Text

Semiannual Effluent Rept for July-Dec 1987
	ML17279A843
Person / Time
Site:	Columbia
Issue date:	12/31/1987
From:	Powers C; WASHINGTON PUBLIC POWER SUPPLY SYSTEM
To:	;
References
	GO2-88-049, GO2-88-49, NUDOCS 8802290394
	Download: ML17279A843 (88)
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FACIL: 50-397 WPPSS Nuclear Progecti Unit 2i Washington Public Poee AUTH. NAME AUTHOR AFFILIATION POWERS'.

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SUBJECT:

"Semiannual Effluent Rept for July-Dec 1987. "

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TITLE: 50. 3&a(a) (2) Semiannual Effluent Release Reports NOTES:

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WNP-2 SEMI-ANNUAL EFFLUENT REPORT JULY TO DECEMBER 1987 WASHINGTON PUBLIC POHER SUPPLY SYSTEM LICENSE NO.

NPF-21 8802290394 87i23i PDR ADOCK 05000397 R

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TABLE OF CONTENTS KU25

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

~

16 23 34 41

LIST OF TABLES 2-1 2-2 3-1 3-2 3-3 3-4 3-5 4-1 4-2 4-3 IZED NNP-2 LIQUID EFFLUENTS - SUMMATION OF ALL RELEASES JULY DECEMBER 1987 HNP-2 LIQUID EFFLUENTS SOURCE TERMS JULY DECEMBER 1987 HNP-2 GASEOUS EFFLUENTS SOURCE TERMS MIXED MODE RELEASES MAIN PLANT VENT JULY DECEMBER 1987 WNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES TURBINE BUILDING JULY DECEMBER 1987 NNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES RADHASTE BUILDING JULY DECEMBER 1987 NNP-2 GASEOUS EFFLUENTS SUMMATION OF ALL RELEASES JULY DECEMBER 1987 HNP-2 GASEOUS EFFLUENTS BATCH RELEASES JULY DECEMBER 1987 SCALING FACTORS FOR REQUIRED NUCLIDES.

SCALING FACTORS FOR CONDITIONAL NUCLIDES NNP-2 SOLID HASTE SHIPMENTS JULY DECEMBER 1987 2

7 10 12 14 15 20 20 21 5-1 5-2 5-3 5-4 5-6 JOINT FREQUENCY DISTRIBUTION FOR THE CALCULATED FROM HOURLY AVERAGES FROM 1ST QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE CALCULATED FROM HOURLY AVERAGES FROM 1ST QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE CALCULATED FROM HOURLY AVERAGES FROM 2ND QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE CALCULATED FROM HOURLY AVERAGES FROM 2ND QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE CALCULATED FROM HOURLY AVERAGES FROM 3RD QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE CALCULATED FROM HOURLY AVERAGES FROM 3RD QUARTER 1987 33 FT.

LEVEL TAPE 245 FT.

LEVEL TAPE 33 FT.

LEVEL TAPE 245 FT.

LEVEL TAPE 33 FT.

LEVEL TAPE 245 FT.

LEVEL TAPE 24 25 26 27 28 29

LIST OF TABLES (Continued) 5-8 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE-4TH QUARTER 1987 30 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE-4TH QUARTER 1987 31 5-9 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT.

LEVEL CALCULATED FROM HOURLY AVERAGES FROM TAPE 1987 YEARLY 32 5-10 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT.

LEVEL CALCULATED AVERAGES FROM HOURLY AVERAGES FROM TAPE 1987 YEARLY 33 6-1 6-2 6-3 6-4 6-5 MAXIMUM INDIVIDUALDOSES FROM WNP-2 LIQUID EFFLUENTS 1987 AVERAGE INDIVIDUALDOSES FROM WNP-2 LIQUID EFFLUENTS 1987 50-MILE POPULATION DOSES FROM WNP-2 LIQUID EFFLUENTS 1987 50-MILE DOSES FROM WNP-2 GASEOUS EFFLUENTS 1987

SUMMARY

OF DOSES FROM WNP-2 GASEOUS EFFLUENTS 1987 35 37 38 39 40

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 WNP-2 during the previous six months of operation with data summarized on a quarterly basis.

2 '

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

Twelve batch releases occurred during the third calendar quarter and 3 batch releases during the fourth calendar quarter.

The total time period for the batch releases was 28.8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months , with the maximum time period being 2.20 hours2.314815e-4 days 0.00556 hours 3.306878e-5 weeks 7.61e-6 months for a release, the minimum time period being 0.02 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months for a release and the average time period was 1.70 hours8.101852e-4 days 0.0194 hours 1.157407e-4 weeks 2.6635e-5 months .

The volume of dilution water used, 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 1987 was 89,125 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 4.0E-03 mrem whole body and 7.6E-03 mrem for the maximum organ.

The fourth quarter calculated dose was 5.1E-04 mrem whole body and 1.1E-03 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 tank samples for each quarter was analyzed for strontium and

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

The percent of MPC limit is based on the total HPC fractions using those nuclides in Table 2-2 and concentrations listed in 10CFR20, Appendix 8, Table 2, Column 2.

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

These estimated errors are based on counting statistics, tank volume, and in obtaining a representative sample prior to discharge.

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 951. confidence level.

Table 2-1 NNP-2 LIQUID EFFLUENTS SUMMATION OF ALL RELEASES July December 1987 Unit 3rd Quarter 4th Quarter Est..

Total A.

Fission and activation products l.

Total release (not including 2.

Average diluted concentration B.

Tritium 2.

Average diluted concentration r

C.

Dissolved and entrained gases 2.

Average diluted concentration D.

Gross alpha radioactivity E.

Volume of waste (prior to F.

Volume of dilution water

At 95%%d confidence level

Table 2-2 HNP-2 LIQUID EFFLUENTS - SOURCE TERMS July December 1987 BATCH MODE

'Nucl 1 des Released Un> t 3rd Quarter 4th Quarter

C a

TABLE 2-2 (Continued) 5':

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

3.0 The gaseous radwaste effluents from HNP-2 were released in a continuous mode.

There are three (3) release points at HNP-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.

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 for the third quarter was 1.8E-03 mrads and 1.0E-01 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' "Member of the Public" was 7.7E-03 mrem for the third quarter and 8.4E-02 mrem for= the fourth quarter.

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

Doses were determined at two special locations.

l.

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.

There were no abnormal releases of gaseous effluent during the third and fourth quarters of 1987.

The increase in total curie output for noble gases in the fourth quarter was due to a leak in a fuel pin.

On the 12th of November a small increase was noted in the post treatment monitors activity.

The following day, during a power descent for condensate filter demineralizer

changes, the activity on the post treatment monitors increased significantly.

Analysis at several points in the off gas system confirmed the main plant vent monitors increase was due to the additional noble gases from the leak.

The resulting effluent dose calculations demonstrated that all levels were well within the 10CFR20 and 10CFR50 Appendix I limits.

The beta air dose was 7.3E-02 mrad and the gamma air dose was 1.0E-01 mrad for the fourth quarter.

These results are ~

l%%d of the quarterly limit (10 mrad/quarter) for beta and 2% of the quarterly limit (5 mrad/quarter) for gamma.

An NCR, 287-291, was issued for an effluent monitor sample rack, WEA-SR-25, being out of service for longer than the four hours allowed by the Technical Specifications.

At the time the sample rack was removed from service, we entered Plant Technical specification action 3.3.7.12.b (Table 3 '.7.12-1, Item 5.b and Action Statement 112).

The action required was to restore the unit to service within four hours or contin-uously collect samples with auxiliary iodine and particulate sampling equipment.

Two mechanics were assigned to perform the work on the fan and Operations informed HP/Chemistry of the auxiliary sampling equipment requirement.

The fan was removed and sent to the Maintenance Shop at 0700 hours0.0081 days 0.194 hours 0.00116 weeks 2.6635e-4 months .

Shift change then occurred and two different mechanics were assigned to the job.

However, one of the mechanics had also been scheduled for training that day and, therefore, was not available.

Although the auxiliary sampling equipment requirement had been passed on during HP/Chemistry shift change, the information was not monitored.

It was then discovered, after the four-hour period had passed, that the sample pump was still disconnected and the tubing on the sample skid was disconnected such that it was not possible to set up an auxiliary sampler.

The Control Room was notified and Radwaste Building Ventilation secured.

Maintenance was notified and two other mechanics were then assigned to the job, which was completed at 1412 hours0.0163 days 0.392 hours 0.00233 weeks 5.37266e-4 months .

The cause was miscommunica-tion between Operations, Maintenance and HP/Chemistry personnel.

The total out of service time was seven hours before the Radwaste Building exhaust was secured.

The pump and sample rack were deemed operable two hours later.

Evaluation of the pre and post ou't of service building effluent activities, indicates no abnormal gaseous effluent releases occurred.

Additionally there were no changes in the in-plant air samplers during the out of service time period.

There was no cause for any concern to the health and safety of the public, plant personnel or the plant.

Total error estimates are based on grab samples, gamma spectrometry, analyzer detectors, and beta scintillation readings.

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

The estimated error was determined to be 36%%d at the 95%

confidence level.

In addition to the reactor site, WNP-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.

Also 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 isotopes present other than those attributable to natural background.

The average energy for fission and activation product gases in airborne effluents was 0.4360 Mev.

Table 3-1 NNP-2 GASEOUS EFFLUENTS SOURCE TERMS MIXED MODE RELEASES MAIN PLANT VENT July December 1987 CONTINUOUS MODE 3rd 4th 1.

Fission gases 4

E-

,7 2.

Iodi nes 5QIK:

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

3.

Particulates Table 3-1 (Continued)

l I

Table 3-1 (Continued) 3.

Particulates 5QIK:

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

Table 3-2 HNP-2 GASEOUS EFFLUENTS SOURCE TERMS GROUND LEVEL RELEASES TURBINE BUILDING July December 1987 CONTINUOUS MODE 31 d 4th 1.

Fission gases 2.

Iodi nes 5QIK:

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

10

1

Table 3-2 (Continued) 3.

Particulates c

4 E

EQK:

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 1987 CONTINUOUS MODE 3rd 4th 1.

Fission gases 2.

Iodines QQIE:

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

12

Table 3-3 (Continued) 3.

Particulates C

~

4

~

5QIE:

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

k 13

Table 3-4 NNP-2 GASEOUS EFFLUENTS SUMMATION OF ALL RELEASES July December 1987 3rd 4th A.

Fission

& activation gases

~otal~le 2.

Average release 3.

Percent of Tech.

B.

Iodines 1

~

Total iodine 2.

Average release 3.

Percent of Tech.

C.

Particulates 1.

Particulates 2.

Average release 3.

Percent of Tech.

4.

Gross alpha D.

Tritium 2.

Average release 3.

Percent of Tech.

" At 95'L confidence level 14

Table 3-5 HNP-2 GASEOUS EFFLUENTS BATCH RELEASES July December 1987 Total Maximum Minimum Mean Purge 1365.1 62 6.5 24.6 15

4.0 A total volume of 5977.5 ft3 (169.22 m3) of solid waste was transported in 21 shipments during the July 1 through December 31, 1987 reporting period.

The total activity of the waste shipped was 425.849 Ci; 425.322 Ci contained in dewatered spent resins, 0.524 Ci in Dry Active Haste (DAH), and 3.48 E-3 Ci in other (absorbed liquids).

A.

Dewatered resins accounted for 3967.5 ft3 (112.3 m3) of the radioactive wastes shipped during the reporting period.

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

The total activity of the resins shipped during the reporting period was 425.322 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, and NUPAC 14-210H, or NUPAC 10-142 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.

A total of 1980 ft3 (56.07 m3) of DAW was shipped in 48 Container Products Corporation, 8-25 steel boxes.

The total activity of the DAW shipped was 0.524 Ci.

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

The conversion factors were based on a nuclide distribution taken from reactor coolant sample analyses which are representative for the time period in which the waste was generated.

Short lived nuclides were eliminated based on decay of the DAW 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 DAH would be subjected to similar error contributions as the spent resins.

16

A total of 30 ft3 (0.85 m3) of absorbed liquids was shipped during the reporting period.

The total activity of the shipped absorbed liquid was 3.48E-3 Ci.

The liquid consisted of sump sludges absorbed in Aqueset and Aqueset II in 55 gallon Type 7A drums in order to meet burial ground requirements.

The drums were

17C, 17H and 17E/H designation

but, were shipped only as strong tight containers (STCs) per DOT requirements.

The values for the activities shipped were determined by using dose-rate-to-curie conversion factors and were based on sample analysis of the liquid at time of absorption.

As with DAN, the total error is assumed to be less than or equal to 20/. due to the likelihood of similar contributing errors to those associated with resins.

Scaling factors are based on outside laboratory (TMA/Norcal) 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 "Radionuclide Correla-tions in Low Level Radwaste",

NP-4037, June 1985 has been used as a

basis for the determination of a scaling factor.

Sampling of individual waste streams was performed with analysis performed 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.

TRU nuclides would be scaled to Ce-144.

As recommended by the AIF report "Methodolgies for Classification of Low Level Radioactive Haste 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.

17

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

Cs-137 and Sr-90 were not available in sufficient concentrations to allow development of reliable scaling factors.

The values obtained in the referenced EPRI report were 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.

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.

18

4.2 The Process Control Program (PCP) used to control solidification at HNP-2 will be prov1ded by the vendor waste processor, Pacific Nuclear Inc. in accordance w1th Contract C-20452, and will be subjected to POC review prior to any solidification of radwaste.

Two Pacific Nuclear gener1c solidification PCP's, TP-04, "Portable Solid1fica-tion System and TP-05, "Radwaste Solidification System" are currently under NRC review.

As an alternat1ve, approved High Integrity Con-tainers (HIC's) could be used for the transport of wastes requiring stabilization.

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

PPM 1.12.2, "Radwaste Process Control Program",

and 1.12.3, "Contract (Vendor) Haste Processing".

No significant changes have occurred in these procedures during this reporting period.

19

\\

P

Table 4-1 Co-60/C-14 Cs-137/Tc-99 Cs-137/I-129 Rx Coolant/H-3 DAN 5.9 E-4 3.0 E-5.

2.0 E-5 +

4.4 E-1 RNCU W

1 1.7 E-4 3.0 E-5 +

2.0 E-5 +

1.75 E-1

++

CFD w

1.0 E-4 +

3.0 E-5 +

2.0 E-5 +

1.75 E-1 EDR/FDR w

1.0 E-4 +

3.0 E-5 +

2.0 E-5 +

1.0 E-1 EDR/FDR

~B~Ri n 1.0 E-4 3.0 E-5 +

2.0 E-5 +

2.25 E-1 OIL 1.0 E-4 +

3.0 E-5 +

2.0 E-5 +

4.0 E-5 +++

Table 4-2 1

r fr i

1N DAN RHCU R

CFD p9wwiRr fQ EDR/FDR EDR/FDR OIL Co-60/Ni-63 Ce-144/Pu-238 Ce-144/Pu-239 Ce-144/Pu-241 Ce-144/Am-241 Ce-144/Cm-242 Ce-144/Cm-244 Cs-137/Sr-90 6.5 E-2 8.0 E-3 +

5.0 E-3 +

5.5 E-1

+

3.0 E-3 +

1.5 E-2 +

3.5 E-3 +

6.0 E-3 +

9.0 E-3 8.0 E-3 +

5.0 E-3 +

5.5 E-1

+

3.0 E-3 +

1.5 E-2 +

3.5 E-3 +

6.0 E-3 +

4.0 E-2 8.0 E-3 +

5.0 E-3 +

5.5 E-1

+

3.0 E-3 +

1.5 E-2 +

3.5 E-3 +

6.0 E-3 +

1.8 E-1 8.0 E-3 +

5.0 E-3 +

5.5 E-1

+

3.0 E-3 +

1.5 E-2 +

3.5 E-3 +

6.0 E-3 +

1.7 E-2 8.0 E-3 +

5.0 E-3 +

5.5 E-1

+

3.0 E-3 +

1.5 E-2 +

3.5 E-3 +

6.0 E-3 +

2.0 8.0 5.0 5.5 3.0 1.5 3.5 6.0 E-2 +

E-3 +

E-1

+

E-3 +

E-2 +

E-3 +

+

Scaling Nuclide not present in enough concentration to make determination of scaling factor.

In these cases the scaling factor obtained from the final EPRI Report "Radionuclide Correlations in Low Level Radwaste" (NP-4037, June 1985), will continue to be used as the HNP-2 scaling factors.

++

The report from TMA/Norcal, showed a concentration of H-3 in RHCU resin of 2.35 times the Rx Coolant H-3 concentration.

The resin mix used in RNCU and CFD is the same and the reactor coolant and condensate H-3 concentration are approximately the same.

The scaling factor for CFD powdered resins is 1.75 E-1 which is more representative of H-3 retention on the dried powdered resins.

+++

Oil is processed at NNP-2 by filtration and dewatering.

This process removes the water from oil.

The report from THA/Norcal was less than 4.0 E-5 for H-3.

The 4.0 E-5 factor was chosen and should be conservative in determining H-3 concentrations in oil.

Table 4-3 HNP-2 SOLID WASTE SHIPMENTS July December 1987 A.

SOLID HASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL 1.

Type of Haste Haste Stream Unit 6-month Est. Total D

a.

Spent resins, filter sludges, m3 112.3 b.

Dry active waste, contaminated m3 56.07 c.

Irradiated components, control m3 No Ship-d.

Other, (absorbed aqueous liquid) m3 0.85 2.

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

a.

Dewatered Spent Resins 4.

7

'Indicates scaled nuclide

, 21

b.

Dry Active Wastes (DAW)

~b-9 E-c.

Irradiated Components None d.

Other Absorbed Liquids Suade 3.

Solid Waste Disposition 21 Flat bed trailer (3) 14-210H Cask (17)10-142 Cask (2)"*

US Ecology

Richland, WA B.

IRRADIATED FUEL SHIPMENTS (Disposition)

None "Indicates scaled nuclide

- Activityfor one of the two shipments was quantified in June 1987 and included in the January 1 to June 30, 1987 release curie amounts.

The actual shipment in the 10-142 cask was made on July 1, 1987.

22

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

The first three quarters of 1987 were drier than normal with moderate precipitation arriving in the fourth quarter.

The 1987 dispersion condi-tions compared well with historical dispersion conditions.

The automated annual data recovery system continued to function at greater than 901.

joint data recovery for the joint frequency parameters.

Data recovery in quarters 1-4 at the 33 foot level was 90'/,

911.,

881. and 98% respectively.

Tables 5-1 through 5-8 list the joint frequency distribution at the 33 ft. and 245 ft. levels for 1987 by quarters.

Additionally, this report includes Tables 5-9 through 5-10 which list the joint frequency distribu-tion for all of 1987.

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

Numerals 1-7 were used for the wind subfields 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.

Calibrations performed in 1987 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.

23

k 7 s J

t II~

I ci TABLE 5-1

~

IGT QUARTER IiC7 NT FREOUEttCY DISTRIBUTION FOR TtlE 33 FT L CALCULATED FRON HOURLY AVERASES FROM TAPE 0.6 ttAXItfUN MIND "I'EEDS fOR EACH CATE6ORY Itt ttPtl ARE:

2 "

3.0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0 t(UNDERS 61YEtt APiE ttOURiS STAB CLAC MIND N

HHE HE EHE CAT ESE SE SSE SSM SM MSM M

MHM NM HHM 2

2 f 2

2 2

2 3

4 4

4 5

5 5

6 4

6 6

4 6

7 7

7 7'1 2

4 5

7 I

2 5

6 7

I 2

5 7

I 2

3 4

5 6

7 0.

1.

20 0.

0.

0, 0.

0.

0, 0.

1.

0.

D.

0.

2 ~

0.

1.

0 ~

1.

20 0.

D.

0.

0 ~

0.

20 D.

0.

1.

i.

1.

0.

4, I ~

0.

D.

0.

l.

0.

D.

0.

D.

1.

0.

D, 20.

0.

20 15.

6.

0.

D.

9.

4.

0.

D.

0.

I"i.

20.

0.

D.

0.

12.

St 0.

D.

0.

0, 6.

nI ~

0.

D.

0.

C.

21 0.

0, D.

0.

4, 0.

0.

14.

13 0.

D.

0.

0, 0.

00 i.

2i 0.

0.

D.

0.

0, D.

0.

2e 20 0.

0.

0, 6.

00 0.

0.

20 0.

0.

1.

0.

~ 0 ~

0.

0.'.

0.

D.

0.

Di 1.

0.

L.

i.

0.

6.

4 ~

0.

20 1.

0.

30 0.

0.

l.

0.

0, 0 ~

0.

O.

0.

1.

l.

0.

2 ~

6.

L.

0.

2.

5.

0.

1.

0.

20 2N 0.

0.

1.

3.

1.

0.

f.

0.

D.

0.

i.

7.

0.

1.

23.

D.

0.

Il.

21.

4.

0.

3 ~

C.

0.

D.

0.

3.

0.

1.

0.

1.

21 0.

0.

4.

11.

70 1.

0, 0.

1.

9.

2/i 7.

0.

15.

44, 15.

1.

0.

21.

35.

7.

0.

i.

L.

11.

0.

01 D.

3.

0.

4.

12.

7i 4.

0 ~

0.

14.

15.

1.

0.

21.

31.

21.

l.

00 0.

00 11.

19.

4 ~

0.

0 ~

0.

20 2i 4.

L.

0.

1.

0.

1.

0.

D.

1.

2i 0.

0.

7.

10.

1.

0.

f.

12.

IC.

lb.

4.

0.

2i 17.

13.

S.

0.

1.

5.

20 0.

0.

3i 24 0

0.

3.

0.

1.

20 0.

D.

0.

1.

Si 5.

Si 0.

0.

6.

17.

15.

5.

0.

1.

2f.

11.

0.

11.

5.

0, 0.

0.

20 2.

6.

0.

4 ~

5.

0.

1.

9.

20 0.

0.

14.

9.

0.

9.

0.

0 ~

0.

I.

0.

D.

0.

l.

0.

4e 7.

7.

0.

12.

14.

11.

0.

D.

0.

12.

4.

0.

4.

0.

0 ~

0.

1.

S.

6.

2 ~

0.

0, 0.

0.

I ~

0, 0.

0.

20 l.

1.

20 0.

0.

C.

21.

C.

0.

I, 30.

54.

18.

0.

2C, 23.

20 0.

0.

1.

17.

0.

D.

0.

6.

0.

30 0.

1.

0.

5.

23.

0.

2 ~

0, 1.

1.

0.

D.

1.

0.

2i 0.

0.

5 ~

1.

0 ~

0.

2$

43.

14.

2$

0.

3D.

23.

0.

14.

21.

0.

0, 0.

22.

1.

20 0.

0.

1.

43, 21.

0 ~

0.

1.

11.

4, 0.

0.

D.

0.

43.

'35.

TOTAL HUNER OF USED =

1930 MDURS iiISSlNC CALN =

VNilACl.E

4 Id

\\

i 4Q

',r I "J

TABLE 5-2 IST DUARTER 1987

%XNT FREQUENCY DISTRIBUTION FOR THE 245 FT L CALCULATED f'RON liOUfiLY AVCfAGES FliON TAPE 0.4 NAXIIIUtl MIHD SPEEDS FOR EACH CATEGORY IN NPH ARE:

2 -

3.0 3 -

7' 4 - 12.0 5 - 10.0 4 '4 0 STAB CLASS MIND CAT IOIC NE CNE NUtlBERS GIVEN ARE HOURS t(NN I

I I

I 2

2 2

3 3

4 4

5 5

5 6

4 6

7 7

7 I

2 3

5 6

7 I

2 4

5 4

7 I

2 4

5 6

7 I

2 5

4 7

I 2

4 5

6 7

I 2

4 5

7 f

2 4

5 6

7 0;

0.

'0

~

0.

0 ~

0.

1.

0.

20 1.

4.

0.

,0.

21.

37.

4.

~ 10.

0.

17.

36.

4.

0.

f.

l.

14.

2 ~

0.

1.

20 0.

0.

1.

0.

30 20 0.

0.

1.

0.

21 2i 0.

0.

2 ~

~0.

0.

0.'.

0.

1.

l.

0.

20 0.

0.

Oi 0.

0.

l.

4e 0.

1.

0.

19.

12.

0.

0; O.

6.

0.

4.

7.

20 0.

0.

5.

1.

0.

20 0.

0.

20 5.

0.

14.

12.

22.

30.

2.

I'.

0.

13.

11.

10.

0.

0 ~

0.

l.

1.

0.

1.

0.

20 71 21 0.

0.

1.

6.

14 0.

0.

10.

6.

f.

0.

4, 0.

0.

f.

0.

1.

0.

l.

0.

1.

0.

0'.

3.

1.

0.

5.

20 1.

0.

1.

f.

0.

1.

0.

20 0.

0.

9 0.

0.

O.

8.

4o 0.

0.

20 1.

0.

1.

0.

1.

0.

2t 14.

f.

0.

1.

15.

0.

O.

19.

4.

0.

4.

2I 0.

0.

4.

0.

2 ~

l.

0.

1.

4.

0.

0.,

0.

4, 6.

C.

20 0.

0.

6.

12.

25.

0.

15.

20.

IO.

1.

0.

9.

18.

5.

0.

0 ~.

1.

20 8.

20 0.

0.

1.

f.

0.

1.

20 0.

0.

3 ~

10.

12.

4e 0.

1.

51 O.

9.

12.

1.

0.

2I 14.

17.

13.

12.

1.

0.

14.

24.

12.

0.

2 ~

20 4.

0.

I ~

0.

1.

I.

0.

1.

0.

l.

1.

0.

1.

6.

10.

0.

4o 12.

19.

11.

0.

0; 0.

10.

14.

13.

1.

0.

1.

14.

9I ~

6.

0.

20 20 0.

0.

0 ~

0.

f.

1.

0.

I.

0.

0, 1.

7t 4.

5.'.

0.

70 10.

12.

10.

1.

0.

21 11.

10.

O.

0.

1.

8.

9 ~

0.

=- 0.

0.

1.

f.

6.

0.

24 1.

0.

1.

0.

1.

0.

I ~

5.

3 ~

1.

0.

20 8.

10.

8.

O.

21 0.

0.

14.

10.

50 0.

0.

6.

0.

20 f.

'0.

0.

1.

0.

1.

0.

1.

0.

8.

10.

S.

0.

11.

12.

11.

IC.

0.

l.

6.

7.

6.

'0',

0.

C.

5.

0.

1.

4.

50 3.

0.

31 0.

0.

21 0.

0.

1.

0.

0, 0.

15.

12.

0.

26.

2f ~

O.

0.

3 ~

11.

13.

l.

.0.

0.

20 2l 20 0.

0.

1.

20 0.

0<<

0.

4.

0.

4.

0.

1.

0.

0 ~

14.

20 1.

0.,

0.

23r 43.

29.

5 ~

0 ~

0.

1.

fil 22.

15.

0.

7 ~

S.

2t 0.

0.

TOTAL NUNBER OF HOURS USED =

1908 iiISSIekG =

CALN =

VAfiIACLE =

IS 25

I

~

I t

E 1

I rt

TABLE 5-3 2HD QUARTER 1987 NT FREQUENCY DISTRIBUTION FOR THE 33 FT L CALCULATED FROtl tiOUPiLY AVEPiASES FROtt TAPE I -

0.4 MAXIMUM MIND SPEEDS FOR EACH CATEGORY IN iMPH ARE:

2 -

3.0 3 -

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

1 1

1 2

2 2

3 4

HIND CAT ii 2

4 5

6 7

1 2

4 5

6

?

1 2

~ 4 5

6 7

1 2

4 5

4 7

1 2

4 5

6 7

1 2

3 5

4 7

1 2

4 6

7 0.

5.

18.

1.

0.

De 0.

l.

0.

0, 0.

0.

5.

13.

0.

De 0.

0.

9 ~

13.

0.

12e 0.

0.

25.

5.

0.

ttieE De 4 ~

16 0 ~

0.

0, 0.

0.

0 ~

0.

0; 0

0 ~

0.

0 ~

0.

6.

8.

0.

4, 5.

0.

D.

38.

11.

0.

D.

2 ~

11.

0.

0 ~

0.

D.

0.

l.

1.

l.

0.

0, 0.

3 ~

2e 0.

0, 0.

0.

l.

0.

7.

4, 0.

0.

0, 0.

0.

6.

0.

'0.

0.

0 ~

0.

1.

2.

0.

1.

4, 0.

0, 0 ~

0.

1.

0.

D.

0.

0 ~

NE Et(E 0.

3.

O.

0.

D.

0.

l.

0.

1.

0.

C;4 ~

0.

D.

0.

1.

0.

2.

0.

ESE 0.

13.

12.

l.

0.

0 ~

0.

6.

7.

0.

7.

6.

0.

4.

0.

0 ~

1.

e

~

0.

0 ~

SE 0.

!4.

16.

5.

0.

4, 0.

0.

l.

1.

0.

9.

lb.

0.

0 ~

1.

2.

14, 2e 0.

0.

14.

O.

0.

nnE 0.

11.

0.

3 ~

0.

.0.

0.

0, 1.

0.

0, 0.

0.

17.

21.

8.

0.

8.

21.

l.

0.

l.

10.

21.

4.

0.

10.

0.

0, 0.

D.

0.

8.

30.

24.

2 ~

0.

1, 0.

0.

l.

2e 0.

0 ~

0.

10.

45.

18.

2.

0.

13.

22 ~

13.

2.

0.

17.

18.

0.

1.

9.

12.

0.

0, 0.

0.

5e 15.

11.

2.

0.

0 ~

0.

1.

0.

0, 0.

0.

1.

0.

2.

1.

0.

6 ~

30.

1.

0.

D.

7.

15.

23.

1.

0.

8.

12.

8.

0.

4.

10.

0.

D.

0.

11.

3.

2.

0.

0, 0.

0.

0 ~

0.

0 ~

0.

0 ~

I.

0.

10.

13.

11.

2e 0.

0, l.

6.

15.

5.

2e 0.

0.

11.

10.

0.

0, 0.

8.

2e 0.

D.

0.

HStt 0 ~

2.

8.

4e 5.

0.

0 ~

0.

1 ~

2e 0.

0.

0 ~

D, 3 ~

0.

7.

11.

n 5e 0 ~

0.

3 ~

O.

13.

0.

1.

4, 10.

1.

0.

5.

2.

1.

De 0.

0.

3.

4e 0.

0.

1.

0.

0 ~

0.

0 ~

~1.

0 ~

0, 0.

0.

11.

2 ~

0 ~

0.

5.

18.

12.

4.

0.

D.

2.

6 ~

9.

2.

0.

1.

0.

0e 0.

0.

0 ~

7.

1.

0, 0.

0.

0, 0.

0.

1.

2 ~

0, 0.

0.

10.

13.

7, 0.

0.

0 ~

7.

28.

31.

7 ~

0.

n

~

13.

2.

0.

7.

10.

0, 0,

0.

0, D.

7 ~

7.

0.

2 ~

0.

0, 0.

0.

'0.

0.

6.

17 1.

0 ~

0.

7 ~

13.

5 ~

0.

1".

10, 0.

0 ~

0.

12.

20.

0.

D.

NttH 0 ~

5.

10.

0.

0, 0.

D.

1.

0.

0, 0

0; 0.

0.

0 0.

0.

13, 40.

7.

0.

10.

17.

0.

13 4e 0.

D.

0.

1.

27.

0.

TOTAL ttUMBER OF HOURS U"CD =

1929 MISSINS

=

CALM VARIABLE =

54 26

J

'1 f'S t"

I F

C

'1

TABLE 5-4 0

2itD QUARTER 1987

'tT FREQUENCY DISTRIBUTIOtt FOR THE 245 FT LQ+

CALCULATED FRON tlOURLY AVERAGES FRON TAP~

0.6 NAXINUN MIND SPEEDS FOR EACH CATEGORY Itt ttPH ARE:

2-3.0 3-7.0 4-12 ~ 0 5-18 ~ 0 6 - 24.0 HUNBERS GIVEN ARE HOURS STAB Mitt D CLASS CAT 0.

25.

20 0.

0 ~

0.

l.

0.

0 ~

0.

8.

2.

5.

1.

0.

1.

0.

8.

6.

2 ~

0.

4 ~

10.

0, 0.

0.

0 ~

11.

21

'1.

2.

0.

5.

15.

0.

0, 0.

0.

0 ~

0.

70 1.

0.

Q.

1, 3 ~

2 ~

0, 0.

0.

5.

6.

0.

8.

12 0 ~

0.

0 ~

0.

4 ~

14 ~

1.

0 ~

0.

Q.

0.

0, 0.

2 ~

1.

0 ~

0.

0 ~

2 ~

6.

0.

0 ~

2 ~

5 ~

0 ~

0.

0 ~

0.

1.

7 ~

7.

2.

0.

e.

'ttttE NE EttE 0.

1.

7.

4.

0.

0 ~

~ 0, 0.

0.

2 ~

0.

l.

0.

0 ~

0.

5 ~

0.

2 ~

1.

0.

0 ~

0.

0, 0.

2.

0.

0 ~

0.

3 ~

7 ~

1.

0.

0, 0.

0.

20 0.

0.

0 ~

l.

2.

0.

2I l.

1 ~

0.

e.

0.

l.

0.

6.

O.

0.

0 ~

0, 0 ~

0.

0 ~

0.

0, 0 ~

0.

1.

2.

0.

0 ~

0.

2I l.

0.

20 5.

1.

0.

0 ~

0, 9.

13.

7I 0 ~

0.

l.

0 ~

0.

0 ~

0.

l.

0.

0 ~

1.

20 0.

0.

7.

5 ~

0.

3I 9.

6.

0 ~

0.

2I 5.

1.

0.

0 ~

0, 7.

19.

4e 0'.

0.

0 ~

l.

0.

l.

0.

0, 2 ~

7I 1.

0 ~

0.

5.

7 ~

4, 0.

0.

0, e.

1 ~

8.

2 ~

0.

2 ~

. 7.

2 ~

0.

SE SSE 0.

6.

11.

21.

2 ~

0 ~

0.

1.

0.

0 ~

0.

Q.

0, 0.

0.

50 13.

7.

l.

0.

0 ~

0.

5 ~

7.

2 ~

1.

0.

2 ~

7.

2I l.

0.

0, 0.

12, 1.

0.

0 ~

2 ~

10.

11.

4 ~

1.

0.

0 ~

0.

1.

0.

0 ~

0.

0 ~

0.

1.

0.

6.

22 ~

20.

1.

0, 0.

5.

9.

2 ~

0.

9.

5.

20 0.

0.

7.

3.

0.

5.

5 ~ i 2 ~

0 ~

0.

1.

0.

nI ~

12.

11.

4 ~

0.

5.

12

't 0.

0.

1.

10.

7 ~

10.

0.

8.

5 ~

2 ~

0, 0.

0.

3 ~

8.

9.

10 '

~

0.

e.

1.

0.

2.

l.

5.

0.

1.

0.

12.

14.

19.

13.

0.

1 ~

0 5.

18.

17.

0 ~

0.

7.

8.

2.

0.

0, 1.

2.

12.

2.

0.

SSM SM MSM 0.

4, 14.

10.

2 ~

0.

l.

2.

0.

0 ~

0.

0, 1 ~

1.

0.

14

'2

'1.

8 ~

1.

0 ~

1.

3.

13.

17.

11.

0.

5.

12.

10.'.

0, 0 ~

0.

10.

12.

0 ~

0.

Mtt¹ 0.

5.

11.

2.

0.

1.

0.

l.

0.

0 ~

0.

1.

0.

~ 0.

0.

25.

38.

12.

11.

4 ~

0.

1.

8.

14.

22.

10.

l.

0.

2 ~

6 ~

17.

1, 0 ~

0.

1.

4, 9.

8.

2.

0.

II¹ 0.

3 ~

17 ~

0.

1.

0.

1 ~

2I l.

0.

20.

30.

10.

4.

0.

0 ~

7.

18 ~

20.

9.

1.

e.

1.

7 ~

15.

5 ~

0.

0 ~

0.

l.

.9.

6.

5.

0.

e.

0, Ntt¹ 0.

7.

10.

0.

0.'.

0.

1.

0 ~

0.

0 ~

0.

5.

18.

7 ~

1.

0.

0 ~

0.

5.

17.

21.

18.

2 ~

0.

6.

20.

10.

8.

0.

7.

16.

13.

5 ~

0.

TOTAL NUNBER OF Ucf'n

=

1n70 HOURS nA) g MP.IdP.I S'

~I 27

l l

I 1<!

TABLE 5-5 3RD QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE 33 FT L~VL CALCULATED FRON f,OURLY AVERAGE FRON TAQI 0.6 NAXINUN MIND SPEEDS FOR EACH CATEBORY IN NPH ARE:

2 -

3.0 3

~

7' 4

12 '

5 - 18.0 24.0 STAB CLASS RIND CAT NNE NE ENE NUNBERS 6IVEN ARE HOURS'E

<<NN NN NNN 1

1 1

1 2

2 2

4 4

5 5

5 6

6 6

7 7

7 1

2 3

4 5

6 7

I 2

5 7

2 4

5 6

7 1

2 3

5 6

7 1

2 5

6 7

I 2

4 5

7 f

2 3

4 5

6 7

0.

. 9.

34.

9.

4 ~

0.

D.

0.

3.

1.

0.

1.

0.

20 2I 0.

1.

0.

nI ~

10.

l.

0.

5.

2I 0.

0.

11.

4.

0.

20 36.

f.

0.

14..

0.

1.

0.

2I 0.

0.

50 7I 0.

0.

4.

0.

1.

0.

D.

14.

0 ~

0.

01 36.

10.

0.

5.

0.

20 0.

0.

2 ~

6.

0.

5.

4.

0.

4 ~

0.

1 ~

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D.

TOTAL NUNBER OF HOURS UCED =

fa67 NICCINS =

CALN -"

VARIABLE "-

63 28

+d

~I/

td

TABLE 5-6 3RD QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATCD COON llOURLY AVERAGES CRON TAP NAXINUN MIND SPEEDS FOR EACH CATEGORY IN NPH ARE:

0;6 2.

3.0 3 -

7.0 4 - f2.0 5 - 18.0 6.

NUNBERS GIVEN ARE HOURS 24.0 STAB CLASS' 1

1 1

2 2

2 2'

3 3

4 4

4 5

5 5

6 6

6 7

7 7

HIND CAT 1

2 4

5 6

7 2

4 5

6 7

2 5

6 7

2 5

6 7

1 2

4 5

6 7

1 2

5 6

7 2

3 4

5 6

7 0.

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H HNH IlH NNH TOTAL NUNBER OF HOURS USED =

fG96 HISSING =

l CALN VARIAELC =

32 29

4 1'I I

Lt'g

,~j I(

L.)

TABLE S-7 4TH QUARTER 1987 T FREQUEtICY DISTRIBUTION FOR THE 33 FT I.

CALCULATED I'RON IlOURLY AVERAGES fROH TAPE 0.6 HAXIHUII MIND SPEEDS FOR EACH CATEGORY IN iHPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0 5 -

1G.O itIUtIBERS GIVEN ARE HDURS 6 - 24.0 STAB CLASS 1

1 1

1 2

2 2

4 4

4 5

5 5

5 6

6 6

7 7

RIND CAT 1

2 4

5 6

7 1

2 5

6 7

1 2

5 6

7.

5 6

7 2

4 5

6 7

1 2

5 6

7 1

2 4

5 6

7 0.

1.

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1.

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'0.

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1.

19.

1.

0.

0, 0.

2.

14.

10.

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2.

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29.

4 ~

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IltN tIN tttttt TOTAL IIUIIBER OF HOURS USED =

2062 HISSING

=

O'ALII=

21 VARIABLE =

89 30.

k

, ~

~

~V, C

4 44 l

"~r 4

t

t'

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TABLE 5-8 4TH QUARTER 1987 T FREQUENCY DISTRIBUTION FOR THE 245 FT L CALCULATED FROil HOUfiLY AVEPiA6ES FPiON TAPE NAXINUN MIND SPEEDS FOR EACH CATE6ORY IN NPH ARE:

0,4 2-3.0 7.0 4-12 ~ 0 NUNBERS 6IVEN ARE HOURS S -

18 ~ 0 4 - 24.0 STAB CLAS Nltt 6

CAT tltlE NE ENE ESE SE SSE SStt SuN tinti IiOil NN tlNN 1

1 1

2 2

2 4

4 4

4 5

5 5

5 C

5 5

6 4

6 7

7 7

2 5

6 7

1 2

5 7

1 2

4 5

6 7

1 2

4 5

IV 7

1 2

4 5

6 7

1 2

5 4

7 2

4 5

6 7

0.

2 ~

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2I 2 ~

0.

D.

4 ~

1 ~

0.

8.

5.

2 ~

1 0.

0.

1.

18.

32.

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0, 2 ~

24 ~

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1.

0.

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21.

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TOTAL NUtlBER OF HOURS USED

=

2094 HISS ItlG =

CALit =

VARIABLE =

57

I I

I 4,,

J~

tl

TABt.E 5-9 1"iG7 AttttUAL NT fREOUEttCY DISTRIBUTIOtt FOR THE 33 FT CALCULATED FRON HDURLY AVERAGES FRON TAPE 1 -

F 6 NAXINUN NltiD SPEEDS fOR EACH CATEGORY Itt NPH ARE:

2 -

3.0 3 -

7.0 4 - 12.0 5 - 18.0 6 - 24.0 s(UttBEPiS GIVEN A&iE HOURS CLAS ttlND S

CAT N

NNE NE ENE ESE SSE SSM SM 1

1 1

I 1

I 2

2 2

3 4

4 4

4 5

5 5

5 6

6 6

6 7

2 3

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6 7

1 2

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6'7 1

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1 2

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99.

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0.

0 ~

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0, 0 ~

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0.

2$

59.

23, 0.

-0 0.

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158.

0 ~

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10.

0.

'0.

0.

5.

10.

5.

0.

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1.

D.

1.

53.

75.

20 ~

7 ~

3.

0.

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109.

132.

32.

0, 0.

2 ~

107, 85.

0 ~

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0, 0.

0 ~

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8.

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0.

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0.

0 ~

TOTAL NUNBER OF HOURS

'SED

=

7790 ifISSfitG "-

ChLM VARIABLE =

237 32

I I

I

p Cf 4

,Fa VNf; 4-

'u

~ I

TAIILE S-10 1987 ANNUAL~IT FREOUEtICY DISTRIBUTION FOR THE 245 FT L~

CALCULATED FPiOM HOURLY AVERAGES'ROM TAPV I -

0.6 MAXIMUM HIND SPEEDS FOR EACH CATEGORY IN MPH ARE:

2 -

3.0 3 -

7.D 4 - 12 '

5 - 10.0 6 - 24.0 NUtlBERS GIVEN ARE HOURS STAB CLASS I

I I

2 2

2 3

4 4

4 5

5 5

5 c'

6 6

6 7

7 7

NltlD CAT I

2 5

6 7

I 2

5 6

7 I

2 6

7 I

2 5

7 I

4 6

7 I

2 5

6 7

i 2

4 5

6 7

0.

40.

&5.

18.

0.

24.

11.

5 ~

2I 0.

0.

16.

20 1.

I ~

0.

I ~

38.

72.

9 ~

10.

l.

0.

6.

57.

61.

14.

16.

2 ~

0.

l.

42.

68.

18.

0.

79

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14.

3 ~

0.

lb.

58.

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0.

7.

2.

0.

7I 15.

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49.

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20 38.

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]4 III

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TABLE 5-2 IST QUARTER 1987 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FRON IIOURLY AVERAGES FRON TAPE 1.

O.C NAXINUN NIND SPEEDS FOR EACH CATEGORY IN NPH ARE:

2 -

3 '

3 -

7.0 4 - 12.0 5.

18.0 24.

NUtIBERS GIVEtt ARE HOURS G TAB HIND CLASS CAT I

1 2

I 3

1 4

1 5

6 1

7 2

1 2

2 2

3 2

4 2

5 2

C 2

7 1

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3 4

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6 3

7 4

I 4

2 4

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4 5

4 C

7 5

1 5

2 55,4 5

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6 5

7 6

1 2

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4 6

5 C

7 7

7 2

7 7

4 7

5 7

6 7

7 0.

1.

0.

1.

0 ~

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0.

21.

37.

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TOTAL NUNBER OF HOURS USED =

1908 NIGGIt(G =

CALN =

44 VARIABLE =

25

0 l

y 4

,I F

TABLE 5-3 2HD QUARTER 1987'OINT FREQUENCY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FRON ItOUtiLY AVERASES FPiON TAPE I -

0.6 NAXINUN ttIHD SPEEDS FOR EACH CATESORY IH NPH ARE:

2 -

3.0 3 -

7.0 4 " 12.0 5 " fG.O 24.0 NUNBERS GIVEN ARE HOURS STAB CLASS 1

1 I

I I

I 1

2 2

2.

2 2

3 4

4 4

5 5

5 6

6 6

7 7

7 HIND CAT 2

5 6

7 2

4 5

6 7

I 2

4 5

6 7

I 23, 5

6 7

1 2

5 6

7 1

2 3

5 6

7 1

2, 4

5 6

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0.

5.

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0.

0 0.

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0.

25.

5.

0.

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4 ~

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0 ~

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tN tati'OTAL HUNBER OF HOURS USED =

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NIGSIHS =

0 CALN

'APilAELE =

54 26

a

~

p r

C I

ll

'V

TABLE 5-4 2ND QIIARTER 1987 0 ~ 4 JOINT FREQUENCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FROH tlOURLY AVERAGES FROW TAPE HAXIHUH WfttD SPEEDS, FOR EACH CATESORY IN,MPH ARE:

2 -

3 '

3 "

7'0 4 - 12,0 5 - 18.0 6 - 24.0 NUHBERS 6IVEN ARE HOURS STA CLAS 1

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TABLE S-5 3RD QUARTER 1987 JOINT FREQI,.

DISTRIBUTION FOR THE 33 FT LEVEL CALCULATCD fRON ttOURLY AVCRAGCG fRON TAPC 1.

0.6 NAXINUN MltjD SPEEDS FOR EACH CATEGORY IN NPH ARE:

2.

3.0 3.

7.0 4

f2.0 5. 10.0 24.0 NUNBERS GIVEN ARE HOURS GTAD NlttD CLASS CAT Nng ttC CNC C

EGC GC GGE GN "Gtt 1

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3

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TOTAL NUNBER OF HOURS UGCD =
1867 NIGGING =
CALN 5
VAfilADLC=
63 28
a'll
ii TABLE 5-6 3RD QUARTER 1987 JOIIIT FREQ
.Y DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FRON tlOURLY AVERASEG FROH TAI'E 0.6 NAKINUN HIND SPEEDS FOR EACH CATESORY IN NPH ARE:
2
~
3.0 3'-
7.0 4 - 12.0 S - 18.0 6. 24.0 NUNBERS GIVEN ARE HOURS GTAD CLASS
IIIIID, CAT tiIIE IIE EIIE GE GGE 8
GGII Gtt IIGN tN tttN 1
1 1
1 1
1 1
2 2
2 2
2 2'2 3
3 4
4 4
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5 5
5 5
5 5
6 6
6 6
6 6'
7 7
7 7
7 7
1 2
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7 1
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1 2
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6 7
1 2
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5.
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0.
0.
0.
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2.
0.
0.
0.
TOTAL tIUNBER OF HOURS USED
=
18nil NIGGltt6 =
CALH =
VARilAELE =
29
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p n
(
I g TABLE 5-7 4TH QUARTER 1987 JOINT FREQUEt{CY DISTRIBUTION FOR THE 33 FT LEVEL CALCULATED FRON ttOURLY'AVERAGES FRON TAPE NAXINUN HIND SPEEDS FOR EACH CATEGORY It{ NPH ARE:
1," 0.6" 2.
3.0 7.0 4. 12.0 5" 18.0 t{UttBERS GIVEN ARE HOURS
- 24.0 STAB CLASS 1
I 1
1 I
1 i
2 2
2 2
2 2
2 3
4 4
4 5'
5 5
5 5
5 6
4 6
6 6
4 6
7 7
7 7
7 7
7
¹It{D CAT 1
2 4
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7 1
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7 1
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t{¹ htN TOTAL t{UNBER OF HOURS USED =
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CALN =
21 VARIABLE =
89 E
30
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P td k
TABLE 5-8 4TH QUARTER 1'987 0.6 JOIHT FREOUEHCY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FPiON HOUPiLY AVEtiAGES FROtf TAPE HAXIHUtt HIHD SPEEDS FOR EACH CATEGORY IH HPH ARE:
2 -
3 '
3 -
7 '
4 - 12.0 5 - 18.0 ttUHBERS GIVEH ARE HOURS
- 24.0 STAB CLASS I
1 1
1 1
2 2
2 2
2 2
2 4
4 4
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5 5
5 5
6 6
6 6
6 4
6 7
7 7
7 7
7 7
¹lttD CAT I
2 5
6 7
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19 VARIABLE =,
57
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gl
'l l 4
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1
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TABLE 5-9 1987 ANtlUAL JOINT [fiEQUEtlCY DISTRIEUTIOtt FOR THE 33 FT LEVEL CALCULATED FRON HOURLY AVERAGES FRON TAPE I
0.6 NA1CIKUII MltlD SPEEDS FOR EACll CATEGORY Itt KPH ARE:
2 -
3.0 3 -
7' 4 - 12.0, 5 - 18.0 ttUKCEPiS GIVEN APiE HOUPiS 6 - 24.0 STAB CLASS 1
1 1
I 1
1 2
2 2
2 2
2 2
3 3
3 4
4 4
,5 5
5 5'5 5
5 6
6 6
6 6
6 6
7 7
7 7
7 7
7 1
2 5
6 7
2 5
6 7
1 2
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2 4
5 6
7 1
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5 6
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87.
67.
b.
0.
0.
0.
SI 6.
6 ~
0.
0.
0.
0.
SI 7 ~
0.
0 ~
0.
33.
74.
47.
15.
0.
0.
0.
47.
80.
51.
11.
0.
0.
3.
65..
71.
40.
1, 0.
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1.
58'3.
7.
0.'.
0.
0 ~
20.
42.
27.
10.
0.
0 ~
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4, 4,
0.
0.
1.
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3.
4.
1 ~
0.
1 ~
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43
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11 0 ~
1 ~
38 ~
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57.
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0.
5 ~
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51.
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4 ~
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31.
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0 ~
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33
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0 ~
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l.
0.
0.
1.
23.
31.
22.
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0.
0.
4 ~
20.
59 39.
'1.
0 ~
50.
30.
4.
0.
0.
0.
3 ~
43.
14 0.
0.
0.
0.
12.
25.
16.
6.
0.
0.
0 ~
, 1.
1.
0.
0.
0.
3 ~
1.
0.
0.
2 ~
1".
19.
22i'.',
0.
0.
34.
34.
18.
2.
0, 0 ~
5 ~
37.
24.
2i 0.
0.
0.
4.
35.
10.
0.
0.
0.
0.
12.
18.
0.
0.
0.
2 ~
2I x5, 0.
0, 0.
0 ~
8.
2I 20 0.
0.
0.
0.
25,'5.
19.
6.
0.
0.
1.
38.
59.
40, 4.
0.
0' 3S.
27 ~
0 ~
0.
0.
2 ~
25 ~
0.
0.
0.
0.
SSM SM MSM M
0.
20.
21.
12.
2.
0 ~
0.
0.
5.
20 3 ~
2 ~
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~ 0.
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2I 5.
7.
0 '
0.
0.
36
'6.
43.
20.
2.
0.
75.
158
'8.
lb.
0.
0 ~
4 ~
70 ~
64.
6 ~
0.
0.
0.
2 ~
59.
23.
0.
-0 0.
0.
i 0.
16.
10.
0.
0.
0, 0.
5.
10.
5 ~
1.
0.
0.
0.
6.
3 ~
2I 1.
1.
0.
1.
53.
75.
20.
7.
30 0.
5 ~
109.
132.
32.
0.
0..
2t
107, 85.
0.
0.
0.
0.
3I 75.
82.
0.
0.
0.
0 ~
0.
23.
52.
14.
0.
0.
0.
0.
9 4 ~
1 ~
0.
0.
0.
0.
10.
6.
'0 0.
0.
0.
0.
54.
92.
13 ~
1.
0 ~
0.'.
78 ~
65 0.
0.
95.
40.
0.
0.
0.
0.
8.
100.
38.
0 ~
0.
0.
0.
TOTAL NUNBER OF HOURS USED
=
7790 NISSIttG =
CALN =
VARIACLE =
237 32
Cl
~
h
TABLE 5-10 O.
1987 ANNUAL JOINT FREQUEt(CY DISTRIBUTION FOR THE 245 FT LEVEL CALCULATED FPiOH HOURLY AVERAGES FPiOtf TAPE 1 -
Oib t(AXIt(Ut( HIND SPEEDS FOR EACH CATEGORY IN HPH ARE:
2-3.0 3"
7.'0 4" 12.D 5-10 ~ 0 NUNBERS GIVEN ARE HOURS 6 - 24.0 STAB CLAS 1
1 I
I 1
1 2
2 2
2 2
2 2
3 4
4 4
4 4
5 5
5 5
5 5
5 6
4 6
6 6
6 7
7 7
7 7
7 7
1 2
5 6
7 2
5 4
7 2
4 5
6 7
1 2
5 6
7 2
5 6
7, 1,
2 t(ft(D S
CAT 0.
40.
05.
18.
0 0.
O.
24.
11.
5I 2I 0.
0.
0.
16.
2I f.
1 ~
0.
1.
38.
72 9.
10, l.
0.
4.
57.
61.
14.
16.
2.
0.
1.
42.
68.
18.
0.
0.
0.
4.
79
'0.
14.
0.
0.
0 ~
16.
50.
15.
0.
0 ~
0.
0 ~
7.
2.
0 0.
0.
0.
7.
15.
0.
0.
0.
0.
15
'9.
12.
20 0.
0.
2 ~
38.
65.
7.
l.
0 ~
0.
0.
4S.
43.
0.
0, 0 ~
0.
1 ~
49.
91.
15.
0 ~
0.
0.
0.
7.
25 ~
19.
0.
0.
O.
50 0.
0 ~
0.
0.
5, 6'.
0.
0.
0.
5 ~
lb.
15.
0.
0.
0.
2&.
53
'8 0.
0.
1.
22.
34.
11.
0.
0.
0.
0.
17.
55.
23.
2 ~
0.
0.
0.
2 ~
10.
7.
5 ~
0 ~
0.
.0.
1 ~
2 ~
1 0 ~
0.
0.
0.
0 ~
1 ~
2I 0.
0.
0.
1.
S.
8.
S.
3.
0.
0.
0 22.
22.
9.
2.
0.
0.
0.
15.
lb.
7 ~
1.
0.
0.
0, 10.,
14.
11.
0.
0.
0.
t(
t(t(E
. t(E Et(E, O.
4 ~
lb.
6.
4, 0.
0.
0 ~
1.
1 ~
0.
0.
0, 0.
0.
0 ~
3 ~
1 ~
Oc 0.
0.
0.
5 ~
9.
4.
10 0.
0.
2 ~
10.
17.
3 ~.
50 0.
0.
0.
lb.
3 ~
2.
0.
0.
0.
12.
13.
6.
4, 0.
0.
0 ~
9.
24.
3 ~
'5
~
2I 0 ~
0 ~
2.
l.
1 ~
2I 0 ~
0.
0 0.
0.
0.
1.
0.
0.
0.
4 ~
8.
30 1,
0.
0.
11.
70 9.
1.
0.
1.
8.
20 2.
0 ~
0.
2.
13.
20 2 ~
0.
0.
0 ~
lb.
35.
13 ~
0.
0.
0.
0 ~
2.
f.
2 ~
D.
0 ~
0.
0.
1.
4.
l.
1.
0, 0 ~
0.
7, 22.
8.
f.
3.
0.
1 ~
10.
22, 20.
2$
0 ~
0.
21.
'25.
lb.
3.
0 ~
0.
0.
17.
24.
1.
0.
SSE 18.
64.
19.
0.
() ~
0.
0.
3 ~
8.
2.
0.
0.
0.
0.
4.
2 ~
2I f,
0.
0.
1.
13 ~
43.
14.
0.
0.
1, 11:
50.
36.
0.
0.
24.
6.
0.
0.
-2 ~
18 ~
40.
14 '
~
0.
0.
0.
15.
54.
51 0,
0 ~
0 ~
50 0.
0, 0.
0 ~
b.
2.
0.
0.
0.
21 ~
41.
26.
18.
30 0
4, 14.
40.
64.
24.
8.
, 0.
0.
24.,
50.
39.
11 ~
f.
0.
0.
27.
50.
22.
2 ~
0.
0,'0.,
34.
40.
2I 0.
0.
3 ~
4.
2 ~
2l 0.
0 0.
4.
7 ~
0.
1 ~
0.
0.
17, 41.
38.
17, 5 ~
0.
l.
18.
31.
27.
26.,
4.
0.
3 ~
26.
37.
30.
24.
2 ~
0.
0.
32
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27.
4.
0.
0.
0.
14
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14.
0.
4I 0.
0, 2.
21 1.
1 ~
1 ~
0.
0 ~
1 ~
2I 7I 20 2I 0.
0.
lb.
25.
19 ~
23.
5 ~
0 ~
2l 18.
25.
39 ~
31.
11.
2I 2.
26.
27.
24
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1.
0.
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35.
20.
13.
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0 ~
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24.
13.
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0 ~
0, 0.
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6 ~
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35.
25.
1.'
~
0.
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35.
35.
7 ~
0.
6 ~
2f.
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21.
6, 0.
Q.
21 18 ~
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8.
0 ~
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0.
0.
14 ~
24'9.
0 ~
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1; 1.
6.
0.
0.
1.
0 ~
1.
0.
0.
0.
19 ~
34 ~
30.
12.
0.
4, 26.
34.
40.
30.
2 ~,
0.
2.
25.
32 ~
10.
4 ~
0.
0.
3I 32 ~
23.
50 1.
0.
0.
0.
1,3.
16 ~
6.
1 ~
1.
0.
O.
2 ~
2 ~
0 ~
2 ~
0.
0.
0.
0 ~
6.
0.
1.
35.
63.
4'9.
13.
6 ~
1.
29.
46.
79.
74 ~
" 15.
1.
5 ~
,20.
44.
40.
16, f.
0.
19.
30.
26.
6.
0.
0.
0.
0.
8.
14.
31.
31 '
~
5 ~
0.
0.
0.
20 7.
2 ~
1.
0.
0.
0.
3.
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1.
17.
0.
0.
0.
2.
2.
1.
0.
0.
0.
b.
13.
0.
0.
0.
35.
72.
39 ~
10.
0.
0.
20 55.
77 ~
89.
23.
1.
0.
44.
78.
23 '
~
0.
0.
1 ~
59.
92.
6S ~
27.
2.
0.
42.
4, 0.
1 ~
16 ~
35.
37.
10.
0.
0, 30.
10.
0.
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0.
26.
44.
32.
12.
1.
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2.
2, 21'5
'1.
72.
TOTAL NUNBER OF HOURS USED =
7840 NISSING =
29 CALtf =
70 VARIABLE =
150
,33
0
~
I ~
4
6.0 QgiiJll~Qg~ The doses to the maximum individual from WNP-2 liquid 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 calculated using the LADTAP II computer code.
sg~Qf1~egLt~
The GASPAR 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 runs utilized the quarterly averaged X/Q and D/Q values, and site specific input parameters pertaining to food productions (e.g.,
goat and cow grazing periods, etc.)
The air doses at the site boundary were used to verify compliance with Technical Specifi-cation 3.11.2.2.
To verify compliance 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 WNP-2 Visitor Center was evaluated for assessment of radiation doses to "Members of the Public",
due to their activities within the site boundary.
The ODCM assumes an eight (8) hour per year occupancy by "A Member of the Public" at the Visitor Center.
The dose assess-ment resulted in an annual calculated whole body dose of 6.1E-03 mrem.
The annual thyroid dose was 6.5E-03 mrem and the maximum dose to any other organ was l,lE-02 mrem.
The annual assessment of radiation doses to the likely most exposed "Member of the Public" to show conformance with 40CFR Part 190 is assumed to be located in the Taylor Flats vicinity (4.2 miles ESE).
The Gaspar 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 3.1E-02 mrem.
The annual thyroid dose was 9.5E-02 mrem and the maximum dose to any other organ was 5.0E-02
mrem, The direct radiation contribution showed no significant amount above normal background for that area which is approximately 90 mrem per year.
Table 6-1 1ST AND 2ND QUARTERS 1987 Whole Body 1987 Cumulative Whole Body Hax. Organ.
1987 Cumulative Max. Organ.
Drinking Shoreline Swimming Fishing Boating Leafy Veg.
Vegetables Milk Meat Total 2.9E-07 4.1E-08
1. 8E-10 3.5E-04 2.2E-09 1.7E-08 1.2E-07 6.1E-08
~&98 3.5E-04 2.9E-07 4.1E-08 1.8E-10 3.5E-04 2.2E-09 1.7E-08 1.2E-07 6.1E-08
~EQB 3.5E-04 1.8E-07 4.8E-08 1.8E-10 5.7E-04 2.2E-09 5.3E-08 2.8E-07 1.1E-07 R9E~
5. 7E-04
1. 8E-07
4. 8E-08
1. 8E-10 5.7E-04 2.2E-09 5.3E-08 2.8E-07 1.1E-07
5. 7E-04 Whole Body 1987 Cumulative Whole Body Max. Organ.
1987 Cumulative Max. Organ.
Drinking Shoreline Swimming Fishing
'oating Leafy Veg.
Vegetables Milk Heat Total
1. 3E-06
1. 8E-06 6.7E-09 1.2E-02 8.0E-08 6.8E-07 3.6E-06 2.2E-06
~F~
1.2E-02
1. 6E-06 1.8E-06 6.9E-09 1.2E-02 8.2E-08 7.0E-07 3.7E-06 2.3E-06 EMMZ 1.2E-02 2.6E-06 2.0E-06 6.7E-09 2.2E-02 8.0E-08 1.5E-06 8.3E-06 4.5E-06 2.2E-02 2.8E-06 2.1E-06 6.9E-09 2.2E-02 8.2E-08 1.6E-06 8.6E-06 4.6E-06
~F~
2. 2E-02 35
I D
D Table 6-1 3RD AND 4TH QUARTERS 1987 (Continued)
Whole Body 1987 Cumulative Whole Body Max. Organ.
1987 Cumulative Hax. Organ.
Drinking Shoreline Swimming Fishing Boating Leafy Veg.
Vegetables Milk Meat Total
5. 3E-07 5.9E-07 2.5E-09 4.0E-03 2.7E-08 2.3E-07 1.3E-06 9.0E-07
~MZ 4.0E-03 2.1E-06 2.4E-06 9.4E-09 1,6E-02 1.1E-07 9.3E-07 5.0E-06 3.2E-06 1.6E-02 9.5E-07 6.9E-07 2.5E-09 7.6E-03 2.7E-08 4.8E-07 2.4E-06 1.2E-06 F~
7.6E-03 3.8E-06 2.8E-06 9.4E-09 3.0E-02 1,1E-07 2,1E-06 1.1E-05 5.8E-06 3.0E-02 Whole Body 1987 Cumulative Whole Body Max. Organ.
1987 Cumulative Max. Organ.
Drinking Shoreline Swimming Fishing Boating Leafy Veg.
Vegetables Milk Heat Total
1. 4E-07
1. 1E-07 6.9E-10 5.1E-04 1.0E-08 1,8E-08 2.4E-07 1.1E-07
'LJ F~
5.1E-04 2.2E-06 2.5E-06 1,0E-08 1.7E-02 1.2E-07 9.5E-07 5.2E-06 3.3E-06 KZMZ 1.7E-02
1. 7E-07
1. 3E-07 6.9E-10 1.1E-03 1.0E-08 3.2E-08 4.0E-07 2.3E-07 XJKHE 1.1E-03 3.9E-06 2.9E-06 1.0E-08 3.1E-02 1.2E-07 2.1E-06 1.1E-05 6.0E-06 ZJ3~
3.1E-02 (1) Age Group Adult:
Maximum individual resides at Richland and fishes at the WNP-2 slough area.
36
4 Table 6-2 1ST AND 2ND QUARTERS 1987 Hax. Organ.
Whole Body Hax. Organ.
Whole Body Fish Drinking Water Shoreline Swimming Boating Vegetables Leafy vegetables Hilk Heat Total 1.4E-06 1.0E-07
1. 4E-09
1. BE-11
1. 1E-11
6. 8E-07 5.8E-07 6.2E-08 ZZ~S 2.8E-06 8.7E-07 6.7E-08 1.4E-09 1.8E-11
1. 1E-11 3.6E-07 2.2E-07 3.5E-08 LZEQB 1.6E-06 4.1E-05 1.6E-06 5.9E-08 6.8E-10 4.0E-10 2.3E-05 2.9E-05 2.6E-06 9.8E-05 2.9E-05 7.9E-07 5.9E-08
6. 8E-10 4.0E-10 1.1E-05 9.8E-06 1.3E-06
~F~
5.2E-05 3RD AND 4TH QUARTERS 1987 P
w Hax. Organ.
Whole Body Hax. Organ.
Whole Body Fish Drinking Water Shoreline Swimming Boating Vegetables Leafy vegetables Milk Heat Total 3.0E-05 5.7E-07 2.1E-08 2.5E-10 1.SE-10 7.5E-06 7.5E-06 1.4E-06
~F~
4.7E-05'.
1E-05 3.3E-07 2.0E-08 2.5E-10 1.5E-10 4.0E-06 3.3E-06 6.8E-07 lZiF~
1.9E-05 2.8E-06 1.0E-07 4.3E-09 8.1E-11 4.7E-11 1.2E-06 4.7E-07 2.1E-07
~EQE 4.8E-06 1.3E-06 8.5E-08 3.6E-09 8.1E-11 4.7E-ll 7.8E-07 2.9E-07 1.2E-07
~MR 2.6E-06 37
~
r
>~a
Table 6-3 1ST AND 2ND QUARTERS 1987 D
E Max. Organ.
Whole Body Max. Organ.
Whole Body Fish Drinking water Shoreline Swimming Boating Vegetables Leafy vegetables Milk Heat Total
9. 2E-07
6. 4E-06 5.3E-07 5.9E-09 1.4E-09 7.4E-06 6.5E-06 9.0E-07 2.3E-05 5.1E-07 4.0E-06 4.5E-07 5.9E-09 1.5E-09 3.9E-06 2.4E-06 5.0E-07 1.2E-05 7.4E-OS 1.1E-04 2.2E-05 2.2E-07 5.5E-08 2.5E-04 3.1E-04 3.8E-05
~F~
8.1E-04
1. 7E-05
4. 8E-05 1.9E-05 2.2E-07 5.5E-08 1.2E-04 1.1E-04 1.9E-05
~EQ6 3.4E-04 3RD AND 4TH QUARTERS 1987 Max. Organ.
Whole Body Max. Organ.
Whole Body Fish Drinking water Shoreline Swimming Boating Vegetables Leafy vegetables Milk Meat Total 8.6E-06 3.5E-OS 7.6E-06 8.2E-08 2.1E-08 8.2E-05 8.2E-05 1.6E-05 2.3E-04 6.9E-06 2.0E-05 6.5E-06 8.2E-08 2.1E-08 4.3E-05 3.7E-05 7.9E-06 j 'iF~
1.2E-04
1. 8E-06 5.9E-06 1.4E-06 2.6E-08 6.6E-09 1.3E-05 5.1E-06 2.4E-06 3.0E-05 8.5E-07 5.1E-06 1.2E-06 2.6E-08 6.6E-09 8.5E-06 3.1E-06 1.3E-06 H2 2.0E-05 38
TABLE 6-4 50-MILE POPULATION DOSES FROM 1987 GASEOUS EFFLUENTS Exposure Railmmc Plume Ground Inhalation Vegetables Milk Heat Total Whole Body 9.7 E-02 1.3 E-02 4.8 E-02 2,2 E-02 6.2 E-03 1'.9 E-01 Max. Organ 3.5 E-01 1.5 E-02 1.6 E-01 4;0 E-02 1.5 E-02 5.8 E-01 AVERAGE INDIVIDUALDOSES FROM 1987 GASEOUS EFFLUENTS~a~
Exposure RaibmV Plume Ground Inhalation Vegetables Milk Meat Total Whole Body
~isa~~
3.9 E-04 5,2 E-05 1.9 E-04 8.7 E-05 2.5 E-05 7.5 E-04 Max, Organ
~8m9 1.4 E-03 6.0 E-05 6.4 E-04 1.6 E-04 6.0 E-05 9 'D~
2.3 E-03
<<>The population doses divided by the population for the 50-mile radius in the year 1980.
39
Table 6-5 CALENDAR QUARTERS 1987 Lou~:
1.2 miles site boundary Calendar Quarters Plus Annual Cumulative, 1987 Beta air dose (mrad)*
Gamma air dose (mrad)*
First Second Third Fourth Annual QuachJ Gum~
k,maker.
Qmzbz. Amuck~
6.8E-02 3.2E-02 1.2E-03 7.3E-02 1.7E-01 1.2E-01 5.8E-02 1.8E-03 1.0E-01 2,8E-01 Taylor Flats, 4.2 miles ESE Calendar Quarters Plus Annual Cumulative, 1987 First Second Quadr'ua~
Third Fourth Annual Qll~tRE QIRI~
CUlllUlktiMR Maximum organ dose (mrem)**
1,2E-02 7.2E-03 7.7E-03 8.4E-02 1.1E-01
Technical Specification 3.11.2.2.
Technical Specification 3.11.2.3.
40
During this semi-annual reporting period, no revisions were made to the Offsite Dose Calculation Manual (ODCM).
41
)
4 f~
C'
Washington Public Power Supply System 3000 George Washington Way P.O. Box 968 Richland, Washington 99352-0968 (509)372-5000 February 25, 1988 G02-88-049 Docket No. 50-397 U ~
S. Nuclear Regulatory Commission Attn:
Document Control Desk Washington, D.C.
20555 Gentlemen:
Subject:
Should you have any questions, please contact Mr.
R.
G. Graybeal,
Manager, WNP-2 Health Physics Chemistry.
Very truly yours, NUCLEAR PLANT NO. 2 SEMI-ANNUAL EFFLUENT REPORT JULY 1, 1987 TO DECEMBER 31, 1987 (Attached)
In accordance with Title 10 of the Code of Federal Regulations, Part 50.36a (a) (2), the subject report is herewith being submitted.
M. Powers NP-2 Plant Manager lw Attachment CC:
RB Samworth -
NRC C
Eschels - EFSEC JB Martin -
NRC RV (2)
D Sherman Amer. Nuclear Insurers TR Strong -
DSHS NRC Site Inspector DL Williams -
BPA
i a
4v

GO2-88-049, Semiannual Effluent Rept for July-Dec 1987

Contents

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SUBJECT:

1.0 INTRODUCTION

SUMMARY

Subject:

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GO2-88-049, Semiannual Effluent Rept for July-Dec 1987

Text

SUBJECT:

1.0 INTRODUCTION

SUMMARY

Subject:

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