ML20090D210

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Radiological Impact Assessment Rept, Jan-Dec 1991
ML20090D210
Person / Time
Site: Sequoyah  Tennessee Valley Authority icon.png
Issue date: 12/31/1991
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TENNESSEE VALLEY AUTHORITY
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ML20090D199 List:
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NUDOCS 9203060090
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i ENCLOSURE 2 SEQUOYAll NUCLEAR PLANT  :

RADIOLOGICAL IMPACT ASSESSMENT REPORT  ;

(S52 920214 088) 1 L.PDR.

9203060090.

r/20302ADOCK 05000327-PDR.

-R.

TEN!!ESSEE VALLEY AUT110RITY RADIOLOGICAL IMPACT ASSESSMENT REPORT SEQUOYAH NUCLEAR PLANT JAllUARY TIIROUGH DECEMilER 1991 Prepared by: '. LL 1/J!fSL x viewca dy: I h 4 rir 4 d a w M/> /9 A Approvedb}[ m a _ /[0, A_

I Radiological Irnpact Assessment Sequoyah Nuclear Plant j January - December 1991 t 1HTRODUCT10H -f

' potential doses to taasimum individunts and the population around Sequoyah {

are calculated for each quarter as required in the Sequoyah Offsita Dose  ;

~

Calculation Manual control 5.2. Measured plant teleases for the reporting period are used to estimate these dosos. Dispersion of radioactive ef fluent s in the environment is estimated in accordance with the guidance provided by Hegulatory Guldes 1.109, 1.111 and 1.113 using meteorological data and riverflow data measured during the period. Using  !

dose calculation methodologies which.are described in detall in the ,QH {

ODCM, the doses age calculated and used to determine compliance with the  ;

dose limits contained in Sequoyah's ODCM. In this report, the dosen +

resulting from teleason are described and compared to quarterly and

_ annual limits established for Sequoyah. _

SUMMARY

_QI_L10VID_AND_0ASE0VS E YLUENT.,EELEASES m 1991 Although nuclear plants are designed to contain the radioactive material ,

created by the fleston process, small amounts of this material escape  :

from the fuel rods. Also, very small amounts of the structures and components of t.he systems becomo activated through the bombardment of neutrons and are_ worn away. This radioactive material can be transported  ;

throughout plant systems and released to the environment.

EIIlvent_MonAtorlns l Plant paths through which radlonctivity is released are monitored. These monitors record the radiation levels for each release. Monitors which  !

are used for liquid releases will automatically alarm and stop any ,

release which-la above regulatory-limits. Gaseous release monitors also provido alarming mechanisms to allow for the termination of any release above limits.

AltbgIne_Releasun -

The noble gas (16plon products do not mix with water and are glven off in a gaseous form. A very small amount of solid redlonctivity is given off along with-these noble gases. These_ releases are_ processed so that the radioactive materici la filtered and/or decayed prior to release through the plant vents.- Sampilng-and monitoring iethods are used Lo determine ,

the amount of radioactive material released. If these methods indicate that radioactivity-in airborne offluents above preset limits, then i releases _are. terminated. ,

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SQN Rad Impset Jan-Dec 1991 Page 2 of 36 Liquid Feleones Some small amounts of radioactive material migrate Anto the primary coolant water. The primary coLlant water la routed through a purification system to remove most of these particles; however, not all are removed. Some of the radioactive liquids may leak from pipes or valves in the system. These liquids are collected in floor and equipment drains and sumps. The collected liquids are then processed through a clean-up system, composed of storage tanks, recycling systems, and dominera11sers, to temove contaminants. The purifled water is then monitored to dete:mine the nmount of radioactive material remaining in the water prior to its release. Steps are taken to ensure that the amount of radioactivity released to the environment is as low as reasonably achievable (ALARA). If the levels of radioactivity are above preset limits, the releases are circulated through the clean-up system again for additional processing. All radioactivity released from the plant into the Tennessee River is quantitled prior to release.

D'JS A'_ LIMITS The U.S. Nuclent Regulator Commission (HRC) requires nuclear power plants to be designed, built, and operated in such a way that the levels of radioactive material released into unrestricted areas is as low as reasonably achievable (ALARA). To ensure that this is done, the plant's operating license includes requirements for Controls which govern the release of radioactivity. These Controls, contained in the Sequoyah ODCM, specify limits for the release of radioactive effluents, as well as limits for doses to the general public from the release of these effluents. These limits are set well below the NRC 10 CFR 20 limits which govern the concentrations of radioactivity and exposures permissible in unrestricted areas. This ensures that radioactive _

effluent releases are ALARA.

The ODCM limits for doses at or beyond the site boundary from airborne noble gases releases are Less than or equal to 5 mrad per quarter and 10 mrad per year for gamma radiation,

- and -

Less than or equal to 10 mrad per quarter and 20 mrad per year for beta radiation.

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SQH kad Impact Jan-Dec 1991 page 3 of 36 The ODCM limit for the dose to a member of the general public at or beyond the site boundary from lodines and particulates released in airborne effluents ist Less than or equal to 7.5 stem per quarter and 15 mrem per yect to any organ.

The ODCM limit for doses to a member of the general public from radioactive material in liquid effluents released to unrestricted arens, 1st Less than or equal to 1.5 mrem per quarter and 3 mrem por year to the total body,

- and -

Less than or equal to 5 mrem per quarter and 10 mrem per year to any organ The epa limits for total dose to the public in the vicinity of a nuclear power plant, established in the Environmental Done Standard of 40 CFR 190, aret Less than or equal to 25 mrem per year to the total body, Less than or equal to 75 mrem per year to the thyroid,

- and -

Less than or equal to 25 mrom per year to any other orgaa.

DDSE_CALCULAT10FS Estimated doses to the public are determined using computer models (the Gaseous Effluent Licensing Code, GELC, and the Quarterly Water Dose Assessment Code, QWATA). These models are based on guidance provided by the NRC (jn Regulatory Guides 3.109, ? ;'l and 1.113) for determining the potential dose to individuals and populations living in the vicinity of the plant. The area around the plant is analyzed to determine the pathways through which the public may receive a dose. The doses calculated are a representation of the dose to a " maximum exposed individual." Some of the factors used in these calculations (such as ingestion rates) are maxiK2m values.

Many of these factors are obtained from NUREG/CR-1004 The values chosen will tend to overestimate the dose to this " maximum" person.

In reality, the expected dose to actual individuals is lower. The 0017v

S9N' Rad Impact Jan-Dec 1991 Page 4 of 36 calculation methods-and results of the calculations are presented in the fol owing sections.

pj)SES FROM AIREQRtifLEErl.UKRIS Tor airborne effluents, the public can be exposed to radiation from se'reral sources direct radiation from the radioactivity in the air, direct radiation from radioactivity depesited on the ground, innalation of airborne radioactivity, ingestion of-vegetation which contalnu radioactivity deposited from the atmosphere, and ingestion o'.' milk cod beef which contains radioactivity deposited f rom the acnosphere onto vegetation which is then eaten by milk and beef animals, The concentrations of radioactivity in the air and the soll are estimated by the computer model GELC which uses the actual meteorc;ogical conditions to determine the distribution of the effluents in the atmosphere. Again, as many of the parameters as

.possible are based on actual site specific data. The model that is used to estimate dose, as well as the' parameters input to the model,

-in-described in detail in Section 7.0 of the Seguoyah Nuclear Plant Offsite Dose Calculation Manusl.

Airborne Releamg_2plnts atd Meteorological Data Meteorological-data at Sequoyah are measured continuously.

Measurements collected include the wind speed, wind direction, and the. temperature at heights of 10, 46 and 91-meters above the ground. Average quarterly joint frequency distributions (JFDs) are calculated for each release point using the appropriate levels of

.meteorslogical data. A joint frequency distribution gives the perceslage of the cime in a quarter that the wind is blowing out of a particular upwind compass sector .in a particular range of wind speeds for a given stability-class A through G. The wind speeds are divided into nine wind speed ranges.- For calculational purposes, calms are distributed into the lowest windspeed' range (0-0.5 mph) according.to the directional probabilities in the 0.6-1.4 mph rango. Stability classes are determined from the vertical temperature gradient between two measurement levels.

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Ai SQN Rad Impact Jan-Dec 1991 Page 5 of 36 4

--All releases from Sequoyah are considered ground-level releases to determine-the dispersion of the airborne effluents. The

. ground-level JTD is-derived from windspeeds and directions measured 10 meters above-ground and from the vertical temperature gradient between 10 and 46 meters.

The JFDs for each quarter of 1991 are listod in Tables 1, 2, 3 and 4.

~Kxtenlal XKposure Dole - Airborne Efflugntg Dose estimates for: maximum external air ex* c c: rc i (gamma-air and beta-air doses)-are made for points at auf i a'; o the site boundary...These doses are c 'cu)e69d ba6"" 1 the reported releases

-for all noble gas nuclides. :Tn; eported dose is chosen for the offsite location with the highest calculated exposure during the quarter. The doses calculated for Sequoyah Nuclear Plant for each quarter in 1991 are'as shown below.

Individual Doses from Airborne Effluents External Air Exposures (mrad)

Dose _ E ssligIt_

First Quarter 19911 Ly Air dose- 1.5E-02 mrad SSW at 1840 meters a Air dose 4.2E-02 mrad SSW at 1840 meters Second Ouarter 1991 Y Air dose '2.6E-02 mrad -N at 950 meters

.B Air. dose- 7.3E-02 mrad N at 950 meters Third Ouarter 1991 y Air dose 5'7E-02 mrad S at 1570 meters B-Air dose 1.5E-01 mrad S at 1570 meters f_gy.Ith Ouatte r 1991'-

y Air dose 2.5E-02 mrad NNW at 730 meters D Air dose 5.2E-02 mrad NNW at 730 meters l

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SON Rad Impact Jan-Dec 1991 Page 6 of 36

-Subm n alDR_ Dale - Airborng_Effinenta External doses to the skin and-total body, due to submersion in a cloud of. noble gases, are estimated for the nearest residence in each sector. These doses are chlculated based on the reported releases for noble gas nuclides. The highest of these exposures is chosen and is assumed to be the maximum individual dose. The submersion doses calculated for Sequoyah Nuclear Plant for each

. quarter in 1991 are as shown below.

Individual Doses from Airborne Effluents Submersion Exposures (mrem)

_pgig_ Location _

  • itat Ouarter 1991 Total Body 1.1E-02 mrem SSW at 2019 meters Skin 2.6E-02 mrem SSW at 2019 meters Sgngnd_Qurter 1991 Total-Body 1.3E-02 mrem N at 1353 meters Skin 3.1E-02 mrom N at 1353 meters Third Quatter 1991 Total Jody 3.6E-02 mrem SSW at 2019 meters Skin 8.2E-02 mrem SSW at 2019 meters hurth Ouarter 1991 Total Body 1.8E-02 mrem SSW at 2019 meters Skin- 3.8E-02 mrem SSW at 2019 meters b

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S9N Rad Impact Jan-Dec 1991 Page 7 of 30 QLgan Dose - AlIbarDD_KUlManta f

LInternal doses to organs due to releases of airborne effluents are estimatec_'or the inhalation, ground contamination, and ingestion pathways._ The ingestion pathway is further divided into four possible contributing pathways ingestion of cow /guat milk, ingestion of beef, and ingestion of vegetables.- Doses from applicable pathways are calculated for each real receptor location defined in Table 5. Doses are calculated based on the reported iodine and particulate releases. To determine the maximum organ dose, the dose contribution from the three pathways are summed for each receptor. For-the ingestion dose, however, only those pathways that exist for each receptor are considered in the sum, i.e.,

milk ingestion doses are included only for farms where milk is consumed without commercial preparation and vegetable ingestion 2s included only for those locations where a garden is ' identified. To conservatively account for beef ingestion, a beef ingestion dose equal to that for the highest site boundary location is added to each identified receptor. For ground contamination, the dose added to the organ dose being calculated is the total body dose calculated for that location, i.e., it is assumed that the dose to an individual organ is equal to the total body dose.

The organ doses calculated for Sequoyah Nuclear Plant for each quarter in 1991 are shown below.

Individual Doses from Airborne Effluents Maximum Organ (mrem)

_QIgan_ Age _GIAMP- _DORA_

First Oggiter 1991 Liver- Child 5.0E-04 mrem Individual Pathway Contributions:

Vegetable Ingestion 1 3.4E-04

_ Beef Ingestion 2 3.3E-05 Inhalation 1 1.3E-04 Ground Contaminationl'6.0E-07 Milk Ingestion N/A 3 Maximum real receptor is located at 2686 meters in the SSW sector.

2 Calculated for the site boundary at 1840 meters in the SSW' sector.

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SQN Rad Impact Jan-Dec 1991 Page 8 of 36 Individual Doses from Airborne Effluents (Continued)

Maximum Organ (mrom)

_QIg AD.. _hge_SLOUP_ _DQEC_

SeconLiluatter_1191 Thyroid Child 4.0E-03 mrem Individual Pathway Contributions:

Vegetable Ingestion 3 2.6E-03 Beef Ingestion 4 3.7E-04 Inhalation 3 9.6E-04 Ground Contamination 3 1,4g_o7 Milk Ingestion N/A 3Maximum real receptor is located at 991 meters in the NNW sector.

4 Calculated for the site boundary at 950 meters in the N sector.

Ihl1QROr.ttt._119.1 Thyroid Child 3.5E-03 mrem Individual Pathway Contributions:

Vegetable Ingestion 5 2.6E-03 Beef Ingestion 6 2.0E-04 Inhalation 5 6.9E-04 Ground Contamination 5 3.7E-06 Milk Ingestion N/A SMaximum real receptor is located at 2362 meters in the S sector.

6 Calculated for the site boundary at 1570 meters in the S sector.

EQMtth_0MoltRI_1911 Thyroid Child 1.7E-02 mrem Individual Pathway Contributions:

Vegetable Ingestion 7 1.1E-02 Beef Ingestion B 9.4E-04 Inhalation 7 4.6E-03 Ground Contamination 7 6.6E-04 Milk Ingestion N/A 7 Maximum real receptor is located at 991 meters in the NNW sector.

O Calculated for the site boundary at 730 meters in the NNW sector.

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SOM Rad Impcct Jan-Dec 1991 Page 9 of 36 D9mE_SMIgnJltry . .. AirbnInc_Killutnia The table below gives a comparison of the calculated doses for 1991 to their respective quarterly limits.

Doses from Airborne Effluents - 1991 Sequoyah Nuclear Plant Quarterly Percent of P_ome Pathv.Jy Quatttt Donn __Limil_ .

Limit __.

Airborne-Janma air Dose 1 1.5E-02 ' rad 5 mrad < 1%

2 2.6E-02 mrad <1%

3 5.7E-02 mrad 1%

4 2.5E-02 mrad < 1%

Airborne-Beta air Dose 1 4.2E-02 mrad 10 mrad < 1%

2 7.3E-02 mtad < 1%

3 1.5E-01 mrad 2%

4 5.2E-02 mrad < 1%

-Airborne-Max Orgsn Dose 1 5.0E-04 mrem 7.5 mrem < 1%

2 4.0E-03 mrem < 1%

3 3.5E-03 mrem < 1%

4 1.7E-02 mrom < 1%

-As is shown.by the table, all calculated quarterly doses were well below the-allowable limits established in Sequoyah's ODCM. -A compar" son of the doses since 1983 is presented by gaarter in

' Table 6.

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. SON Red Impact Jan-Dec 1991 Page 10 of 36 DQEEE_IROM h10UID_EELUEETE Tor liquid effluents, .the public can be exposed to radiation from three sources:

the ingestion of water from the Tennessee River, the ingestion of fish-caught in the Tennessee River, and direct exposure from radioactive material deposited in the river sedinant (recreation).

The concontrations of radioactivity in the Tennessee River are

-dstimated by a computer model which uses measured hydraulic data downstream of Sequoyah. Parameters used to determine the doses are based on guidance given by the NRC (in Regulatory Guides 1.109) for maximum ingestion rates, exposure times, etc. Wherever possible, parameters used in the dose calculation are site specific use j -factors determined by TVA. The models that are used to estimate

, doses, as well as the parameters input to the models, are described in Section 6.0 of the Sequoyah Nuclear Plant Offsite Dose

_ Calculation Manual.

Ligyld Release Points and Rive.I_DALA 2

Radioactivity concentrations in the Tennessee River are calculated assuming that releases of liquid effluents are continuous. All routine liquid releases'from Sequoyah are made through-diffusers which extend into the Tennessee River. It is assumed that releases to the river through these diffusers will initially be entrained in one-fifth of the water which flows past the plant. The QWATA code makes the assumption that this mixing condition holds true until the water is completely mixed at the first downstream dam, at Tennessee River milo 471.0. The average river flows past the plant site were 57,536 ft 3 /s for the first quarter of 1991, 28,775 ft 3/s for the second quarter of 1991, 32,101 ft3 /s for the third quarter of 1991 and 45,329 ft 3 /s for the fourth quarter, l'

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SON Ra6 Impact Jan-Dec 1991 Page 11 of 36 ECtse_ Estimates - Liquisl_Elilutata Doses are calculated for recreation, consumption of fish, and drinking water for. locations between the plant site and the mouth of the Tennessee River. The maximum potential recreation dose is calculated for a location immediately downstream from the plant outfall. The maximum individual dose from ingestion of fish is assumed to be that calculated for the con- stion of fish caught anywhere between the plant and the first downstream dam (Chickamauga Dmn) . The maximum individual dose from drinking water is assumed to be that calculated at the nearest downstream public water supply (C. F. Industries). This could be interpreted as indicating that the maximum individual, as assumed for 11guld releases from Sequoyah, is an individual'who obtains all of his dr!nking water at C..F. Industries,. consumes 21 kg (6.9 kg for a child) per year of fish caught from the Tennessee River between Sequoyah and Chickamauga Dam, and spends 500 hours0.00579 days <br />0.139 hours <br />8.267196e-4 weeks <br />1.9025e-4 months <br /> per year standing on the shoreline just below the outfall from Sequoyah. Dose estimates for the maximum individual due to liquid effluents for 1991 are presented below.

Individual Doses from Liquid Effluents (mrem)

_QLg DIt_ Age Group ,_D(ttit,

. E1Lat_Qgart e r 1991 Total Body Adult 3.2E-03 mrom Individual Pathway Contributions:

Water Ingestion 5.8E-04 Fish Ingestion -2.1E-03 ,

Recreation 5.1E-04 Liver Adult 3.9E-03 mrem Individual Pathway. Contributions:

Water Ingestion 5.9E-04~

Fish 1 Ingestion 2.8E-03 Recreation: . 5.1E 0017v v -** em ,.

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SON Rad Impact Jan-Dec 1991 Page 12 of 36 Individual Doseb from Liquid Effluents-(Continued)

(mrem)

Sicond_0uarter 1991- Total Body Adult 9.5E-03 mrem Individual Pathway Contributions:

Water Ingestion 1.3E-03 Fish Ingestion 5.8E-03 Recreation 2.4E-03 Liver Adult 1.2E-02 mrem.

Individual Pathway Contributions:

Water Ingestion 1.4E-03

^

Fish Ingestion 7.9E-03 Recreation 2.4E-03 ,

Third Ouarter 1991 Total Body Adult 1.2E-02 mrem Individual Pathway Contributions:

Water Ingestion 1.3E-03 Fish Ingostion .8.2E-03 Recreation 2.3E-03 Liver Adult 1.5E-02 mrem Individual Pathway Contributions:

Water Ingestion 1.3E-03 Fish Ingestion 1.1E-02 Recreation 2.3E-03

'Equrth Guarter 1991 Total Body ~ Adult 1.6E-02 mrem Individual Pathway Contributions:

Water Ingestion 9.1E L Fish Ingestion 1.3E-02 Recreation 1.7E-03 Liver Adult 2.1E-02 mrem Individual Pathway Contributions:

Water Ingestion 9.5E-04 Fish Ingestion 1.8E-02 Recreation 1.7E-03 0017v

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S9N Rad Impact-Jan-Dec 1991-Page 13 cf 36 DARB_ Summary - Lignid_Elfluents The table below gives a comparison of the calculated doses for 1991 to their respective quarterly limits.

__ +

Doses from Liquid Effluents - 1991 Sequoyah Nuclear Plant Percent of Quarterly Quarteily D.gse Pathway Quprter Dann ___ Limit LLrg t Liquid-Total Body Dose 1 3.2E-03 mrem 1.5 mrem < 1%

2 9.5E-03 mrem < 1%

3 1.2E-02 mrem < 1%

4 1.6E-02 nrem 1%

Liquid-Max Organ Dose 1 3.9E-03 mrom 5 mrem < 1%

2 1.2E-02 mrem < 1%

3 1.5E-02 mrem < 1%

4 2.lE-02 mrem <1%

As is shown by the table, all calculated quarterly doses were well

-below the allowable limits established-in Sequoyah's ODCM. A l- . comparison of,the doses since 1983 is presented by quarter in Table 6.

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SON Rad Impact

!? Jan-Dec 1991 1

, Page 14 of 36 RDEULhIl0H_DDEES  :

Population doser for highest exposed organ due to airborne effluents

- are calculated for an estimated 1,060,000 persons living within a.

50-mile radius of the plant site. Ingestion population doses are calculated assuming that each individual consumes allk, vegetablesi and meat produced with'the sector annulus in which he resides.

' Doses from external pathways and inhalation are based on the 50-mile

- human population distribution. Population dose est.8 nates for airborne ef fluent.s are presented below.

From_ liquid releases during 1991, the total population along the Tennessee River.was estimated to receive population doses as shown below.

SSERQyAh_Ruclger Plant EOPMAAtion Dolca - }j.91 Total Body Dose Maximum Organ Dose (organ) '

Eiyst Ouarter__1991 Liquid 8.3E-02 man-rtm 8.7E-02 man-rem (livet i Airborre 6.8E-02 man-rem 6.8E-02 man-rem (liver)

Second Ouartar 1991 Liquid 3.3E-01 man-rem 3.4E-01 man-rem'(liver)

Airborne 6.9E-02 man-rem 6.9E-02 man-rem (thyroid)

Third Ouarter 199.1 Liquid 3.8E-01 man-rem 4.0E-01 man-rem (liver)

Airborne 1.6E-01 man-rem 1.6E-01 man-rem (thyroid) l EgnIth Ouarter 1991 I'

Liquid 2.0E-01 man-rom 2.3E-01 man-rem (Liver)

Airborne 2.0E-01 inan-rem 2.1E-01 man-rem (Thyroid) 5

' Population doses can be compared to the natural background dose to the

- same population of about 159,000 man-rem /yr (Based on 150 mrem / year for natural background.).

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L SQH Red Impact Jan-Doc 1991 Page 15 of 36

- DIRECT RADIAIIDH External gamma radiation levels were measured by thdrmoluminescent dosimeters (TLDs) deployed around SQN. During the preoperational period from August 1975 to January 1980, these levels averaged approximately 23 mR/ quarter at onsite stations and 19 mR/ quarter

.offsite. These higher values measured onsite may be attributable to natural variations in environmental radiation levels, earth moving activities onsite, the mar:s of concrete employed in the construction of the plants, or other undetermined influences.

Analysis of environmental TLD data for the period of November 1990 to November 1991 showed that the cuar'.erly gamma radiation levels determine 6 from these TLDs during this reporting period averaged approximately 14.4 mR/juarter at onsite stations and approximately

'12.6 mR/ quarter at offsite. stations. This is consistent with levelp reported at.TVA's nonoperating nuclear power plant construction sites where the average radiation levels onsite are generally 2-5 mR/ quarter higher than the levels offsite. Fluctuations in natural background. dose rates and in TLD readings. tend to mask any small increments which may be due to plant operations. Thus, there

.w as no identifiable increase in done rate levels attributable to direct radiation from plant equipment and/or gaseous ef fluents.

DQSE TO ME@HS._QLT11E PUBLIC INSIDE THEJIIE BOUllDhEX No routine' activities within the site boundary by. members of the public have been identified which would lead to their-radiation exposure.

191AL_DQE LTo determine compliance with-40 CFP, 190, annual total dose

-contributions to the maximum individual from SON radioactive effluents and all other nearby uranium fuel cycle sources are considered.

The annual total body dose to the maximum individual is conservatively estimated by summing the following doses the total body air submersion dose for each quarter, the critical organ dose from a.rborne effluents for each quarter, the total-body dose from liquid effluents for each quarter, the maximum organ dose from liquid effluents for each quarter, and 0017v i

SON Rad Impact Jan-Dec 1991 Page 16 of 36 any identifiable. increase in direct radiation dose levels as measured by the environmental monitoring program.

.This dose is compared to the limit for total body or any organ dose (other than thyroid) to determine compliance.

The annual thyroid dose to the maximum individual is conservatively -

estimated by summing the following dosest the total body air submersion dose for each quarter, the1 thyroid dose from airborne effluents for each quarter, the total body dose from liquid effluents for each quarter, the thyroid dose .f rom liquid effluents for each quarter, and any identifiable increase in direct radiation done levels as measured by'the environmental monitoring program.

This dose is compared to the limit for thyroid dose to determine compliance.

Total Dose from Fuel Cycle - Calendar Year 1991 Segouyah Nuclear Plant

__ Dose _ First Second Third Fourth Quarter Quarter Quarter Quarter IDialf Body or RDy_Q19M.J1QH (except. thyroid)

Total _ body air submersion dose 1.1E-02 1.3E-02 3.6E-02 1.8E-02 Critical organ oose (airborne) 5.0E-04 4.0E-03 3.5E-03 1.7E-02 Total body dose (liquid) 3.2E-03 9.5E-03 1.2E-02 1.6E-02 Maximurn organ dose (liquid) 3,9E-03 1.2E-02 1.5E-02 2.1E-02 Direct radiation dose 0.0E-00 0.0E-00 0.0E-00 0.0E-00

-Total 1.9E-02 3.9E-02 6.7E-02 7.2E-02 Cumulative Total Dose (Total Body or other organ) 2.0E-01 0017v J

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S9H Rad Impact ,

/ s-; Jan-Dec 1991 Page 17 of 36 Total Dose from Fuel Cycle - Calendar Year 1991 Segouyah Nuclear Plant Dose First Second Third Fourth Quarter Quarter Quarter Quarter

.Thyrcid Dosa-

. Total body air submersion dose 1.1E-02 1.3E-02 -3.6E-02 1,8E-02 Thyroid dose (airborne) 4.9E-04 4.0E-03 3.5E-03 1.7E-02 Total body dose (liquid) 3.2E-03 9.5E-03 1.2E-02 1.6E-02 Thyroid dose (liquid) 1.3E-03 4.2E-03 4.9E-03 3.3E-03 Direct radiation dase 0.0E-00 0.0E-00 0.0E-00 0.0E-00 Total (Thyroid) 1.6E-02 3.1E-02 5.6E-02  :, . 4 E -0 2 Cumulative Total Dose (Thyroid) 1.6E-01 i

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SQN Rad Impact Jan-dec 1991 Page 18 of 36 CONCLUSIDH-As a result-of operation of Sequoyah Nuclear Plant, radioactive effluents were released to the atmosphere and the Tennessee River.- The released radioactivity resulted in estimated potential doses to the public which are well below the ODCM Limits and Regulatory Guidance. Cumulative doses for the calendar year are given below along with a compar3 son _to the respective annual limits for the doses.

Cumulative Doses from Effluents Soquoyah Nuclear Plant Percent of Annual Anr.dal Dag.e Pathny prig kLm_Lt_ J Jmit Airborne-Gamma air Dose 1.2E-01 mrad 10 mrad 1%

-Airborne-Beta air Dose 3.2E-01 mrad 20 mrad 2%

Airborne-Max Organ Dose 2.5E-02 mrem 15 mrem <3%

Liquid-Total Body Dose 4.1E-02 mrem 3 mrem 1%

Liquid-Max Organ Dose 5.2E-02 mrem 10 mrem < 1%

Total Deze - Total Body 2.0E-01 mrem 25 mrem < 1%

or organ other-than_ thyroid Total Dose - Thyroid 1.6E-01 mrem 75 mrem < 1%

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Jan-Dec 1991 1 Page 19 of 36 TABLE 1 (page 1 of 4)

SEOuGYAILNUCLEAR PLAJIT_.METEQRQLQGICAL_. RATA fjftST OUARTER_1.911 JQ.DTT FREQUEHCLDlEIRIBUTION_ IN PERCIHI EQR GROUHP-LEVEL EELEASIS JOINT PIDCENT Att PPR00tNClit or wir0 SPtFD OT WIND O!9tCTteN ree OTAotLITV CLA80 A (CELTA T a e-4.0 C/100 al astueTAN NvCLEAA

  • tat.

JAs -1, 91 - MA3 31, el

-WIND wlND AFTEDlMPR)

  • =?4.1 T l+12.4 12,5-10.4 10.9-24 4 total 0:st:T!cu CALM - 0 0+1 4 1 1-1;4 $.$-l.4 5.1 1.4 0.0 0.0 0.011 0.404 0.0 0.0 0.0 0.451 N 0.0 0.0 0.0 0.0 1.101 -

NNE 0.0 0.0 0.0 0.0 0.304 0.063 0.0 0.0 0.0 0.0 tiill 0 192 0.152 G0 0.0 0.0 9.441 NS st 0,0 0.0 0. 0 - 0.0 0.0 0.0 0.0 0.0 rgt 4.0 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 t 0.0 0.0 0.0 0.0$l 0. 0 0.0 0-0 0.0 0.0 0,0 0.084 8., 00 0.0 0.0 0.181 st 0,0 0,0 0.0 0.101 0.0 0.0 0.0 0, ell 0.0 0.0 0.0- 0,401 058 8.0 5.0 0.0 0.0%I 0-0 0.0 0.0%1 0.108 0.0 0.0 0.0 0.452 5 00 0.0 - 0.0 0,0 0.0 4 424 SSw 0. 0 - 0.0 0.05L 0,051 0 840 0.600 0.0 0.0 0.0 0.0 0.152 0.254 0.203 0.0 0.0 0,0 0.000 sw wsw 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0$1 0. 0 - 0.0 0.0 0,0 0.* 0.8 0.051 w 0.0 W4w 0.0 0.0 0.0 0.0 0.091 0.400 0.0 0.0 0,0 0 4$1 Nw 0,0 0.0 0.0 0 ,4 0.051 0.152 0.051 0.0 0.0 0.264 0,0 0.0 0.0$1 0.194 0.0 0,0 0.0 0.30)

NNw 0.0 0.0 0.152 1.434 3.140 0.0$4 0.0 0.0 5.4TO -

DVOT4TAL- 0.0 0.0 0.!07 TcTAL NSVas OF WAL30 OTAsTLITY castavAT3ous 3424 100 TOTAL hoV04 0F STA43LITT CLASE A 100 TOTAL NOUta 0F WALID wt0** CistcTt0N.wiWD $9EED-sTA0!LITT class A TOTAL Routs et TALIS wtha 018tCT803-wlND GFEED ST ASIL%TV 09358VATIONS 1911 0 TOTAL route 4 ALM STASILast Lass 0 1 6.04 DELTA-t4e-4.1 C/100 m) 889VOTAN NUCLEAR PLANT JAN 1, 91 y MAR 31 GL WIND- w!ND SPttbtMPN) p!0tcT!cN - CALM 0,6.t.4 3.S.1 4 3.5 5,4 5 5-1.4 T 5-13.4 12 5-10.4 18.5-14.4 5 14.5 g N 0.0 0.0 0.0 0.0 0.051 0.101 0.0 0.0 , 0.112 NNT ~ 0.0 0.0 0.081 0.304 0.314 0.303 0.051 0.0 03 0.00) 31 0.0 0.0 0.051 0.355 0.0 0.051 0.0 0,4 0.0 0.4$1 INE U.0 0.5 0,053 0.104 0.0$1 0.0 0.0 0.0 0.0 0 20) t 4.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 Est 0.0 0.0 8.101 0.051 0.0 0.0 0.0 00 0.0 0 451 st 0.0 0.0 0.051 0.101 0.0 0.0 0.0 0.0 0.0 0.153

$$1 0. 0 . - 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 5 . 0.0 0.0 0.0 0.058 0.201 0.051 0.0 0.0 0.0 0.304 Asw 0.0 0.0 0.0 0.101 0.2?4 0.20) 0.0 0.0 0.0 0.550 Sw 00 - 0. 0 0.101 0.104 0.141 0.0 0.0 0.0 0.0 0.300 wsw 0.0 0.0 0.0 0.0 0.054 0.011 0.0 0.0 0.0 0.101 W '0.0 0.0 0.0 0.0 0.0 0.054 S.0 0.0 a.0 0.051 www 0.0 0.0 0.0 0.0 0.0 0.051 0.0 0.8 0.0 0.051 Nw 0.0 0.0 0,0 - 0.0 0,0 0.355 .0.0 0.0 0.0 0,355 N ww 0.0 0.0 0.0 <

0.0 0.101 0.051 0.0 0.0 0.0 0.153-SV070TAL 4.0 0.0 0.400 1.181 1.06S 1.167 0.051 0.0 0.0 3.05a l

taTAL m3Ups of VALIO STAa ttITV nB A ERVAT10N0 2124 TOTAL MOURS OF STAtt(ITY CLASS 9 19 TOTAL N0025 of VALt B w!ND D!BICTION-WIND $7 TID-STA3 tLITT class 0 . 10 TOTAL EnVR$ OF VAL 10 wtNO 010tCT30N wtRD $PERD-STAS!LITT USSERVATICNS 1811 TOTAL NOUS $ CALM 0 METEct0 LOG 3 tAL F AC!LITT t SEQUOTAN NUCLTAR PLANT STA0!L2fT SASED ON LAP 55 BATE ME ASL'atD SETwEtN 0 25 AND t$.09 PETIB3 w!N3 SF8tD AND O!RtCTION MEASDMgp AT THE 9,13 METES LEV 5L DATE PRINTIC 04/J6/04 MEAN w!ND 5P513 a 6.7 MPs N3'f t TOTALS ASD SV070tALS A30TE A31 05f AINIO FRGM 95ROUNDE0 NUMBER $

SQN Rad Impact Jan-Dec 1991 Page 20 of 36 TABLE 1 (page 2 of 4)

SEQUOYMLMUCLEAR. RMT_ MET 110ROL.0GICAL_PATA flBST_QUMTER.1991 J0lFLfE QU E N CLDIST R11tHT19L1RJEE CE MI hb h. E

{0 INT PtSctRTauf FDtyCMfitt OF WINfa y TED S f wl Nt* ${DECTION F00 gTAgtLITY CLAS4 C i-4 14 lettta-74.-l.l C/100 m) sCQV01Ah FULLRAR PLANT 2aN 1, 91 - MAh 11. 91 y;gg WIND AFEEp(hrH) 1.3 '4 I 9-13'4 li 9'II 4 l '_1.g i.74 1 TM AL ft9ttff0w c A g.M 0 6-1 4 1 9-14 1 6-5 4 0.0 0.0 0.201 0 152 0.0 0 0 0.0 8.)il M 0.0 0.0 0.21a 0.153 0.051 00 0me 6 012 NM8 00 0.0 0.162 0.201 0.13e 0.152 0.550 0.0 0.0 00 0.0 0.0 Nt 0.0 0.0 0.0 0.203 0 011 0.0 0.0 0.0 0.0 0.0 0.294 tut 6.0 9.354 0.0 0.254 0.0 0.0 0 0 0.0 0.0 0.0 5 0.0 0,051 0.8 0.014 0,0 0.0 0 0 0.0 0.0 0.0 ist 0.0 0.462 52 0.0 0,0 0.011 0,101 e.0 00 0.0 0.0 0 0 0.0 0.t 0.0 0.0 0.0 0.0 0.0 00 f.0 est 0 0 0.0 0.0 0,101 0.051 0.051 0.0 0.0 0.0 0.308

$ 0.0 0.0 0.051 0 .3 0.254 0.idt e0 0.0 0.G 0.lle Esw 0.0

$w 0.0 0.0 0.0 0.152 0 104 t.101 C.0 0.0 0:0 0 lle 0.0 0.4 0.0 0.0 0.0 0.0 0.0 0o 0.0 wsw 0.0 0.0 0,0 0.0 0.0 0 3 0.0 0.0 v 6.0 0.0 0 0 0.0 6.0 0.603 wNw 0.0 0.0 0.0 0.9 a 0 0.101 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 06 0.0 Nw 0.0 e llt 0.0 0.0 0 i01 0 101 9.152 0.0 00 0.0 FNw 0.0 supt 0TAL 4.0 0.0 0,313 1.411 1.06% 0.44) 0,051 0.0 0.0 4.301 TOTAL NOUSE Of VALIO ATA8ILITY 09589 VAT!0NE 2124 80 TOTAL 30488 0F STABILITV CLAS$ C 04 TOTAL NOUSS Of VALIO w!nD 9tatCT80s+wtWe Sit:0-sTAatf4TY CLA48 C TOTAL ROURS OF WALID wtN8 DID8CT10N+w3AD SPEED-8TAllLITY 09stsVAT10NS left 4

TOTAL NOUse fALn MINT PERPfMTA93 F7f QVf F f t f OF WIPD GPft0 ST wtWC OlbtfTION Fep CTASILITd 6LA50 t (*L.3, tiLTA+T**-0.5 c/lat n)

S E Q US A R NVCLEAR PLANT JAN 1 91 - MAR 31 91 w!ND WIND 3PEEDiMpu}

StpttTT04 CAL 4 0 4-1.4 1 5-1.4 3.1 1.4 1,9-1 4 1 1-17.4 12.1-14.4 13 5 24.4 . 34.g yetAL N 0.004 0.141 1.319 0.141 1.524 1.219 U,051 0.0 0.0 1.105 ENE 0.004 0 101 1.065 1.616 1.319 1.514 0.104 0.0 0.0 $.943 Nt 0.006 0.0 0 463 0.5 1 0.101 0.101 0 i. 0.0 0.0 1.l'10 tNE O=003 0.051 0.40s 0.0 00 0.0 0.9 0.0 00 8.469 5 0.001 0.0 0.203 0.s 0.0 0.0 0,0 0.0 0.0 0.304 tst 0.061 0.0 0.104 0.0 0,0 0.0 0.0 0.0 0.0 0.102 st 0.003 0.0 0.051 0.0 0.0 00 0.0 a.0 0.0 0.011 sst 6.001 0.0 0,254 0.051 0.0 0.0 0.051 s.0 0.0 0,351 8 0.004 0.141 0.518 0.161 0.20) 0.501 0.051 0.0 0.0 2.155

$sw 0.000 0.051 1.110 2,140 1.471 1.01% 0.054 0.0 0.0 4.10) 8W 0.041 0.014 1.240 4.110 0.164 0,101 0.0 0.0 0.0 4.llt w$w 0.002 0.051 0.25% 0.$0? 0 152 0.35% 0. Sit 0.0 00 1.414 W 0.001 0.0 0.201 0.404 0.152 0.254 0.0 0>0 0.0 3.016 www 0.001 0.0 0.101 0.457 0.201 0.101 0.0 0.0 0.0 1.369

  1. W 0.401 0.0 0.201 0.013 0.91) 1.015 0.0 0.0 0.0 2,911 RNw 0,002 0.0 0.lil 4 015 1.919 0.t63 0.0 0.0 0.0 4.J17 JuBTCTAL 4.051 0,501 8.616 11,114 0.018 1.712 0.115 0.0 0.0 11.291 I

TOTAL N00** 9F VA',Ik STABILITY OD$t3 VAT 10N5 2114 tat AL M9 '5 - of STABILITY class 0 til TOTAL ROURS OF WALID WIND DIRECT 10N-WINL $ PEED-STASILITT CLA85 D lit I TOTAL 43Ups 0F VALID WINp platcT!cm wlaD S PEED-5fA51 LITY OD5ENVATIONS 1971 TOTAL NOWpl CALM 1 I

l Rttt090 LOG 1:AL F A I t.! T Y 2 55QUOYA4 N'J'LEAA FLANT STA5!Liff Salt 0 ON LAF5t Raft MEAsUptD BETwEtm 3.11 An; 45.99 METEPs w!ND GPEED AND !!RECil0S NEASUSED AT THE 1.11 METta LEVE L CATE FBINTtt 04/26/1i MEAN w;N3 SPEED e 1.1 M7n 50186 TOTALS AND SUDTOTALS AbOVE A88 OST AINED F80M UWA0VNptD svnstas

SON Rad Impact Jan-Dec 1991 Page 21 of 36 TABLE 1 (page 3 of 4)

S E QUQY AILUUCL E ALMAHL MET E OR0kQG LC % _ D AT A FIRSI_ QUARTER _1991 dQIt[TEQuHCLMSTMDUTIQHllLNECEFI f.0R_GROUFD LEVIk_ RELEASES P f RT PiprtWTAGE FPtgu g itt oF Win,p sptt) e LW g ittltffen Pot STASILITV CLAst t t-4 be Dtt.TA-Teo 1.6 C/100 MB StqWT AM N U " L t i. A PLANT ,

5 .,5 I JAN 1. 11 + MA9 11, 91 j' W180 W1PB SittttMFM) le S-24 4 .=24.6 TSTAL h

g  ?

t!necttre cAlw e 6-1.4 1=%-1 4 3 %,%-4 t %,1 4 1.1-1J 4 13 l-19 4 u 4.006 0-153 1.622 9.91) 0 sto 0.161 0 0 0.0 c.a 3.401 3 NNt NE c 008 O 002 0.355 0.316 3.Is2 0 llt 1 314 0 , '. 51 0.151 0.C11 s.st; 0.0 s.0 L.0 0.0 0.0 0.0 0.0 4.;1*

e.814 \ ,.M,p.

(Nt 0.001 0.101 0.101 0.0 a 0 0.0 0.0 0.0 9 6 4.304 j-0 021 0.114 0.651 0.0 e.0 0.0 6 0 0 0 0.0 8.344 -.4 N t

868 6.430 0.811 4.0 6.0 0.0 0,0 00 0.0 0.0 0.011 N8 45 0.001 0.113 0.26) 0.0 0.0 0.0 0.0 0 0 0D 8 856 55E 3,002 0.))4 0,494 0.20) 0.c51 0 0 0.061 0.0 0 3 1 611 8 0 G04 0.30) 1. cal 0.a4) 0.6,0 0.660 8.0 0.0 0.0 3.464 SIW 0.009 0.304 2.J4) 3.454 1.210 0.964 B.0 0.0 C.0 1.164 Sw 4.001 0.104 1.017 1 411 0 411 0.1$3 0.0 0.0 0,0 4.269 Wsw 0.86J 0.101 0.6C9 0 104 0 091 0.101 00 0,0 0.0 1.169 W 0,001 0,051 0.193 8.467 0.091 0 . Q 'J 1 0.0 0.0 0.8 9.747 WmW 0.031 0.214 0.133 0.20) 0 103 0.091 00 0.0 0.0 0.864 NW 0.003 0.061 0.4%7 0.304 0.404 0.101 8.0 6.0 0.0 1.871 NWW 0 90) 0.303 0.161 0.104 c.304 0 Ill 0,0 0.9 0.0 1.611 IVITOT AL 4.011 3,196 1) 111 5.17? 4,465 2,610 t 461 0.0 0.0 31.)ll TOTAL ucVR8 QF VALID STAtlLITT ctSERVATIONS 3124 TOTAL 59055 0F $1A5ILITT CLASS I 863 TOTAL ucuss 0F vaLib WINh DtStettos-Wisp 873 8 0-4T ABIL3 f t class t 616 T0TAL NOVBS Of VALIO W199 Ot9SCTION-WIB9 8 F E E D- BT A514.!T T eB889 VAT 10a8 1911 TOTAL NOURS CALM 1 MR T PtfrtETAGE F9,ty NC1tt CF WTHS 3rttD SV WIND O l p t cT T '> R F09 STABIL8TT CLASS f i 1454 DLLTA-T4e 49 C/100 MI

$tquotAn NUCLEAR yLANT JAR 1. 91 - MAA 11. 91 WI4D WINO IFtttl mfd)

O!pffTt04  ! ALM 0 6-1.4 1 5-) 4 1 9-5 4 9 l1 4 1 i-17.4 l} t-le 4 14.$-14.4 s=24 % ttTat h 0.0 0,351 setti 0.0$1 0.0 0.0 0.0 0.0 0.0 1.015 WNE 3.9 0.134 4.119 0.S 0.0 0.6 0.0 00 0.0 4.36) 92 0.0 -L 119 . 06) 0.0 0.0 0.0 0.6 0.0 0.0 1.s31 ENE 0.0 0.163 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0;&lJ t 0.0 0.264 8 101 1 0 0.0 0.0 0.0 0.0 0.c 0.llt tat 0.0 0.354 0.0 040 0c Q.0 0.0 0.0 0.6 0.294 St 0.0 4.152 0.0 0,0 6.0 0.0 0.0 0.0 0.0 0.192 885 6.0 0.111 0.101 0.0 0.0 0.0 0.0 0.0 0.0 0 att 3 0.0 0.0 0.451 0.101 0.0 0.9 0.0 0.0 0.0 4,150 35W 9.4 0.152 0 137 0.404 0.101 0.0 0.0 0.0 0,0 1 141 SW Q.0 0.0 0.404 0.107 0,051 0.0 00 0.0 0.0 9.944 WSW O.0 0.0 0.101 0.011 0.0 0.0 0.0 0.0 0.0 0.11)

W 0.3 0.0 0-153 0.101 0.0 0.0 00 0.0 0,0 0.254 WWW 0,4 0 0 1.101 0.491 s.0%1 0.0 0.0 0,0 0.0 4 35)

NW 0.0 0.0 0.214 0.401 0.0 0.0 0.0 0,0 0.0 0.35%

NNW 0G. 0.0 0.101 0.0 0.0 0.0 0.0 0.0 0.0 6.101 SVETUTAL Q9 1.774 E.311 1. 173 0.J01 040 0.0 0,0 c.0 11.178 T3TAL H CJ S 1 0F WALID ETARTLITY 095t*VATIONS $1J4 TOTAL 80VD$ Of BTAt!LITV CLA38 F 231 TOTAL W)UR$ Of VALID WIND t!RICTION-WINb SPEED-ATABILITY CLASS F 211 TOTAL V0235 CF VAL!D WIND DitttTIvN-WIND SPCtD-STABILITY OS1tFVATICN5 4971 T.7 T al, u;URS CALM 0 MI T 5 3 R 3 LM I C A L FA0!LITY: StWQfAM NUOLEAR PLANT STASILITY #hSED ON LAPit RATE MEASURto BETWtrN  %,21 A40 4$.99 METt33 W!ut attt0 AND L:ptCT30N MIA10910 AT THE 9.71 MCttp Lf VEL LATE PBINTfD 34/34'91 NEAM WIME EfttD

  • 3.4 MP3 33tt! TOTALS ARD SVSTOT ALs AsoVE A$ t OST AINES PROM UR 30'1M D E D BUMBER$

SON Rad Impact.

Jan-Dec 1991 Page 22 of 36 TAliLE 1 (page 4 of 4)

S RQUOYNLNUCLRAR_l%M!T_METEOROLOGI C AL_ D AT A FlRSLOUARTER_1991 J 0111L ER E QU E NCLDI S TJil HUT 10 tL1H3r RC ENT f0R_0ROUND-LEVEL 3ELEASES jo197 FIDPfRTAGf.ftEQbtNCitt OF wiPD SPFtD WY W1h9 Oltttty s Fct

  • STABILt?Y CLA8E 4 It6LTA T a 4.0 t/100 kl BEQV0 VAN NuCLCAD PLANT JAN 1. 91
  • NAD 11. 91 WIND WIND Sitt&tMid) cietcTTrw cALu e a.1 g 3 s.34 $ %.4 4  % l1 4  ?.6-11 4 17 %-18 4 10 b J4 4 >a74 5 t e T3 G0 0.0 0.031 60 0 0 C.D 0 0 0.9 00 0.9th N

0,151 1.174 00 0c 0.0 0.0 0.0 0.0 1.01?

Nut 0.0 c.0 4 218 W5 0.6 0.714 d.964 0.0 0.6 0.0 h 9 0 0 0,0 4.134 0.404 0.0 6.0 0.0 a.0 0.0 s.0 e.456

$NE 8 8.9 0,161 0.163 0 ( c.0 0e 6.0 0-4 60 0.304 0.141 9.661 4.0 00 0 0 0.9 0.0 # 0 9.393 881 0.6 6.383 48 0.0 0.162 0.951 00 0.0 0.0 0.0 0.0 0.0 0.101 0 0 0.0 0.0 0.0 0.0 0.0 0.214 lit 0.0 0 lla 8 0.9 A G11 0.39% 0.0 0.6 8,0 0.0 0.0 0.0 0 404 46 0.8%) 0.254 6.203 0,0 0.0 0.0 9.0 0.0 0.18?

Alw Sw 0.0 0.0 0.20) 0.101 e.c 0.0 6,P 0.0 6.0 9.405 0 0 0.0 0.0 00 0.0 6.0 6.0 6.0 0.0 9.9 W6w k 0O-0,0 0.011 0.0 0.0 0,0 00 0.0 0.0 9.011 www 0.6 0.3 0e 4.9 9.9 0.0 0.0 o.6 4.6 9.0 8.9 0.0 0,0 9 0 6.0 8.0 00 0.8 9.0 tw 0 0 N5w G6 6.0 0.011 U.0 0 0 0.0 0.0 0,0 0.0 6.014 4.140 0.406 60 0 0 0 0 e.0 00 l.tle

$U510TAL 0.0 1.310 TOTAL #0081 OF VALID STAB 8Liff CB8CRVAttcus 3124 TOTAL 40Vas of STA33LITY CLASA 4 in1 TOTAL 50UBS OF VAL 10 v1RD b!Btttt0N+W1MD SPEtD-STAstLitt CLASS 4 117 total poVad of VALID wtyp DISECT!cN-wind steth-sTAstL:Tt onstavaTiens 4971 0

TJtAl. NOUb3 CALM MRTIGBOLOGICAL FACILITVt SEQUO1AW NUCLt&& PLDNt STABILITY DAlt0 DE LAPGE Raft MEASUtt0 SETwEtu 9.25 AND 45.99 Mittta -

WIND SDtRL AND D18Ettipu MLA3utt0 AT TWE 9.13 MCTt8 LEVEL LATI P A I NT E L i 64/34/41 ntAB WIND $7580 e 30 ifu Notti TOTALS AMD SVSTOT ALS ABOVE ARR OBTAINtb Flon UnacVNStb M9 Mat &S 0017v

SON Rad Impact Jan-Dec 1991 Page 23 of 36 TABLE 2 (page 1 of 4)

SEQUOYMLHUCLEAILPLAHIETEDRO LOGIC ALDAT A

~SECORD_ QUARTER-1991-

- JQ1NT_fREQUEECLDlRTRlHUIl0N HLEERCENI I.QR_GRQUHD-LLYEk_.BELEASES 30tpf PttetwTAos fetgyttetts 0F wtWD St$t6 tt WIND bittfTinW POS 51 At t L3 T1 CLA45 A (DtLTA Tee-4.9 C/699 N) 880UQ1Au kuCLt&B plant AFB 1. 94 = JUN 30 91 WINC w!WD SittDtMtN!

CAL 4 0 6-1;4 QM S l-1 J 43-9-1914 10 1 34 4 isle t TOTAL (19FOTICE 4 S-3.4 1.5-13.4 s N 9.0 6.0 4.0 0.046 0.4 4.9 0.0 4.0 4.0 4.948 548 9.5 0.0 0.0 6.stl 4.154 0.94$ 9,0 D.$ 0.0 0.816 st 9.3 0.0 c.130 a e45 0.091 0.044 69 8,0 0,0 9.633 4N8 0.9 6.9 f.9 0.104 0.0 0.0 0.9 e .$ 6.6 0.404 1 0.0 8.9 6.946 0.0 0,0 9.0 0,0 9.4 0.0 6.446

$$t 0.9 5.0 6.944 0.003 0.0 6,4 8.4- 4.8 0-0 0,138 88 4.9 $.0 0,0 0.0 0,0 9.0 0.0 9.6 0 0.0 alt f.0 9.6 4.046 9.446 e 093 9.993 6.9 9.0 6.0 0 0.3??

8 0.e 9.9 0.9 0.331 0.093 9.0 0.0 0.6 0.0 4 333 ,

Saw 6.6 0,0 0.0 8.993 9.999 0.044 8.0 0.9 9.5 4.443 4W 0,0 9.4 0.944 0,461 0.194 6,0 9.0 0.8 eme 4.693 Wlt 4.0 0.0 0.0 0.5 0.046 0.046 0.0 6.0 0.0 0.893 w 0.0 00 0.0 0.0 0.046 0.046 4.0 9.0 0.9 9.693 wsw 0,0 4.0 0.0 4,4 0.946 9 0t3 0.0 Os0 0-9 5.138 Nw - 0.0 0.6 0.0- 0.0 0.e44 0.0 0.0 0.0 5.S 9.044 NNW 0.0 90 9.9 0.8 9.046- 8.e44 9mt 0.0 0.0 3,093 SU8 TOTAL 0.0 9.e 9,333 3.tle 1.418 9.464 0.9 0.0 9.4 S.146 TOTAL EdV35 of VAtit STAtlLITT OpetRVAft0W8 3173 TOTAL MOURS OF ST ABILlTT CLA4$ A 111 TOTAL SOURS OF TAL39 Mrs0 StatCTI0e-WIND 8F440-5fASILITV CLASS A Ill TOTAL M9URE Of WALID WIND DittCTION+ WIND S pitD+3TASILITV etSERVAT3ONG 3149 TOTAL WOUSS CALM 4 fe,,1NT PTSCENTAet PptQv8Mel54 0F w!NB $Pttp ST WIND StptCTtON F68 8?A41LITT class S l-4 9s 98LTA,Tte-4,1 C/195 Nt SEQVOYAN NUCLEA9 FLANT Atk 1, il

  • JUp 30 91 W1ND WIND SPttD4MPS)

.ttpteTION _ CALM D 6-1.4 4.5-3,4 3.5-3.4 4.6 1.4 T.5-13.4 13.5 10,4 10.6-14.4 ,*36,6 TOTAL N 9.0 0.0 0.044 4.693 8.0 0.0 0.0 9.6 0.0 0 130 NNt 0.0 6.0 6.093 a.3aB tiete 0.0 6,4 0,0 e-$

. 4.lsT at 4.0 4,0 0.441 0.401 0.0 0.0 0.0 0.0 0.0 0.933 BN4 0.0 4.4 S. <* 9.130 0.0 0.0 4.0 0.0 4.4 4.446 '

3 0.0 3.9 0.381 4.0 0.0 0.0 4.0 0.0 0.0 9 331 Ret 9.9 4.0 4.311 0.0 0.0 0.6 0.8 9.9 0.0 0.317 88 0.0 0.0- 0.104 4.993 0.9 0.0 0,0 0.9 9.0 4.371 est 0.0 044 0.693 0.19e 0.544 B.046 9.6 8.0 0.0 9.33) a 6.4 9.0 3.046- 9.377 0.046- 0.134 0.0 0.9 0.0 9.191 saw 4.0 0.0 9.184 1.161 0.415 9.444 4.0 9,8 6,4 1.141 IW 6.0 9.0 4.4 0.661 4.144 0.0 0.8 0.0 0.8 4.893 vsw -0.6 4.4 0.0 0.s - 4. 0 e.0 0.4 0.4 0.e 6.0 W 9.4 0.0 6.0 6.0 0,046 0.0 0.0 4.9 0.! 4,844 WWw -0.0 0.4 'O.9 0.646 0.0 0.0 0.0 0,0 4.0- 9.9 e6 -

WW f.0 9.0 0.0 0.9 0.130 4.0 0.9 0.0 4.0 4.130

WWW 9.4- 9.4 0.0 4.494 9.846 0.446 8.0 9.9 4.9 4 144

$UBTOTAL. -6.0 0.0 1.890 - 8.349 4.948 9.377 5.9 4.0 0.0 6.494

- TOTAL NOUps of VALID STA33LITf '0BitpfkT10NS 311)

TOTAL 50'JAS OP stat t LITT CLA3B 4 til TOTAL WOURS of VALIO WINO DIRfCTION-WINO SPttp-STABILITY CLA5s e 140 TOTAL 20U18 0F WAL$D WINO DIRECT 109* WIND S PRID+3TABILITT 0881RVATION8 3559 TOTAL NOUps CALM- 0 Mtft083LO4tCAL FACILITTt $t9VOYAN NUCLtAA PLAa?

$7AstLITV 4AJED 04 LAPSI R Af t MEASURED SitwtEN l.35 AnD 45.99 METERS w!hD $P85$ AND CIR5CTION REASUpt0 AT THE S.73 METER LEVEL I DATI P91NTtC. 9?/30/91 MEAN WIND 47850 e 4.4 PPR

. NOTE: TOTALS ARD $UST0TALS AgeV8 A55 OSTAINED Ptost vakOUN950 Benatas

. . . ~ . . ,,.____ . _ _ . . _ m - . _ . , - , .

SQH Had Impact.

Jan-Dec 1991 Page 24 of 36 TABLE 2 (page 2 of 4)

S f'QUQY AIL FUC L E A RlLANLMETEO ROLOGI Calc DATA SECOND_ QUARTER _L991 J0 l HLFREQU EECLDIEIRIDUTl0M_ l H JERCE NT IRR_GROUFD4EVELEELEAGSS M Q EDCEWThnt ?*1tfucit5 of klND SFttp af W!WD cittcTann Fet STAGLLtTY CLk38 C dal.74 &tLTA+74=-1.9 C/199 NI SEQUCTAM MVCLLAR PLANT APR 4. #1 - JUN 30, 91 WING t!**' tie 4 O Lu 4.6-1 4 1,4-1 4 wfRD 8PttbtMtuo i %-l.4 9 t' 4

  • N 0.0  % 12 4 12 4-18 4 le %-!4 4 WNC 04 0.0 0.0 C,444 0.0 MM y T

St Q.6 0,999 0,23' 0.6 0.4 0.0 0.0 0.0 0,1)$ 0.0 0 0 0 144 Ett D.0 4.130 0.062 0.0 00 9.4 0.0 00 0.144 0.0 4.t 4 toB 1

0.s 0.0 0.046 0.9 0.0 c.0 0.0 e sie tSt 0,144 0.0 00 00 0C 3.044 04 316 0 0 0.0 4.311 SE 5.0 0 0 0.0 0.0 6.0 4c

$3E 0.0 0.44$ 0,045 0-9 0.0 00 t,lte 4 5 0,0 9.6 0.0 0,0 4.044 5 9;0 0 093 6.3)$ 9.0 0.8 0.0 0.0 0,0 0,4 6 441 83w D0 0 134 0 32) 0,0 0.0 v.0 0.0 0.211 9 est 6.144 6 0 4.111 SW 0.0 0.Sti 4.164 0.0 04 0.0 WSW 0.0 0,371 0.693 0.8 0.0 0.110 w

0.0 0.4 0.0 0.646 a.o 0,0 0.0 t.464 0.6 0.044 6.9 0.0 6.0 1,440 WWW 0.9 G.c 0.0 0.0 9.6 4.0 0 0 0.0 00 KW 0.0 0.046 0.044 0sG46 00 0.0 9.846 3.0 0.0 9 0 e9 0 o e.9se NNW 0.0 0 044 0.0 6,0 0.0 0,0 0.0 0.6%1 c0 0 0 s.O s.003 0,044 D !?8 9.0 0 0 9VRTSTAL 0 0 0,0 0,5 6.164 0.4 0.0 1.64) eo 0.144 2.%)1 0.444 0.2)! c.6 0.0 0.0 4.%46 TOTAL N0VDs Df vnLIP STAT!LITT eBstBVAtlONA TOTAL 50VR$ OF SfASILITE CLASS C J11)

T31kb NOUll OP VALID w!BB L43 TOTAL ROVR4 CP VAllo WIND SDIR ECT!0h-WlRD SDtID-RTA3f L!1Y CLAS SC I R E CT IOW -w1 W D 14L 70TAL ROVS$ CALA 99ttD*07A88LITT 0888tVAT30#8 J459 0

JJ_I_ R t 9tErtuY Aus PR$WENCitp ct wiwo SFtt6 By wfMC t!Dr* Ties Pot

$1A51LITT (LA38 6 l*l,$4 CELTA-Tse-S.S C/100 mi EtQVOYAN WVCLEAA PLANT APR 1.

WIND ll = JVW 30 94 CTRICT1tM CALM WIND SPE5DiMPM) 0.8-1 4 1.6- ,4 1.5-9 4 3. % M 4 1.5-13 4 1) 1-14 4 N 0.0 18 l-24 4 0.Gli 1.311 .=24-l TSTAL NN8 0.0 0.641 0 !??

N1 0.046 2.444 4.0s0 4.e 46 0.0 0.0 Q.0 0.044 0.111 6.046 0,0 3.191 ENE e0 1.47% 0.349 0,017 0.0 0.0 0.0 I

0.0 0.54% 0.046 6.0 0.0 0.0 3.021 0.0 0.0 0,0 fat 0.0 0.49J 0.0 0.0 1 602 0.0 6.6 0.046 0,0 6.0 0.0 0.0 9.493 58 0.0 6.32) 0.044 0.0 0.0 0.0 6.4 0.0 4.0 4.130 Sst 4.0 0.699 0,044 4.0 0.0 0.0 6.6 8 0.135 0.493 4.111 0.0 0.0 4.0 t.3s9 saw 0.0 0.134 2.901 0.144 0.0 0.0 0.0 4.645 0.0 0.046 1.411 0.449 0.211 0.6 0.0 1.133 sw 2.917 0.0 0.0 Wsw t.0 0,0(4 1,982 4.0Lt 0.118 3.092 0,0 0.0 4.112 9.8 0.946 1.61% 0.271 0.6 9.6 W 0.128 4.111 0.0 0.0 0.0 7.434 0.0 0.114 0.149  %.042 0.0 0.0 4.366 WWW t.0 0.044 0.0%2 0.0 0.0 RW 9.4 0.093 0.4 0.0 C0 0.6 0.0 0.144 0.0 0.048 0.184 6.046 0.092 4.0 9.84%

NNw 8.4 0.052 4.118  %.092 6.0 0.0 9.6 0,144 4,199 9.992 S.0 4.9 4.236 0,483 8.444 0.0 0.3%)

SUITOTAL 6.9 0.0 0.0 0.416 17.24) 14,947 0.0 L.931 3.331 0.144 0.0 0.0 0.0 14.417 TOTAL MOURA 0F VALIC STAal"'TT 043tBVAT!0NI TOTAL NouR$ Cr STAttLITY CLASS D 317)

TQTAL 20031 0F 143 TOTAL MSU$3 CF YALID wtaD clatCTsun-ulub $PttD- ATAa t LITY class D 740 TOTAL MOVM CALMVAL 10 wtnD s t LECTion-winn a rtsc stas t LITY CS2140 SE RV ATIONS 6

MET 80BOLOGICAL FAC!LITit SitVOYAH NtJC LR A p PLAAT STASILITY SA38D ON LAtti SAtt MEASVRED SETWrfN 9.25 AND 4

w!ND $P850 AND D!8tCTION MEASUttG AT THE 9.7) MITtp LEVtL 45.19 Mtfral MEAN WIND SPEED = 3.4 RFN Daft PRINTED: 01/13/91 NOTEt TOTALS kND SUSTOTAL4 ASOTI ADS OST Af st D F30M Unsouwoto NUMatas M -- - ~

- 4 ___

SQN Rad-Impact Jan-Dec 1991 Page 25 of 36 TABLE 2 (page 3 of 4)

SRQUQYM UIUCLEAR-PLANT MSIEQRQLQQlCAL DATA fiffQED_QUARTIR 1991 JQlHT Fl@QUENCY DISTRIRUT101LIN PERCIMI EQE_GRQ. U EQ&EYIL_.BELEASES 20!*T PLpctNTAGE PPT 0"t#fitP OF Wf8D GPlte SY WINO 01950T388 P08 3Tas t LITT CLate t l-0.5i $<tStA-14e 1.9 C/100 80 4 S$9UOTA4 BUCL8AS P LANT APD 4. 91 - JUN 904 ll WINO WIND $PttDiRPu) 519tCTf0N CALM # 4-1 4 1.5-3 4 345-% 4  % Sal.4 15ld il S-II.4 Il 6-34:4 **34 1 EAJ 4.664 0.349 0.194 0.0 0.4 0.4 0.0 9.414 A 0 601 0.493 3 331 put 6.694 0.643 1.194 0.151 9.184 0.0 0.4 0.0 00 4.419 0.134 4.0 4.0 0.0 6.6 B.0 4.111 NB 0.00% 0.331 0. 55 INE 9.040 0.131 0.046 0.0 0.0 0.9 8.4 4.0 0.0 0.164 0.044 0.0 0.6 0.9 9.0 4.414 3 0.501 0.484 0.4

  1. 10 6.8 f.fre 0.001 0,117- 4.448 0.0 0.0 9.9 0.0 488 6.0 $.0 9.164 as 0.004 4.333 0.104 0.046 0,0 0.0 0.0 3.418 493 6.553 0.333 0.9 8.e 0,0 g.4 0.0 Sat 0.493 s#

6.116 4,5 0.9 96 0.0 4.34a 8 0.006 9 599 3.96% 0.493 8.6 4 463 35W 9.40% 6.149 4.044 1.014 0.169 0.0 94 s.0 8.gil 3.534 1 415 0.311 0.093 0.0 0.4 0,0 4 918

$W O.001 0.4 0.0 1.361 4.903 0.34% 5.613 0.333 0,0 0.044 0.0 WSN 0.0 9 411 N 4,481 6.331 0.333 0.331 0 6e6 0.0 00 0.0 9.6 0,604 Wnw 0.001 0.311 0.331 0.644 0.063 0.0 0.0 0.0 4.093 v,046 0.0 0.4 6.0 6.0 ~ 8 184 mW $.003 0.101 6.441 0.0 0.0 1.714 0.814 0.311 6.sel 0.0 0.4

$NW 0.003 0.$55 30,45% g.333 g,475 0,134 8.4 0.0 0,0 14.634

$Ul?OTAL 4.844 6.113 all) total movts or VALID STAstLtTT 00stav&TIONs 164 TOTAL Eovp3 Of STASILITT CLASS 8 TSL TOTAL NOUtl of VAL 19 W189 DIRECTION 4 WIND SPl$3.statILITT class I TOTAL NOVR$ OF WALID WIND DISECTIOW-WINS SP848 5 FAD 3LITY 045tsvatt0NS Illt4

- TOTAL WOUS$ CAta 3015T 78pCENT A05 P REQtNf18 5 SL r$#9 SPtti SV WIND OtStCTION F69 ST ABILITT CLA88 P t 4,$< 9tLTA*T** 4.0 C/444 nl

$$QUOVAR WVCLEAA PLANT APA 1. 91 - JUN 35. 11 WtRD WIND SPBE9(MPut DIttcT!cN CA&M 0 4-1.4 1.5-1.4 1,1-5,4 5 . ',- 1, 4 1.5-13.4 13.5-18 4 30.5-34.4 >=34 $ TOTAL N 0.018 0.104 1.337 8.184 - 0.0 - 4. 4 4.4 4.0 0.0  % 131 ung 9.03% 0.441 3.431 0.331 a.4 0.0 0. 6 - 0.0 0.0 3.E34 Et 0.904 S.164 0.104 0.0 0.4 6.0 $48 9.9 8.9 0.313 ENE 0.803 9.144 0,044 0.0 0.0 0.0 0.0 0.0 0,0 4.333 8 9.001 0.134 0.6 9.0 8.0 9.0- 0.4 0.0 0.0 4.449 858 6.003 S 138 9.046 9.0 0.0 0.0 0.0 0.0 0.9 0.144 at 0.005 - 0.333 - 8.331 0.0 0.4 4.0 0.0 9.0 9.0 4.llt sat 4.004 0 131 0.144 0.0 0.0 00 0.0 8.0 6.0 - 4.410

$ 4.481 0.331 0, lei 4.444 0.0 . 8. 9 6.0 0.0 6.0 0.791-asW 6.40T 4.053 ' 9.599 4.093 9.5 . 9.446 0.4 9.9 0.4 9.R41 SW ' 4.004 4.046 9.899 0.093 0.0 0.8 9.9 9.6 9.4 0.144 WSW .4.003 0.044 0.134 - 4.134 0.0 9.9 . 0.0 8.8 0,0' 4.335

'W 4.0 0.6 0.0- 4.0 0.0 4.0 0,0 9.0 0.0 9.9 WNW -0.003 9 946 0.311 0.0 . 4.0 9,0 09 e.e 5.0 s 319 NW - 9.001 0.0 4.138 0.493 0.046 0.8 v.9 0.0 0.0 9.318 New 0.001 - 0.130 0,553 0.044 4.0 0.0 40- 0.0 e.0 8.144

$UBTOTAL 9,093 3.444 4.914 - 0.933 6.044 4.044 0.0 6.0 0.0 49.444 TOTAL ECURS OF VALID STABILITT Cl$ttV&TIONS 3173 TGTAL E00k1 0F ST A83 bitY class F all TOTAL NOURS OF T ALID WIND DIRBCTION-WING $ PEED-STABILITT CLASS F 331 TOTAL NOURS OF VALip WINO DIDECTION-WIND SPttD-$TABILITT 09589VATIONS 3149 TOTAL B0VRS CALM 1 R$tt0ROLOGICAL FACILITTI $$QUCTAM NUCLIAA PLANT STA5!LITT 9ASED OM LA788 7 Aft NEASURBD SETWEEN 9.35 AMG 4$.99 METERS WIND SPIBD AND CIntCTION NEASURED AT TBB 9.13 METIA LEVik DATE PRINTED: 01/30fth MBAR VtND EFEED e 2.4 RPR

.50T8; TOTALS AND $UST07ALS A40V8 ARE OSTAIntD FROM UNROUND89 NUM8tRS

~

.S9M Rad' Impact

'Jan-Dec 1991 Page 26 of'36 TABLE 2 (page 4 of 4) l EEQUQYAH _ NUCLEAREANT. METIQRQLQDICAL_ DATA I EECDHD_ QUARTER _19.11 JOINT FREQUERCLDIS.TRIRUT1QR_llLfERCMT EQB_GRQUND-LEVEL RELEhEES T

Jetut ptartpTAst Fet0Vtactts or wtat ottis GT wipD pilgrT1)W POR_

OTA0!LITT CLA30 4 (ttLTA T p . 9 t/300 M1

$8900 VAN #UCLEAR OLANT Att 1. On - JUN 30, el WlND WIND EF5tD4EPHI ettleTirN CALw 0.4 3,4 1.0.).4 3,6-l.4 5 5-1.4 1.1-12 4 17.t-10.4 It l-74.4 >=)4 4 TaTAL 5 0.0 0.0 0,100 0.040 0.0 0.0 0.0 0.0 0.0 0.231 sut 0.0 0.046 6.153 0.104 0.0 0.0 0.0 0.0 0.0 0.704 NE 0.0 0.0 0.300 0.0 0.0 0.0 00 0.0 9.0 0.300 Ext 0.0 0.130 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,430 8 0.0 0.104 0.652 0.0 0.0 0.0 0.0 0.0 0.0 0.311 848 0.0 0 130 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.430 st 0.0 0.333 0.040 0.0 0.0 0.0 0.0 0.0 0.0 0.300 Set 0.0 0,040 0.0 0.0 0 0 0.0 0.0 0.0 0.0 0.040 0 0.0 0.004 0.130 0.0 0.0 0.0 0,0 0.0 0-0 0.434 tow 0.0 0.040 0.0 0.0 0,0 0.0 0.0 0.0 0.0 0.040 th 0.0 0.0 0.0t0 0.0 0.0 0.0 0.0 0.0 0.0 0.046 usw 0.0 0,0 0.040 0,0 0.0 0.0 0.0 0.0 0.0 0.040 W 0,0 0.0 0.0 0.0 0.0 00 0.0 0.0 0.0 0.0 www 0.0 0.0 0.0 0.0 00 0.0 0.0 0.0 0.0 0.0 Nw 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 a.0 erw 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.0 GUGT0tAL 4.0 1.014 1,415 0.131 0.0 0.0 0.0 0.0 0.0 8,170 total #0988 of TALib STASILITV 000tBVATION5 III)

TOTAL NOURS OF STA0!LITT CLASS G le TOTAL NOURS OF WALID WIND Statttion-Wint a t t E D-3f A3 3 LITY class e le TDT AL MOUS$ OF VAL 10 w!No DIttCT105-w1ND atttpest ABILITY 000ESV ATIONS 2400 TOTAL Meuss CALM 0 pttt030L00! CAL FACILITTt SEQUOTAa NUCLEAR PLANT SThenLITY 4Asto CN LAP 38 Raft MEASURED DETwtts 0.34 AND 4$.90 Mttths ulWB OPEED AND DIStCTION MEASURED AT TME 0.11 METER LEVtk GAft 731NTED4 01/30/91 -

MEAN WINO 57850 a 1,0 MFA ROTEI TOTALS AND OUOTOTALS A00VB A38 00TAINED PROE UNROUNDi$ SUM $tS$

I 0017v L-j..

1 SQN Rad Impact Jan-Dec 1991 Page 27 of 36 j TABLE-3 (page 1. of 4)

S E QUQYAILEUC LE MLELAHI_ METXQRQLQDIC AL_DAIA TEIRD_ QUARIER 1991 JDIFT FREQUENCY .DRIRIBUIl0llitLEERCIET i EQA_GRQUED M YEk 3.ELEASIS sTAetL4TT class A (DELTA T8**4.0 C/100 N) t StgUOTAN NUCLEAN PLANT JUL 1, el - B&P 30, el WlED W!ND IPEEDIRPN)

DISSCTION y N_ 0 8-1 1 1 l-).4 1.l-5.c n,9 1.0 9.6-12 4 12.6-10.4 10.5-24 0 pe14.6 TOTAL 0 0.0 0.0 0.0 0.092 0.131 0.0 0.4 0.0 0,0 0.220 SWE 0.0 4.4 0.0 0.026 0.468 0.215 0.0 0.0 0.0 .1.950 Nt 0.0 0.0 0.103 0.401 0.0 0.831 0.0 0.0 0.0 1.000 4.0 0.0 0.0 0.437 0.0 0.0 0.0 0.0 0.0 0,131 INE ' c.

E- 4.0 0.0 0.0 0.046 0.0 0.0 0.0 0.0 0.046

. Est 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0, a 0.0 st 4.0 0.0 0.0 0.048 0.0 0.0 0.0 0.0 0.0 0.044 ast 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 8 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0

-88W 0.0 0.0 0.0 0.003 0.046 0.0 0.0 0.0 0.0 0 431 SW 0.0 0.0 0.0 0.097 0.046 0.0 0.0 0.0 0.0 0.151 Wsw 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 W 0e 0.0 0.0 0.046 0.0 0.0 0.0 0.0 0,0 0.044 WNW 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WW 0.0 0.0 0.0 0.0 0.046 0.0 0.0 0.0 0.0 0.044 NwW 0.0 0.046 0.0. 0.0 0.045 0.046 0.0 0.0 0.0 0.131 SUGTOTAL 0.0 0.046 0.14) 2.062 0,110 0.450 0.0 0.0 0.0 3.929 TOTAL NOVR$ OF YALID STA0!LITV 08850VATIONS 2500 TOTAL NOUSS OF STA0!LITT CLASS & 71 TOTAL Nouns of V AtlO WIND D198CTION-WIND 578 8D-4 PABILITY CLASS A 77 TOTAL nouns 07 VALID WlND DirtCTION-WTWD SPR50-STASILITY 08883VATIONS J102 TOTAL NOUS $ CALM 0 1

5 87A0!LtTT CLAS$ 0 (+4.01 DELTA *T(e-l.7 C/100 Ni l-( SEQUOTAN NUCLtAR PLANT l- JUL 1. 01 - SEP 20. el WIND . . WIND SPEtD(RPN) i SIBICTION CALN 0.4-1.4 1.5-3.4 3.5-l.4 S.S-1.4 1.5-l!.4 12 5-10.4 10.5-24.4 >=24.1 TOTAL j

l' N 4.0 0.0 0.0 0.0 0.003 0.040 0.0 0.0 0.0 0.137 i NNt' O.01% 0.0 0.131 1.054 0.275 0.012 0.0 0.0 0.0 1,800

!~ R$ 0.021 0.0 0.275 0.412 0.046 - 0.0 0.0 0.0 0.0 0.154 3NE ' O.001 0,0 -0.002 0.044 0.0 0.0 0.0 0.0 0.0 0.445 l

t 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 Est 0 A04 0.0 0.046 0.048 0.0 1.0 0.0 0.0 0.0 0.005 38 0.004 0.0 0.044 0.0 0. 0 - 0.0 0.0 - 4. a 0. 0 - 0.040 558 4.0 0,0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 8 0.0 0.0 0.0 0.0 0.002 0.0 0.0 0.0 0,0- 0.002 ssW 0.4. 0,0 0.0 0.046 0.275 0.0 0.0 0.0 0. 0. 0.324

0. 0 - 0.0 0.092 04137 0.0 0.0 0.0 0.0 0,220

$W 0.0

' Ws w 0.0 0.0 0.0 0.002 0.0 0.0 0.0 0.0 0.0 0.002 W 00. 0,0 0.0 0.046 0.0 0,0 0.0 0.0 0.0 0.044 WWW 0.0 0.0 4.0 d.0 0.0 0.0 0.0 0.0 0.0 0.0 KW 0.0 0.0 0.0 00 .0.0 0.0 0.0 0.0 0.0- 0.0 NNW . 0.0 0.0 0.0 0.0 0,046 0.0 -0.0 0.0 0,0 0.046 8V3 TOTAL ' '0.044 0.0 0.596 1.433 0.062 0,131 0.0 0.0 0,0 3.511 TOTAL N00R3 0F VALID STASILtTV OSSEATATIONS ,2100

~

TOTAL NOUR8 DF STABILITY CLASS 8 .

74 TOTAL NOV93 0F YALID WIND DIRECTION-WINO $TRED- tTABILITY CLA$1 8- 70 TOTAL NOURS OF WALID WIND D35tCTION-WIND $PttD-STANELITY OSSb8V Af t0Ms . 210 2 1

TOTAL W3URS CALM NIT 86AOLOGICAL FAC1LITTt $$QUCTAN NVCLEAR PLANT STAS!!,1TT SA$tD ON LAPS $ RATR REASURED SETWISN 0.25 AND 45.99 RETERS WIND SPEED AND DIRECTION REASUR3D AT Tut 0.73 NETtt LEVEL DATE PRINTED: 10/20/91 6

NEAN wtND 8P180 e 4.7 RPM

^

NOTtt TOTALG AND SU3 TOTALS ABOVE ARE 001A$5FD F00M UNROUNDED NUMSROS

SON Rad Irnpact Jan-Dec 1991 Page 28 of 36 TABLE 3 (page 2 of 4)

SEQUQYMLEUCLEAR PLAUI.EEIE.QROLOGICAL._ DATA TEIED 0UARIER 1991 J0lRT . f R EQUEBCLDlEIRIRM.ILQRltLEERCEHI f0R_GRQUND:LEYELBELEASIS OTAptLtTV CLAA$ C (+5.74 DELT A-T v e* 4. 6 C/100 M )

540"0 VAN WVCL8A8 f t. ANT JUL 1. 91 - sit 30, 91 W1pD WIND SPEED (MPNI ptPttfl0N CALM 0,8+1.4 1 3-3.4 3.5-1.4 S 6-7.4 7 5-12.4 12.5-18.4 18 S-24.4 2 74.5 3T3 N 0.0 0.8 0.0 0.147 0.0 0.0 0.0 0.0 0.0 0.347 NNE 60 0.0 0.367 0.425 0.137 0.0 0.0 0.0 0.0 4.329 W8 0.0 0.0 0.275 0.092 0.0 0.0 0.0 0.0 0.0 0.367 0.046 0.046 0.0 0.0 0.0 0.0 0,0 0.092 ENt 0.0 0.0 B p.0 0.0 0.131 0.0 0.046 0.0 0.0 0.0 0.0 0.163 188 0.0 0.0 0.046 0.0 0.0 0.0 0.0 0.0 0.0 0.946 st 0,0 0.0 0.092 0.137 0.0 0.0 0.0 0.0 0.0 0.239 888 0.0 0.0 0.046 0.046 0.0 0.0 0.0 0.0 0.0 0.092 a 0.0 0.0 0.046 0.046 0.092 0.0 0.0 0.0 0.0 0.103

$8W 0.0 0.0 0.044 0.412 0.046 0,0 0.0 040 0.0 0.504

$W 0.0 00 0.147 0.550 0.183 0.0 0.0 0.0 0.0 0.071 0.6 0.0 0.0 0.044 0.0 0,0 0.0 0.0 0.046 WSW 0.0 W 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 WWW 0.0 0.0 0.0 0.046 0.0 6.0 0.0 00 0.0 9.e46 NW 0.0 0.0 0.0 0.044 0.044 0.0 0.0 0.0 0.0 0.002 NRW 0.0 0,048 0.0 0.0 0.046 0.0 0.0 0.0 0,0 0.092 Sutt0TAL 4.0 0.046 1.23T 2.413 0.442 0.0 0.0 0.0 0.0 4.531 TOTAL NOUps 0F V ALID ST Abt L!tt 003tpV AT10N A 2868 TOTAL NOUts OF STABILITY C LA t 3 C 99 TOTAL NOUka CF VAL 10 W 8 ND Dit ECT10N. WIND SPEED-ST A$!LITT C LAsl C 99 TOTAL MOVDS OP VALID WIND SI$$CTION. WIND S PRID-STASILITT 093 38V ATIONS 2142 TOTAL NOURS CALM $

STAatttTV CLASS O (.1.54 DELTA-Tee-0.5 C/300 N)

SEQUOTAN NUCLSAR PLANT JUL 1. 94 - sit 30, 91 WIND WIND SPEED (MPN) p!R$CTION CALM 0.6 1.4 1.5-3.4 3.s.S.4 1.s.7.4 1. 6 12 d 12.5 14.4 18.5-24.4- 6 24.5 t0TAL E 0.004 0.131 4.373 0.942 0.321 0.094 0.0 0.0 0.0 2.001 NN4 0.064 0.092 1.696 2,291 1.000 0.092 0.0 0,0 0.0 5.101 NE 0.b04 0.131 1.512 0.367 0.131 0.0 0.0 0.0 0.0 3.150 ENS 0,002 0.892 0.179 0.0 0.0 0.0 0.0 0,0 0.0 0.013 8 0.004 9.132 0.J75 0.0 0,0 0.0 0.0 0.0 0.0 0.413 Est 0,001 0.046 0.412 0.0 0.0 0.0 0.0 0,0 0.0 0.459 48 0.004 0.0 0.196 0.0 0.0 0.0 0.0 0.0 0.0 0.807 SSE 0.001 0.092 a.304 0.550 0.0 0.0 0.0 0.0 0.0 1.147

.3- 0.000 0 n37 2.979 2.337 0.550 0.0 0.0 0.0 0.0 6.811 SSN 0.009 0.093 - 3.437 5.729 0.643 0.0' O.0 0.0 0.0 9.908 SW 0.006 0.044 2.295 2.198 0.137 0.0 0.0 0.0 0,0 5.214 wsw 0.004 0.092 0.347 0.687 0.092 0.0 0.0 0.0 0.0 1.239 W 0.001' O.092 0.321 0.37% 0.0 0.0 0.0 0.0 0.0 0.684 WNW 0.001 0.002 0.27% 0.229 0.092 0.0 0.0 0.0 0.0 0.648 NW 0.00n 0.0 0.229 0.0 0.0 00. 0.0 0.0 0.0 0.234 __

NNW - S.001 0.183 0.215 0.432 0.143 0.0 0.0 0.0 0.0 1.055 30sfotAL 0.046 1.467 17.324 14.836 3.362 0.463 0.0 0.0 0.0 38.818

-TOTAL NOUSS OF YALID STABILITT GE988 VAT 10NS 2188 TOTAL N0035 0F ST A8!LITT CLA$$ D 449 TOTAL HOURS OF YALID W1ND DIRECTION-WIND SPEED-STA8!LITY CLASS D 447 70TAL NOURA OF VALID WIND Ot 9ECTION WIND $ PEEL *STA8 t LITY 085tRYAff0NS 2142 TOTAL NOUR8 CALM 1 l7 I

i NETE0$0LOGICA' FACILITY; $tOU0 TAN NUCLEAR PLANT l ITABIL1TY BASED DR LAP 11 Raft MEASURED 827WEIN 9.2% AND 41.99 METERS WIND SPEED t.ND D(A(CY:ou MEA $USED AT THE 9.73 MET 59 LEVEL Daft FRtRTEDs 10/29/91 NEAN WIND SPEED s 3.4 MPH 20T81 TOT ALS AND SU$ TOTALS ABOTS &&C OSTAINED PRON UNIOUNDED NUMatAS l

SQN Ra6 Impact Jan-Dec 1991 Page 29 of 36 TABLE 3 (page 3 af 4)

SEQUQYNLlIUCLEAR PLANT METURQLQGLCALDATA IliLED_.QUMTIR_1191 dQlMIIBIQURCY DIETRIBUT10lL1H_HECERT EQlLGRQUND-LEVEL RELEASIS STA01L3ff CLAts I t-0 Se DELTA *Tt* 1.5 C/100 NI SEQUDIAN NUCLEAR PLANT JUL 1. el e $$P 30, 01 WINb WIND SPttD(NPNI OlkSCTION CALM 0.6 1,4 1.l.),4 3,6-1,4 S.1-7.4 7,1-12.4 12.9 10,4 19.5-54.4 >e24,9 TOTAg 5 0.234 1.879 4.629 0.412 0.367 0.042 0.0 0.0 0.0 1.813 NNE 0.196 1.054 4,354 0,133 0.137 0.0 0.0 0.0 0.0 6.473 NE 0.021 0,321 0.275 0.040 0.0 0.0 0.0 0.0 0.0 0.643

$Nt 0.012- 4.137 0.183 4.846 0.0 0.0 0.0 0.0 0.0 0.378 8 0.010 0.092 0.183 0.0 0.0 0.0 0.0 0.0 0.0 0.20%

Ett 0.000 0.092 0.131 0.0 0.0 0.0 0.0 0.0 0.0 0.231 st 0.021 0.331 0.275 0.046 0.0 0.0 0.0 0.0 0.0 0.463 588 0.030 0.850 0.375 0.092 0.0 0.6 0.0 0.0 0.0 0.944 8 0.076 0.733 1,31) 0.131 0.0 0.0 0.0 0.0 0.0 2.321

- 86W 0.172 0.917 3.450 0.917 0.044 0.0 0.0 0.0 0.0 6.900 SW 0.109 0.696 2.429 0.713 0,046 0.0 0.0 0.0 0.0 3.913 W3W 0-059 0,733 0.917 0.321 0.046 0.0 0,0 0,0 0.0 2.076 W 0.040 - 0.596 0.504 0.046 0.0 0.0 0.0 0.0 8.0 1.105 WNW 0.011 0.604 4.412 0.0 0.0 0,0 0.0 0.0 0.0 0.060 NW 0,423 0.229 0.412 0.137 0.046 0.0 0.0 0.0 0.0 0.840 WNW 0.058 0.458 1.146 0.103 0.0 0,0 0.0 0.0 0.0 1,045 800 TOTAL 1.100 9.212 21.157 3.890 0.687 0.092 0.0 0.0 0.0 34.297 TOTAL NOUR$ OF VALID STADILITT 00$tRVAT10NS 2188 TOTAL NOUR$ QF STASILITY CLAS8 E 795 TOTAL NOUS $ OF VALID WINO DISECTIOE-WigD SPRED*tT At t LITT CLASS 5 792 TOTAL NOUA8 0F VALID W1ND DISSCTION-WIND SPt3D-STA8!LitY D084t?AT1085 2142 .

TOTAL NOUS $ CALM 24 STA31LITT CLAS$ 7 l 1.44 DELTA-Tie 4.0 C/100 N) j- SSQUOTAR NUCLEAA PLANT JUL 1. 01 - stP 30, 91 P

wtND= w!ND SP8tD(NPNI DlatCTION CALN 0.6-l.4 1.5-3.4 3.5-5.4 5.5-7.4 7.5-12.4 12.5-10,4 10.5-24.4 s 24.5 TOTAL N 0.114 0.458 2.750 0.361 0.0 0,0 0.0 0.0 0.0 3.400 Nut 0.132 1.376 3.331 0.044 0.0 0,0 0.0 0.0 0.0 3.890 NE -0,006 0.229 0.0 'O.0- 0.0 0.0 0.0 0.0 0.0 0.237 BN8 0.00$ 0.092 0.046 0.0 0.0 0.0 0.0 0.0 0.0 0.142 2 0.003 0.092 0.0 0.0 0,0 0.0 0.0 0.0 0.0 0.096 ISE 4.00$ 0.092 0.044 0.0 0.0 0.0 0.0 0.0 0. 0 - 0.142 et 0.000 0.229 0.0 0.0 0.0 0.0- 0.0 0.0 0.0 0.237 885 0.013 0.129- 0.137 0.0 0.0 0.0 0.0 0.0 0.0 0.340 l 8 0.033 0.229 6.412 0.0 0.0 0.0 0.0 0.0 0,0 0.684 88W 0.026 0.13 7 ~ - 0.198 0.0 0.0 0.0 0.0 0.0 0.0 0.150 sw 0.020 0.045 0.504 0.046 0.0 0.0 0.0 0.0 0.0 0.415 W5w 0.011 0.131 0.183 0.092 0.0 0.0 0.0 0.0 0.0 0.424 W 0.010 0.092 0.181 0.0 0.0 0.0 00. 0.0 0.0 0.30l' WNW 0.002 0.0 0.046 0.0 00 0.0 0.0 0,0 0.0 0.047 NW 0.011 0.092 0.229 0.04E 0.0 0.0 0.0 0.0 0.0 0.374 NNW 0.021 0.092 0.504 0.092 0.0 0.0 0.0 0.0 0.0 0.709 AUNT 0TAL 0.412 3.621 1,974 0.687 0.0 0.0 0.0 4.0 0,0 12 49%

TOTAL NOURS OF YALID STAT!LITY 005PRVATIONS 2108 TOTAL NOURS Of STASILITY CLASS P 277 TOTAL NOUR5 OF VALID WIND DIRECTION

  • WIND $PRID+5TABILITT CLASS P 277 TOTAL ROURS OF YALID WIND DIRECTION-WIND SPEED-STASILITY 091tRVAT10NS 2182 TOTAL NOURS CALP 9 NET 80ROLOGICAL f 7CILITT1 GEQUOTAN NVCLEAR PLANT STASILIIT DAstD ON LAPSE RATE REA8VRED BETWtru 9.25 AND (1.99 NETERE WIND $P280 AND DIRECTION NEASURED AT THE 9.13 NITER LEYtk DATE PRINTED 10/29/91 R$AN WIND $PSED o 1.9 NPN NOTE: TOTALS AND SUSTOTALS A30TS AR$ 00TAIN8D PRON UNRO' WDED J NUMatR$

,~ - . ~ ~ -

SON Rad Impact Jan-Dec 1991-Page 30 of 36 TABLE 3f(page 4'of 4)

SEQUQY AILIBICLEARJ1 ANT _ MET EDR0h001 CAL _ DATA THIRD _QUARIER_1991 1011G_ERE^UENCLDJIIRIDUIl0lLDLPIRCENT EOLDEQUND:1EYERELEASES STAtlL3ty CLASB e (DELTA t > 4.0 C/404 Ni

$$900 TAN NUCLEAR PLANT JUL 4. et - 88P 30. On utaD wtRD stt/D(MPN)

D100CTIcu CALM 0.8-l.0 1.5-3.4 ).5-5.4 S.6-1.4 1,5+43.4 13,5-10.4 13,6-24.4 p.24.4 Tofat N 0.0 0.0 0.0 0.046 0.0 0.0 0.0 0.0 0.0 0.046 .

NNE 0.0 0.046 0.0 0.0 0.0 0.0 0,0 NI 0.0 0.0 0.0 0.044

, 8.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 SWE 4.0 0.0 0.0- 4.0 0.0 0.0 0.0 0.0 4.0 0,0 5 8 0,0 One 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 t 884 0.0 0.046. 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.040 et 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0

  1. 88 0.0 0.0 0.044 0.0 8.0 0.0 0.0 0.0 0.0 0.040 8 0.0 0.0 0.040 a.0 0.0 0,0 0.0 0.0 0.0 0.046

$$w 0.0 0.0 0.103 0.0 0.0 0,0 0.0 0.0 0.0 0.103 SW 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.0 6.0 0.0 WSW 0.0 0.0 0.0 0.0 0.046 0.0 0.0 00 0.0 0.044 W 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 www 0. 0 . Dit 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 tw 0.0 0.0 0.044 0.0 0.0 0.0 0.0 0.0 0.0 0.040 -

NNw 0.0 0.0 0.048 0.0 0.0 0.0 0.0 0.0 0.0 0.060 8VOTOTAL 0.0 0.002 0.341 0.044 0.046 0.0 0,0 0.0 0.0 0.560 k'.

TOTAL NOURS OF VALID STAttLITY 004t9 VAT 10A3 3408 TOTAL NOUSS OF STAN1LITY CLASS 4 12 TOTAL N00R$ OF VALID WINO DIBSCTION-WIND SPEED-STA0!LITT CLASS 0 12 TOTAL NOUSS OF VALID WIND Dl%$CTION-WIND Stt tD-STASILITY DBSERVAft0NS 2442 TOTAL NOURS CALM 4 RETROSCLOGttAL PAf!LITT3 $$QUOTAN NUCLEAR PLANT STA03LITT SASED ON LAPER DATE NEASURED SETwdEN 0,19 AND 45.90 METERS W1NO SfttD AND DIRECTION MEASURED AT TNE 4.13 MRTth LAVEL DATR 751NTEDs 10/20/01-MEAR WIND $715D *' 2.4 NPN Notti TOTALS AND SUOTOTAL5 ASOVE Akt 09?AINED F804 UN00VNDtD NUM38E8 j 0017v L

-. - , _ , - - , . - . .- - , e - , . - - .

SON Rad I npact Jan-Dec 1991 Page 31 of 36 TABLE 4 (page 1 of 4) b S E QURY ALLHUCLEArLELA!LIJJTIOR0h0GIC McDM A EOURTILOUARTER_1191 JQLHLEEEQUEFCLD1HIRIBUTIDILHLPERCENT 0

E0R.SRQUND-LEVIk._ RELEASES JofNT tt9CtNTAot FptgUtNetts of WIND SP$to Of WIND DratrTtDN F09

$TAttLITY CLAAS A IDELTA T4o-1.9 C/100 NI St0VOYAB NUCtCAR PLANT OCT 1, 91 - Dic 31. 91 w!ND WIND StttDlMPMI 01steTION CALM 0.6 1.4 1.5-1,4 3.5-5.4 ,5.$.1.4 1.5-12 4 12.%-10.4 10,9+24 4 >e24.6 73 [

N 0,0 0.0 0.0 0.041 0.231 0.041 0.0 0.0 0.0 0.131 NMt 0.0 0.0 0.041 0.189 0.560 0.109 0.0 0.0 0.0 0.994 NE 0.0 0.0 0.041 0.426 0.426 0.041 0.0 0.0 0.0 0.941 l

INE 0.0 0.0 0.041 0.041 0.0 0.0 0.0 0.0 0.0 t ett t 0.0 0.0 0.0 0.041 0.0 0.0 0.0 0.0 0.0 0.041 tst 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 85 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 Sit 0.0 0.0 0.0 0.0 0.0 0,0 0.0 0.0 0.0 0.0 5 0.0 0.0 0.0 0.041 0.041 0.995 0.7 0.0 v.0 0.149 ESW 0.0 0.0 0.0 0.0 0.142 0.047 0.0 0.0 0.t 0,100 sk 0.0 0.0 0.0 0.142 0.2'4 0.041 0.0 P.0 0.0 0.413 W3W 0.0 0.0 0.041 0,0 0,0 0.0 0.0 0.0 0.0 0.041 w 0.0 0.0 0.0 0.0 0.0 0.041 0.0 0.0 0.0 0.041 www 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 Nw 0.0 0,0 0.0 0,0 0.041 0.041 0.0 0.0 0.0 0.005 NNW 0.0 0.0 0.0 0.0 0.0 0.231 0.0 0.0 0.0 0.231 SUDToTAL 0.0 0.0 0.189 0.941 1.192 0.80% 0.0 0.0 0.0 3.493 TOTAL HOURS OF VALID $TASIL1TY 095tRVAT10MB 2113 TOTAL NOURS OF STABILITY CLAs$ A 10 TOTAL NOUR5 0F VALIO WIND DIRECTION-WIND EVESD-STABILITY CLASS A 14 TOTAL NOUR5 DF VAL 1D WIND D191CT!DN+ WIND 8tttD-STABILITY COGERVATIONS 2112 TOTAL 90033 CALM e

+ -

JetNT PtpCENTA6. thigUENCitS OF W1ND SPttD OT WIND OTR$CTION FOR STARIt.1TT CLASS 5 1*1.94 DELTA *T4**1.1 C/100 M1 SEQVOYAN NUCLEAR FLANT OCT 1. 91 - DEC 31. 11 WIND WIND SFttDIMPNI 10.5-24,4 **24,5 TOTAL 3.5-5.4 5.5-1.4 1.5-12 4 12.5-10.4 )

CALM 0.5-1.4 1.5-3.4

_DISICTION 0.0 0.0 0.104 0.0 0.041 0.065 0.041 0.095 0.0 N 0.0 0.109 0.0 0.0 0,0 1.130 NNE 0.0 0.0 0.041 0.231 0.463 0.0 0.0 0.540 0.413 0.041 0.0 0.0 NE 0.0 0.0 0.041 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 INE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.041 0.0 0.0 0.041 0.0 0.056 1 0.0 0.0 0.0 0.0 0.6 0.0 0.091 0.0 0.0 Est 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.099 58 0.0 0.095 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.231 35E 0 095 0.142 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0,0 0.413 s 0.424 0.041 0.0 0.0 0.0 0.0 0.0 0.0 0.331

$$W 0.095 0.0 0.0 0.0 sw 0.0 0.0 0.0 0.142 0.005 0,0 0,041 0.0 0.0 0.041 0.0 0.0 WSW 0.0 0.0 0.0 0.0 0.0 0.095 0.0 0.0 0.0 0.041 0.041 0.0 w 0.0 0.0 0.0 0.0 0.0 0.041 00 0.0 0.0 0.0 0.041 0.100 WNW 0.0 0.0 0.0 Nw 0.0 0.0 0.0 0.0 0.095 0.095 0.0 0.995 0.0 0.0 0.095 0.0 0.0 NNw 0.0 0,0 0.0 0.941 0.0 0.0 0.0 3.141 4.0 0.0 0.204 0.941 1.562 551570TAL 211]

g TOTAL 20V35 0F YALID ST ABI LITY OBSERVATIONS 19 p TOTAL HOURS OF STABILITY CLASS 5 19 3 TOTAL MOVR5 0F VALID WIND DI8 tCTION-WIND SP1tD-STASTLITY CLA$5 8 M TOTAL NOURS OF V ALID WIND DIBICTION-WIND SPEED-STABILITY OBSERVATIONS0 2112 TOTAL ROURE CALM

5011 Red Impact Jan-Dec 1991 Page 32 of 36 T AllLI: 4 (page 2 of 4)

S l;0MYNL FVC LE MLf LMT3ETl;0 R OLOG I C Ak D AT A 00VRTILOVAKTERJ991 J 03 HTJ PJ 0.U ERCL D I S TRI DUII 0lL1 tL pr 8c titi TDR.0 POUT 4D AEVE k REI.tAsrs

?ftet tiertWTA.9J y pftN, fit,p er Witt 3,M tt.J1 wikti t i e t t tit W y _ _

$ TAD 1titt (LAtt f t-l.1# ittTA Tee +1.5 C/IS$ mi StGVotA1 WUtttAt PLANT OCT 3. 91 - Elf II. 91 Wikb StttLiptpl with 1.%+1.4 1 14 4 6 6 1,4 1hi Q S-ll 4 Q l+34 4 *

  • 3 4 . 5, qty

[fptrYttW CALM 0.6 1.4 1 9.143 0.641 9.8 0.6 9 ,6 0.334 9 0.0 9.9 0.0 0.144 0ze 0.0 6.909 0.0 0.098 9.449 0.319 0.331 0.6 6.418 put 9,0 4.331 0.0 0.994 6.9 0.0 0.0 pt 0.0 9.0 0.143 6.0 $ tel 6.095 6,9 0.0 6.0 0.6 0.0 tut 0.0 0.0 6.6 0.0 0,6 0.641 08 0.0 0.041 9.0 $.0 0.6 6.9 0.9 8

0.0 0.9 Pe 6.6 0.6 888 $.0 6.0 6.0 6.6 6.0 0.0 9.0 9.4 0,441 et 0.9 9.0 9.9 9.641 0.0 4 . f 41 D,0 9.9 0.0 0.0 6.641 9.6 0.8 486 6.9 9.441 8.14' t,D 9,6 0.0 6.304 9.0 09 0.099 6.168 8 0.0 0.096 0.331 0,Ill 0.49. 9.6 9.9 0.9 Stw 6.0 0.0 0.364  ? '.6 6.0 9.6 6.4Tl 0.0 0.0 0.9 0.819 0.0 9.889 SW D.641 0.941 0.0 0.0 9.0 0.0 9.8 D. ell 9.443 wsw 0.696 0.9 0.0 0.041 0.0 0.0 0.0 g W D.9 9.6 0.9 0.0 0.9 8.6 0.0 4.0 6.9 9.6 WNW 9.6 0.0 0.143 0.6 0.0 4.0 9.6 9.448 pu 0.0 0.0 0.6 9.0 0.6 0.0 4,364 9.9 0.0 0.0 9.143 0.041 0.696 0.0 DNw 1.430 0,813 0.0 0.0 9.0 4.344 5VpftTAL 0.0 9.0 0.948 1.313 3115 TOTat Doval or VALip 91&sttlTY cpttDVAf tett 49 TOT. , 90US$ OF BTAt!L1TV CLA88 C 59 TOTAL MLUt9 Of V Allt. W1Nb $ !W L CT10#* WIND Stttb-STAllLITY CLAta C OtttDVAftons all)

Te T AL Hebt s CF V Abib w t >C L t 9 E CTION + WIND S P E F D 0T A31LITY $

TOT AL HOUD3 CALM

{t;t FT tipC(kTAur FttgUtWrits OF wtut *rt te tT _ W!nti 0195r110W 709 STAT!LlTY CLA84 D l-1.54 CELTA*Tio.0 $ C/100 mi 680VofAW WUtttAR PLANT OCT 1. 91 + tit 31 91 WIND w!RD ifftD Pt4) gttCTfew Calm L.6-1 4 1.t+3.4 3.5-l 4 5 l-1.4 1.5-13 4 33.9-le,4 je ,l 34.4 sett i total a 0,0 0.143 0.149 1.136 1.113 04381 0.9 9.0 6.0 3 49) put 0,0 0.098  %.563 9.994 1.043 3.116 6.0 0.0 0.0 1.011 0.0 0.041 4.336 0.311 9.100 0.981 0.0 00 0,0 1.041 N2 0.0 9.'46 Cat 4,0 0.0 0.316 0.0 0.041 0.0 v.0 0.0 0.6 0.0 00 0,0 0.stl 6 0.0 9.0 0.096 0.0 9.9 0,0 0.9 4.0 0.0 9,0 0.0 0.0 0.6 ist 0.0 0.0 0,0 0.041 0.449 0.041 0.0 9.0 0.0 0.0 0.0 6.364 st 6 41)

SSE 0.0 0.0 9.33? 0.0 9.041 0.096 0.0 0.0 0.0 0.531 0.304 0.140 0.043 4.0 0.0 0.0 n.4tt 2 6.0 0.041 4,0 6.019 88w 0.0 0,143 1.134 3.443 1.136 0.443 6.0 0.0 8W 9.9 0.046 1.610 1.041 0.900 0.041 0.0 0.0 0.0 4.lt) 0.0 0.364 0.331 0.143 e 189 0.0 0.0 0.0 6 lli WSW 0.0 0.941 W 0.0 0.041 0.331 0.381 0.311 0.169 0.0 0.0 0.4 WMW 0.0 0.041 0.0 4.344 P.144 0.J31 0.0 0.0 0.0 4.154 0.095 0.143 0.119 0.131 0.331 0.0 0.0 6.9 n.144 uw 4.0 0.0 4,941 Wrw 9.5 0.096 6.436 0.631 4.616 9.384 0.0 0.0 4.$00 9.949 6.159 1.339 4.439 0,0

  • 0 00 St.114 SUtTotAL 4.0 TOTAL NotPS cf VALIO $TAstLIT1 OlttRVAT!DNS 311)

TOTAL ROUBS of STABILITY CLASS h 664 tit TOTAL 59U$$ OF T ALID WI?tD DIRECTION-Wlab Sit tD.rTASILITY CLAll D TOTAE WOVtl 0F YALID wt#D DIRECTION-w!ND 5tE80-81At!LITY 098ttvAtlCR4 3413t TOT AL ROVR$ CALM

l i

SQll Rad Irnpact.  :

Jan-Dec 1991 L Page 33 of 36  ;

i TADLE 4 (pege 3 cf 4)  ;

i S EQUDYAILEUC LEAILP1AHLMEILDE OLOC.LC ALD AT A  :

f IOURTE_QUARTIR_1121  :

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I

  1. 91NT Ptt_itptA98 ftttYfuel R OF wip0 etfID $1 wisp pittriles 70L i

stA6fLitt CLA$$ $ let.le t>titA*tte 3.5 t/160 N) 8t$vetAN avtttAt DLAst ett 1. ll a $tt 31. 61 1 WIND witb 8tstD4RPut gj 8 4 ct i e st c Al n C . .j,, ($;)] p,).S,g ,

).6 1,4 1.3 13.4 43.4 39,4 3,j,$.34.4 3.j g totAt 9 9.088 e.a.3 f.884 8.441 9.643 0.941 6.4 4.9 6.6 l.014 wat 4.660 8.436 A.414 1.388 4.t', 0.0 9.4 0.0 6.4 #.605 pt 4.430 0.819 6.418 *

.100 4.4 9.9 0.4 9.4 0.0 14448 tht 9.908 9.441 4.441 9.641 5.9 0.0 0.4 0.6 0,4 4.444 5 0.044 9.448 9.941 4.0 6.0 0.0 9.6 0.0 0,6 f.494 889 0.004 6.143 p.941 9.0 0.0 9.9 9.4 8.9 6.4 0.894 es 0.066 9.996 4.442 0.9 9.0 9.4 c.5 0.8 9.6 4.343 1 sat 9.414 9.434 0.304 0.0 9.941 0.641 9.9 4.5 9.9 6.038 6 0.666 0.994 3.313 3.919 4.413 0.338 0.4 9.9 9.6 4.900 ,

j 98w 0.010 0.660 3.841 1.163 0.149 9.409 9.4 0.0 9.6 6.818

$w 9.0$4 9.381 3 ill 4.16% 0.381 9 143 9.4 9.0 8.0 4,let i usw 9.684 4,849 9.436 6.143 9.843 6.641 6.4 9.6 9.6 0.968 y 94009 0.849 0.186 4.518 9.6 d.441 0.0 9.9 9.0 9.166 www 9.464 6.641 0.143 4.391 6.041 4.0 0.6 0.4 0.6 4.410 sw 9.013 0.047 9.41) 6.41) 0.041 6.041 0.9 0.0 9.6 1.144 Nww S.639 0.304 94994 1.114 8.331 9.641 6.9 6.9 9.9 3.944

$V6tetAL 0.438 1.498 14.439 46.148 $.684 0.941 0.9 6.0 a.$ $4.$41 +

total Housa er vatte stAtlLitt obat'sVAttons till total 90Ut3 0P STASILitV (LASS $ itV r total 99994 0F WAtle wl#b SitBCt100-ul#9 f t48D*01 Alf Litt rLAss t 139 TOTAL N0006 9F VAtlb WIND $1&BCil00*WlR$ 5988Da$1Alltitt $$0$$VAtt058 $44)

TOTAL 80U40 (ALM t gjpt P$PHPLA66 fkt00 $ } Q t J1Db SPltp DV ulBD tityCTISW 700.

StASILitt (LAtt F ( l.$t ptLTA tee 4.0 C/869 ap S$9UotAN WVCOBAA PLANT Oct 4. 98

  • pte ll, il wip& WIND $PitDtktal

- QP,,t,,c,tJ0,3 ,,CA1 L 6.t.l.4- 1,l-3.1 9.lan.4 4.5 1.4 1,6-13.e J1.6 10 9 10.5-84.4 Jele.1 total i N 4.084 6.488 3.380 0.648 t=641 8.8 6.0 6.0 0.0 3.446 I put 8.113 0.534 5.884 9.384 9.6 4.4 0.0 9.8 6,4 6.068 NE 0.016 3.134 1.136 9.9 0.0 4.4 0.9 0.0 6.0 3.348 tut 6.699 4.354 0.0 0,0 6.9 9.6 0.0 0.0 0.0 0.393 l 5 0.960 0.304 6.4.1 6.0 6.6 9.6 0.6 0.0 0.0 0.348 I tot 4.904 6.443 8.4 9.0 6.0 6.9 0.4 0.0 6,9 4.146 ft $.940 0.!!1 0.0 0.0 0.6 0.6 0.6 e.6 4.0 4.343 885 0,945 9 384 9.199 9.9 9.9 4.0 S.6 8.8 0.0 9.460 j $ '4.046 0.043 8.413. 0,941 9.4 4.0 0.6 0.0 0.0 0.684

  • sw 0.011 0.343 0.45) 0 941 0.0 6.6 9.0 9,6 6.0 4.41J -

$w 9.033 9.941 9.461 0.189 9.9 0.6 t4 6.6 0.0 0.938 waw 9.066 9.9 9.489 0.996 0.4 6.9 4.9 6.0 9.4 _ 9.3e6

-w 0.061 6.9 9.941 0.041 9.4 0.4 6.9 9.9 0.4 0.694

- WNw 4 0.0 6.041 8.$ 9,9 3.6 9.6 8.696

.w . 9.01

. .- 0. 041

. 9. 41 ... .. 41 ... 4...6 4.. .6 9. 4 l 0.096 0.168 9.684 6,6 0.8 6.9 0.0 1.361 E

  1. pw 4.630 0.0 SUt?OTAL 6.41) 3.104 11.648 1.094 9.696 0.9 0.4 0,0 4,9 41.090

(~

l total ROUT 8 of VAL 3D 8tA83ttft opstpvAt9084 1813 total soups et STAtiLift CLAS$ F .

108 TOTAL 80Vl$ Of VALib WIND Di$$Cfl0N+wlND SVtED*STABIL1tt CLA$$ f $10 T0t&L NOUka OP VALip Wlub tlk&cT405-wlND 4tt#9-STAtl%3f t 0$$ttvatsopt Ill) total 80Ute CALA 16 ,

t l

l -.

+

SON Rad tropact Jan Dec 1991 Page 34 of 36 TAtlLE 4 (page 4 of 4)

S E QUOY AILW C LEAR _MAHI.RIE 0KO LQQl C AW AT A LOURTILOVARTEILR91 J0l NLfR E QUIELD LS T RI WII 0lLilLEE RCE NT folLGEQUllD-LEYEWELEASIE g g f,1 Q Q WTAtt FtitytetIts 0F wtat ettt g g gg,,fity ys pts

$tADIbitt CLAlt G IDttia i a 4.9 t/lte M1 889UOTAN WUCLEAA PLANT cet i, 9 * .tc st, 9 vine wind tttleintui Qtf(flop _(AL A tit =1 4 1 b l. , 4 3,$-9 7 4 .$.l=1.4 11S+13,4 Q.4-It J 10,1 34:4 d L4 ff1AJ s 6.9:1 9.i43 6.169 9.0 4.4 9.4 0.0 0.0 9.6 6.340 est 4.tel 4.349 e.s s 4,6 e.$ 9,e e0 6.0 0.0 0,s41 38 4.483 9.319 6.331 0.6 6.9 0 9.4 44 0.0 0.449 tot 9.466 0.941 0.941 0.0 0.6 0. 4.4 6.4 9.6 9 464 8 9.613 9.189 4.941 4.6 9.0 4.0 9.9 0.4 9.4 4.349 set 6.G43 6.641 4.9 9.9 4.0 9.6 0.6 9.6 9.4 4.tle at 6.443 0.381 9.6 0.0 0.0 9.6 0.0 0.0 0.0 9.340 est 6.434 0.181 4.381 4.9 4.4 0.0 0.4 0.0 9.9 0.966 9 9.934 0.140 4.849 6.4 0.6 9.9 4.4 6.0 9.9 0.399 stw 9.033 6.996 4.411 9.4 4.e 0.0 4.4 9.9 tot 9.648 tw 4. ell 4.9 0.411 4.310 4.9 0.0 9.9 4.0 9.0 9.411 wsw 9.903 0.0 0.941 0.6 9.6 4.0 0.0 0.0 4.f 4 944 w 9.6 9.4 6.4 9.ie? 4.0 9.9 9.9 9.4 4.4 9.941 www 4.0 0.6 9.9 9.0 0.9 9.9 6,0 4.0 6.9 0.6 NW t.4 0.0 0.0 0.0 4.0 6.0 0.0 6.0 0.0 9.9 spw 6.003 9.647 9.4 9.0 9.9 0,0 9.4 9.4 9.9 9.0$$

SUttetAL 6.331 4.494 3.444 9.436 0,6 0.0 6.9 9.6 9,9 6.461 total movat CF WALID STAi!LITT $3880Vatt0NS 2115 total NOUS 0 DF statttttf CLAtt e lit total NOVat Of VALID vlND D3ttCTIONewtWD 8tttD* STAB!Litt CL&80 e let tDTAL Woul8 OF TALID WIND D16tCit05-wtWD St$tD*STABILITt 0$sttVATION8 3443 TOTAL MOValt (ALM S MEtt 9801008 0 AL F ACILitV1 $$9UOTAN BUCLSAs PLANT STAttt!TT SAstD ON LAttt satt alAattt0 887wt85_ 9.13 ptftt t4Vtb t.39 AND 46.99 WE1884 W1pD attt0 AND DIntCTION MEAsvttD At 158 DAtt tStattDt 91/43'?9 MEAU W1hD Sitt0 e 1.4 Mid sotti TOT ALS AND SVlt0TALS ADOTE Att OttAINED f BOM VRDOUN9tt NUMettl 0017v l

i i

_ 5

f SON Rad impact Jan-Dec 1991 Page 35 of 36 TA!!LE 5 S COUQY All_14UCLE AIL I1 ANT _:. RECEPIOR. LOC AT1011S Site Boundary Locations (used for both all quarters)

Sector Distance (m) Sector Distance (m)

Site 11oundary N 9LO Site Boundary 5 1570 Site Boundary HilE 2260 Site lioundary SSW 1840 Elto Doundary NE 1910 Site boundary SW 2470 Site Doundary EllE 1680 Site Boundary WSW 910 Site Doundary E 1570 Site Boundary W 670 Sito Doundary ESE 1460 Site Boundary WiiW 660 Site Boundary SE 1460 Site Boundary WW 600 Site Boundary SSE 1550 Site Doundary HNW 730 Actual Receptor Locations (based on the "all 1991 Lt.nd Use Survey)

Sector Distance (m) Sector Distanco (m)

Resident. N 1353 Garden N 1829 Resident NNE 2400 Garden NNE 3048 Resident HE 2248 Resident ENE 2096 Garden ENE 2496 Resident E 1619 Garden ESE 1791 Resident ES" 1638 Garden SE 3162 Realdent SE 1662 Cardon S 2362 Resident, Car den SSE 1943 Garden SSW 2686 Roaldent S 2286 Garden SW 3353 Resident SSW 2019 Gardon WSW 1524 Resident SW 2972 Garden W 1987 Resident WSW 1143 Garden WNW 1867 Resident W 1010 Garden NW 1372 Resident WNW 1753 Garden NNW 991 Resident NW 1448 Milk Cow Adult N 4515 Resident NHW 895 Milk Cow Adult NE B686 Milk Cow Adult WNW 2096 Milk Cow Adult NW 2134 0017v

SQW Had Impact Jan-Dec 1991 Page 36 of 36 TABLE 6 SUMARLOLOUARTERLLDOS ES*

Air Submersion Real Pathway Liquid Effluents

_Ain y_ Air 2D_ __._7D_.__ Skin _ _ Eex._Orgatt _ ID _ Eox u0rgort Year QTR (mrad) (mrem) (mrem) (mrem) 1983 1 0.03 0.18 0.04 0.02 <.001 Bone 0.21 0.34 Bone 2 0.12 0.48 0.21 0.10 0.02 GIT 0.15 v.23 Bone 3 0.07 0.40 0.11 0.05 0.03 Bone 0.09 0.20 Bone 4 0.07 0.41 0.09 0.04 0.003 Thyroid 0.11 0.14 Liver 1984 1 0.11 0.55 0.19 0.08 0.004 Thyroid 0.04 0.05 Liver 2 0.17 0.94 0.29 0.12 0.04 Bono 0.04 0.04 Liver 3 0.18 0.99 0.26 0 . '.1 0.03 Thyroid 0.13 0.22 Bone 4 0.07 0.39 0.12 0.05 0.005 Thyroid 0.04 0.06 Liver 1985 1 0.12 0.65 0.18 0.09 0.18 Thyroid 0.03 0.04 aone 2 0.10 0.63 0.18 0.07 0.003 Th)rold 0.34 0.21 Bone 3 0.05 0.32 0.08 0.03 0.015 Thyroid 0.17 0.43 Bone 4 <.001 0.001 0.0 0.0 0.018 Thyroid 0.02 0.02 Bone 1986 1 <.001 c.001 <.001 c.001 0.004 GIT 0.007 0.009 Liver 2 <.001 <.001 c.001 c 001 0.014 Liver 0.018 0.021 Liver 3 c.001 <.001 0.0 0.0 0.010 GIT 0.038 0.044 Bone 4 <.001 <.001 0.0 0.0 0.010 GIT 0.011 0.012 Liver 1987 1 <.001 <.001 0.0 0.0 0.004 GIT 0.002 0.003 Liver 2 c.001 <.001 0.0 0.0 0.006 GIT 0.017 0.021 Liver 3 <.001 4.001 0.0 0.0 0.008 GIT 0.084 0.095 Bone 4 <.001 <.001 0.0 0.0 0.006 GIT 0.034 0.039 Bone 1988 1 <.001 <.001 0.0 0.0 0,001 Liver 0.055 0.074 Liver 2 0.003 0.014 0.004 0.002 0.003 Thyroid 0.18 0.21 Bone 3 0.007 0.036 0.008 0.003 0.007 Bone 0.054 0.064 Bone 4 0.007 0.037 0.012 0.005 0.003 GIT 0.009 0.01 Liver 1989 1 0.02 0.02 0.01 0.02 0.007 Thyroid 0.001 0.002 Thyroid 2 0.03 0.06 0.02 0.03 0.003 Liver 0.002 0.002 Liver 3 0.07 0.17 0.04 0.08 0.03 Thyroid 0.001 0.001 Liver 4 0.22 0.61 0.15 0.34 0.009 Thyroid 0.005 0.006 Liver 1990 1 0.26 0.69 0.17 0.41 0.002 Liver 0.001 0.001 GITract 2 0.05 0.15 0.04 0.09 0.002 Thyroid 0.002 0.005 GITract 3 0.10 0.27 0.07 0.17 0.002 Thyroid 0.002 0.003 GITract 4 0.008 0.02 0.006 0.015 0.002 Thyroid 0.001 0.002 Liver 1991 1 0.02 0.04 0.01 0.03 c.001 Liver 0.003 0.004 Liver 2 0.03 0.07 0.01 0.03 0.004 Thyroid 0.010 0.012 Liver 3 0.06 0.15 0.04 0.08 0.003 Thyroid 0.012 0.015 Liver 4 0.03 0.05 0.02 0.04 0.017 Thyroid 0.016 0.021 Liver

  • Note All calculated doses are below limita specified in Appendix I to 10 CFR 50.

0017v s

M ENCLOSURE 3 CORRECTION PACE TO THE EFFLUENT AND WASTE DISPOSAL SEMIANNUAL REPORT 2ND HALF 1990

- SOLID WASTE (RADIOACTIVE SHIPMENTS)

(S$2 920214 088) f t

i 9

3 b

F h

I h

i

-. . _ - , , . - - - . . . . - ..- , . _ , . _ . . _ _ _ , _ . - - , --e.-- _ _ . . __,,,..~_..,_,,_._,,,.__-,,,...,.-,._,,_._.,,....<,_,.,...,.a -

CElTLUENT AND WASTE DISP 0 SAL SI:Hl ANNUAL l<El' ORT 2nd ilALP 1990 SOLID WASTE (RADIDACTIVE SillpHENTS)

A. Solid Waste Shipped offsite for burial or Disposal (not Irradiated Fuel) 6 Honth Est. loL..

1. Type, oLWasio Unit l'ori os! Error,_h
a. Spent repitio, f11ter sludgeo, in3 3.01E41 31. 00E- 1 evaporator bottoms, etc. Ci 6.20K+2 11.50E+1
  • b. Dry Active Waste, comproccible Waste m3 1.37E+2 + 1. 00E- 1 Contamincted Equipment, etc. Ci 2.72E+1 11.50E+1
c. Irradiated Componento, m3 None N/A Control Hods, etc. Ci Nono N/A
d. Othert (describo) m3 None N/A Composito liners (containing wet rages, Ci None N/A resin, incehanical i11tero and inclui oxideo in boric acid concent rateo) and oil liners
2. Entlinato of Halor Hitgl_ido_Componit ion My_ type pf _wagt_el
a. Spent resin, filter sludgeo, ovaporator bottomo, etc.

(nucliden determined by steucurement)

.cu.rif g ['epqmit

1. Manganene 54 3.14E+1 5.01E+0
2. Iron-55 1.13E+2 1.81E+1
3. Cobalt-58 2.34E+2 3.74E+1
4. Cobalt-60 1.03E+2 1.64E+1
5. liickel- 6 3 3.55E+1 5.67E40
6. Cesium-134 4.88E41 7.79E40
7. Cecium-137 5.79E+1 9.26E+0
b. Dry active waste, comprecoible waste, contaminated equipment etc.

(nuclides determined by entiinate)

1. Chromium-51 2.34E+0 8.64E40
2. Iron-55 1,14E+1 4.21E+1
3. Cobalt-58 7.11E+0 2.62E41
4. Cobalt-60 3.51E+0 1.30Et1
5. Nickel-63 1.58E+0 5.83E+0
6. Niobium- 95 6.03E- 1 2.22E40
c. Irtadiated Componento N/A N/A
d. Other: None N/A N/A
  • An nrror in the exponent was detected in the Solid Waste portion of the Second Half 1990 Effluent and Waste Dispocal Semiannual Report. Thio page in being resubmitted with the corrected DAW curio amount. The original submittal was incorrect by a power of 10.

The actual amount 10 27.2 curies rather than 272 curica.

419/1

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