ML20107J226

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Insp Rept 50-219/74-04 on 740320.Violations Noted.Major Areas Inspected:Enforcement Action,Environ Monitoring,Mgt Interview
ML20107J226
Person / Time
Site: Oyster Creek
Issue date: 04/16/1974
From: Bores R
NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION I)
To:
Shared Package
ML18039A986 List: ... further results
References
FOIA-95-258 50-219-74-04-01, 50-219-74-4-1, NUDOCS 9604250008
Download: ML20107J226 (8)


See also: IR 05000219/1974004

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U. S. ATOMIC ENERGY COMMISSION

DIRECTORATE OF REGULATORY OPERATIONS

REGION I

R0 Inspection Report No:

50-219/74-04

Docket No:

50-219

Licensee:

Jersey Central Power & Light Company

License No:

DPR-16

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Madison Avenue at Punch Bowl Road

Priority:

Morristown, New Jersey 07960

Category:

C

Location:

Oyster Creek Nuclear Station (OC)

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Forked River, New Jersey

Type of Licensee:

640 MWe - BWR (GE)

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Type of Inspection:

Special - (Environmental Monitoring)

D:tes of Inspection:

March 20, 1974

Dates of Previous Inspection:

February 6-13, 1974

UMd

R; porting Inspector.:

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J. Bores, Radiation Specialist

Date

Accompanying Inspectors:

Date

Date

Date

W. M. Lowder - Physicist - USAEC - HASL

Date

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K. M. Miller - Physicist - USAEC - HASL

Other Accompanying Personnel:

A. 2nwintowski - N..T. Rurenti nf Rad. Protect-

C. McNally - N. J. Bureau of Rad. Protect.

Date

R.

essler

.USAEC - DL (RAB)

Rcviewed By:

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J.P/St'ohr,Se'niorEn41ronmentalScientist

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9604250008 960213

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FOIA

DEKOK95-258

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SUMMARY OF FINDINGS

E nforcement Action (Environmental Monitoring)

None

Licensee Action on Previously Identified Enforcement Items

Fbnitoring)

(Environmental

None - within the scope of this inspection.

Design Changes

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_ Unusual Occurrences

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Other Significant Findings (Environmental Monitoring)

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Current Findings

None

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B.

_ Status of Previously Reported Unresolved Items (Environmental Monitoring)

None identified

Management Interview

on March 20, 1974,

office of Mr. J. T. Carroll at Oyster Creek Nuclear Station.follow

following individuals were in attendance:

The

Mr. R. J. Bores, Radiation Specialist, AEC, RO:I

Mr. R. Lessler, Radiological Assessments Branch, AEC, DL

Mr. J. T. Carroll, Plant Superintendent, OC

During this meeting the inspector stated the purpose of this inspecti

was to provide an independent determination of the gamma radiation le

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over and adjacent to the discharge canal. The_ types of measurements

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made were discussed and that sediment samples were taken from both the-

intake and discharge waterways for independent analyses by New Jersey

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and IHSL. The inspector stated that the preliminary gamma radiation

measurements indicated the levels along the canal were no higher than

elsewhere in the area, but that the final results would have to await

the report from HASL.

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DETAILS

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Persons Contacted

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Mr. J. T. Carroll, Station Superintendent,

OC

Mr. H. Kurtz, Oyster Creek Marina

2 . General

The stated purpose of this inspection was to determine whether

there was an observable effect on the ambient gamma radiation

levels associated with radionuclides in the sediments along

the discharge in Oyster Creek.

Radiation measurements were made

and sediment samples were obtained.

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3.

Environmental Radiation Measurements

The inspector accompanied and observed representatives of USAEC

Health and Safety Laboratory, New York, N.Y. as they made

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radiation measurements along the banks and over Oyster Creek.

The

detailed results of these measurements, including instruments

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used, locations, etc. , are included in the attached report (attachment

1), " Gamma Radiation Measurements at the Oyster Creek Discharge

Canal March 20, 1974." The inspector observed that there was no

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evidence of elevated gamma radiation levels along the banks or

over Dyster Creek.

In addition, the inspector obtained four sediment samples (three

from Oyster Creek and one from Forked River) which were split with -

personnel from the State of New Jersey, Bureau of Radiological'

Protection.

The RO:I samples were sent to the USAEC Idaho Health

Services Laboratory for analysis. When the results of these analyses

are available they will be included as a supplement to this report.

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ATTACHMENT I

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Gamma Radiation Measurements at the Oyster Creek Discharge Canal

March 20, 1974

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Wayne M. Lowder and Kevin M. Miller

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Radiation Physics Division

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USAEC Health and Safety Laboratory

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1 New York, N. : Y.

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In response to a request dated March 5,1974, from D. F. Knuth, Regulatory-

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Operations, to J. L..Liverman, Director, DBER, we undertook a series of, gamma

radiation measurements over and adjacent to the waters of Oyster Creek, which

is the liquid effluent discharge canal for the Oyster Creek nuclear power

station.

The purpose of these measurements was-to establish if th~eFe was any

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observable effect on ambient gamma ray levels of the presence of plant-p ^4uced

radionuclides in the water or the associated sediments.

Present during tne survey

were R. J. Bores, R0 Region I; R. Lessler, DLR; and A. Zawistowski and C. McNally,

N. J. Bureau of Radiological Protection.

The New Jersey team collected sediment

samples from both Oyster Creek and Forked River which are being independently

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analyzed at their laboratory and by HSL, Idaho Falls.

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The instrumentation used for the measurements included two lO-inch diameter

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argon-filled ionization chambers (24 and 40 atm., respectively) with 2.4 g/cm

steel walls, and two portable NaI(Tl) scintillometers.

The ionization chambers

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are calibrated to an overall accuracy of 13 percent, and have a range of 0.05

to 100 pR/h.

The portable instruments are field-calibrated against the ionization

chambers,andcanbereadtothenearest{2pR/h.

The i

chamber response to

the cosmic ray exposure rate of 3 7 gR/hb

was subtracte from the total ion

chamber readings in order to infer the gamma radiation intensity.

The data obtained on the survey are indicated in the accompanying table.

Loc-

ations 1, 4, 7, 8, 9 and 13 are normal background locations, and the observed

gamma exposure rates of 1-2 R/h

e consistent with our earlier. background data

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from the Oyster Creek plant site

Such levels, corresponding to an annual

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gamma exposure of ~ 15mR, are much lower than is typical of the eastern United

States.

This is due to the low concentrations of uranium (~ 1p,m), thorium

(~ 3 ppm) and particularly potassium (~ 0 3%) in the sandy soil 13].

Locations 2, 5 and 14 are situated along the banks of Oyster Creek, where radio-

nuclides in the water discharged from the plant might be deposited.

No evidence

of-any elevated gamma radiation levels.was observed.

This result is consistent

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with the previous observation by the New Jersey group that most of the effluent

radioactivity was deposited in mid-channel rather than on or near the shoreline [4].

ATTACHMENT I

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Locations 3 and 10 are situated near the center of the creek, approximately

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200 ft. from the nearest bank.

The measurements agree with our estimate [1]

of the cosmic ray intensity at sea-level plus a small additional contribution

of gamma radiation from radon daughters in the atmosphere, potassium in the

water, natural radionuclides in the wooden pier, and air-scattered radiation

from the shore.

It is noteworthy that this fairly unambiguous " measurement"

of cosmic ray intensity was made over the discharge canal of a large nuclear

facility, and represents nearly the lowest radiation level that is physically

possible in the outdoor environment.

Location 6 is situated at a place in the parking area where the hulls of the

boats are scraped.

Small quantities of sediment that are removed,may have

mixed with the sand and gravel, as indicated by the darker color of this area.

The gamma level is slightly higher here than in the rest of the parking area

(e.g., location 7), and this may be indicative of the presence of very small

quantities of radionuclides of plant origin.

However, the level is no higher

here than that in the lot across the street (location 9)

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Location 11 and 12 are boats of wood and galvanized metal construction that are

moored near the center of the creek.

To answer the question whether the close

proximity of the bottom of the hull of each of these boats to the underwater

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sediments resulted in an enhanced gamma radiation level, these boats were sur-

veyed with a portable scintillometer.

The gamma levels were exceedingly low,

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except near a large compass in boat 11.

Within 3 ft. of the compass, a gamma

field of greater than 10 R/h was noted, and the level at the operator's chair

was ~ 5 R/h,

i.e.,

more than twice the normal gamma background on shore.

There

was no indication of increased radiation levels at accessible points near the

hull bottoms.

This is not surprising if the water depth beneath the hull was at

least 6 inches, as seems likely.

Such a depth would absorb essentially all

gamma ladiation emitted by the bottom sediments.

In summary, our measurements indicate that the local population,

e.g., fishermen

and boat owners, receives no measurable exposure from external ganma radiation

emitted by radionuclides of plant origin in the discharge canal.

It should be

pointed out, however, that the dredging of the bottom sediments of the main

channel and their removal to a local land site might produce excess gamma levels

nearby comparable to or somewhat higher than the local natural background level,

depending on the depth of sediment removed.

This estimate is based in a cal-

culation, using the New Jersey sediment radioactivity data [5], of the air exnosure

rate (~ 100 R/h) above the exposed mid-channel sediments if the water were removed,

and consideration of the mixture of the more radioactive surface layers (< L-in.

depth) with the deeper layers after transport to another site.

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References

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1.

W. M. Lowder and H. L.' Beck, " Cosmic-ray ionization in the lower atmos-

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phere", J. Geophys. Research, 71. ~ 4661, 1966.

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' 2. . H. L. Beck, et al., "HASL Studies at the Oyster Creek' Nuclear Electricity

Generating Station", USAEC . Technical Memorandum HASL 'D4 72-3,1972. .

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et al.

" Experimental investigations of the environmental

W. ' M. Lowder, 5'F ,c. Second Int. Symposium on the Natural Radiation

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radiation fiel

Pro

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Environment, to be published, 1974.

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D. E McCurdy, "1971 Environmental Radiation Levels in the State of -

New Jersey," N. J. State Dept. of Environmental Protection,1CJf3

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D. E. McCurdy, et al.,

" Environmental Radiation Surveillance of the Oyster

Creek Nuclear Gene'ritting Station", ' N. J. State Dept. of Environmental

Protection, 1973

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Oamme Radiation Measurements

Location

7 Exposure Rate *

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(1) Field, E. side of Rt. 9, 200' N. of creek

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N. bank of creek, at Rt. 9 bridge

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(3) Sands Point Yacht Club, on wood pier, center

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of creek

(4) Sands Point Yacht Club, gravel parking lot

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(5) Sands Point Yacht Club, wet silt, S. side of creek

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(6) Oyster Creek Marina, " hot spot" in parking lot

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(7) Oyster Creek Marina, gravel parking lot

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(8) Oyster Creek Marina, asphalt street

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(9) Oyster Creek Marina, lot across street

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(10) Oyster Creek Marina, end of wooden pier,

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center of creek

(11) On board 40' boat, end of pier (slip 228)

(12) On board 40' boat, end of pier (slip 128)

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(13) Small park, 1/4 mile E. of Oyster Creek Marina,

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S. side of creek, sandy soil

(14) Over sandy beach at park, S. shore of creek

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(washed by tide)

Exposure rates are given to the nearest 0.1 R/hforionchambermeasure-

ments, and to the nearest i for portable scintillometer readings.

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