ML17285A261

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Semiannual Effluent Rept,Jul-Dec 1988
ML17285A261
Person / Time
Site: Columbia Energy Northwest icon.png
Issue date: 12/31/1988
From:
WASHINGTON PUBLIC POWER SUPPLY SYSTEM
To:
Shared Package
ML17285A259 List:
References
NUDOCS 8902230545
Download: ML17285A261 (92)


Text

8902230545 8902i5 PDR ADOCK 05000397 R

PDC

REFERENCE:

10CFR50.36a(a)(2)

WNP-2 SEMIANNUAL EFFLUENT REPORT JULY TO DECEMBER 1988 WASHINGTON PUBLIC POWER SUPPLY SYSTEM LICENSE NO.

NPF-21

TABLE OF CONTENTS

~ECCH

1.0 INTRODUCTION

2.0 LIQUID EFFLUENTS 3.0 GASEOUS EFFLUENTS 4.0 SOLID HASTE 5.0 METEOROLOGICAL DATA 6.0 DOSE ASSESSMENT IMPACT ON MAN 7.0 REVISIONS TO THE ODCM 1

1 5

16'2 35

~

42

I

LIST OF TABLES 2-1 2-2 JL3 LE WNP-2 LIQUID EFFLUENTS SUMMATION OF ALL RELEASES JULY DECEMBER 1988 2

WNP-2 LIQUID EFFLUENTS SOURCE TERMS JULY DECEMBER 1988 3

3-1 3-2 3-3 3-4 4-3 WNP-2 GASEOUS EFFLUENTS SOURCE TERMS MIXED MODE RELEASES MAIN PLANT VENT JULY DECEMBER 1988 WNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES TURBINE BUILDING JULY DECEMBER 1988 WNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES RADWASTE BUILDING JULY DECEMBER 1988 WNP-2 GASEOUS EFFLUENTS SUMMATION OF ALL RELEASES JULY DECEMBER 1988 WNP-2 GASEOUS EFFLUENTS BATCH RELEASES JULY DECEMBER 1988 SCALING FACTORS FOR REQUIRED NUCLIDES.

SCALING FACTORS FOR CONDITIONAL NUCLIDES WNP-2 SOLID WASTE SHIPMENTS JULY DECEMBER 1988

~

~

7 10

~

~

12

~

14

~

15 19

~

19 20 5-1 5-2 5-4 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

CALCULATED FROM HOURLY AVERAGES FROM TAPE-1ST QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

CALCULATED FROM HOURLY AVERAGES FROM TAPE-1ST QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

CALCULATED FROM HOURLY AVERAGES FROM TAPE-2ND QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

CALCULATED FROM HOURLY AVERAGES FROM TAPE-2ND QUARTER 1988 LEVEL LEVEL LEVEL LEVEL

~

~

23 24 25 26 5-5 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

CALCULATED FROM HOURLY AVERAGES FROM TAPE-3RD QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

CALCULATED FROM HOURLY AVERAGES FROM TAPE-3RD QUARTER 1988 LEVEL LEVEL 27 28

'IST OF TABLES (Continued) 5-7 5-8 5-9 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE-4TH QUARTER 1988 29 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE-4TH QUARTER 1988 30 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE 1988 ANNUAL..

31 5-10 5-11 5-12 6-2 6-3 6-4 6-5 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

LEVEL CALCULATED AVERAGES FROM HOURLY AVERAGES FROM TAPE 1988 ANNUAL JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE VENTS AND PURGES 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE VENTS AND PURGES 1988 MAXIMUM INDIVIDUALDOSES FROM WNP-2 LIQUID EFFLUENTS 1988 AVERAGE INDIVIDUALDOSES FROM WNP-2 LIQUID EFFLUENTS 1988 50-MILE POPULATION DOSES FROM WNP-2 LIQUID EFFLUENTS 1988 50-MILE DOSES FROM WNP-2 GASEOUS EFFLUENTS 1988

SUMMARY

OF DOSES FROM WNP-2 GASEOUS EFFLUENTS 1988 32 33 34 36 38 39 40 41

1.0 This report is submitted in compliance with Technical Specification 6.9.1.11.

It includes a

summary of the quantities of radioactive liquid and gaseous effluents and solid waste released from NNP-2 during the previous six months of operation with'data summarized on a quarterly basis.

2.0 The radwaste liquid effluents were released in a batch mode only during the reporting period.

Four batch releases occurred during the third calendar quarter and 2 batch releases during the fourth calendar quarter.

The total time period for the batch releases was 10.8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br />, with the maximum time period being 2.3 hours3.472222e-5 days <br />8.333333e-4 hours <br />4.960317e-6 weeks <br />1.1415e-6 months <br /> for a release, the minimum time period being 1.1 hours1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> for a release and the average time period was 1.8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br />.

The volume of dilution water considered, is the total volume of recirculating cooling tower blowdown flow for the period.

The average flow rate of the Columbia River during July through December 1988 was 96,743 cubic feet per second.

Periodic LADTAP II computer runs were performed to verify compliance with Technical Specification limits.

The calculated dose to the adult individual due to liquid releases for the third quarter was 7.9E-05 mrem whole body and 1.2E-04 mrem for the maximum organ.

The fourth quarter calculated dose was 1.5E-05 mrem whole body and 3.3E-05 mrem for the maximum organ.

The liquid batch releases were recirculated prior to sampling, A repre-sentative sample was obtained and analyzed for each batch release.

A composite of batch samples for each quarter was analyzed for strontiums and irons.

The method for measurement of total radioactivity was by gamma spectroscopy, liquid scintillation and proportional counters.

The percent of HPC limit is based on the total HPC fractions using those nuclides in Table 2-2 and concentrations listed in 10CFR20, Appendix B, Table 2, Column 2.

The estimated total errors are listed in Table 2-1.

These estimated errors are propagated from individual error estimates of sample activity, sample

volume, tank volume and tank homogeneity.

The estimated total errors were calculated by obtaining the square root of the sum of the squares of the errors of the individual contributors and multiplying by 1.96 for a 95% confidence level.

Table 2-1 WNP-2 LIQUID EFFLUENTS SUMMATION OF ALL RELEASES July December 1988 Unit 3l d Quarter 4th Quarter Est.

Total A.

Fission and activation products 1.

Total release (not including 2.

Average diluted concentration ri B.

Tritium 1.

T 1

2.

Average diluted concentration P r C.

Dissolved and entrained gases E-2

~F~ ~2F~

1.1 2

2 '

+

2.

Average diluted concentration

~2E-5 D.

Gros s al pha radi oac tiv ity 0

4.

T 1 r 5.

E-0 3.

E-1

2. 3 E+01 E.

Volume of waste (prior to il in li er 2.

E+05 1.1E+

5 1.5 E+01 F.

Volume of dilution water r

"At 951. confidence level 5.

E l.

E+

Table 2-2 NNP-2 LIQUID EFFLUENTS SOURCE TERMS July December 1988 BATCH MODE Nuclides Released Unit 3rd Quarter 4th Quarter 02 E-w 4.4

.4 I

n-4 4

(

~

~ 7

~ 2.

E-

.1

TABLE 2-2 (Continued) 4 2 l.

E-4 1

,2 -2 5QIK:

Less than (~) values are not included in the Total For Period values.

3.0 The gaseous radwaste effluents from HNP-2 were released from three (3) release points at NNP-2.

1.

Main Plant Vent mixed mode release 2.

Turbine Building ground level release 3.

Radwaste Building ground level release The gaseous source terms from each release point are listed in Tables 3-1 to 3-3.

Table 3-4 provides a summation of the total activity released, the average release

rate, the percent of Technical Specification limit, gross alpha radioactivity and the estimated total error associated with the measurements of radioactivity in the gaseous effluents.

Radioactivity measurements for gaseous effluent releases are performed for fission and activation gases by collecting the samples on charcoal traps and analyzing them using gamma spectroscopy.

Tritium is sampled by freeze trapping and analyzed by liquid scintillation counting.

Particu-lates and iodines are sampled using particulate filters and charcoal cartridges and analyzed by gamma spectroscopy.

To verify compliance with Technical Specification limits, calculations were performed for each month's releases using the GASPAR II computer program and parameters as outlined in the ODCM.

Doses were determined at two special locations.

1.

The Site Boundary at 1.2 miles from the plant and for the sector with the maximum X/Q value.

2.

Taylor Flats at 4.2 miles ESE.

The "Percent of Technical Specification Limit" calculations were based on exposure at specified locations.

Air dose due to noble gases was deter-mined at the site boundary with the quarterly limit of 5 mrads for gamma being the more restrictive for each time period.

The gamma air dose from noble gases f'r the third quarter was 3.5E-02 mrads and 4.5E-02 mrad for the fourth quarter.

Iodines, particulates and tritium calculations were determined at Taylor Flats, located 4.2 miles east southeast.

A limit of 7.5 mrems per quarter to any organ was used in these calculations.

The maximum organ dose to a "Member of the Public" was 4.6E-03 mrem for the third quarter and 3.5E-03 mre'm for the fourth quarter.

There were no abnormal releases of gaseous effluent during the third and fourth quarters of 1988.

Total error estimates are propagated from individual error estimates of sample

volume, sample activity and effluent flow rate measurements.

The overriding uncertainty is the measurement of the effluent and sample volumes.

The estimated error was determined to be 36/. at the 95/

confidence level.

HNP-2 has a permanent laundry facility located approximately 0.75 miles from the site.

Its ventilation system contains HEPA filters on the discharge and is continuously monitored for particulates.'lso at this location is a backup chemistry lab within the EOF.

The radiochemical hood containing HEPA filters is monitored for radioactive releases when in operation.

Gamma spectrometry indicated no radioactive material present other than that attributable to natural background.

There were four NCRs during this reporting period, they are summarized below:

NCR 288-0365 The environmental monitoring program requires that liquid samples be taken in our discharge line to the Columbia River.

The sampling compositor is experiencing intermittent failures.

Sampling is being assured by the use of grab samples taken periodically and at times of liquid radwaste discharges.

The compositor problem is currently being evaluated by plant engineering.

NCR 288-0413 Continuous sampling by the reactor building effluent monitor was interrupted by the shutting down of the HVAC system and turning on the Standby Gas Treatment System (SGTS).

Two four-hour sampling periods were missed during the 10.62 hour7.175926e-4 days <br />0.0172 hours <br />1.025132e-4 weeks <br />2.3591e-5 months <br /> time period; estimation of offsite dose consequences yielded no effect as the reactor was shut down and other in-plant monitoring showed no activities above normal.

NCR 288-0445 Engineering evaluation is currently in progress on the inability to adequately sample the reactor building effluents when stack flow is less than 4,000 cfm.

Full evaluation of the stack sampling system capabilities for the low flow conditions is schedule for next outage.

The current solutions are to operate both SGTS trains when the HVAC is secured and/or install a portable sampler.

NCR 288-0565 Standby service water sampling periods were missed because of a missunderstanding of the operability of the particular loop.

The sampling was instituted 2.4 days after the LCO was instituted for a process monitor failure.

Changes in procedures and specific training for the departments involved, especially emphasising Tech.

Spec.

actions,

'ave been instituted.

l J

(

~

F, I

Table 3-1 HNP-2 GASEOUS EFFLUENTS SOURCE TERMS MIXED MODE RELEASES MAIN PLANT VENT July December 1988 CONTINUOUS MODE 1.

Fission gases 3rd 4thr r

n-en n-1 2,

2.

E-1 E-1 l.

E l.

E E

E-l.

E E-1 E+

E 1

l.

E 2.

T 1 fr 2.

Iodines

,1 E

I dn-1 I

T ri E-4.2 E-4

+ 5.

E-4 E-4 E-04 4

4.

E 4

Kr-85 value is a fission product ratio from other fission gas isotopes.

3.

Particulates Table 3-1 (Continued) l.

f-4 4

2.

f-

~num 4

~3 M;L, T

1 r

r 2.4

Table 3-1 (Continued) 3.

Particulates 4,

2 5QIK:

Less than (~) values are not included in the Total For Period values.

9

Table 3-2 WNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES TURBINE BUILDING July December 1988 CONTINUOUS MODE 3l d 4th 1.

Fi ss ion gases E

E-E 4.

c, 1

2.

Iodines 59K:

Kr-85 value is a fission product ratio from other fission gas isotopes.

10

0 0

Table 3-2 (Continued) 3, Particulates r

m-c E

c2

-0 4,

5QIK:

Less than (~) values are not included in the Total For Period values, 11

Table 3-3 NNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES RADHASTE BUILDING July December 1988 CONTINUOUS MODE 3l d 4th 1.

Fission gases

-1 <l.

-1 E-1 E-e

-1

~1.

E 0

uU-.~

c, 1

~P~1 r

r E

1 2.

Iodines I

n 3

2.

E-l.

E-4 2.0 E-4 E-

.7 E-4

< 1.7

-04 E-0 Kr-85 value is a fission product ratio from other fission gas isotopes.

12

Table 3-3 (Continued) 3.

Particulates

~ 2.

E-E-

e E-c 4

<l.

-5 Ir n-c

~ngm 4

~Z~ er w l.

E-

<2 E-4.

T E-1 T

il in 1

1 E+

2.

E+

1 5QTT,:

Less than (~) values are not included in the Total For Period values.

13

Table 3-4 HNP-2 GASEOUS EFFLUENTS SUMMATION OF ALL RELEASES July December 1988 A.

Fission

& activation gases 3l d 4th r

Tata1~m 2.

Average release f

3.

Percent of Tech.

,4 B.

Iodines 1.

Total iodine 2.

Average release 3.

Percent of Tech.

E-

.1 -2

,4 C.

Particulates 1.

Particulates 2.

Average release 3.

Percent of Tech.

4.

Gross alpha vi D.

Tritium

~

2 20 Q~rlMRk 2:

Average release r

f r ~eri 3.

Percent of Tech.

i

  • At 951. confidence level 1/

c 3

2.4 E-1 4.

Table 3-5 WNP-2 GASEOUS EFFLUENTS BATCH RELEASES July December 1988 Purge m

e 13 Total 255 Maximum Tim 127 Minimum T'.2 Mean 19.6 15

A total volume of 6786.3 ft3 (192.2 m3) of solid waste was transported in 23 shipments during the July through December 1988 reporting period.

The total activity of the waste shipped was 816, 1 Ci; 813 Ci contained in dewatered spent resins and 3.10 Ci in Dry Active Haste (DAH).

A.

Dewatered resins accounted for 4196.3 ft3 (118.8 m3) of the radioactive wastes shipped during the reporting period.

The burial containers were ES-190, ES-142, EA-142 and PL-142 liners provided by NUPAC Services, Inc.

The total activity of the resins shipped during the reporting period was 813 Ci.

The principle nuclides and their percent contribution to the total activity are listed in Table 4-3.

The solid wastes were shipped to the U.S.

Ecology, Hanford burial site using flat bed trailers, shielded van and LN-142, NUPAC 10-142, LN 14-170, or U.S.Ecology 14D-2.0 casks as appropriate.

The counting error associated with the total activity has been found to be less than 1.0% at one standard deviation in previous effluent reports and to decrease with increasing activity.

The statistical counting error is assumed to be 1% for the purpose of this error evaluation.

Other parameters considered in estimating the total error of the activity shipped included the error in measuring the absolute

volume, the weight of the waste in the liners, the representative-ness of the sample
taken, the homogeneity of the nuclide distribu-tion within a batch or liner and the geometry error in the gamma spectroscopy analysis.

The gamma spectroscopy calibration error was approximately 5%.

The best estimate of the total error in the activity of spent resin shipped was assumed

.to be less than or equal to 20%.

B.

D A total of 2590 ft3 (73.3 m3) of DAW was shipped in 28 Container Products Corporation, B-25 steel boxes.

The total activity of the DAH shipped was 3.10 Ci.

The values for the activities shipped were determined by using dose rate-to-curie conversion factors.

The con-version factors were based on a nuclide distribution taken from analysis of contamination found in each of the major DAH production areas.

The nuclide distribution is updated monthly.

Short lived nuclides were eliminated based on decay of the DAH prior to shipment.

A meaningful counting error cannot be generated for the DAH, however, the total error may be assumed to be less than or equal to 20% since DAW would be subjected to similar error contributions as the spent resins.

16

4.1 Scaling factors are based on outside laboratory (SAIC) analysis of hard-to-measure nuclides.

The process of updating scaling factors is being initiated.

For those waste streams where the scaling or the scaled nuclide concentration is not sufficient to provide a

viable scaling factor, the final EPRI Report "Updated Scaling Factors in Low Level Radwaste",

NP-5077, March 1987 has been used as a basis for the determination of a scaling factor.

r Sampling of individual waste streams was performed with analysis provided by an outside

lab, The H-3 concentration was measured per gram of waste material.

This value was compared to the Reactor Coolant System H-3 concentration.

The scaling factor is derived from the ratio of the H-3 concentration in the waste stream to RCS H-3 concentration, Sampling of the individual waste stream was performed with analysis by off-site lab to determine isotopic concentration, Ratios were developed between the scaled nuclide to the scaling nuclide concen-tration determined by analysis.

In those cases where the scaling nuclide is not available in large enough quantities to develop reliable (viable) scaling factors, the recommendations made in section 7 of the referenced EPRI report for the plant in the initial stages of operation are used.'RU nuclides were scaled to Ce-144, as recommended by the AIF report "Methodolgies for Classification of Low Level Radioactive Waste from Nuclear Power Plants".

These nuclides are not considered to be present if the scaled values are less than:

1 nCi/g for TRU, 35 nCi/g for Pu-241 or 200 nCi/g for Cf-242.

TRU nuclides will be reported if the scaling nuclide (Ce-144) is reliably detected and Cs-137 is also present.

Sampling of individual waste streams has been performed with analysis by an outside laboratory.

Cs-137 and Sr-90 concentrations were measured in each waste stream except waste oil.

The ratio of Cs-137 to Sr-90 has been determined and is used as the scaling factor for Sr-90 from Cs-137.

For waste oil, the values from the referenced EPRI Report will be used for scaling factors.

Co-60 and Ni-63 concentrations were measured in each of the sampled waste streams.

The ratio of Co-60 to Ni-63 has been determined and is used as the scaling factor for Ni-63 from Co-60.

17

4.2 Table 4-1 lists those scaling factors by waste stream for those nuclides that are required to be reported.

Table 4-2 lists those scaling factors for the conditional nuclides that are reported only when the scaling nuclide is found to be present.

The Process Control Program (PCP) used to control solidification at WNP-2 will be provided by the vendor waste processor, Pacific Nuclear Inc. in accordance with Contract C-20452, and will be subjected to POC review prior to any solidification of radwaste.

Two Pacific Nuclear generic solidification PCP's, TP-04, "Portable Solidifica-tion System",

and TP-05, "Radwaste Solidification System",

are currently under NRC review.

As an alternative, approved High Integri ty Containers (HIC's) could be used for the transport of wastes requiring stabilization.

Other portions of the radwaste program are controlled by the WNP-2 procedures PPM 1.12.1, "Radwaste Management Program",

PPM 1.12.2, "Radwaste Process Control Program",

and 1.12.3, "Contract (Vendor)

Waste Processing".

There were no significant changes during the reporting period.

18

SCALING FACTORS H-3/Rx Coolant C-14/Co-60 Tc-99/Cs-137 I-129/Cs-137 3.5E-l 1.47E-4 4.6E-4+

4.6E-4+

RWCU POWDER KMH 4.55E-1 1.69E-5 1.94E-6 2.23E-S CFD POWDER KSZH 4.55E-1 6.2E-4++w 9.3E-5+

3.9E-5+

EDR/FDR POWDER KSLH 4.55E-l 1.18E-3 9.3E-5+

3.9E-5+

EDR/FDR BEAD KSLH 3.56E-l 5 '1E-2 9.3E-5+

3.9E-5+

3.10E-1

8. 81E-5 9.3E-S+

3.9E-5+

4.0E-5+

1.3E-2+

4.2E-5+

6.3E-5+

Ni-63/Co-60 Fe-55/Co-60 Sr-90/Cs-137 Pu-239/Ce-144 Pu-238/Pu-239 Pu-241/Pu-239 Am-241/Pu-239 Cm-242/Pu-239 Cm-244/Pu-239 1.86E-2 2.62E-l 2.6E-3+

4.5E-3+

1.5EO+

1.1E2+

9.1E-1+

9.5E-1+

7. 2E-1+

7.73E-3 2.37E-1

1. 19E-4 9.1E-3+

1.3EO+

8.8E1+

9. OE-1+

1.0EO+

8.3E-1+

1.3E-2 5.16E-l 3.88E-2 9.7E-3+

1.7EO+

9.6El+

6.6E-1+

9.7E-l+

7.6E-1+

4.53E-2 6.03E-1 2.92E-3 9.7E-3+

1.7EO+

9.6E1+

6,6E-l+

9. 7E-1+

7.6E-1+

6.36E-2 1.9E-2 1.11E-3 9 'E-3+

1.7EO+

9.6El+

6 'E-1+

9.7E-1+

7.6E-l+

1. 5E-2+++
4. 10E-1 2.67E-5 8.7E-4+

1.7EO+

9.6El+

1.7EO+

5.7E-1+

7.8E-1+

1.2EO+

1. 5EO+

3.3E-1+

l. 1E-2+

1.6EO+

1.2E2+

4 'E-1+

3. 1E-1+

2.9E-l+

+ Scaling or scaled nuclide not present in enough concentration to make determination of scaling factor.

In these cases the scaling factor obtained from the "Updated Scaling Factors in Low-Level Radwaste" EPRI NP-5077 Final Harch 1987.

++ The report from SAIC, showed the H-3 concentration in RWCU equal to Reactor Coolant concentra-tion.

The resin mix used in RWCU and CFD are the same.

The reactor coolant and condensate H-3 concentration are approximately the same.

The Scaling Factor for CFD is a 4.55E-l which is more representative of H-3 retention on the two resin streams.

+++ The report from SAIC showed the Ni-63 concentration of sludges at 4.03E-3 uCi/gm which compares to the Co-60 concentration of 3.52E-2 uCi/gm.

This comparison would yield a Scaling Factor of 1.14E-l.

The above mentioned EPRI Report recommends a Scaling Factor of 1.5E-2.

Because of the long period of time between the generation of the waste and the counting of the sample (approximately 1 year) the EPRI Number is considered more accurate.

++++ The report from SAIC showed the C-14 concentration in CFD of 1.12E-2 uCi/gm which compares to the Co-60 concentration of 1.08E-2 uCi/gm.

This comparison would yield a Scaling Factor of 1.02EO.

The above mentioned EPRI report recommends a Scaling Factor of 6.2E-4.

It is felt that there was cross contamination of the sample at the lab resulting in high concentration of C-14.

The recommended EPRI number will be used.,

19

'C I

I

,1 tI

Table 4-3 HNP-2 SOLID HASTE SHIPMENTS July December 1988 A.

SOLID HASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL 1.

Type of Haste Haste Stream a.

Spent resins, filter sludges, eZm r b.

Dry active waste, contaminated Unit m3 1

m3 6-month P

118.8 1

73.34 Est. Total E

c.

Irradiated components, control m3 d.

Other, (absorbed aqueous liquid) m3 No 2.

Estimate of major nuclide composition (by type of waste):

a.

Dewatered Spent Resins 3

2

  • 7.

,7

.2 4.

E2 2

4.4 E

2 ~l 5

1

  • Indicates scaled nuclide 20

I',

II I

V'

b.

Dry Active Hastes (DAH) 0 Fe-5*

N-5 c.

Irradiated Components None d.

Other Absorbed Liquids None 3.

Solid Haste Disposition E-1

~QE-2 E-

' 7 2

E-2 E-23 14D-2.0 Cask (ll)

Flat bed trailer (4)10-142 Cask (2)14-170 Cask (3)

LN-142 Cask (2)

Shielded Van (1)

US Ecology

Richland, HA B.

IRRADIATED FUEL SHIPMENTS (Disposition)

None

  • Indicates scaled nuclide 21

5.0 The meteorological data contained in Tables 5-1 through 5-10 were obtained from the WNP-2 meteorological tower located 2500 ft. west of WNP-2.

Data were recovered from 33 ft. and 245 ft. levels.

The meteorological data is a composite file from both manual and automated data recovery systems.

All four quarters of 1988 were drier than normal with moderate precipita-tion arriving in the fourth quarter.

The 1988 dispersion conditions compared well with historical dispersion conditions.

The automated annual data recovery system continued to function at greater than 90%

joint data recovery for the joint frequency parameters.

Tables 5-1 through 5-8 list the joint frequency distribution at the 33 ft. and 245 ft. levels for 1988 by quarters.

Additionally, this report includes Tables 5-9 through 5-10 which list the joint frequency distribu-tion for all of 1988.

The tabulated stability classes, A-G, are denoted by numerals 1-7 respectively.

Numerals 1-7 were used for the wind sub-fields as is noted at the top of each sensor level reported.

The 16 compass sectors in Tables 5-1 through 5-8 pertain to the direction the wind is coming from.

Tables 5-11 and 5-12 are representative Joint Frequency Tables for vents and purges during 1988.

Calibrations performed in 1988 produced no values exceeding WNP-2 FSAR meteorological equipment tolerances.

Therefore, no correction has been made to the raw data.

The NRC Delta Temperature Stability Classification scheme was utilized in the production of all joint frequency tables.

A new magnetic disk data recovery system was installed during Quarter 3

with significant data recovery to near 1001. for Quarter 4.

22

TABLE 5-1 1ST QUARTER 1988 JOINT FREOUEtiCY DISTRIBUTIOH FOR THE 33 FT LEVEL CALCULATED FRON HOURLY AVERAGES FRON TAPE 0.6 MAXIMUMHltiD SPEEDS FOR EACH CATESORY IH NPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0 5 - 18.0 tiUNBERS GIVEN ARE HOURS 6 - 24.0 STAB CLASS 1

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TABLE 5-3 2HD QUARTER 1988 JOINT FREQUENCY DISTRIBUTIOH FOR THE 33 FT LEVEL CALCULATED FRON HOURLY AVERASES FROH TAPE 1 - '.6 NAXlttUH MIND SPEEDS FOR EACH CATESORY IN MPH ARE:

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0.

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0.

0.

0.

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13.

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0.

0.

0.

0.

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0.

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0.

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0.

0.

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0.

0.

0.

0.

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11.

20 0.

0.

0.

9.

7 ~

1.

0.

0.

0.

0.

2 ~

0.

0.

0.

0.

0.

0.

7.,

18.

4.

1.

0.

0.

0.

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2.

0.

1 ~

0.

0.

0.

0.

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2.

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0.

0.

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11.

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11.

0.

0.

0.

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19.

1 ~

0.

0.

0.

12.

13.

0.

0.

0.

0.

0.

b.

0.

0.

0.

0.

TOTAL HUHBER OF HOURS USED 1921 HISSI 0

CALM VARIABLE =

40 25

g'I r

II

!II f

TABLE 5-4 2HD QUARTER 1988 JOINT FREQUENCY DISTRIBUTIOH FOR THE 245 FT LEVEL CALCULATED FRDN HOURLY AVERAGES FRON TAPE HAXINUH MIND SPEEDS FOR EACH CATE60RY Itl HPH ARE:

0.6 2 -

3.0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0 NltlD H

tNE NE ENE NUttBERS 6IVEH ARE HOURS t

E ESE SE SSE S

SSN SN NSN NttN

tlN, HHN CLAS 1

1 1

1 1

2 2

2 2

2 2

3 3

3 3

4 1

2 3

4 5

6 7

1 2

4 5

6 7

1 2

3

'4 5

6 7

1 2

4 5

6 7

1 2

3 5

6 7

I 2

5 6

7 1

'2 3

4 5

6 CAT 0.

0.

lb.

1.

0.

0.

0.

0.

1.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

20 8.

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0.

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0.

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7.

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0.

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0.

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7.

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0.

0.

0.

22.

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4, 0.

0.

4.

4.

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0.

1.

0.

0.

0 ~

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1 ~

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8.

0.

0.

0.

12.

16, lb.

0.

1.

0.

2.

7.

b.

2l 0.

0.

0.

1 ~

5.

1.

0.

0.

Q.

0.

0.

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0.

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0.

0.

0.

0.

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0.

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0.

0.

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8.

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0.

0.

7.

21.

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12.

0.

0.

0.

5.

6.

5.

1.

0.

0.

0.

1.

5.

0.

Q.

TOTAL NUNBER OF USED =

1594 HOURS NISSItlG -"

0 CALN VARIABLES-"

2&

26

I 0

4

'I

'l l

'I

TABLE 5-5 3RD QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FROH HOURLY AVERAGES FROM TAPE 0.6 lfAXIHUN 2-MIND SPEEDS FOR EACH CATEGORY IN HPH ARE:

3.0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0 NUMBERS GIVEN ARE HOURS MIND C

SS CAT HHE HE EHE ESE SSE SM NHM HM HHM I

1.

1 I

I I

I 2

I 2

2 2'2 2

3 4

4 5

5 5

5 5

5 6

6 6

6 6

6 6

7 7"

7 7

7 I

2 5

6 7

1 2

4 5

6 7

1 2

5 6

7 1

4 5

'6 7

0.

20 1.

0.

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0, 0.

0.

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0.

0.

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0.

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0.

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0.

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0.

0.

11 ~

0.

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0, 10.

31.

0.

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23.

12.

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21.

0.

0.

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0.

8, 1.

0.

0.

0.

1 ~

7.

20 0.

0.

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10.

0.

0.

0.

0.

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2.

0.

0.

0.

1.

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0.

0.

1.

2.

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14.

0.

0.

0.

1.

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29.

8.

0.

0.

0.

0.

8.

8.

1.

0.

0.

8, l.

7.

0.

1.

0.

0.

0.

0.

l.

2.

3 ~

0.

0.

0.

0.

0.

I ~

0.

0 ~

0.

l.

0.

0.

3.

0.

0.

0.

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13.

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0.

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45.

32.

3.

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20.

16.

0.

0.

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4.

20 0.

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6.

TOTAL HUHBER OF HOURS USED =

1916 HISSIHG "-

CALH =

10 VARIABLE =

55 27

II J

'A A

U d

II'I J,

E r

'h

TABLE 5-6 3RD QUARTER 1988 JOIttT FREQUENCY DISTRIBUTIOtt FOR THE 245 FT LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE 0.6 ttAXIMUN MIND SPEEDS FOR EACH CATEGORY Itt NPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0

'5 - 18.0 6 - 24.0 HUNBERS GIVEH ARE HOURS CL SS 1

1 1

1 1

2 2,

2 2

2 2

2 3

'3 3

4 4

4 4

1'I 5

5 5

5 5,

5 6

6 6

6 6

6 6

7 7

7 7

7 MIND CAT 1

2 5

6 7

1 2

5 6

7 1

2 4

5 6

7 1

2 5

6 7

2 3

4 5

6 7

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l L

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TABLE 5-7 4TH QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FRON HOURLY AVERASES FRON TAPE 0.6 NAXINUN HIHD SPEEDS FOR EACH CATE6ORY IH NPH ARE:

2 -

3.0 3 -

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I I

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=

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=

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34 29

'ff l>

l' Ib 4i lt

\\

TABLE 5-8 4TH QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FRON HOURLY AVERASES FRON TAPE 0.&

NAXINUN MIND SPEEDS FOR EACH CATESORY IN NPH AREl 2 -

3.0 3 -

7.0 4 - 12.0, 5 - 18.0 6 - 24.0 NUNBERS GIVEN ARE HOURS CL SS 1

1 1

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1.

70 0.

1.

0.

0.

2.

1.

1.

0.

3.

0.

0.

0.

1.

0.

0.

7.

2 ~

8.

12.

12.

20 0.

11.

9.

10.

12.

6 ~

0.

0.

4.

9.

5.

1 ~

1.

0.

0.

20 7.

2.

0.

0.

0.

0.,

0.

1.

1.

2.

0.

0.

0 ~

1.

20 0.

1 ~

0.

0.

0.

"1.

1.

0.

1.

0.

0.

0.

3.

1.

b.

50 0.

0.

0.

6.

7.

11 l.

0.

0.

5.

50 4.

0.

0.

0.

0.

50 5,

1 ~

0.,

0 ~

0.

SE SSE S

SSM SM MSM 2.

0.

0.

0.

0.

0.

0.

1.

0.

0.

0.

0.

0.

1.

1.

1 ~

0.

0.

0.

0.

4.

5.

1.

2.

0.

0.

0.

8.

8.

11.

1 ~

0.

0.

0.

50 4.

1.

0, 0.

0.

2.

0.

0.

0.

0.

l.

30 3.

0.

0.

0.

3.

4.

2.

0.

0.

0.

0.

0.

0.

0.

0.

0, l.

7.

10.

8.

0.

0.

1.

9.

18.

19 '

9.

0.

0.

0.

8.

16.

6 ~

0.

0.

0.

6.

4.

10.

0.

0.

0.

0.

6 ~

b.

4, 1.

1.

0.

0.

5.

6.

0.

1.

0.

0.

4.

3.

2.

2.

0.

0.

0.

1 b.

30.

24.

8.

0.

0.

1.

13.

23.

22.

10, 0.

0.

0.

10.

25.

15.

20 0.

0.'.

4 ~

20.

lb.

0.

0.

0.

0.

8 ~

15.

11.

2.

0.

0.

0.

2.

b.

0.

0.

0.

8.

0.

,0.

0.

0.

0.

15.

26.

8.

1 ~

0.

0.

1.

23 8.

0.

0.

0.

lb.

31.

5.

0.

0.

0.

0.

8 ~

9.

6.

0.

0.

0.

TOTAL NUNBER OF HOURS USED

=

2172 NISSIMS =

CALM =

VARIABLE =

1&

30

"j

~ V N

4

TABLE 5-9 1988 ANNUAL JOIHT FREQUENCY DISTRIBUTION FDR THE 33 FT LEVEL CALCULATED FROM HDURLY AVERAGES FROM TAPE 0.6 MAXIMUM MIND SPEEDS FOR EACH CATEGORY IH HPH AREl, 2-3.0 3-7.0 4-12.0 5" 18.0 NUMBERS GIVEN ARE HOURS 6 - 24.0 STAB CLASS 1

1 1

1 I

I 2

2 2

2 2

2 2

3 3

MIND CAT 5

6 7

TOTAL HU USED =

, H NHE NE ENE SE 0.

15.

36.

70 l.

0.

0, 0.

5.

7I 1.

0.

0.

0, 0.

7.

b.

4o 0.

0.

0.

0, IS.

42.

18.

S.

0.

0.

0.

98.

97.

10.

5.

0.

0.

2I 100.

2.

0.

0.

0.

1.

65.

37.

0.

0.

0.

14.

0, 6.

15.

0.

0.

0.

0.

0.

30 0.

0, 0.

0.

0.

0.

1.

0.

0.

0.

0.

0.

0.

4 ~

11.

l.

0.

O.

0.

2l 10.,

1.

13.

16.

4.

0.

0.

0.

0.

0.

2.

0 ~

0.

0.

0.

0.

2.

0.

0.

0.

0.

0.

11.

22.

7.

2t O.

0.

20 31.

65.

0.

0.

O.

l.

35.

36.

1.

0.

0.

0.

1 ~

25.

15.

0.

0.

0.

0.

2.

0.

0.

0.

0.

0.

1.

0.

0.

0.

0.

0.

0.

2 ~

1.

0.

0.

0.

0.

0, 5.

6.

0.

0.

0.

0.

21.

26.

0.

0.

0.

0.

11 0.

O.

0.

2l 10.

l.

0.

0.

0.

0, 0.

7 ~

7.

0.

0.

0.

0.

0.

0.

30 0.

0.

0.

0.

0.

4.

3.

0.

0.

0.

0.

0.

9.

0.

0.

0.

0.

1.

26.

32.

l.

0.

0.

0.

1.

20.

14.

1.

0.

0.

0.

0.

8.

2.

0.

Q.

0.

0.

23.

29.

0.

0.

0.

0.

0.

2.

0.

0.

0.

0.

8.

1.

0.

0.

0.

22.

32.

11.

0.

O.

0.

0.

4 ~

l.

0.

0.

0.

0.

0.

l.

0.

0.

0.

0.

0.

0.

i.

1 ~

0.

0.

0.

0.

5.

6.

2.

0.

0.

0.

0.

8.

12.

3I 0.

0.

0.

0.

11.

12.

0.

0.

0.

0.

1.

30 8,

0.

0.

0.

0.

73.

30.

8.

0.

0.

O.

4.

Q.

0.

0.

2I 72.

29.

1.

0.

0.

0.

1.

43.

13.

0.

0.

0.

14.

20.

18.

0.

0.

0.

0 ~

20 18.

,.16.

0.

" 0.

0.

10.

NBER OF 7825 HOURS NISSINB =

0 CALM =

20 SSE 1,

14.

14, 20 0.

0.

0.

0.

2.

6 ~

42.

0.

0.

0.

0.

4 ~

8.

2.

0.

0.

0.

0 ~

17.

28.

6.

0.

0.

0.

20 30.

87.

15.

l.

0.

0.

l.

36.

82.

11.

0.

0.

0.

18.

45.

20 0.

0.

0.

16 '

22.

9.

0.

~ 0.

0.

0.

30 0.

7 ~

0.

0.

0.

0.

0; 1.

7 ~

"l.

0.

0.

0, 21:

59.

26.

1 ~

0.

0.

20 54.

162.

43.

l.

0.

0.

0.

51.

125.

9.

0.

0.

0.

0.

32.

39.

0.

0.

0.

VARIABLE =

SSM 8.

17.

24.

50 0.

0.

0.

20 5.

'0.

0.

0.

0.

0.

5.

9.

1.

0.

0.

0.

15.

78 ~

103.

19.

0.

0.

1.

52.

194

'1.

70 1.

0.

0.

53.

81

'4.

0.

0.

0.

2.

27.

. 38.

0.

0.

0.

0, 1.

9.

lb.

33.

18.

0.

0.

0.

0.

3 ~

12.

1 ~

0.

0.

0.

5.

16.

0.

0.

0.

20.

67.

68.

29.

1.

0.

20 56.

119.

52.

12.

1.

0.

2I 52.

48.

12.

0.,

0.

0.

20 22.

25.

1.

0.

0.

0, 0.

16.

22.

26

'0.

0.

Q.

0.

0.

3 ~

10.

1.

i.

0.

1.

4.

8.

12.

6.

0.

0.

0.

21.

40.

41 ~

17.

0.

0.

0.

65.

66.

38.

12.

1.

0.

0 ~

51.

32.

3.

0.

0.

0.

l.

20.

8.

1.

1 ~

0.

0.

31 0.

13.

27, 10.

10.

20 0.

0.

1.

5 ~

8.

0.

0.

0.

1.

7.

11.

0.

0.

0.

19.

30.

29.

10.

0.

3.

50.

82.

23.

5.

0.

0.

2.

48.

27.

3.

1.

0.

0.

20 30.

4, 1.

1.

0.

0.

0.

0.

18.

20.

19.

12.

70 0.

0.

0.

8.

7.

8.

2 ~

0.

0.

0.

4.

6.

9.

0.

0.

2I 26.

3S.

50.

10.

0.

0.

6.

66.

31.

17.

70 0.

0.

0, 9.

20 0.

0.

1.

6.

8.

7I 3.

0.

0.

1.

32.

78.

4&.

5.

0.

6.-

95.

66.

39.

8.

0,

'0.

0.

27.

9.

'1.

O.

0.

0.

69.

62.

7.

0 ~

O.

8.

1.

56.

12.

1.

O.

0.

0.

72.

123.

18'3.

6, 3.

0.

0.

0.

0.

3 ~

2.

l..

19.

34.

2.

0.

0.

0.

6.

8.

2.

2I 0.

0.

0.

8.

10.

4e 4,

0.

0.

2l 64.

66.

32.

l.

0.

2.

98.

150.

72 0.

0.

l.

95.

51.

1.

0.

0.

3 ~

4, 76.

34.

0.

0.

0.

6,

flf fi

,4

,l

TABLE 5-10 1988 AttNUAL jOINT FREQUENCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FRON HOURLY AVERAGES FROM TAPE 0.6 HAXINUN MIND SPEEDS FOR EACH CATEGORY IN NPH ARE:

2" 3.0 3-7.0 4-12.0 5-18.0 NUMBERS GIVEN ARE HOURS 6 - 24.0 STAB CLASS 1

I 1

I 1

1 2

2 2

2 2

2 2

3 3

4 4

4 4

4 5

5 5

5 5

5

'5 6

6 6

6 b

6 6

7 MIND CAT 2

5 6

7 2

4 5

6 7

I 2

5 6

7 I

2 4

5 6

7 1

2 3

5 6

7 I

2 4

5 6

7 1

2 4

0.

5.

32.

9.

1.

0.

0.

0.

5.

20 1.

0.

0.

0.

Q.

20 3.

2I 0.

0.

1 ~

17.

37.

26.

4.

0.

0.

1 ~

65.

98.

29.

2.

0.

0.

0.

50.

74 14.

0.

0.

0.

0.

26.

43, 7.

5 1.

6 0.

7 0.

TOTAL NUNBER OF USED =

7569 EHE 0.

7.

2I 0.

0.

0.

0.

2.

1.

0.

0.

0.

0.

2I 20 0.

0.

0.

0.

l.

8.

23.

14.

2t 0.

0.

0.

26.

77.

16.

2.

1.

8.

7.

5I 0.

0.

0.

0.

2.

0.

0.

0.

0.

0.

0.

1.

0.

0.

0.

0, 0.

0.

5.

7.

2.

20 0.

0.

1.

14.

18.

15.

1.

0.

11.

24.

2 ~

0.

0.

0.

0.

2.

0.

0.

0.

0.

0.

0.

4.

30 0.

0.

0.

0.

0.

16.

27.

14.

4 ~

0.

0.

2.

51.

,69.

25.

0.

0.

0.

1.

47.

46.

7.

0.

0.

0.

0.

13.

0.

" 0.

0.

1.

21.

29.

3.

0 ~

0.

0.

0.

7 ~

18.

0.

0.

0.

0.

0.

28.

49.

8.

0.

0.

0.

0.

9.

27.'.

0.

0.

0.

30.

4.

0.

0.

0.

HOURS HISSI NG "-

NNE NE ESE SE SSE SSM 0.

1.

5.

1.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

0.

4.

8 ~

4.

l.

0.

0.

0.

13.

16.

0.

0.

0.

0.

9.

20.

2.

0.

0.

0.

0.

9.

9.

1.

5.

0.

0.

1.

2.

0.

0.

l.

0.

1.

2.

0.

0.

0.

0.

0.

Q.'.

1 ~

0.

0.

0.

0.

1.

8.

5.

0.

" 0.

0.

1.

21.

20.

8.

1.

0.

0.

1.

23.

12.

0.

0.

0.

0.

0.

13.

8.

0.

0.

0.

1.

6.

4.

0.

0.

1.

0.

0, 1.

0.

2.

0.

0.

0.

0.

3 ~

2, 2I 0.

0.

0.

0.

50 0.

0.

0.

1.

12.

44.

13.

0.

0.

0.

l.

28.

33 7 ~

20 l.

0.

10.

14.

12.

8.

5.

31.

1.

9.

13.

1.

0.

0.

0.

0.

0.

2.

20 0.

0.

0.

5.

5.

0.

0.

0.

0.

20.

0.

6 ~

12.

14.

2.

1.

0.

0.

2.

1.

1.

0.

0.

0.

0.

2.

8.

3.'.

0.

0.

13.

34., 38.

13.

0.

0.

1.

34 ~

57.

37.

3.

0.

0.

0.

37.

53.

32.

1 ~

0.

0.

0.

14.

29.

8.

0.

0.

0.

35.

6.

0.

0.

1.

45.

127.

66.

0.

0.

0.

41.

75.

42.

10.

0.

0.

0.

14.

47.

16.

0.

0.

0.

0.

9.

7.

15.

13.

2I 0.

0.

1.

4.

5.

2I 0.

0.

0.

2I 1.

11 0.

0.

0.

12.

49

'8.

38.

17.

1.

41.

138.

93.

42.

1.

1.

l.

37.

60.

45.

9.

0.

0.

0.

22.

42.

16.

0.

0.

0.

CALN =

366 VARIABLE =

106 0.

5.

7.

28.

20.

9.

0.

I, 0.

1.

11.

4.

0.

3.

0.

2.

8.

1.

0.

0.

14.

41.

81.

34.

14.

2I 0,

35.

92.

67.

45.

16 0.,

44, 13.

8.

2.

0.

1.

17.

37.

13.

0.

0.

0.

0.

50 lb.

'4.

0.

0.

l.

2I 0.

1.

0.

1.

12.

8.

1.

0.

0.

12.

27.

33.

23 0.

20 39

'2.

28.

29.

11 28.

14.

5.

0.

0.

0.

18.

6.

1.

0 ~

0.

32 2.

6.

6.

11.

6.

8.

0.

0.

0.

3I 2 ~

0.

0.

1.

5l 7I 3.

1.

0.

0.

8..

24.

24.

25.

10.

1.

27.

53.

23.

6 ~

0.

2 ~

28.

25.

11.

3 ~

0.'.

1.

18.

13.

6.

0.

1.

0.

Mti NM PNM 0.

1.

4.

12.

14.

1.

0.

0.

8.

70 9.

2 ~

0.

0.

8.

17.

15, 3.

0.

0.

0.

0.

4.

6.

0.

2.

50 6.

7.

1.

0.

0.

3 ~

8.

6.

2 ~

0.

l.

15, 270 43.

30.

0, 1.

24

'6.

51.

23.

8.

0.

1.

30.

22.

34.

lb.

l.

0.

0.

21.

16.

15.

0.

0.

8.

1.

3 ~

1.

0.

1.

70 5.

5.

6.

0.

0.

0, 27.

48

'2.

24 0.

3.

40.

1.

2 ~

0.

0.

1.

8.

20 2.

0.

l.

25.

55.

37.

15.

0.

2.

63.

4.

20 29.

56.,

12.

0.

0.

0.

12.

36.

37.

1.

0.

0.

11.

0.

'0.

42.

79.

40.

0.

0.

0.

20.

34.

37.

1.

0.

0.

91.

119.

73.

91

'3.

59.

V

~ 4 k

ft t

U l:

lI t

I 1

TABLE 5-11 VENT AHD PURGES 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FROH HOURLY AVERAGES FRDH TAPE 0.6 HAXIHUN MIND SPEEDS FOR EACH CATEGORY IH HPH ARE:

2 -

3,0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0 HUHBERS GIVEN ARE HOURS CLASS 1

I 1

1 I

1 2

2' 2

2 2

2 3

3 4

4 4

4 5

5 5

5 5

5 5

6 6

6 6

6 6

6 7

7 7

7 MIHD CAT 2

5 6

7 1

2 5

6 7

2 4

5 6

7 1

2 4

5 6

7

,1 2

3 4

5 6,

7 1

2 3

5 7

1 2

3 4

6 7

TOTAL H USED =

H NHE NE EHE 1.

6.

.7 ~

0.

0.

0.

0.

0 ~

1.

0 ~

0.

0.

0.

0.

0.

1 ~

0.

0.

0.

0.

0.

0.

3.

4.

1.

0.

0.

0.

0.

20.

lb.

0.

0.

0.

0.

1.

23.

5 ~

0.

0.

0.

0.

1.

10.

0.

0.

0.

5.

HOURS HISSIN 1,

5I 20 1.

0.

0.

0.

0.

0.

'0.

0.

0.

0.

0.

Q.

0.

0.

0.

0.

0.

0.

0.

4.

1.

0.

0.

0.

0.

7$

11.

1.

0.

0.

0.

l.

7.

7 ~

0.

0 ~

0.

0.

1.

9.

3.

0.

Q.

0.

b.

0.

2l b.

0.

Q.

0.

0.

0.

1 ~

0.

0.

0.

0.

0.

Q.

1 ~

Q.

0.

0.

0.

0.

0.

30 2 ~

0.

0.

0.

1.

2I 3.

5I 0.

0.

0.

0.

9.

0.

2r 9.

1.

0.

0.

0.

2.

1.

Q.

0 0.

0.

0.

1 ~

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2 -

3.0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0; NUNBERS GIVEN ARE HOURS N

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TABLE 5-1 1ST QUARTER 1988 JOINT FREOUEHCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FRON HDURLY AVERAGES FRON TAPE 0.6 NAXINUN MIND SPEEDS FOR EACH CATEGORY IH NPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0 5 - 18,0 6 - 24.0 HUNBERS GIVEN ARE HOURS STAB CLASS MIND CAT HHE HE EHE ESE SE SSE SSM SM MSM M

MHM NM HHM 0.

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TOTAL HUNBER OF USED =

1821 HOURS NISSI CALN =

VARIABLE =

65 23

TABLE 5-2 1ST QUARTER 1988 JOlttT FREQUENCY DISTRIBUTIOtt FOR THE 245 FT LEVEL CALCULATED FRON HOURLY AVERAGES FRON TAPE 0.6 NAXINUN MlttD SPEEDS FOR EACH CATEGORY IN NPH ARE:

2-3.0 3-7.0 '-12.0 5" 18.0 24.0 HUNBERS GIVEtt ARE HOURS STAB CLASS MlttD H

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TOTAL tlUNBER OF HOURS USED =

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CALN =

VARIABLE =

41 24

TABLE 5-3 2HD QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEI.

CALCULATED FRON HDURLY AVERASES FRDN TAPE 0.6 NAXINUN MIND SPEEDS FOR EACH CATESORY IH NPH ARE:

2 -

3.0' 7.0 4 - 12.0 5 - 18.0 6 - 24.0 STAR M}HD CLASS CAT 1

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0 VARIABLE -"

40 25

TABLE 5-4 2HD QUARTER 1988 JOINT FREQUEHCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FRON HOURLY AVERAGES FRON TAPE 0.6 NAXINUN MIND SPEEDS FOR EACH CATEGORY ltt NPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0 5 - 18,0 6 - 24.0 ttUNBERS GIVEN ARE HOURS STAB CLAS 1

1 1

1 1

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TABLE 5-5 3RD QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FROM HOURLY AVERAGES PRON TAPE 0.6 MAXIMUM HIHD SPEEDS FOR EACH CATEGORY IH NPK ARE:

2 -

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27

TABLE 5-6 3RD QUARTER 1988 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FRON HOURLY AVERASES FRON TAPE Q.b NAXINUN MIHD SPEEDS FOR EACH CATE60RY IH NPH ARE:

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HHE HE EHE ESE SE SSE S

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TOTAL HUNBER OF HOURS USED

=

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22 28

TABLE 5-1 4TH DUARTER 1988 JOINT FREQUENCY DISTRIBUTIDH FOR THE 33 FT LEVEL CALCULATED FRON HOURLY AVERABES FRON TAPE 0.6 NAXINUN MIND SPEEDS FOR EACH CATEBORY IN NPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0 ttUttBERS 6IVEN ARE HOURS STAB MIND CLASS CAT tt HHE HE EKE E

ESE SE SSE SSM SM LSM M

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0, TOTAL HUNBER OF HOURS USED

=

2155 NISSINB =

CALN =

VARIABLE 29

TABLE 5-8 4TH QUARTER 1988 JOINT FREQUEttCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FROH HOURLY AVERASES FROH TAPE 0.6 HAXIHUH MIND SPFEDS FOR EACH CATESORY IH HPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0.

5 - 18,0 6 - 24.0 NUHBERS 6IVEN ARE HOURS STAB CLAS MIHD H

ttttE NE S

CAT EHE E

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TOTAL HUHBER OF HOURS USED

=

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=

CAt.< =

VARIABLE =

16 30

TABLE 5-9 1988 AHHUAL JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FRON HOURLY AVERAGES FROH TAPE 0.6 NAXINUN MIND SPEEDS FOR EACH CATEGORY IN NPH ARE:

2 -

3.0 3 -

7.0 4 -,12,0 5'- 18.0 NUNBERS GIVEN ARE HOURS 6 - 24,0 STAB CLASS I

I I

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2 2

2 2

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5 6

6 6

b.

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7 7

MIND CAT 2

5 6

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6.

SSM SM MSM M

MHM HM NHM TOTAL NUNBER OF USED =

7825 HOURS NISSJNS

=

CALH =

20 VARIABLE =

196 31

TABLE 5-10 1988 ANNUAL JOINT FREQUENCY DISTRIBUTIOH FOR THE 245 FT LEVEL CALCULATED FROM HOURLY AVERABES FROM TAPE 0.6 NAXINUN MIND SPEEDS FOR EACH CATEBORY IN NPH ARE:

2-30 3-70 4-120 5-180 6 - 24.0 NUNBERS GIVEN ARE HOURS STAB CLASS MIND CAT H

NHE HE EHE ESE SE SSE SSM SM KSM M

MNM NM HHM I

I I

2 2

2 2

2 2

4 4

4 4

4 5

5 5

5 5

5 5

6 6

6 6

6 6

6 7

7 7

7 7

7 7

0.

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I.

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0.

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0.

0.

0 ~

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3 ~

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I ~

17.

37.

26.

4.

0.

0.

65.

98.

29.

2l 0.

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50.

74.

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0.

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9.

4, 2 ~

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6.

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5.

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6.

0.

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91.

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53.

4.

l.

2.

29.

56.

41.

12.

0.

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8.

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a.

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79.

40.

4 ~

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0.

0.

20.

34.

37.

I.

0.

0, TOTAL USED HUNBER OF HOURS NISSIHB =

CALN 366 VARIABLE =

Ia&

32

TABLE 5-11 VEtti AtiD PUR6ES 1988 JOINT FREOUEttCY DISTRIBUTIOtt FOR THE 33 FT LEVEL CALCULATED FROtt HOURLY AVERAGES FROh TAPE 0.6 ttAKIttUtt MIND SPEEDS FOR EACH CATEGORY IN ttPH ARE:

2-3.0 3-7.0 4-12.0 5-18.0 6 - 24.0 NUHBERS 61VEN ARE HOURS STAB CLASS MIND CAT N

ttHE NE EttE ESE SE SSE S

SSM Stt MSM M

MttM tN ttttM 1

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2 ~

0.

0.

0.

1.

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0.

0.

0.

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1.

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TOTAL ttUttBER OF HOURS ttSED

=

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VARIAB1E =

33

TABLE 5-12 VEtfTS AttD PURSES 1988 30ltlT FREQUENCY DISTRIBUTIOtt FOR THE 245 FT LEVEL CALCULATED PRON HOURLY AVEHABES FRDM )APE 0.6 tfAXItfUtfMlttD SPEEDS FOR EACH CAEEBDRY IN ttPH ARE:

2 "

3.0 3 -

7.0 4 - f7.0 5 - 18.0

- 24.0 NUNBERS 61VEN ARE HOURS STAR CLASS MIND CAT N

ttNE ttE ENE E

ESE SE SSE S

SSM SM MSM M

MNW NM ttNM 1

1 1

1 1

1 2

2 2

2 2

2 2

3 4

L' 5

5 5

5 5

6 6

6 6

6 6

6 7

7 7

7 7

7 7

7 1

2 5

~

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2 6

7 1

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6 7

2 5

6 7

1 2

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7 1

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1.

0.

Q.

0.

0 ~

0.

5 ~

7.

0.

0.

0.

0.

0.

2 ~

0.

0.

0.

0.

0.

5 ~

5.

0.

0.

0.

1~ 4 0,

20 0.

0.

l.

0.

0.

0.

0.

0.

0.

0, 0.

0.

0.

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0 ~

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0.

0.

0 ~

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0 ~

0.

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1.

ff.

3 ~

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0 ~

0, 1,

9.

8.

0, l.

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1.

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10.

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7, 4.

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2.

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0, 0.

0 ~

0 ~

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3 ~

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1.

0 ~

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0.

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0.

0 ~

0.

2.

5.

4.

.6 ~

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2.

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0.

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3 ~

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12, 25.

5.

11.

0.

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0 ~

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0 ~

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10.

12.

16.

7.

0.

1 ~

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8.

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8, 4.

5l 4,

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0.

0, 0.

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0 ~

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0.

0, 0.

1 ~

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13.

10

'0 51 l.

9 ~

20.

15.

8, 1.

0.

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7.

16.

f2, 2 ~

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0.

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50 8.

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0.

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1 ~

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6, 2.

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6 ~

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2 ~

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TOTAL NU USED c MBER OF HOURS 1604 tfISSfttB =

CAf N =

VARIAB' 22 34

0

6,0 D

E E

E I

A T N HA IJa~

Th d

t ~ th I

I dl id I I'IIP-I \\q Id effluents were calculated using the LADTAP II computer code and the site specific input parameters.

Table 6-1 lists the doses to the maximum individual by calendar quarters respectively.

The doses to the average exposed individual are listed in Table 6-2.

The 50-mile population doses are listed in Table 6-3.

All doses were calcu-lated using the LADTAP II computer code.

An evaluation of the nearest orchard (approximately 3 miles downstream) using Columbia River water for its irrigation showed an adult total body dose value of 1.02E-05 mRem/yr and an organ dose value of 1.45E-05 mRem/yr.

The population doses at this location showed a total body value of 2.58E-05 person-rem and an organ value of 4.57E-05 person-rem.

g~gug~Ef 3~~

The GASPAR II computer code was used to calculate doses at the 1.2 mile site boundary, Taylor Flats which is located 4.2 miles east southeast plus the 50-mile population and individual doses listed in Table 6-4.

The quarterly GASPAR II runs utilized the quarterly averaged X/Q and D/Q values, and site specific input parameters pertain-ing to food productions.

The air doses at the site boundary were used to verify compliance with Technical Specification 3.11.2.2.

To verify com-pliance with Technical Specification 3.11.2.3, the maximum organ dose to the maximum exposed individual located at Taylor Flats was evaluated.

Table 6-5 lists the doses at these special locations.

6.1 The HNP-2 Visitor Center was evaluated for assessment of radiation doses to "Hembers of the Public",

due to their activities within the site boundary.

The ODCH assumes an eight (8) hour per year occupancy by "A Hember of the Public" at the Visitor Center.

The dose assess-ment resulted in an annual calculated whole body dose of 2.6E-03 mrem.

The annual thyroid dose was 5.0E-03 mrem and the maximum dose to any other organ was 4.8E-03 mrem.

The annual assessment of radiation doses to the likely most exposed "Member of the Public" i.'o show conformance with 40CFR Part 190 is assumed to be located in the Taylor Flats vicinity (4.2 miles ESE).

The Gaspar II computer code with annual source terms and XOQDOQ meteorological data was used to obtain the dose assessment from gaseous effluents.

It is assumed there is no dose contribution from liquid effluents at Taylor Flats.

The assessment resulted in annual calculated whole body dose of 2.6E-02 mrem.

The annual thyroid dose was 6.8E-01 mrem and the maximum dose to any other org'an was 4.3E-02 mrem.

The direct radiation contribution showed no significant, amount above normal background for that area which is approximately 99 mrem per year.

35

Table 6-1 ID DS 1ST AND 2ND QUARTERS 1988 Hhole Body W

r Fir 1988 Cumulative Hhole Body Max. Organ.

/

1988 Cumulative Max. Organ.

Fishing Drinking Shoreline Swimming Boating Vegetables Leafy Veg.

Milk Meat Total 2.1E-05 4.2E-07 2.7E-08 5.3E-11 1.5E-09 3.8E-07 4.0E-08 1.1E-07

~FMG 2.2E-05 2.1E-05

4. 2E-07
2. 7E-08 5.3E-11 1.5E-09 3.8E-07 4.0E-08 1.1E-07 4~E~
2. 2E-05 3.9E-05 8.8E-07 3.1E-08 5.3E-11 1,5E-09 2.8E-06 5.0E-07 2.2E-07

~F~)

4.3E-05 3.9E-05 8.8E-07 3,1E-08 5.3E-11 1.5E-09 2.8E-06 5.0E-07 2.2E-07

~E~

4.3E-05 Fishing Drinking Shoreline Swimming Boating Vegetables Leafy Veg.

Milk Meat Total Nhole Bodyr 2.0E-03 3.2E-06 2.4E-06 6.7E-09 1.9E-07 7.9E-06 1.7E-06 4.9E-06 1J&Q6 2.0E-03 ezia~8 1988 Cumulative Hhole Body

/

2.0E-03 3,7E-06 2.4E-06 6.8E-09 1.9E-07 8.3E-06 1.7E-06 5.0E-06

~lE-2.0E-03 Max. Organ, 3.3E-03 1.2E-05 2.8E-06 6.7E-09 1.9E-07 1.4E-05 4.0E-06 1',4E-05 3 (~K 3.3E-03 1988 Cumulative Max. Organ.

/

3. 4E-03 1.3E-05 2.8E-06 6.8E-09 1.9E-07 1.7E-05 4.5E-06 1.5E-05
3. 1~

3.5E-03 36

DI D

Table 6-1 3RD AND 4TH QUARTERS 1988.

(Continued)

Whole Body 1988 Cumulative Whole Body Max. Organ.

1988 Cumulative Max. Organ.

Fishing Drinking Shoreline Swimming Boating Vegetables Leafy Veg.

Milk Meat Total 7.8E-05 3.6E-07 7.8E-08 1.3E-10 3.6E-09 4.4E-07 6.9E-08 2.1E-07 Z~~

7.9E-05 2.1E-03 4.0E-06 2.4E-06 7.0E-09 1.9E-07 8.7E-06 1.8E-06 5.2E-06

~<-05 2.1E-03 1.2E-04

3. BE-07 8.7E-08 1.3E-10 3.6E-09 8.5E-07
1. 7E-07
2. 8E-07

~MB

1. 2E-04 3.5E-03 1.3E-05 2.9E-06 7,0E-09 1.9E-07 1.8E-05 4.7E-06 1.5E-05 X2$~

3.6E-03 Fishing Drinking Shoreline Swimming Boating Vegetables Leafy Veg.

Milk Meat Total Whole Body 1.5E-05 1.1E-07 3,7E-08 1.3E-10 3.6E-09 1.3E-07 2.7E-08 1.1E-07 M6 1.5E-05 1988 Cumulative Whole Body 2.1E-03 4.1E-06 2.4E-06 7.1E-09 1.9E-07

'.8E-06 1.8E-06 5.3E-06

1. 4F~

2.1E-03 Max. Organ.

/

3.2E-05 1.2E-07 4.4E-08 1.3E-10 3.6E-09 2.6E-07 7.9E-08 2.2E-07

~E~

3.3E-05 1988 Cumulative Max. Organ.

3.5E-03 1.3E-05 2.9E-06 7.1E-09 1.9E-07 1.8E-05 4.8E-06 1.5E-05 3.6E-03 (1) Age Group Adult:

Maximum individual resides at Richland and fishes near the WNP-2 outfall area.

37

E E

D Table 6-2 1ST AND 2ND QUARTERS 1988 D

E L

Hax. Organ.

Whole Body Hax. Organ.

Whole Body Fish Drinking Water Shoreline Swimming Boating Vegetables Leafy vegetables Milk Heat Total

5. 5E-07 4.0E-07 5.9E-09 2.9E-11 7.3E-12 1.8E-06 3.7E-07 1.7E-07 E~

3.3E-06 3.0E-07 1.9E-07 5.0E-09 2.9E-11 7.3E-12 2.3E-07 2.5E-07 8.8E-08 1.1E-06 4.6E-05 5.6E-06 5.3E-07 3.7E-09 9.3E-10 1.1E-05 2.8E-06 9.6E-06 7.7E-05 3.1E-05 1.5E-06 4.5E-07 3.7E-09 9.3E-10 4.4E-06 9.2E-07 3.6E-06 RJF~

4 'E-05 3RD AND 4TH QUARTERS 1988 Hax. Organ.

Whole Body Hax. Organ.

Whole Body Fish Drinking Water Shoreline Swimming Boating Vegetables Leafy vegetables Hilk Heat Total

1. 7E-06 1.7E-07 1.6E-08 7.0E-11 1.8E-11

,6.3E-07 1.3E-07 2.5E-07 423~

2.9E-06 1.1E-06 1.6E-07 1.4E-08 7.0E-11 1.8E-11 2.5E-07 3.8E-08 1.3E-07 ZM 1.7E-06 4.1E-07 5.6E-08 3.4E-09 3.1E-11 7.9E-12 4.3E-08 2,7E-08 4.5E-08 LZJ~i 6.0E-07 1.9E-07 5.1E-08

'2.9E-09 3.1E-11 7.9E-12 3.6E-, 08 1.6E-08 2.7E-08 LM2 3,3E-07 38

Table 6-3 1ST AND 2ND QUARTERS 1988 D

L E

P h

Max. Organ.

Whole Body Max. Organ.

Whole Body

-r Fish Drinking water Shoreline Swimming Boating Vegetables Leafy vegetables Milk Meat Total 1.3E-06 3.3E-OS 1.0E-06 5.1E-09 1.3E-09 1.7E-05 3.8E-06 1.7E-06 2 4~

5.9E-05 6.1E-07 1,5E-05 8.8E-07 5,1E-09 1.3E-09 2.3E-06 2,6E-07 7.7E-07 2.0E-05 1.1E-04 4.6E-04 9.3E-05 6.6E-07 1.6E-07 1.1E-04 3.0E-OS 9.3E-05

~La>

9.1E-04 3.3E-OS 1.1E-04 7.9E-05 6.6E-07 1.6E-07 4.4E-05 9.5E-06 3.4E-05 3.1E-04 3RD AND 4TH QUARTERS 1988 Max. Organ.

Whole Body Max. Organ.

Whole Body Fish Drinking water Shoreline Swimming Boating Vegetables Leafy vegetables Milk Meat Total

3. 9E-06 1.4E-05 2.9E-06 1,2E-08 3.1E-09 6,3E-06 1.3E-O6 2.4E-06 3 2E~

3.1E-05 2.2E-06 1.2E-OS 2.5E-06 1.2E-08 3.1E-09 2.5E-06 3.9E-06 1.3E-06

~E~1 2.1E-05

9. 4E-07 4.4E-06 5.9E-07 5.5E-09 1.4E-09 4.3E-07 4.3E-07 4.4E-07

~2E-7.3E-06 4.5E-07 4.0E-06 5.1E-07 5.5E-09 1.4E-09 3.6E-07 1.5E-07 2.6E-07

~2E~

5.8E-06

, I 39

TABLE 6-4 50-MILE POPULATION DOSES FROM 1988 GASEOUS EFFLUENTS Exposure M~wey Plume Ground Inhalation Vegetables Milk Meat Total Whole Body 1.7"E-01 3.3 E-02 1.2 E-02 1.5 E-02 1.5 E-02 JM 2.5 E-01 Hax. Organ 5.6 E-01 3.9 E-02 1.2 E+00 2.1 E-02 4.5 E-01

~~K 2.3 E+00 AVERAGE INDIVIDUALDOSES FROM 1988 GASEOUS EFFLUENTS~

Eailmav P 1 ume Ground Inhalation Vegetables Milk Heat Total Whole Body

~i8am) 6,7 E-04

1. 3 E-04 4.8 E-05 5.9 E-05 5.9 E-04 1.5 E-03 Hax. Organ

'~liJJg~

2.2 E-03 1.5 E-04 4.8 E-03 8.3 E-05 1.8 E-03 9.1 E-03 The 50 mile population doses divided by the population within 50 miles of the Plant by direction and radii interval and converted to mrem.

40

Table 6-5 D

F

-2 A

CALENDAR QUARTERS 1988 1.2 miles site boundary d

tt t

1 1C 1ti 999 Beta air dose (mrad)*

Gamma air dose (mrad)*

First Second Third Fourth Annual 9V.Ll~ gJLLLtRL ger~ ~~r ~Luu Liiv 4.2E-02 1.8E-02 2.3E-02 4.1E-02 1.2E-01 3.0E-02 1.1E-02 3.5E-02 4.5E-02 1.2E-Ol Jucaiian:

~e Maximum organ dose (mrem)**

Taylor Flats, 4.2 miles ESE C1 d

I I

91 1>>

t'I 99 First Second Third Fourth Annual Quar km~

Qu&ZZ Qu~eJ:

Gumv3~iv.

1.2E-01 6.2E-01 4.6E-03 3.5E-03 7.5E-01

41

7.0 D

During this semi-annual reporting period, Amendment No.

6 was issued to the Offsite Dose Calculation Hanual (ODCH). 'his Amendment is included.

42