal.IINC. ~ Cl2CI-LLI CRITICAL PENSON: AD= ADULT, INz!NFANT e

Table 3.2-1 al- Als a 1111- F sie 11 sine

.g A x i mud ,00s t::', OJto) m F hliL 11.ai. r we + L li.ii) :' FF Fleit t T%

Pipittle OF M LF ASF - 1/ 1 Wi TI' 1//31/e3 LALCleLATto 02/09/P.4s e IST s.'s f. .h li 4FH Ala b O A L OnSt TYPE woad 1F. a.itah re w s.esattif w. una4TFh 1/n3 3/M4 4/M3- e/63 7/o3 4/63 10/n3 17/83 TOTAL 1.7ei-03 2.4bf-03 4.75E-04 1.57E.03 6.7eE.03 anpY INTkHNAL 5.35E-03 "3.43F-03 1. 4 84 E -0 3 2.31t-03 1.02E-02 ONGAN B0hf LIVER Livkh LIVFH e4Dr.E e THIS IS A REPopi Fn,t THE CALEr.DAk YEAN 1983 3

Cf.Hi 1 Isori .%T Afsi8 t o LFi< *iG AFP. I ,

.............. g eF .py I. ......... .

OTHLY IST e Th 2hp n19' Skti i Th ' 4 T H 5.167 YHLY 1 0F ORJ 1/83 4/63 7/83 10/83 tiR J APP. I 3/83 6/M3 9/63 12/83 TOTAL RODY'(MRFM) 1.5 0.12 0.16 0.06 0.10 3.0 0.23 CN17. (IRGAN(MHFM) 5.0 0.11 0.07 0.03 0.05 10.,0 0.10 RONE' "' LIWhF L!vkR LIVEN BONE I

i I

i 1

42

i Table 3.2-1 (continued) -

- on.at. 0111t s ti.,IT ' lido F A x imum Cust'S ( P.Wr'al e t'StiLi l ot. F Waim t.14tlIn E F t LisF*lTS PEkIllD OF Rtt.FAbE - 1/ 1/63 TO 12/31/d3 CALCellaTED 02/u4/84 e

, 19T 2s0 340 4 Te1 4t:HtJAL 00SE TYPE I4HARTEk Oti A n T t.P usAiTFn (JuANTER 1/83- 3/83 4/83- 6/b3 7/63- 9/83 10/83-12/e3 TOTAL 1.7.60=ul 2.40E-03 9.75t-04 1.57E-03 6.76E-03 A t>0 Y IHTERNAL 5.35F-0 3~.' 7.43E-03 1.44E-03 2.31t-03 1.02E-02 ORGAN .

uphE, LIVER LIVEN LIVEN RUNE

THIS 18 A REPORT F0k THE CALFt.DAR YEAN 1963 t

CearLI Ar rr. d1 Tt:$ = lu (F4 S t? arP. 1

T OF AFP 1. --------------

OTRLY 1:41 nTk 2: I f:19 364D OTh 4 T H sai38 YWLY % OF OtiJ 1/63- h/M3- 7/03- 10/83- OpJ. APr'. I !

3/63 6/83 4/o3 12/d3 TIITAL BODY (mRFet) 1.5 0.12 0.16 o.06 0.10 -3.0 0.23 CRIT DNGAN(MNEM) 5.0 -0.11 0.07 v.03 .0.05 10.0 0.10 Rut:E ~~~ LIVER LIVER LIVER BONE 4

t .43

QOhD CITIES NUCLEAR POUErl STATION April 1981 l Revision 1 Figure 5.0-1 LOCATIONS OF FIXED ENVIRONMENTAL RADIOLOGICAL MONITORING STATIONS Air 3amotore I-Desite Stellen I ,

1-Oeslie Sletion 2 9

)[: y 3-Oeslie Staties 3 jE w cistes station 4-NITRIN * =

en .=

5-Seddle Club Delry 7

"* "$ fr .=

~

4-Hossea's Best Leading -

7-Clistes s

0-Sittene Form ,

i O hem W- AJ l L L I N O I S 9-Erle es 10 Hillsdale ,

11 Pori Byree Additionat i 10 ,/

It-Bellendorf _

"" I "

13 Princeton g'ggj g, ,,

..,,,,, y

= -

b i TLD @

f Same as air samplers plus a sufficient number of additional dosimeters placed

' near the site and near 5 miles to assure, i ~to the extent practical, that one dosimeter e e T' , . .u.

1- is' located at each range in each of the . . . . . . .

i 16 meteorological setors, 44'

QUAD CITIES NUCLEAR POWER STATION 3

Standard Radiological Sampling Program 4

Media L 5

$ B %

11 s

u"

! u E m Old New Loc. .b $$ $$ $!

Code Code ga Location Description < H E ' u

u- U .

, IFl9I Q!Ul? On-site No. 1 X X

-02 On-site No. 2 X X.

-16 -03 On-site No. 3 X X

-01 ' 04

- Nitrin X X

-06 -05 Saddle Club Dairy X- X

-12 -06 Hanson's Boat Landing X X

-02 -07 C Clinton X X

-03 -08 C Sikkema Farm X X

-04 -09 C Erie- X X

-05 -10 C. Hillsdale X X

-07 -11 C Port Byron X X

-08 C Bettendorf X X i' -09 -13 C Princeton X X

-10 -14 C Utica Ridge Road X X

-11' C DeWitt X X

-13 -16 C Low Moor _ X X

-17 Musal Dairy Farm X X

-34 -18 Turner Farm .

X X

-20 -19 East Moline Water Works X

-21 -20 Davenport Water Works X

-18 -21 C Inlet Canal X

-19 -22 Discharge Canal -

X

-27 -23 Lock & Das No.14 (Mississippi River) X

-27 Davenport Fish Market (Pool No.14, Mississippi River) X a

Control (background) locations are indicated by a "C" in this column.

All other locations are indicators.

~45

TABLE 5.0-1'

, QUAD CITIES STANDARD RADIOLOGICAL MONITORING PROGRAM a

Non-Routine b Sample Media Collection Site Type of Analysis Frequency Reporting Levels C

1. Air Monitoring (a) Onsite and near Field 1. Filter - gross beta 1. Weekly Cs-134 10,Cs-137 20 pC1/m3 (1) Onsite Station il 2. Charcoal 131 2. Bi-weekly d 0.9 pC1/m3 (2) Onsi.te Station #2

-(3) Onsite Station #3 .3. Sampling Train -

(4) Nitrin Test and Maintenance 3. Weekly

. (5) Saddle Club Dairy Farm (6) Hanson's Boat Landing (b) Far Field 1. Filter Exchange 1. Weekly Same as 1 (a)

(1) Clinton (2) Sikkeaa Farm 2. Charcoal Exchange 2. Bi-weekly When analyses (3) Erie (4) Hillsdale 3. Sampling Train - 3. Weekly are made

.M (5) Port Byron Test and Maintenance (6) Bettendorf (7) Princeton (8) Utica Ridge Road (9) DeWitt (10) Low Moor

2. TLD Same as 1 Gamma Radiation Quarterly ,

3. Fish Pool 14 of Mississippi Gamma isotopic Semi-annually Mn-54 3x10 ,Fe-591x104 Co-58 3x10 .C0-60 1x104 In-65 2x10 Cs-134 1x103 Cs-137 2x103 pC1/Kg wet weight

4. Milk (a). Hansen Dairy I-131 1. Weekly - I-131 3 pC1/1 Grazing Season - Cs-134 60 pC1/1 May to Oct (b) Musal Dairy Cs-137 70 pC1/1

2. Monthly -

Now to Apr Ba-La-140 300 pC1/1 v

TABLE 5.0-1 (continued)

QUAD CITIES STANDARD RADIOLOGICAL MONITORING PROGRAM

~Non-Routine-Reporting Levelsb Sample Media Collection Site -Type of Analysis Frequency 5.' Public Water (a)- East Moline Water Works 1. Gamma Isotopic. 1. Monthly Analysis (See footnote e)

(b) -Davenport Water Works of Weekly Composites y

6. ' Cooling Waterf (a) Inlet' 1. Gross Beta 1. Weekly (b), Discharge

7. Sediment (a) Lock and Das No.14 Gamma' Isotopic Annually

~ 8. Dairy Census . (a) Site Boundary to (a) Enumeration by Annually, during 2 miles' a door-to-door or grazing season '

equivalent counting technique (b) 2 miles to 5 miles (b) Enumeration by using referenced information from county agricultural a ' agents or other reliable M

sources.

(c) At dairies listed in item 4. (c) Inquire as to-feeding practices.

(1) pasture only (2) Feed and chop only (3) Pasture and feed;

' -if both, ask farmer to estimate fraction

-of food from pasture (25%

25-50s 50-75%

>751 i

a Additional. information giving the distance and direction of individual sampling locations may be b

found in Appendix 111 of.the 1978 Annual Report.

e Average' concentration over calendar quarter.

A' gamma isotopic analysis shall be performed whenever the gross beta concentration in a sample ,

exceeds by five times (5x) the average concentration of the preceding calendar quarter for the d sample location.

.' 81-wee shall mean .

H-3 gul I , Mn-541x10 . . ghat Fe-59the tv10freqpncy is once every 2x10other pZn-65

'Co-58 6x10 2

, Co-60 , 2 2x10 , 2r-Nb-95 2

'g 4x10% I-131 2, ts-134 30, Ct 137 50,' Ba-La-1401x10 pC1/1.

Provided by station personnel.

s

Table'5.0-2 Environmental Radiological Monitoring Program Quarterly Summary Name of facility Quad Cities Nuclear Power Station Docket No. 50-254. 50-265 ,

location of facility Rock Island, Illinois ' Reporting Period 1st Quarter 1983 (County, State)

Indicator Location with Highest Control

. Sample Type and Locations Quarterly Mean Locations Number of Type Number of 'Heana Mean Meana non-routine (Units)' ' Analyses LLD Range Location Range Range Results Gross Beta 77 0.01- 0.022 (76/77) Q-03, Onsite #3 0.026 (13/13) 'None 0 Air Partjculates (pCi/c) (0.011-0.039) 0.6 mi 0 170* (0.015-0.039)

Airborne 19 dine I-131 36 0.10 (LLD' - - None 0 (pC1/m3)

Gamma Background Gamma Dose 16" 3.0' 12.9 (6/6) .Q-11, Port Byron 15.9 (1/1) 13.1 (10/10) 0

-(TLDs) (mR/Qtr.) (11.7-13.4) 8.0 mi 9 170* -

(11.6-15.9)

Milk .. 1-131- 6 5.0 -. <LLD - - None 0 4, (pCf/11 cm Cooling Water - Gross Beta 136 2.0 4.6 (24/24) Q-228, Spray Canal 5.4 (12/12) 4.4 (12/12) 0 (pC1/1) (2.7-9.9) Blowdown at (3.8-9.9) (3.6-5.7)

Station Tritium . 1 200 <LLD - - None O Public Water. Gamma Spec. 6 (pC1/1)

Cs-134 10.0 (LLD - - None O Cs-137' 10.0 (LLD -

- None 9

<tLD None 0 Other Gammas - 20.0 - -

a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

v

- Tabla 5.0-3 Environmental Radiological Monitoring Program Quarterly Summary

- Name of facility Quad Cities Nuclear Power Station Docket No. 50-254, 50-265 Location of facility Rock Island, Illinois Reporting Period '2nd Quarter 1983 (County, state)

Indicator Location with Highest Control Sample -Type and Locations Quarterly Mean Locations Number of Type Number of Meana Mean Mcana non-routine (Units) Analyses LLD Range Location Range Range Results Air Particulates Gross Beta 78 0.01 0.019 (69/78) Q-03, onsite #3 0.021-(12/13) None 0 (pC1/m3). (0.010-0.034) 0.6 mi 9 170' (0.011-0.034)

Airborne lodine. 1-131 42 0.10 <LLD - - None 0 (pCi/m3)

Gamma Background Gamma Dose 16 3.0 12.5 (6/6) Q-11, Port Byron 14.8 (1/1) 12.6 (10/10) 0

.(TLDs) (mR/Qtr.) (11.0-13.4) 8.0 mi 9 170* - (11.2-14.8)

Milk I-131 18 5/0.5* <LLD - - None 0 ,

(pCi/1)

Cooling Water Gross Beta 39' 1.0 4.2 (26/26) Q-22B, Spray Canal 4.6 (13/13) 4.2 (13/13) 0 (pC1/1) (2.8-5.4) Blowdown at (2.8-5.41 (2.6-6.0)

Station

$.. Tritium 1 200 (LLD - - None O Public Water Gamma Spec. 6 (pci/1)

Cs-134 10.0 (LLD - - None O Cs-137 10.0 <LLD - - None 0 Other Gammas- 20.0 <LLD - - None 0 Fish .

Gasma Spec. 9 (pCi/g wet)

Cs-134 0.1 <tLD - - None O Cs-137 0.1 <tLD - - None 0 Other Gammes 0.2 (LLD - - None 0 a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

November - April LLD = 5.0; Mg - October LLD = 0.5.

l V ' - - - - - - _ _

Table 5.0-4 Environmental Radiological Monitoring Program Quarterly Summary Name of facility Quad Cities Nuclear Power Station Docket No. 50-254, 50-265 Location of facility Rock Island, Illinois Reporting Period 3rd Ouarter 1983 (county, statel Indicator Location with Highest Control Sample Type and Locations Quarterly Mean Locations Number of Type' Number of Meana Mean Meana non-routine (Units) Analyses LLD Range Location Range Range Results Air Particulates Gross Beta 78 0.01 0.033 (76/78) Q-02, Onsite #2 0.035 (13/13) None 0 (pC1/m3) (0.010-0.118 ) 0.5 mi 9 70* (0.016-0.092)

Airborny Iodine I-131 36 0.10 <LLD - .

None 0

.(pti/m3)

Gamma Background Gama Dose ' 16 3.0 12.7 (6/6) 0-09. Erie 21.3 (1/1). 13.7-(10/10) 0 (TLDs) (mR/Qtr.) (11.4-15.0) 13 mi 9 110' -

(11.7-21.3)

Milk 1-131 26- 0.5 (LLD - - None 0 g (pC1/1 ) .

Cooling Water Gross Beta 42 1.0 4.6 (26/26) 0-228, spray Canal 5.3 (13/13) 4.0 (13/13) 0 (pC1/1) (1.6-7.7) Blowdown at (1.6-7.7) (2.6-5.5)

Station Tritium 1 200' <LLD - -

None O Public Water Ganna Spec. 6 (PCi/11 Cs-134 10.0 <LLD - - None O Cs-137 10.0 <LLD - - None O Other Gammas 20.0 <LLD - -

None 0 Bottom Sediments Gaassa Spec. I t Cs-134 0.1 '<LLD - - None 0 Cs-137 0.1 0.35 (1/1) Q-23, Lock & Dam 0.35 (1/1) None 0

14 Mississippi River 15.0 mi 9 210*

Other Gamenas 0.2 <LLD - - None 0

'

Mean and range based on detectable measurements only. Fractions indicated in parentheses.

Table 5.0-5 Environmental Radiological Monitoring Program Quarterly Sumary Name of facility Quad Cities Nuclear Power Station Docket No. 50-254. 50-265 Location of facility Rock Island. Illinois Reporting Period 4th Quarter 1983 (County, State)

Indicator Location with Highest Control Sample Type and Locations Quarterly Mean Locations Number of Type Number of Meana Mean Meana non-routine Analyses Range Location Range Range Results (Units). LLD 0.01 0.047 (78/78) Q-04,Nitrin 0.050 (13/13) None 0 Air Particulates Gross Beta- 78 (pC1/m3) (0.029-0.090) 1.5 at 9 40' (0.035-0.090) 0.10 - None 0 I-131- 42 <LLD -

Airborng)

(pC1/ma Iodine Gaume Background Gasuna Dose 16 3.0 13.4 (6/6) Q-08, Sikkema Fars 15.7 (1/1) ' 13.7 (10/10) 0 (11.4-15.5) 7.0 mi 0 70' - (11.9-15.7)

(TLDs) (mR/Qtr.) ,

None 0

'E. Milk (pCf/1) 1-131 14 ' 5/0.5* (LLD - -

Cooling Water Gross Beta 38 1.0 68.3 (25/25) Q-228 Spray Canal 137.8 (12/12) 4.2 (13/13) 1 (pCi/1)- (2.8-1586) 810wdown at (4.3-1586) (3.2-6.7)

Station

- None 0 Tritium 1 200 <LLD -

Public Water Gamma Spec. 6 (pC1/1)

Cs-134 10.0 <tLD - - None O 10.0 (LLD - - None 0 Cs-137 Other Gauunas 20.0 <tLD - - None 0 Fish Gamuna Spec. 8

-(pC1/g wet)L - None O Cs-134 0.1 <LLD -

0.1 (LLD - - None 0 Cs-137 0.2 . <LLD - - None 0 Other gammas a Mean and range based on detectable measurements only. Fractions indicated in parentheses.

-

November - April LLD = 5.0; May - October LLD = 0.5.

[

QUAD CITIES l

Table 5.1-1

' Gamma radiation as measured by Thermoluminescent Dosimeters (TLDs)

Standard Radiological Monitoring Program

, 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter i Date Placed: 12-31-82 4-01-83 7-01-83, 8-10-83* 10-01-83 Date Removed: 4-01-83 7-01-83 10-01-83 12-31-83 Days in the Field: 91 91 92,52* 91 4-Location- Average mR/Qtr i

On-Site Indicator Locations Q-01 On-Site No. I 13.2i0.8 13.0tl.0 12.lil.0 13.0i0.6 Q-02 On-Site No. 2 13.4i0.9 13.0il.1 15.0il.6 15.5i0.8 Q-03 On-Site No. 3 12.6tl.0- 12.8tl.5 11.6i0.8a 12.8tl.2 Mean i s.d. 13.li0.4 12.910.1 12.911.8 13.8tl.5 -,

~

- Off-Site' Indicator Locations Q Nitrin 11.7i0.8 11.Dil.1 11.410.8 11.4i2.6-

, Q-05 Saddle Club Dairy 13.110.7 11.8i0.9 12.1*0.4 12.8i0.8

Q-06 Hanson's Dock 13.411.0- 13.4i0.7 13. 9tl.6 -15.lil.2 12.Sil.3 13.111.9

~

- Mean i s.d. 12.710.9- 12.111.2 Background Locations' 4

Q-07 Clinton . - 11.610.7- 11.2il.0 12.2il.0- 11.9tl.4 Q-08. Sikkema Farm 13.2i0.6 13.110.8 12.6i0.6 .15.7tl.0 Q-09*~ ' Erie 13.7i0.9 13.Si0.6 : 21.3fl.7' 14.0tl.41 Q-10 . Hillsdale 14.010.7' 13.lil.1 13.0f0.9- 14.2f0.9' Q-11. - Port Byron -15.9t0.9 14.8i0.9 -

11.0il.4 6 :15.1*3.1 13.li0.9

~

. :Q . Bettendorf -14.3i0.9 - 13.210.7 13.2*0.8' Q Princeton. 211.6tl.2 12.4t0.9 13.0tl.0 - 13.3i0.8; E

- Q-14 ' Utica. Ridge Road 12.410.8' '11.210.6 11.7f0.7 12.7tl.3 Q-15. DeWitt 11.9t0.9 11.6i0.9 12.4i0.9 13.7i0.9 ,

Q . Low Moor, 12.2i0.7- 12.0f0.6 11. 8tl . 8 -. 12.8tl.0 Mean't s.d.- 13.lil.4 12.6fl.1 L13.7t2.9- 13. 7t1~.1 a

l- Q-03C TLDs'results;-TLDs from Q-03 were lost:in the field.

L s '

^

=. 5g _ .

+j t 3 p r 3 y q v ,-

g --n+- -m -m - e-- ~v- e- sm-

l' n

4 r

! QUAD CITIES ~

Table 5.1-1 (continued) ,

, Gamma radiation 'as measured by TLDs-(continued)

Special Program

.L Inner Ring, Near Site Boundary, Indicator Locations i.

1st Quarter 2nd Quarter 3rd Quarter 4th Quarter

-4 F Date Placed: 12-31-82 4-01-83 7-01-83, 7-29-83* 10-01-83

Date Removed: 4-01-83 7-01-83 10-01-83 12-31-83 5

Days in the Field: 91 91 92,65* 91 i Location Average mR/Qtr-Q-101-1 11.5t0.6 11.011.2 12.6il.0 12.0fl.2 Q-101-2 11.5t0.6 10.910.6

10.810.6 11.Si0.7 Q-102-1 12.9i0.5 12.2i0.7 13.0il.7 13.8i0.9-F Q-102 12.4i0.5 12.910.7 11.2i0.6 14.lil.0

. Q-103-1 11.5i0.8 11.110.6 11.Sil.1 11.6i0.8 Q-103-2 11.0*0.6 10.Si0.9 9.5tl.2, 11.111.0

' Q-104 11.3*1.0 11~.110.8 11.0*1.2 11.7i0.7' ,

~ Q-104-2 11.310.9 '10.511.1 11.5t0.9 11.6i0.9

Q-105-1 11.3tl.4 ~10.7i0.6 9.8i0.7 12.4*0.8 1 Q-105-2 11.6*1.0 11.6t0.9 11.3i0.8 12.0i0.8

Q-106-1 11.9i0.7- 9.8tl.8 11.410.6 11.910.8 Q-106-2 12.3i2.1- 12.210.9 11.4i0.7 12.7i0.7 Q-107-1 11~6i0.6

. 12.5i0.7. 11.910.8' '13.011.1

_ Q-107-2 11.li0.6' 10.8i0.9 10.8i0.4 11.310.9-Q-108-1 11.8tl.0 -11.2il.3 11.1*0.8 11.4tl.7.

Q-108-2' 12.2i0.5 11.3i0.7 11.0il.4_ ~12.8i0.7:

Q-109 11.6i0.8 10.4i0.7_ 10.7f0.7 10.9tl.3 Q-109 10.910.8 11.0il.0 11.0f 0.9 ' .12.211.2 Q-111 14.110.7 .12.4tl.0 12.5i0.6 15.6i0.8 '

Q-111-2 11.5tl.0 10.6i0.7 10.8*0.8. 112.7tl.1 Q-112-1 11.210.5 11.411.2 ~12.0i0.8 12.3i0.9~

Q-112 13.4*l.1 12.4i0.7' -

12.110.6 13.4*1.3_ .

Q-113-1. '11.5i0.7 11.8i0.5 10.810.8 -11.7i0.9 4

Q-113-2* NDa .NDa- 16.410.9- ~11.911.2

_-Q-114-1* NDa_ . NDa -.17. 6tl .1 - 10.4*0.8L ,

- Q-114-2 11,8*0.6 11.4t0.9- 11.110.8. 12.1*0.6 :

Q-115-1~ 12.0f0.5 11.4t0.7- '10.9i0.7! 12.5tl.I l' Q-115-2 13,2i0.8 NDb '

12.0i0.4 12.7i0.9 Q-116 12.6tl.0- 12.210.6 - 11.7i0.5L l13.5tl.0

- Q-116-2: -11.4*0.5 11.Si0.7-' 10.5i0.6' '12.7i0.7 Mean i s.d. ~11.9i0.8 11.4*0.8 11.7tl.6- <12.311.1" - .

- b ND: =~ No data; TLDs were' not placed:due to construction * :in the area. -

-ND = No data; TLDs were lost;in the field.:

_ 53 v -

3 3 > ' ;s _ , , 4 ..

i QUAD CITIES Table 5.1-l'(continued)

' ~

Gamma radiation as measured by TLDs (continued)

Special Program Outer' Ring, Near 5 Mile Radius Indicator Locations

. 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Placed:- 12-31-82 4-01-83 7-01-83 10-01-83 Date. Removed: 4-01-83 7-01-83 10-01-83 12-31-83

-Days in the Field: 91 91 92 91 l Location Average'mR/Qtr Q-201-1 13.6t0.5' 12.6i0.6' 12.6i0.5 14.7i0.8

Q-201 11.7tl.7- :13.Si0.7 12.2*0.4 13.Sil.2

! Q-202-1 11.1i0.5 10.8i0.8 .10.810.5 11.8i0.7 Q-202-2 11.610.8 11.3i0.6 .10.6*0.6 11.9tl.0

i. Q-203-1 12.6i0.9 11.6tl.1 11.6i0.6 13.3tl.8 Q-203-2 13.9tl.0 13.0i0.6- 12.810.8 14.Sil.1 Q-204-1 14.5i0.9 14.011.2 13.lil.0 c14.3tl.1- '

Q-204-2 NDa 13.111.0 13.2i0.8 15.7tl.5 i Q-205-1. 13.4*1.0 13.8i0.7- 13.6fl.8- 17.8tl.8 Q-205-2 13.4tl.4 .12.8i0.9- 13.0i0.'7- 14.6i0.5 Q-206-1 .12.6t0.5- 12.510.9 12.2il.2- 13.8i0.6-

, Q-206 13.2i0.5- 12.8i0.6 12.9tl.8 14.511'.1

, Q-207-1 13.4tl.1 13.7*0.8 12.9*0.5: 13.9tl.0 Q-207-2 11.7i0.9 11.2i0.8 11.4i0.7' 12.0f0.6~

, Q-208-1 12.6*1.2 10.8i2.0- 11.2iO.6- 12.910.7-Q.208-2 13.310.7 12.9tl.0 11.9*0.6 13.9i0.7- ~,

Q-209-1 13.2i0.6. 13.110.6 12.6i0.9 13.0t0.6 Q-209-2L 12.3f0.9, 10.6i2.1 11.3i0.5- 12.0tl.0-12.0i0.7 12.310.5 11.110.5 13.911.6 Q-210-1 F

-Q-210-2 '13.6i0 7 .14.7f0.8. -13.0i0.7: :14.li0.6

.Q-211-1 :14.9tl.0. 14.5i0.9: :13.0f 0.8 - 15.1*0.7 Q-212-1 115.5t2.1 '14.2i0.9

,12.210.9 13.910.7 i ~Q-212-2 :11.3i0.4; D 11.9tl'. 5 10.410.4- 12.6*0.9 I -Q-213 12.1*0.7. L12.5i0.9- 10.8i0.8 12.6i1.2 l Q-213-2' 11.210.51 11.0*0.9f 10.3i1.0 :11.8tl.2:

p 10-214 13.Sil.2 12.4tl.1- 11.6tl.4 .13.4i1.5 Q-214-2 .13.3i0.7 13.3i0.7. =13.8i0.7 -15.0i0.7

Q-215-1' 14.3i0.6 '13.610.7- 12.7*0.5- -15.2tl.2-Q-215-2. '14.7*0.7-: 14.7tl.0' 13.3i1.0 14.7i0.9'

.Q-216-1 ~12.8i0.6- 12.910.7 ;11.9i0.5' 12.112.5.

Q-216-2 '13.4*0.8 13.9*1.2- -13.2i0.6 :15. 5tl.0 - ,

! .Mean~* s.d.- :- 13.0il.1 12.8tl.2- .

12.2il.0 13.8*1.4 I "ND'=Nodata;:TLDs1ost(inth'e?1 field.-

'( :p 54 ~

-t' e ,

. - - . .~ . ..

]

APPENDIX II METEOROLOGICAL DATA 55

l QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY - MARCH 1983 STABILITY CLASS - EXTREMELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET !

WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 0 0 0 0 0 0 NNE 1 0 0 0 0 0 1 NE O O O O O O O ENE O O O O -0 0 0 E O O O O O O O ESE O O O O O 1 1 SE O O 1 0 1 0 2 SSE O O O 3 1 0 4 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 2 0 0 2 WSW 0 0 0 1 0 0 1 W 0 0 0 2 0 0 2 WNW 0 0 2 0 0 0 2 NW 0 0 1 0 0 0 1 i NNW 0 0 0- 0 0 0 0 I

VARIABLE O O O O O O O

'i TOTAL 1 0 4 8 2 .1 - 16 l

HOURS OF CALM IN THIS STABILITY CLASS - 0

HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0'

' HOURS OF MISSING,, STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 2 56

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY - MARCH 1983 STABILITY CLASS - MODERATELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O 1 0 0 0 0 1 NE 1 0 0 0 0 0 1 ENE O O O O O O O E O O O O O O O ESE O O O O 1 0 1 SE O O O O O O O SSE O O O 3 1 0 4 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 1 0 0 0 1 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0

VARIABLE O O O O O O O TOTAL 1 1 1 .3- 2 0 8 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY ~ CLASSES - 2 i

f

~57 b

l QUAD CITIES NUCLEAR POWER STATION PERIOD'0F RECORD - JANUARY - MARCH 1983 STABILITY CLASS - SLIGHTLY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 0 0 0 0 0 1 NNE O O O O O 0 0 NE 1 0 0 0 0 0 1 ENE O O O O O O O E O O O 0 0 0 0 ESE O O O O 2 1 3 SE O O O 1 0 0 1 SSE O O O 2 0 0 2 S 0 0 0 3 0 0 3 SSW 0 1 1 0 0 0 2 SW 0 0 1 1 0 0 2 WSW 0 0 1 0 0 0 1 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0' NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 ,

VARIABLE O O O O O O O TOTAL 2 1 3 7 2 1 16 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING-STABILITY MEASUREMENTS IN ALL' STABILITY CLASSES -

2 i

58

'Ts s

QUAD CITIES NUCLEAR POWER STATION I PERIOD OF RECORD - JANUARY - MARCH 1983 STABILITY CLASS - NEUTRAL -

(DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND ,' WIND SPEED (IN MPH)

DIRE 3 TION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL

......... ..... ..... ..... ..... .....~ ..... .....

s .

N O O 8 21 5 0 34

~

NNE 0 5 24 5 0 0 34 NE O 8 20 28 28 3 87

^

ENE O 15 14 19 #' 8 0' 56 E 2 7' 13 21 ~- 18 3 64 ESE O 9 ,;,

20 25 11 '3 68

. - 18 11

/ 0 2 42 SE 1 1,T4.

, .a r

_ SSE 1 7 31 23 18 4 84

~

- S ~. 'l 2 5 26 36 10 0 79

- SSW 1 24 21 15 4 -LO_ 65 SW 2 11 10 6 0 0 29

_ WSW 0- 4 19 ,

5 2 0 30 W 0 4 20 51 29 6 110 rf WNW , 1 7 17 33 6~~, 10 74 NW 1, ^ D 7 25 54 16 1 103 NNW .

f - , -

, b -7 29 79 30 , 0 -145

-VARI ABLE , ,0 0 0- 0 0 0 0 i - TOTAL -

10 1IO 315 432 185 32 1104 1

.- J j

~

l l HOURS OF CALM IN THIS STABILITY CLASS - 0

HOURS OF MISSING WIND MEASUREMfNTS IN THIS STABILITY CLASS - 103 I

2 .,

HOURS OF MISSING STABILITY MEASUREMENTS N ALL STABILITh CLASSES - 2 w +g- w~w, ye, _

h r

. ,7

<j 'e

, 59

, . .e? p'>

r ~

l QUAD CITIES NUCLEAR PohER STATION PERIOD OF RECORD - JANUARY - MARCH 1983 STABILITY CLASS - SLIGHTLY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 4 8 21 4 0 37 NNE O 1 13 17 3 0 34 NE O 3 16 37 11 0 67 ENE o 3 17 15 18 9 62 E 1 15 35 19 8 2 80 ESE O 3 17 20 7 0 47 SE 1 11 22 18 3 1 56 SSE O 2 18 49 6 0 75 S 2 5 15 34 12 0 68 SSW 0 9 9 1 2 0 21 SW 0 5 8 4 0 0 17 WSW 1 3 11 5 0 0 20 W 0 2 8 37 6 0 53 WNW 0 3 16 24 2 0 45 NW 0 5 19 20 3 0 47 NNW 0 4 12 1 0 0 17 VARIABLE O O O O O O- 0 TOTAL 5 78 -244 322 85 -12 746 HOURS OF CALM IN THIS STABILITY CLASS - 0-HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 34-HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - .2 l

l l

60 !

i .

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JANUARY - MARCH 1983 STABILITY CLASS - MODERATELY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 0 1 0 0 0 1 NNE O 1 1 2 0 0 4 NE O 1 3 3 1 0 8 ENE O O 3 2 0 0 5 E O O 1 4 0 0 5 ESE O O 5 5 1 0 11 SE 0 0 3 8 6 0 17 SSE O O 2 10 0 0 12 S 0 1 7 10 0 0 18 SSW 0 0 2 2 0 0 4 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 1 2 1 1 0 0 5 W;iW 2 2 6 2 0 0 12 NW 0 1 1 0 0 0 2 NNW 1 0 0 0 0 0 1 VARIABLE O O O O O O O TOTAL 4 8 36 49 8 0 105 HOURS OF CALM IN THIS-STABILITY CLASS - 0 ,

HOURS OF MISSING. WIND MEASUREMENTS IN THIS STABILITY CLASS - 8_

HOURS OF MISSING STABILITY MEASUREMENTS IN ALL-STABILITY CLASSES - 2-l

_ 61e ;

,yr

')

2 1

. - - - -. - _ _ - - =

i OUAD CITIES NUCLEAR POWER STATION i PERIOD OF RECORD - JANUARY - MARCH 1983 STABILITY CLASS - EXTREMELY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 1 0 0 0 1 ENE O O O O O O O E O O 1 0 0 0 1 ESE O O 1 0 0 0 1 SE O O O O O 0 0 SSE 0 0 1 0 0 0 1 S 0 1 4 0 0 0 5 SSW 0 2 2 0 0 0 4 SW 1 1 0 0 0 0 2 WSW 0 0 0 0' O 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O l TOTAL 1 4 10 0 0 0 15 l

HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 3 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL. STABILITY CLASSES - 2 62

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - APRIL - JUNE 1983 STABILITY CLASS - EXTREMELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N -

0 0 0 0 0 0 0 NNE O O O O O O O NE O O O O 0 0 0 ENE O O O O O O O E O O O O 0 0 0 ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O 0 0 0 TOTAL 0 0 0 0 0 0 0 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 11 63 L - ;

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - APRIL - JUNE 1983 STABILITY CLASS - MODERATELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH) i DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL NNE O O 0 0 0 0 0 l

0 NE O O 0 0 0 0 ENE O O O O O O O E O O O O O O O ESE O O 0 0 0 0 0 SE O O O O O O O SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS Or MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 11 64

l l

l QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - APRIL - JUNE 1993 STABILITY CLASS - SLIGHTLY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 0 0 0 0 0 0 NNE O O O O O 0 0 NE O O 0 0 0 0 0 ENE O 0 0 0 0 0 0 E O O O O O 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 5 1 0 0 6 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 2 0 0 0 2 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 1 0 1 l VARIABLE O O O O O O O TOTAL 0 0 7 1 1 0 9 i

! HOURS OF CALM IN THIS STABILITY CLASS - 0 l . HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS -

0

! HOURS OF' MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 11 l

65 i

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - APRIL - JUNE 1983 STABILITY CLASS - NEUTRAL (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 1 13 12 5 5 36 NNE O 2 17 13 5 2 39 i

NE O 2 4 7 4 0 17 ENE O 2 2 7 7 1 19 E O 2 4 3 0 9 18 ESE 0 3 21 16 2 0 42 SE O 2 13 20 2 0 37 SSE 1 6 6 10 3 0 26 S 0 8 14 7 14 4 47 SSW 1 17 31 18 3 2 72 SW 1 9 17 12 5 3 47 WSW 0 7 to 8 6 13 44 W 0 10 21 26 12 4 73 WNW 1 10 16 13 24 7 71 NW 0 6 12 24 6 1 49 NNW 0- 1 12 35 4 1 53 VARIABLE 0 -0 0 0 0 0 0 TOTAL 4 88 213 231 102 52 690 HOURS OF CALM IN THIS STABILITY CLASS.- 0 HOURS OF MISSING WIND MEASUREMENTS IN-THIS-STABILITY CLASS - 1 HOURS OF MISSING STABILITY MEASUREMENTS IN.ALL STABILITY CLASSES - 11 66 .

l QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - APRIL - JUNE 1983 STABILITY CLASS - SLIGHTLY STABLE (DELTA T 296-33 FT)

) WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 6 23 22 7 0 59 NNE 1 6 20 20 4 5 56 NE 2 18 5 26 25 23 99 ENE 1 16 22 30 12 3 84 E 2 5 22 53 24 9 115 ESE 1 6 24 27 11 4 73 SE 1 R 10 25 8 0 52 SSE 3 3 17 28 31 12 94 S 1 2 15 18 31 7 74 SSW 2 12 30 15 6 3 68 SW 2 5 17 24 6 0 54 WSW 3 5 11 18- 9 0 46 W 1 5 33 45 7 0 91 WNW 1 7 18 40 10 1 77 NW 0 6 21 33 13 0 73 NNW 1 7 17 18 3 0 46 VARIABLE O O O O O O O TOTAL- 23 117 305 442 207 67 1161 i HOURS OF CALM IN THIS STABILITY CLASS - 0 j HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 10 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 11 1

67

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD . APRIL - JUNE 1983 STABILITY CLASS - MODERATELY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET (

WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 3 2 0 1 0 6 NNE O 1 1 0 1 0 3 NE 1 2 1 0 0 0 4 ENE 1 2 3 2 0 0 8 E O 3 8 7 1 0 19 ESE 2 3 3 13 2 0 23 SE O 2 4 14 3 0 23 SSE O O 9 17 3 0 29 S 0 1 5 to 2 0 18 SSW 1 6 3 6 0 0 16 SW 1 2 7 11 4 0 25 WSW 1 0 7 7 1 0 16 W 0 0 7 6 0 0 13 WNW 1 2 3 9 0 0 15 NW 1 3 5 3 0 0 12 NNW 0 3 0 1 0 0 4 VARIABLE O O O O O O O TOTAL 9 33 68 106 18 0 234 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 11 l

1 l

68 l

QUAD CITIES NUCLEAR POWER STATION -

PERIOD OF RECORD - APRIL - JUNE 1983 STABILITY CLASS - EXTREMELY STABLE (DELTA T 296-33 FT) .

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

-DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE 1 0 0 0 0 0 1 ENE. 0 2 1 0 0 0 3 E O O 1 0 0 0 1 ESE O O O 2 1 0 3 SE 1 0 1 4 O O 6 SSE O O 1 7 0 0 8 5 1 0 1 2 0 0 4 SSW 0 3 3 2 0 0 8 SW 1 2 4 6 0 0 13 WSW 1 0 3 2 0 0 6 W 0 2 4 4 0 0 10 WNW 1 2 1 0 0 0 4 NW 0 1 0 0 0 0 1 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O 0.

TOTAL 6 12 20 29 1 0 68 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 11-i 69 i

. QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JULY - SEPTEMBER 1983 STABILITY CLASS - EXTREMELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 0-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O 0 0 5 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O 0 0 0 0 TOTAL 0 0 0 0 0 0 0 HOURS OF CALM IN THIS STAHILITY C1 ASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - O t

70

f.

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JULY - SEPTEMBER 1983 STABILITY CLASS - MODERATELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 0 0 0 0 0 0 NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE 0 0 0 0 0 0 0 S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - O' HOURS OF-MISSING: STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 0'

/

71 c: -.

l QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JULY - SEPTEMBER 1983 STABILITY CLASS - SLIGHTLY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH) l DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL !

N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O 0 O SSE O O O O O O O S 0 0 0 4 0 0 4 SSW 0 0 1 1 0 0 2 SW 0 0 2 0 0 0 2

, WSW 0 0 0 0 0 0 0 W 0 0 0 1 0 0 1 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE 0 0 0 0 0 0 0

. TOTAL 0 0 3 6 0 0 9 HOURS OF CALM IN THIS STABILITY CLASS - 0

. HOURS OF MISSING WIND NEASUREMENTS IN THIS STABILITY CLASS -

0 i

I HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 0 D

72

QUAD CITIES NUCLEAR PODER STATION PERIOD OF RECORD - JULY - SEPTEMBER 1983 STABILITY CLASS - NEUTRAL (DELTA T 296-33 FT)

WINDS-MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 5 9 8 2 0 24 NNE O 1 3 16 0 0 20 NE O 3 4 0 1 0 8 ENE O 1 1 1 0 0 3 E O 2 3 1 0 0 6 ESE O 6 2 2 0 0 10 SE O 4 12 7 3 0 26 SSE O 7 24 14 3 1 49 5 0 9 23 13 3 2 50 SSW 0 28 31 11 1 0 71 Sh 1 22 32 23 1 0 79 WSW 1 23 17 7 2 1 51 d 0 17 24 11 5 0 57 WNW 0 11 11 14 6 0 42 NW 0 3 12 3 7 0 :25 NNW 0 2 8 5 4 0 19 VARIABLE O O O O O O O TOTAL 2 144 216- 136 38 4 540 HOURS.0F CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 14 HOURS OF MI'SSING STABILITY-MEASUREMENTS IN ALL STABILITY CLASSES - 0 73 -

L J

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JULY - SEPTEMBER 1983

' STABILITY CLASS - SLIGHTLY STABLE (DELTA T 296-33 FT) ,

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION ' .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 18 27 8 0 0 53 NNE O 23 17 8- 0 0 48 NE 1 22 25 17 0 0 65 ENE O 17 33- 9 0 1 60 E 2 12 14 9 2 1 40 ESE 1 6 11 10 0 ,0 28 SE O 12 20 21 5 0 58 SSE O 13 15 15 15 1 59 S 0 16 25 43 24 5 113 SSW 1 16 39 '14 8 3 81 SW 1 12 20 22 12 4 71 WSW 1 9 19 25 6 0 60 W 1 3 12 25 6 1 48 WNW 0 12 9 40 1 0 62 NW 0 12 28 21 1 0 62 NNW 3 17 18 15 1 0 54 VARIABLE O O O O O O O TOTAL 11 220 332 302 81 16 962 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 67 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL: STABILITY CLASSES - 0 74

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - JULY - SEPTEMBER 1983 STABILITY CLASS - MODERATELY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 1 5 3 0 0 0 9 NNE 2 1 7 2 0 0 12 NE O 2 8 9 1 0 20 ENE O 2 3 4 0 0 9 E 1 0 5 5 0 0 11 ESE 2 3 7 8 3 0 23 SE 1 2 14 18 4 0 39 SSE O 3 10 34 6 1 54 S 2 4 17 26 9 0 58 SSW 0 5 15 4 0 0 24 SW 0 1 9 7 2 0 19 WSW 0 1 7 11 2 0 21 W 0 1 2 4 7 0 14 WNW 1 2 0 10 0 0 13 NW 1 3 1 0 0 0 5 NNW 0 3 2 0 0 0 5 VARIABLE O O O O O O O TOTAL 11 38 110 142 34 1 336

. HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 25 HOUHS OF. MISSING STABILITY MEASUREMENTS IN'ALL STABILITY CLASSES - 0 l

75

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

l l

l QUAD CITIES NUCLEAR POWER STATION l PERIOD OF RECORD - JULY - SEPTEMBER 1983 l STABILITY CLASS - EXTREMELY STABLE (DELTA T 296-33 FT) i WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION 8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE 1 0 0 0 0 0 1 NE 1 0 0 0 0 0 1 ENE 3 6 2 0 0 0 11 E 1 2 5 0 0 0 8 ESE O 3 2 5 0 0 10 SE O 1 5 41 2 0 49 SSE 2 2 10 31 1 0 46 S 0 8 21 30 2 0 61 SSW 0 11 15 2 0 0 28 SW 0 6 10 4 0 0 20 WSW 1 0 4 4 1 0 10 W 0 0 1 3 0 0 4 WNW 0 0 0 1 0 0 1 NW 0 3 0 0 0 0 3 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O 0 TOTAL 9 42 75 121 6 0 253

' HOURS OF CALM IN THIS STABILITY CLASS -' O HOURS OF MISSING WIND MEASUREMENTS-IN THIS STABILITY CLASS - 2 l

HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES -

0

(

I l

76

l l

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 1983 STABILITY CLASS - EXTREMELY UNSTABLE (DELTA T 296 33 FT)

WINDS MEASURED AT 296 FEET 4

WIND WIND SPEED (IN MPH) .

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL !

N 0 O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O 4

S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O 4

TOTAL 0 0 0 0 0 0 0 HOURS OF CALM IN THIS STABILITY CLASS - ' O HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 H0tlRS.0F' MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 3 77

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 1983 STABILITY CLASS - MODERATELY UNSTABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED.(IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N 0 O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O l

E O O O O O O O ESE O O O O O O O SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 'O 2

W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 r

0 0 ' O NW 0 0 O O NNW 0 0 0 0 0 0 0 I VARIABLE O O O O O O O i i

. TOTAL 0 0 e 0 3 0 0 l

I HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS :IN ALL STABILITY CLASSES - 3 h

78

l l

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 1983 STABILITY CLASS - SLIGHTLY UNSTABLE (DELIA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O O O O O O NNE O O O O O O O NE O O O O O O O ENE O O O O O O O E O O O O O O O ESE O O O O O O 0 SE O O O O O O O SSE O O O O O O O S 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 W 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 VARIABLE O O O O O O O TOTAL 0 0 0 0 0 0 0 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 3 79

QUAD CITIES NUCLEAR PODER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 1983 STABILITY CLASS - NEUTRAL (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH) i DIRECTION .R-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 11 8 41 22 3 85 NNE 1 6 4 19 2 11 43 NE 0 3 3 14 7 0 27 ENE 1 1 5 7 6 15 35 E 1 6 22 34 8 9 80 ESE O 13 22 9 2 3 49 SE 1 4 18 8 0 0 31 SSE O 4 7 11 2 1 25 S 1 10 12 to 6 0 39 SSW 1 13 28 12 18 0 72 SW 2 10 7 11 7 0 37 i WSW 1 8 13 19 16 32 89 W 2 12 22 26 11 4 77 WNW 0 R 49 55 19 0 131 NW i 8 11 35 23 0 78 NNW 0 8 8 26 8 2 52 VARIAHLE O O O O O O O ,

I TOTAL 12 125 239 337 -157 80 950 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 41

. HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES.- 3

/

l OUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 1983 STABILITY CLASS - SLIGHTLY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 8 16 5 0 0 29 NNE O 7 21 12 1 2 43 NE O 2 10 26 3 0 41 ENE 2 6 13 40 31' 0 92 E 1 2 9 19 24 1 56 ESE i 6 9 28 11 4 59 SE 1 4 12 23 5 0 45 SSE O- 3 14 32 14 4 67 S 1 8 10 22 21 3 65 SSW 0 8 13 17 19 1 58 SW 5 9 28 31 9 0 82 WSW 2 6 11 23 10 2 54 W 3 5 10 27 20 10 75 WNW 3 5 9 27 14 20 78 _

NW 0 8 31 14 8 0 61 NNW 1 8 4 6 2 0 21 VARIABLE O O O O O O O

' TOTAL 20 95 220 352 192 47 926 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - :16 HOURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - '3 81 L

t --

QUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 19R3 STABILITY CLASS - MODERATELY STABLE (DELTA T 296-33 FT)

MINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION 8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O O 2 2 0 0 4 NNE 1 0 5 0 0 0 6 NE 1 1 3 1 3 0 9 ENE O 1 1 4 0 0 6 E O 2 1 7 1 0 11 ESE O 1 3 8 1 0 13 SE O O 1 8 5 0 14 SSE O 2 8 10 1 0 21 S 0 3 10 4 0 0 17 SSW 0 2 6 11 0 0 19 SW 0 1 3 2 0 0 6 WSW 0 1 0 1 2 0 4 W 0 2 6 5 4 0 17 WNW 0 0 4 2 9 0 15 NW 1 0 3 2 1 0 7 NNW 1 1 3 6 0 0 11 VARIABLE O O O O O O O TOTAL 4 17 59 73 27 0 -180 HOURS OF CALM IN THIS STABILITY CLASS - 0 HOURS OF HISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0

!!OURS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - 3 l

l l 182

OUAD CITIES NUCLEAR POWER STATION PERIOD OF RECORD - OCTOBER - DECEMBER 1983 STABILITY CLASS - EXTREMELY STABLE (DELTA T 296-33 FT)

WINDS MEASURED AT 296 FEET WIND WIND SPEED (IN MPH)

DIRECTION .8-3 4- 7 8-12 13-18 19-24 GT 24 TOTAL N O 1 0 0 0 0 1 NNE 1 5 1 0 0 0 7 NE O 3 0 0 0 0 3 ENE O O O O O O O E O 2 5 2 0 0 9 ESE O O O 1 1 0 2 SE O O 1 5 0 0 6 SSE O O 5 7 0 0 12 S 0 1 11 8 2 0 22 SSW 0 1 4 7 1 0 13 SW 0 1 3 1 0 0 5 WSW 0 0 0 0 0 0 0 W 0 0 0 0 5 0 5 WNW 0 0 0 0 4 0 4 NW 0 0 1 0 0 0 1 NNW 0 0 1 1 0 0 2 VARIABLE O O O O O O O TOTAL 1 '14 32 32 13 0 92 H0tlRS OF CALM IN THIS STABILITY CLASS - 0 H0tlRS OF MISSING WIND MEASUREMENTS IN THIS STABILITY CLASS - 0 HollRS OF MISSING STABILITY MEASUREMENTS IN ALL STABILITY CLASSES - ll 83 L

APPENDIX III ANALYTICAL PROCEDURES 84

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i SECTION 1.0 i

SAMPLE PREPARATION 4

Different classes of samples require different preparations. In general, food products are prepared as for home use, while others are dried and ashed as

! received. ,

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1.1 Fish

1. Wash the fish. ,

2. Fillet and place the flesh immediately (to prevent moisture loss) in a 500 cc plastic container. Add a few cc'of formaldehyde. Seal and record wet weight.

NOTE: If bones are to be analyzed, boil remaining fish in water for about 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months . Clean the b^ones. Air dry, weigh and record as wet weight. Dry at 125' C. Record dry weight. Ash at 800*

C, cool, weigh, and record the ash weight. Grind to.a homogeneous sample. The sample is' ready for analysis.

3. Gamma scan fillet without delay or store in a freezer.

4. After gamma spectroscopic analysis is completed transfer the sample to a drying pan and dry at 125' C.

5. Cool, weigh, and record dry weight.

6. Ash by gradually increasing the temperature to 450* C. If consider-able amounts of carbon remain. after overnight ashing, the sample should be brushed and placed back in the muffle furnace until ashing is completed. Record . ash weight. The sample is now ready for-analysis.

NOTE: If there is suffic.ient quantity, us'e surplus flesh;for drying and ashing, instead of . waiting for gamma scanning to-be completed.

t 9

86-L -

4

1.2 Bottom Sediments and Soil

1. Air dry the entire sample. Grind or pulverize the sample and sieve through a #20 mesh screen.

s

2. Forf gamma-spectroscopic analysis, seal 500 cc of the ground sample

in 'a Mari nelli beaker. Record dry weight.

- ,' /

w;

3. Seal the remaining sample (up to 1 kg) in a plastic container and save for other analyses or for possible future rechecking.

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1.3 Drinking (clear) water (EPA Method 900.0)

A representative sample must be collected from a free-flowing source of drinking water, and should be large enough so that adequate aliquots can be taken to obtain the required sensitivity.

It is recommended that samples be preserved at the time of collec-tion by adding enough IN HNO3 to the sample to bring it to (15 ml IN HNO 3 per liter of sample is usually sufficient)pH If 2 samples a~re to be collected without preservation, they should be brought to the laboratory within 5 days, then preserved and held in the original container for a minimum of 16 hours1.851852e-4 days 0.00444 hours 2.645503e-5 weeks 6.088e-6 months before analysis or transfer of the sample.

The container choice should be plastic over glass to prevent loss due to breakage during transportation and handling.

. If the sample was not acidified at the time of collection, use the following procedure: .

Procedure

1. Remove 100 ml of sample for tritium analysis, if required.

NOTE: Water should not be acidified for tritium analysis. If samples are acidified in the field, an additional aliquot should be collected.

2. Add 15 ml of IN_ HNO3 per liter of sample in the original container.

3. Hold the sample in the original . container for a minimum of 16 hours1.851852e-4 days 0.00444 hours 2.645503e-5 weeks 6.088e-6 months before analysis or transfer of the sample.

4. When taking an aliquot for analysis, take acid addition into account. For example:

l l Sample volume Volume of aliquot l to be analyzed required 200 ml 203 ml 400 ml 406 ml 600 ml 609 ml 800 ml 812 ml

( 1000 ml 1015 ml 2000 ml 2030 ml 3000 ml 3045 ml 3500 ml 3552 ml i

For other volumes, ' adjust aliquots correspondingly, at the

! rate of 1.5 ml per.100 ml of sample.

t i

I 88

j. .

l r

i i

l l

l 2.1 Airborne Particulates 2.1.1. Gross Alpha and/or Gross Beta Activity Procedure

1. Store the sample for 5 days' from the day of collection to aliow for decay of short-lived radon and thoron daughters.

2. Place a 47 mm filter on a stainless steel planchet and count the sample in a proportional counter.

3. Calculate the activity in pCi/m3 using computer program AIRPAT.

Calculations Gross alpha (beta) activity:

E 3 ) .

A

+2 Efb b (pC1/m B x C x 2.22 B x C x 2.22 Where:

A = net alpha. (beta) count rate (cpm)

B = efficiency for counting alpha-(beta) activity (cpm /dpm)

C = volume of sample (m3) ,

Esb = counting error of sample plus background Eb . = counting error.of background ,

r k

i 89:

I l

2.2.2 Gross Alpha and/or Gross Beta Activity in Dissolved Solids (see note) !

Principle of Method -

Water samples containing suspended matter are filtered through a membrane filter and the filtrate is analyzed. The filtered . mater sample is evapor-ated and the residue is transferred to a tared planchet for counting gross alpha-and/or gross beta activity.

Reagents ,

Lucite: 0.5 mg/ml in acetone Nitric acid, HNO 3: 3N Nitric acid, HNO3 : clincentrated Apparatus Filters; Millipore, membrane Type AA, 0.8 p Filtration equipment Planchets (Standard 2" x 1/8" Beckman planchet)

Proportional counter Procedure

1. Filter a volume of sample containing not more than 100 mg of dissolved solids for alpha assay, or not more than 200 mg of dissolved solids for beta assay.

Note: For gross alpha and gross beta assay in the same sample limit amount of solids to 100 mg.

2. Wash the non-filterable solids on the filter. (Save the filters with suspended matter for separate analyses. See Section 2.2.1).

3. Evaporate the filtrate to NEAR dryness on a' hot plate.. Add 25 ml concentrated HNO3 and evaporate to NEAR' dryness.

Note: For analysis of total residue (for clear water) proceed as described -above but do not fiter the water. Measure out the' appropriate amount-and proceed with step 3.

2

.90 C

1 l

Section 2.2.2.(continued)

4. With distilled water and a few drops of 3N HNO 3, transfer the residue to a 50 m1 beaker. Evaporate To NEAR dryness.

5. Transfer quantitatively the residue to a TARED PLANCHET, using an eye dropper.

6. Wash the beaker with distilled water and combine the washing and the residue in the planchet. Evaporate to dryness.

7. Bake in muffle furnace at 500* C for 45 min., cool and weigh.

8. Add a few drops (6-7 drops) of lucite solution and dry under the infrared lamp for 10-20 minutes.

9. Store the sample in a desiccator until it is to be counted.

10. Count the gross alpha and/or the gross beta activity in a _ low background proportional counter.

11. Calculate the activity in pCi/l using computer program OWATAB.

Calculations:

Gross alpha (beta) activity:

2 (pCi/ liter) = A 1' Efb + E b B x C x D x 2.22 B x C x 0 x 2.22

'- Where:

A = net alpha (beta) count (cpm)

B = efficiency for counting alpha (beta) activity (cpm /dpm)-

C = volume of sample (liters)

D = correction factor for self-absorption in the sample-Esb = counting error of sample plus background

.Eb = counting _ error of background

Reference:

Radioassay Procedures for Environmental Samples, U.S. ~ Department of Health, Education and rWelfare. . Environmental Health Series, January 1967.

r 91- .

1 3.1 Airborne Particulates - Gama Spectroscopic analyses by Ge(Li) Detector

1. Put the air filter in a fiiter cup container.

2. Place the filter cup on a Ge(L1) detector.

3. Determine the gama spectrum using 4096 or 8192 channel of gama spectrometer with a setting of 0.5 kev or 0.25 kev per - channel.

4. Identify gamma emitters-(if present) by their respective energy peaks.

Calculations

1. Calculate the gama activities using the computer program GAMMA 1 or GAMMA 2.

se .

+

'92 .

k _

1

'l l

j l

l l

3.2 Airborne Iodine 3.2.1 Spectroscopic Analyses by Automatic Gamma Counter Transfer charcoal to a plastic scintillation vial. Place the vial in the Automatic Gamma Counter (Packard Instrument Co. Model 5975) and count.

Record the time.

Calculations 0

- A=

2.22 x C x D x e -At Where:

A = activity of I-131 at the time of collection (pCi/m3)

B = net count rate of I-131 in the 0.36 MeV peak C = efficiency for counting I-131 activity in 0.36 MeV peak (cpm /dpm) ,

D = volume of sample (m3) e = the base of the natural logarithm = 2.7183 0.693 0.693 A = decay constant t 8.08 1/2 t= time (days) between the midpoint of collection and counting.

3.2.2 Spectroscopic Analysis by Ge(Li) Detector-

1. Transfer charcoal to a small plastic bag.

2. Label the plastic bag with the corresponding project, location and date of collection and seal it.

3. Place packed charcoal in a 500 cc. Marinelli beaker (all locations) and seal with tape.

4. Place it on the Ge(Li) detector and count. Record time.

Calculations Calculation is done by the . computer by running the Program GAMMA 2.

1 93

I 3.3 Water - Gamma Spectroscopic Analyses by Ge (Li) Detector Procedure +

1. Measure 3.5 liters of water into a Marinelli beaker.

~

2. Place the beaker inside the shield on a Ge(L1) detector.

3. Count long enough to meet LLD requirements.

4. Af ter counting, identify gamma emitters (if present) by their respective energy peaks.

5. Store the spectrum on a disc using computer by executing "RUN STORE."

6. After storing, calculate gamma ' activities, using computer program GAMMA 1 or GAMMA 2.

7. Transfer the sample 'back to the original' container for further

analyses.

e I

~94 .

3.4 Soils and Bottom Sediments - Gamma Spectroscopic Analyses by Ge(Li) Detector Procedure

1. Transfer the portion of the ground sample set aside for gamma scan-ning into a 500 ml Marinelli centainer.

2. Record the dry weight.

3. Place the container inside the shield on a Ge(L1) detector.

4. Count the gama activity long enough to meet the minimum sensitivity requirements.-

5. After counting, identify gamma emitters (if present) by their respec-tive energy peaks.

Store the spectrum on a disc using the computer by executing "RUN

~

6.

STORE."

7. After storing, calculate gamma activities using computer Program GAMMA 1 or GAMMA 2.

t

8. Transfer the ' sample back to the original container for further analyses.

d 95

1 l

l 3.5 Fish and Wildlife - Gamma Spectroscopic Analyses by Ge(Li) Detector

~

Procedure-

1. Transf$r a portion of the clean wet flesh of fish or animal into a 500 ml Marinelli container.

2. Record wet weight.

3. Add a few cc- of formaldehyde and seal the container.

4. Place the container ins,ide the shield on a Ge(Li). detector.

5. Count long enough to meet the minimum serisitivity requirements.

6. After counting, identify gama emitters (if present) by their respec-tive energy peaks.

7. Store the spectrum on a disc using computer by executing "RUN STORE."

8. After storing, calculate gamma activities using computer program GAMMA 1 or GAMMA 2.

9. Transfer the sample back to the original _ container for further analyses.

I t

i i

f' .

96

f 3.6'. Ambient Gamma Radiation A. Thermoluminescent Dosimeters (TLD) - Licht Response (Efficiency) .

s, Harshaw -Lithium Fluoride TLD-100 chips,1/8" x 1/8" 'x 0.035".

. Procedure .

1. Rinse the chips with warm -trichloroethylene followed by the methanol rinse. Dry.-

2. Place the chips in a platinum crucible.

3. Anneal for 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months at 400*C.

4. -Cool quickly by placing the crucible on a metal plate.

5. Anneal- for 2 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months at 100*C.

T Note: Avoid exposing the chips to the fluorescent. light.

> 6. Seal 5 chips'each in black plastic.

i._ 7. Mount the packs on the turntable.

8. Position the' Ra-226 needle in the middle of the turntable and I- start rotation (appr. 60 revolutions per minute). -Record the-

~

time.

9. Irradiate the chips.for 2-6. hrs.

[

I' 10. Remove the packages from the turntable.- Return the Ra-226:

needle t6 the_ lead container. Record the time. .

11. Take - the chips out of the plastic bag and . place- them in the

! = vial.

12. Postanneal the chips for 10 minutes at~100*C.

n 13._ '_ Read each chip in the TLD Reader -(For test procedure see'

" Performance Test Procedur'e for.TLD_ Reader").

l 14. -Calculate mean + one_sigmaideviation of-five chips.

15. " Calculate light response _. of ' TLD's '(correction f actor) by the'

_following equation:

i-I ,

L

~

l ,

s-

>97

[ , .

r Section 3.6 (continued)

' Calculations

- }

A ;

[ C.F. (nanocoulombs/ mrem) =

8 Where: ~

C.F = cor'rection factor to be applied in calculating exposure of field TLD's A = Net reading in nanocoulombs B = known exposure to TLD's-The exposure to the TLD's (B) is calculated as follows:

mrem /hr = 8400 x'mg Ra-226 r2 For our setup use the following parameters:

Ra-226 = 0.0922 + 1.5% -

r = 19.6 cm Thus:.

mrem /hr = 8400 x 0.0933 = 2.040

< 384.16 The total exposure (B) is equal to:

i. -B-(mrem)=l2.040xhours ,

L T

,I..

(-

c- .

I i-o I

L 98 . ,

. m. :.

. -- e - , , , - ,

3.7 Procedure for Preparation and Readout of TLD Chips Materials j Harshaw Lithium Fluoride TLD-100 chips,1/8" x 1/8" x 0.035". l Black plastic bags or boxes Plastic sealer Vacuum needle (for handling the chips)

TLD reader Note: Never handle the chips with bare hands. Use plastic-covered forceps or vacuum needle. Handle them gently, e.g. do not drop them into the vial or on the table. They chip off easily, resul-ting in efficiency change.

Procedure

1. Rinse the chips with warm trichloroethylene followed by the methanol rinse. Dry.

2. Place the chips in a platinum crucible.

3. Anneal for 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months at 400*C.

4. Cool quickly by placing the crucible on a metal plate.

5. Anneal for 2 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months at 100*C,

6. Seal 3 to 5 chips (depending on the specifications) in black plastic or plastic boxes.

7. Label and send out by U.S. Mail.

8. Upon arrival at the lab, store TLDs in the big shleid until readout day. Do not store longer than a few days.

9. Connect chips reader one day prior to readout.

10. Turn on gas for a few minutes before readout. Adjust to the mark.

11. Set parameter on the 2000P as follows:

~

HV - 470 V (It is 970 V, internal volts = 500).

Readout time: 20" T1 - 140* C (Preset)

T9 -

'60* C (Preset)

Rise time: -12*/sec (Preset)

Preheat - 100* C (Preset)

Start reading - 90* C.

99L

Section 3.7 (continued)

12. . Prepare the chips as follows (do this before proceeding to the next step).

12.1.-Turn on small muffler furnace or drying oven and adjust . to 100*C.. Use glass thermometer. Muffler's indicator is not accurate. Let furnace stabilize.

12.2 Unpack the chips (under reduced incandescent light) and gently.

place them in the glass vials marked with appropriate location numbers.

12.3 Place . the -vials in the furnace. - Preanneal for 10 min. at-100*C, t .

13. Open. the drawer and read. the standard. It should read . 5.70+0.04.

Adjust HV, ;if needed. Take 3 readings after final adjustment.

Record.

. 14. Close-the drawer.

15. Check bkg.. It should read about 0.7-0.8 in- 20". If-it is higher, adjust the' knob in the back of 2000 P (on left. side when facing the instrument).

~

Note: Adjust bkg as low as possible but do not let the needle hit.

zero. The instrument will not record below zero.

16. Make 10 bkg readings (no chip in). Record. , Read (do not record) at least 2 dumies to stabilize the temperature.-

17. Place 'the chip in, wait until temperature goes down to 90* C and

press " read" button. Make sure the chip is in the cavity of the heating plate.

18. After readout-is completed, record the reading, open the drawer, and place next chip.- ~

~

119. Repeat Steps,17,and 18 until all: chips are. read out.

Note: If reading will -l'ast longer than 1~.5-2.0 hrs. , check the standard and bkg about every 2.0 hrs.-

~

, 20. After readout is completed, turn off the gas.

21. For calculations, use computer. program ~0GTLD. PUB =.

l: 100- .

3.8 Tritium in Water (Direct Method)

, Principle of Method The water sample is purified by distillation, and portion of the distil-h late is transferred to a counting' vial' containing a scintillation fluid.

l The contents of the. vial are then mixed and counted in a liquid scintilla-tion counter.

Reagents Scintillation medium, insta-gel scintillator

Tritium standard solution j

. Apparatus i

Condenser Distillation flask, 250-m1 capacity

! Liquid scintillation counter Liquid scintillation counting vials Procedure'

1. Distill a 30 m'1 aliquot of the sample in a 250-m1 distillation

- flask. . Add - a boiling chip to the flask. . Connect a side arm adapter and a' condenser to the outlet of- the flask. Place a i- glass vial at the outlet of the. condenser. Heat the sample to.

100'- 150*_ C to distill, just to. dryness. Collect the distil-

-late for tritium analysis. .

2. Dispense 13 ml of the distillate to a low potassium glass . vial. .

3. Prepare background and standard, tritium-water solutions for counting, using 'the same amount .as the sample. Use low tritium background ' distilled water for these' preparations 1(distillate-of most deep well water sources is' acceptable,,but each ' source I should be checked for tritium activity before using).

l l- 4. Dark-adapt _all samples, backgrounds, and : standards' ; Add ml ~

of insta-gel . scintillator. Count the samples, backgrounds and

. standards. . Count : samples. containing less than 200 pC1/1 for 300 minutes' and samples containing nere than-200 pCi/1 for 200 l minutes.

F; l

101-h s -y qr * , v , ,w- -- c -w --.--w--

i Section 3.8 (continued)

5. Counting efficiency:

Eff = cpm of Standard-cpm of background dpm Standard

6. Sample Activity:

A pCi/ml =

2.22 x E x V Where:

A = net count rate (cpm)

-E = efficiency (cpm /dpm)

V = volume (ml)

7. Calculate tritium activity using computer program H3.

4 9

~

102

3.9 Iodine-131 Milk by Ion Exchange on Anton Exchange Column After samples have been treated to convert all iodine in the sample to a common oxidation state, the iodine is isolated by solvent extraction or a combination of ion exchange and solvent extraction steps.

Iodine, as the iodide, is concentrated by adsorption on an anion ex- ,

changed column. Following a Nacl wash, the iodine is eluted with sodium l

.hypochlorite. Iodine in the iodate form is reduced to 12 and the elemental iodine extracted into CC1, 4 back-extracted into water then finally precipitated as palladium iodide. ,

Chemical recovery of the added carrier is determined gravimetrically from the PdI2 Precipitate. I-131 is determined by beta counting the PdI2-Reagents Anion exchange resin, Dowex 1-X8 (50-100 mesh) chloride form.

Carbon tetrachloride, CC14 - reagent grade.

Hydrochloric acid, HC1, IN_.

Hydrochloric acid, HC1, 3N_.

,- H2O - HNO 3 - HN20H HCL wash solution: 50 ml H20; 10 ml 1M - NH 0H-HC1;

~ 2 10 ml conc. HNO3 -

Hydroxylamine hydrochloride, NH20H hcl - 1 M_.

Nitric acid, HNO3 - concentrated.

Palladium chloride, PdI ,2 20 mg Pd++/m1. 1.2 g pdc 12/100 ml 6N HC1).

Sodium bisulfite, NaHS03 - 1 M,

-Sodium chloride, Nacl - 2M_

Sodium hypochlorite, Na0C1 - 5% (Clorox).

i l

l -103

Section 3.9 (continued)

Special Apparatus Chromatographic column, 20 mm x 150 mm (Reliance Glass Cat.#R2725T).

Vacuum filter holder, 2.5 cm2 filter area Filter paper, Whatman #42, 21 mm Mylar Polyester gummed tape,1 1/2", Scotch #853 Drying oven '

A. Ion Exchange Procedure

1. Set up an ion exchange column.of 20 mm diameter and 150 mm length.

2. Pour 20 ml of a slurry of Dowex 1-X8, Cl- form (50-100 mesh) into the column and wash down sides with water. Add 2 m1 of I carrier to 2 liters milk, stir for 20 minutes.

3. Pass the sample through the ion exchange column at a flow rate of 20 ml/ min. Save the effluent for other analyses and label it

" iodine effluent".

4. Wash column with 500 ml of hot distilled water for milk samples or 200 ml of distilled water for water samples. Discard wash.

5. Wash column with 100 ml of 2 M Nacl at a flow rate of 4 ml/ min.

Discard wash.

6. Drain the solution from the column.

7. Measure 50 ml 5% sodium hypochlorite in a graduated cylinder.

Add sodium hypochlorite to - column in 10-20 ml ' increments, stirring resin as needed 'to eliminate -gas bubbles- and maintain flow rate of 2 ~ ml/ min. Collect eluate in 250-m1 beaker and discard the resin.

B. Iodine Extraction Procedure .

!' 1. Acidify the eluate from step 7 using concentrated HNO3 to make the sample 2-3 N in HNO3 , and transfer- to 250 m1 separatory l' funnel. (Add the acid slowly with stirring until the vigorous-i reaction subsides.) Volume of concetrated - HNO3 required will

! - depend on eluate volume as follows):

104 y

4 J

. Section 3.9'(continued)

B. Iodine Extraction Procedure (continued)

. eluate volume concentrated HNO3 i

(ml) (ml) l 50-60 10 60-70. 12

, 70-80 14 80-90 16

2. Add 50 ml of CC14 ' and 10 ml of 1 M hydroxylamine hydrochloride (freshly prepared). Extract, iodine into organic phase (about 2 minutes equil.ibration).- Draw off the organic phase (lower

phase) into another separatory funnel.

3. Add 25 ml of CCl4 and 5 ml of 1 M hydroxylamine hydrochloride to ;the first separatory funnel and again : equilibrate for 2 minutes. Combine the organic phases. Discard the aqueous phase (Upper ~ phase) if no other analyses are_ required. If Pu, U or Sr is required on the same sanple aliquot, submit .the aqueous phase

!-- and data sheet to the approprate laboratory section.

4. Add 20 ml H20-HNO 3 -NH 2 0H hcl wash solution to the separa -

tory ~ funnel containing the ; CCl 4 Equilibrate 2 minutes.

Allow phases.'to separate and transfer CC14 (lower phase) to ' a clean separatory funnel.- Discard'the wash' solution.

5. - Add 25 ml H2 O and '10 drops of 1 M sodium bisulfite (freshly prepared)' to the separatory funhel containing the CC1. 4-Equilibrate for 2: minutes. Discard the organic phase (lower

phase). Drain _ aqueous phase (upper phase).into a 100-m1 beaker.

j Proceed to the Precipitation of.PdI2-

.C. . Precipitation of Palladium' Iodide.

CAUTION: AMMONIUM HYDROXIDE INTERFERES WITH THIS PROCEDURE.

i

1. . Add 10 =m1 of 3' N hcl _ to the - aqueous _ phase from the' iodine extraction procedure-in step 15~.-

~

c L _

! 2. Place the beaker on a stirrer-hot plate. - Using the magnetic

! stirrer, _bof1 'and -stir the. sample until:it evaporates to 30~ al or

. begins to turn yellow.

3. Add 1.0 : ml 'of -. 20 mg Pd++/ml palladium chloride . per ' liter of _

milk used dropwise,-to the solution.

k

(:

Section 3.9 (continued) 1 C. Precipitation of Palladium Iodide (continued)

-4. Turn the heat off, but continue to stir the sample until it cools to room temperature. Place the beaker in a stainless steel tray and put in the refrigerator overnight.

5._ Weigh a clean 21 mm Whatman #42 filter which has been stored over silica gel in a desiccator.

6. Place the weighed filter in the filter holder. Filter the sample and wash the residue with water and' then with absolute alcohol .

7. Remove filter from filter holder and place it on a stainless steel planchet.

8. Dry under the lamp for 20 minutes.

9. Cut a 1 1/2" strip of polyester tape and lay it on. a clean surface, gummed side up. Place the filter, precipitat'e side ug, in the center of the tape.

10. Cut a 1 1/2" wide piece of mylar. Using a spatula to press it-in place, put it - directly over the precipitate and seal the L- edges to-the polyester tape. Trim to about~5 mm from the edge of the filter with scissors.

11. Mount the sample on the plastic disc and write the sample number on the back side of the disc.

12. Count the sample on a proportional beta counter.

Calculations Calculate the sample activity using computer program 1131.

Reference:

" Determination of 1-131 by Beta-Gamma coincidence Counting of PdI2 ". Radiological Science ' Laboratory.- Division of Laboratories and Research, New York State Department of-Health, March 1975, Revised February-1977.-

106

.,

ML20087P396

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