ML20044H212

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Reactive Insp Rept 50-219/93-07 on 930517-18.Violations Noted.Major Areas Inspected:Events Involving Work in Fill Aisle of New Radwaste Bldg on 930507-11
ML20044H212
Person / Time
Site: Oyster Creek
Issue date: 05/28/1993
From: Joseph Furia, Pasciak W
NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION I)
To:
Shared Package
ML20044H208 List:
References
50-219-93-07, 50-219-93-7, NUDOCS 9306080076
Download: ML20044H212 (8)


See also: IR 05000219/1993007

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U.S. NUCLEAR REGULATORY COMMISSION

REGION I

9

Report No.

50-219/93-07

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Docket No.

50-219

License No.

DPR-16

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Licensee:

GPU Nuclear Corporation

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l Upper Pond Road

{

Parsippany. New Jersey. 07054

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Facility Name:

Ovster Creek Nuclear Generatine Station

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Inspection At:

Forked River. New Jersev

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Inspection Conducted:

May 17-18.1993

t

b do, b hd

6hf[f3

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Inspector:

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J. Furia, fIeoior Radiadon Specialist,

date

Facilities Radiation Protection Section (FRPS),

Facilities Radiological Safety and Safeguards

,

Branch (FRSSB), Division of Radiation Safety

and Safeguards (DRSS)

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Approved by:

/ ff C

C~-d c

5-2M3

W. Pasciak, Chief, FRPS, FRSSB, DRSS

date

Areas Inspected: Reactive inspection of the events involving work in the fill aisle of the

New Radwaste Building on May 7 and May 11, 1993.

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Results: Five apparent violations of NRC requirements were identified. These include:

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failure to follow plant Technical Specifications and procedums in initiating a radiation work -

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permit (RWP) in that the RWP did not clearly define the work; failure to survey a work area

and failure to provide adequate instructions to workers (grouped as a single apparent

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violation); failure to follow plant Technical Specifications and procedures in not conducting

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an ALARA review of the work being performed in a highly contaminated area; failure to

perform air sampling required to properly select respiratory protection equipment, and;

failure to conduct appropriate air sampling during work.

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9306080076 930531-

PDR

ADDCK 05000219'

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DETAILS

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1. Personnel Contacted

l.1 Licensee Personnel

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  • F. Applegate, Quality Assurance Monitor
  • J. Barton, Vice President and Director, Oyster Creek
  • T. Blount, NCSS Staff, GPU Nuclear
  • W. Cooper, Radiological Engineering Manager

H. Daniels, Group Radiological Controls Supervisor

  • B. DeMerchant, Licensing Engineer

<

J. Derby, ALARA Supervisor

  • R. Hillman, Manager - Radwaste Operations

L. Johnson, Radiological Shift Technician

  • S. Levin, Director, Operations and Maintenance

D. Morris, Site Supervisor, Chem-Nuclear Systems, Inc.

R. Nash, Radiological Engineer

C. Pollard, Manager, Radiological Controls Field Office

M. Selvage, Radiological Controls Technician

  • R. Shaw, Radiological Controls Director

M. Zott, Westinghouse /HydroNuclear Technician

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l.2 NRC Personnel

  • S. Pindale, Resident Inspector
  • D. Vito, Senior Resident Inspector

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  • Denotes those present at the exit interview on May 18, 1993.

2. Description of Events

On May 7 and May 11,1993, the licensee identified events which were not in

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accordance with licensee expectations, and potentially not in compliance with

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regulatory requirements, regarding work being conducted in the New Radwaste

Building (NRW). Prior to May 7,1993, the license's Radwaste Operations section -

had identified a need to clean-up and decontaminate an area of the NRW on the 23'

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elevation, known as the fill aisle. This area, a posted locked high radiation area

which also required respirator usage, included areas for storage of filled waste liners,

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the processing of waste liners, associated pumps and equipment, and the batch tank.

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The batch tank was located in a shielded cubicle on the nonheast side of the fill aisle,

the shield creating an 8 foot deep pit around the batch tank. Over the course of

several years, the floor of this pit had become covered with spilled powder type resin,

from overflowing the batch tank, and miscellaneous wood, cement and herculite. No

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entries had been made into the pit for several years.

On May 3,1993, a contractor to the licensee submitted a request for a Radiation

Work Pennit (RWP), to allow for the hydrolasing of the fill aisle, and the removal of

all obstructing debris. The RWP (No. 930254) was prepared by an ALARA

technician and approved by the ALARA Group Radiological Controls Supervisor.

Although it was the intention of the Radwaste Operations section to decontaminate all

areas of the fill aisle, which would include entry into the batch tank pit area, this was

not clearly communicated to the ALARA technician orally or by means of the RWP,

as it did not clearly derme the areas to be worked and/or entered. Due, in pan, to

this miscommunication, the licensee determined that an ALARA myiew was not

required for this work. In addition, the miscommunication resulted in the preparation

of an RWP that did not adequately describe the scope of the task, panicularly as it

related to work in the batch tank pit. This is an apparent violation of Technical Specification 6.11, as licensee procedure 9300-ADM-4110.04, " Radiation Work

Pennit," pamgraph 7.2.3, states in pan that the RWP, in Block No. 3: Work

Description, shall provide sufficient detail for Radiological Controls personnel to

understand the scope of the task (50-219/93-07-01).

On May 7,1993 thme contractor workers went to the Radiological Controls (RadCon)

yard office for the purpose of entering the proposed work area and scoping the work

to be perfonned. Two workers, who would be responsible for the hydrolasing

activities, signed in on RWP 930254, and wem involved in a pre-job discussion with

the Group Radiological Contmls Supervisor (GRCS) for the yard area. The

Radiological Controls Technician (RCT) assigned to provide job coverage was not in-

attendance at the meeting. At this meeting it was discussed that entry into the batch

tank pit was going to be made. The GRCS instructed the workers to dress out in the

protective clothing mquired by the RWP, including wearing of alarming dosimeters

by at least one member of each work group, and contacted the RCT by telephone,

instructing the RCT to perfonn a survey, as required by the RWP, of the fill aisle-

prior to anyone in the work group entering the area. The GRCS assumed that the

RCT understood that a survey of the batch tank pit was to be a pan of this survey,

but did not provide explicit instmetions on this point. The RCT assumed that this

entry was like other entries made over the past several years, and that no entry to the

batch tank pit was to be made. The RCT met the work group outside the entrance to

the fill aisle, and instructed them to remain outside the fill aisle for several minutes

while she conducted the survey. After several minutes, the work group entered the

fill aisle and were met by the RCT, who informed them of dose rates in the various

areas, including a dose mte of 350 to 500 millimm per hour (mR/hr) at the batch

tank. This reading was, in fact, taken on top of the shield wall adjacent to the tank,

but was not the reading inside the batch tank pit,'which had not been taken. The two

hydrolasing contractors assumed that such a survey of the batch tank pit had been

conducted, and that the readings given by the RCT were for inside the pit.

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The two hydrolasing contractors proceeded to the batch tank area while the RCr

continued to survey areas of the fill aisle, specifically the pump area, which was not

expected to be an area entered by the workers that day. One of the contractors went

up a ladder onto a block wall around the batch tank, and then went down a second

ladder into the batch tank pit. The worker immediately noticed that the alarming

dosimeter he was wearing was accumulating dose at a rate much greater than he

would expect in a 350-500 mR/hr field. Within approximately 10 seconds, the

worker climbed back up the ladder to the top of the block wall, and asked his co-

worker to get the RCT. The RCT arrived at the pit area, discussed the situation with

the contractor, and the contractor offered to take a meter from the RCT and re-enter

the pit in order to determine dose rates (the RCT was not wearing a set of plastics,

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which were required for entry into highly contaminated areas, such as the batch tank -

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pit, while the two contractors were wearing full plastics) The RCT checked the

contractor's alarming dosimeter and noted a dose of 25 millirem at that time. The

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contractor re-entered the pit, with the RCT observing from on top of the block wall.

Dose rates were measured as high as 12 R/hr on contact with the batch tank and 10

R/hr on the floor. The contractor then exited the pit, and, together with the RCT,

discussed the situation with the other workers in the fill aisle. The RCT determined

that no further entries should be made into the pit, but that the workers could remain

in the general fill aisle areas. The RCT checked the contractor's alarming dosimeter,

which indicated a dose of 55 millirem. The dose of record was subsequently

determined to be 72 millirem for this entry, correcting for dose stratification within

the pit. The RCT then contacted the GRCS and informed him of the events and dose

rate readings.

The worker entered the pit area without a survey having been performed and without

receiving instructions of the radiological conditions. This is an apparent violation of

10 CFR 20.201(b) and 10 CFR 19.12. Surveys of radiation hazards, in accordance

with 10 CFR 20.201(b), are required to be made by the licensee as necessary to

comply with regulations and as are reasonable under the circumstances to evaluate the

extent of radiation hazards that may be present. Further, all individuals working in a

restricted area are required by 10 CFR 19.12 to be instructed of the radiological

conditions, with the extent of the instructions commensurate with the potential

radiological health protection problems. These apparent violations are aggregated as a

single apparent violation. (50-219/93-07-02)

On the afternoon of May 7, the GRCS, together with the RCT, contractors and a

representative from Radiological Engineering conducted a meeting to discuss the'-

cause of that morning's events and to better understand the scope of work to be

performed under the RWP. In spite of the significant work scope changes in the

RWP, the intention of the work to include entries into the batch tank pit, a highly

contaminated area, and to remove highly contaminated materials from the pit, an

ALARA review was not initiated for this work. This is an apparent violation of

Technical Specification 6.11, as licensee procedure 9300-ADM-4010.02, "ALARA

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Review Procedure," paragraph 7.3.2, requires that an ALARA review be performed

if one or more of five criteria exist. Criterion five includes any task inside highly

contaminated systems or components. (50-219/93-07-03)

.

On May 11, with work continuing in the fill aisle, four contractor technicians, split

into two groups of two members each, together with an RCT, entered the fill aisle,

wearing full sets of protective clothing, plastics, and negative pressure full-face

respirators, as required by RWP 930254. Two contractors, one group, went to the

top of the batch tank pit, where, using long-handled tools, they began to remove

debris from the pit, continuing a job that had started on May 10. The RCT covering

the work was principally frisking items removed from the pit, prior to their being

placed in a liner inside a shielded container located nearby. Prior to the start of work

on May 11, the RCT had entered the pit to determine radiation levels and found them

to range as high as 20 R/hr next to the batch tank and floor interface. Only one

member of the work group was wearing a breathing zone air sampler (BZA). The

licensee did have a 500 cfm High Efficiency Particulate Air (HEPA) unit available,

which was utilized when the workers completed the clean-up activities that could be

conducted from the top of the block wall, and was also utilized after the workers

entered the pit in order to complete thejob. Due to the confined space present in the

pit, only one person at a time could enter it and work. The contractor wearing the

BZA sampler entered the pit first, and worked for several minutes, after which the

second worker, not wearing a BZA, entered the pit for several minutes. While in the

pit, the workers were bent over scooping up debris and placing it in a bucket. The

HEPA unit hose was periodically moved around by the workers to keep it near the

work area. The hose extended down approximately four feet into the pit, leaving the

end of the hose four feet above the pit floor. The licensee did not take air samples in

the pit during the time the workers were removing debris with long-handled tools.

Subsequent analysis of the one worker's BZA indicated ' air concentrations equal to

56.1 times the maximum permissible concentration (MPC), while the negative

pressure full-face respirators that were worn gave a protection factor of only 50.

Title 10 CFR 20.103(c)(2) requires that the licensee's respiratory protection program

include, as a minimum, air sampling sufficient to identify the hazard and permit

proper equipment selection. Licensee procedure 9300-ADM-4020.03, "Use of

Respiratory Protection Equipment," paragraph 7.9.2, requires that respiratory

protection equipment be selected to provide a protection factor greater than the

multiple by which peak concentrations of airborne radioactive materials are expected

to exceed the values specified in Appendix B, Table I, Column I, of 10 CFR 20, as

determined by the sampling of airborne contamination. This is an apparent violation

of 10 CFR 20.103(c)(2), as the licensee had the opportunity on May 10 while workers

were removing debris from the pit with long-handled tools to perform air sampling of

the pit air for the purpose of selection of respiratory equipment for the next day when

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the pit was to be entered and did not do such air sampling. As a result, respiratory

equipment was selected that did not provide an adequate protection factor. (50-

219/93-07-04)

Having only one of the two workers wearing a BZA sampler, when each had to enter

the pit separately, is an apparent violation of the requirements of 10 CFR

20.103(a)(3), which require that for the purpose of determining compliance with the

requirements of 10 CFR 20.103, the licensee use suitable measurements of

concentrations of radioactive material in air. (50-219/9307-05)

3. Exit Interview

The inspectors met with the licensee representatives denoted in Section 1 at the

conclusion of the inspection on May 18, 1993. The inspectors summarized the

purpose, scope and findings of the inspection.

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Enclosure 2

.Page 1 of 3,

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/ vol. 57,.h us /- Pray, July a 1982 / Notices

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acessesse: send coma =nte ta:m

secretary a thee--won. u.s.

NuclearRaseteteryc

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Washlagteo.DC20555. ATTN:

Dodeting and Servise Braarh-

Head deliver =====to to: One White

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Flint North.11555 Rockville Pike.

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Redvtlle, bdD between 7:45 aJa. to 415

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pJa.FederalM hp.

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Copies of eesseente may be e==minad

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at the NRC Petdic Docuamat Room.2220

LStreet.NW.(14wer14 vel).

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received on or before this date.

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sdjudicedoo mey also be opened. For

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the pcrposee d tile trial progam, this

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