ML20198Q909
ML20198Q909 | |
Person / Time | |
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Site: | Haddam Neck File:Connecticut Yankee Atomic Power Co icon.png |
Issue date: | 01/14/1998 |
From: | NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION I) |
To: | |
Shared Package | |
ML20198Q900 | List: |
References | |
50-213-97-10, NUDOCS 9801230171 | |
Download: ML20198Q909 (74) | |
See also: IR 05000213/1997010
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. . U.S. NUCLEAR REGULATORY COMMISSION REGION I Docket No: 50-213 License No: DPR-61 Repoit No: 50-213/97-10 Licensee: Connecticut Yankee Atomic Power Company P.O. Box 270 Hartford, CT 06141-0270 Facility: Haddam Neck Station Location: Haddam, Connecticut Dates: October 8 - November 28,1997 Inspectors: Ronald L. Nimitz, CHP, Senior Radiation Specialist William J. Raymond, Senior Resident inspector Haddam Neck Station Approved by: John R. White, Chief, Radiation Safety Branch Division of Reat. tor Safety 9901230171 990114 <DR ADOCK 03000213 G- PDR l _ _ - _ . - - _ - - - _ _ _ - - _ _ _ - - _ - _ _ - _ - _ - _ - _ _ _ _ _ _ - - _ _ - _ - - _ - _ _ _ _ _ _ _ _ - .
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EXECUTIVE SUMMARY
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Haddam Neck Station NRC Inspection Report No. 50 213/97-10 This inspection was an inspection of the radiological controls program at the Connecticut Yankee Atomic Power Station, Haddam, Connecticut. Areas reviewed included the applied radiological controls program and actions on commitments to the NRC relative to NRC Confirmatory Action Letter (CAL) No. 1-97-082, dated March 4,1997. The inspectors performed independent evebation and observations of work planning and performance during removal of a section of reactor coolant letdown piping on November 22 and 23, 1997, and independently observed and participated, with State of Connecticut representatives, in offsite surveys conducted to locate potentially contaminated material removed from the Connecticut Yankee Station. The inspection of the cutout of the six foot section of the letdown line indicated very good overall radiological controls were provided. Management and supervisor oversight of this activity was good. Phase I of the Radiation Protection Improvement Plan was completed. NRC independent reviews indicated good efforts were underway to locate and evaluate potential offsite contamination concerns. Based on review of radiological survey data obtained by the end of the inspection period, independent sampling and analysis of environmental samples, and performance of independent radiological surveys, no apparent significant residual radioactive contamination, that would pose an immediate health and safety concern to the public, was identified. Good efforts were underway to review, evaluate, and implement, enhanced sampling and monitoring of systems as outlined in NRC Bulletin 80-10. NRC reviews and independent analyses of the occupation exposure of those individuals involved with the November 2,1996, fuel transfer canal airborne radioactivity event indicated no occupational exposure in excess of NRC limits occurred, ii - _ - - _ - _ - - _ - _ - -. .
. . .. _ __ - _ . _ . 7. . :, , ; TABLE OF CONTENTS : PAGE EX EC UTIV E S U M MARY ~ . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . Il PLANT SUPPORT . . . .- . . . . . . ........................................1 . , R1 Radiological Protection and Chemistry (RP&C) Controls . . . . . . . . . . . . . . . . . . 1- ' R 1.1 Applied Radiological Controls ...............................1 R1.2 - Contamination Control Practices . . . . . . . .....................4 R1.3 Radiation Surveys of Offsite Private Residences and Property . . . . . . . . . 7 ' R7 Quality Assurance in RP&C Activities . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 15 R8 Miscellaneous Matters . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 16 . : R8.1 Confirmatory Action Letter Review . . . . . . . . . . . . . . . . . . . . . . . . . 10 7 R8.2 (Closed) URI 96-12-01,02: Exposure Assessment, Dose Calculations ... 19 R8.3 -(Update) URI 97-01 11: Contamination Controls Calculations . . . . . . . . 23 R8.4 Licensee Actions to Review NRC Bulletin 9 0- 10 . . . . . . . . . . . . . . . . . 24 R8.5 UFSAR .............................................. 25 VI. M anagement Meeting . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 5 X1 Me eting Summ ary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 5 'X2 Exit Meetings ..............................................26 *
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Rep 3rt Detalla PLANT SUPPORT R1 Radiological Protection and Chemistry (RP&C) Controls R1.1 6patied Radioloalcal Controls a. 101oection Secoe (92904) The inspector toured the radiological controlled areas and reviewed applied radiological controls including external and internal exposure controls; contamination controls; posting, barricadirg, and access control, as appropriate, to radiation and high radiation areas; radiological surveys; radiation work permits; and personnel monitoring practices. The inspectors review r! ridiological work activities indicated that limited radiological work activituc were ongoing. The licensee did, however, perform cutting and removal of a six foot section of internally centaminated letdown piping in the lower level of the reactor containment. The non-routine work activity was authorized for performance in accordance with commitments made by the licensee to the NRC as documented in its March 7,1997, response to NRC Confirmatory Action Letter (CAL) No. 1-07 007, dated March 4,1997. The inspectors selectively reviewed applicable radiological controls documentation for the task including radiation work permits, radiological surveys, training records, and occupational radiation exposvee results. The inspectors reviewed the planning and preparation for the task, and reviewed the actual work, b. QJaervations and Findinas As part of its efforts to reduce sggregate radiation exposure during station decommissioning, the licensee was evaluating various techniques and methods for decontamination of reactor coolant system piping systems. To assist in this evaluation, the licensee removed a lepresentative section of reactor coolant system piping (six foot section of letdown piping referred to as an artif act) and cut the pipe into sections (specimens) for shipment to vendors for the purpose of testing decontamination methods and techniques. A replacement section of pipe was installed at the location of the removed pipe ocction. The inspectors' review of this work activity indicated that the licensee constructed a mock up of the pipr4 section to be cut out and provided specific training of oersonnel on the tr.sk. The inspectors selectively reviewed the mock-up and observed ongoing training of personnel. The mock-up was r?onsidered realistic and included pressurized water to simulate expected water pressure within the pipe. The mock up training activities were considered overall very good. The inspector noted that essentially all aspects of the pipe cutout and tMt;oning were mocked-up for training purposes. 1 i . _ _ - - - _ _ - _ - _ _ _ _ _ _ . _ _ - _ _ _
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2 Overall, very gooa radiological controls were provided for the activity. There was a good level of management and supervisor involvement and oversight of this activity. Tht, licensee's management and staff were particularly sensitive to potential transuranic contamination within the pipe section and the prevention of airborne radioactivity during the work activity. The work area was under visual observation in the control room via an installed camera. Properly qualified radiological controls personnel were assigned job coverage for the activity, special procedures wvre developed anu approved for the activity, and personnel were provided extensive mock up training and briefings. The licensee performed appropriate radiological surveys of the activity and used respiratory protection and engineering controls to minimize the potential for personnel'ntake of radioact ve material. Personnel provided with respiratorv protective equipment were trained ud qualified in accordance with the Ic.,nsee's tr spiratory protection mogram. Radiation protectio 1 personnel performed effective realtime monitoring of ' radiological conditions during the cutout activities. No hot particles were identified and overall contamination controls were effective. Water drained from the pipe, via drain lines, was conta'ned and monitored via handhold and installed portable area radiation monitoring equipment. Nu unexpected radiological conditions were encountered. Real time air monitoring was provided within the area and leakage of water was controlled during cutting activities. Workers were provided lapel air samplers for collection of breathing zone air samples. Dosimetry was repositioned to th- workers' heads, as appropriate, to measure points of highest whole body exposure. Extremity dosimetry was provided. Cutting techniques used were selected based on limiting unnecessary radiatica exposure and airborne radioactivity. The work activity received a detailed ALARA review for planning purposes, an ALARA exposu.o controls checklist was developed, and accrued occupational radiation exposure compared f avorably to prejob estimates. During removal of the pipe section, freeze seals were used to preclude leakage of water from the pipe. The inspectors observed good industrial safety practices during the activity including constant monitoring of oxygen levels while the liquid nitrogen was in use for freeze seal application. A pre job aggregate dose estimate of 2.10 rem was calculated for the task as compared to an actud :.ccruod dose of 2.19 rom. A post Job ALARA review was completed which indicated the licensee attributed the additional exposure, in-part, to difficulty m:h draining the letdown piping and longer duration mechanical work on the pipe to install the replacement spool piece. The licensee held various post- job ALARA review meeting, . The documented post-Job ALARA review meeting had generally good attendance with fifteen individuals attending the meeting.
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3 The inspectors' review of post work activity radiological survey data and personnel monitoring infwmation indicated no significant airborne radioactivity was generated, no significant external radiation exposure of personnel was sustained, and based on whole body counting, no intakes of airborne radioactivity occurred. Radiological surveys did not indicate significant transuranic contamination. Two minor personnel contaminations occurred and were attributable to residual contamination within protective clothing. No personnel done assessment was considered necessary by the licensee for this contamination. The inspector made the following observations which were discussed with cognizant radiation protection po'sonnel. Action was taken to resolve the inspectors' questions at the time of their identification, as appropriate. - The licensee had planned to use service air to slightly pressurize, from 'Se containment charging floor elevation, the letdown piping and force water out of the hs .t exchanget> Nr purposes of draining the letdown line. The inspector., questioned tne potential for generation of airborne radioactivity. The licensee subsequently pumped the water from the line using pumps at the lower level containment elevation. - One worker, while preparing to enter the work area was observed to be wearing his extremity monitors (finger rings) outside his protective gloves. The dosimetry was susceptible to contamination. The worker was directed by lead radiation protection technicians to place the finger rings under gloves. - The radiation protection personnel at the work location were not knowledgeable as to the alarm setpoint for the local realtime air monitor. The personnel subsequently determined the monitor to have a conservative alarm setpoint. - Personnel did not havt a preconceived plan as to how to exit the pipe cutting area and remove respiratory protective equipment and potentially contaminated protective clothing to preclude inadvertent personnel contamination when leaving the work location. The inspector noted some confusion and the potential for limited personnel contamination. A radiation protection supervisor, observing the activity, subsequently airected area exit activities to minimize potential contamination concerns. This observation was noted not to have been included in the post-job ALARA review. - Locked High Radiation Area doors, consisting of locked chainlink fence type g. 'or access points to the lower level inner loop areas (i.e., areas inside the biological shield), appeared to be potentially scalable. The licensee's Radiation Protection Manager immediately reviewed this matter and initiated action to close off the upper portion of the locked High Radiation Areas doors to preclude potential unauthorized, undetected personnel entry thereto. The upper portion of the doors were subsequently closed off to preclude potential unauthorized entry to locked high radiation areas.
- . - . _ _ . . -- - .. . - .- * i . 4 ) c. Conclusion r The licensee successfully removed a six foot section of contaminated letdown i piping for di. :ontamination testing purposes. This radiological work activity was generally well controlled indicating sign!ficant improvement in licensee capabilities , to support and manage work activities with incraased radiological risk. , !
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extremity dosimetry and radi6 tion protection technician understanding of radiation ' monitoring equipment alarm setpomts. Modifications of High Radiation Area access doors were made to reduce the potential of unauthorized and undetected entry to such areas. Overall, licensee performance during this high risk activity was considered generally very good. , R1.2 Contamination Control Practices a. Inspection Scone (8372PaF2Q4) The inspector selectively reviewed contamination control practices. In particular, the inspector reviewed the licensee's surveys and monitoring of dumpsters contained within the protected area, b. Observations and Findinan i b.1 Survevs of Dumnsters The licensee previously maintained two dumpsters within the protected area, but outside the radiological controlled area. One dumpster was used to collect wood scraps while the other was for metal scraps. The inspectc.: reviewed licensee surveys and monitoring of the dumpsters to identify the potential for unmonitored contaminated material to be removed from the station. The licensee had performed periodic monitoring of the dumpsters at a varied frequency. The frequency differed for outage versus non outt,ge periods. At some j time both dur"psters were removed from the protected area. The dumpster for metal scrape was subsequently returned to the protected area. Currently the material contained in the metal dumpster is surveyed, as appropriate with portable instrurnents, to detect the presence of contaminated material placed therein. Any detectable activity prompts additional evaluation of dumpster contents. The inspector was not able to clear!y identify a fixed survey frequency for the dumpsters, it appeared that the dumpsters previously received weekly surveys. According to radiation protection personnel, weekly surveys were discontinued when surveys upon dumpster removal were initiated. Similar surveys arc made for non radioactive trash removed from the non radiological portions of the station. This trash was placed in trailers for final disposal. : _ - - _ . - _ _ -
_ - _ _ - - _- - - _ _ _ - __ ____ -- - . . O 5 The inspectors noted that the licensee had experienced instances of identification of contaminated material released from the station due to weaknesses in the contaminated material control program. The inspector noted that the licensee previously implemented a " conditional release" program which allowed certain materials with non removable fixed contamination, that were labeled and markec , to be used outside of the radiological controlled eroa but within the protected area. The inspectors' review of contaminated material release events at the station identified previous examples of weaknesses in control of radioactive material. For example, in 1981, the licensee released contaminated metal (i.e., heat exchangers from the station). This was the subject of an NRC Enforcement Action (See NRC Inspection Report inspection 50 213/81-05, dated August 3,1981). In October 1991, the licensee inadvertently release f non-contaminated transducers to an offsite calibration f acility for calibration without def acing the radioactive material stickers, in November 1994, the licensee was informed by a local contractor that pressure gauges, labeled as radioactive material were found in a dumpster from the f acility. One gauge indicated low level contamination. The event and NRC follow- up action were described in NRC Inspection Report 50 213/94 27, dated February 15,1995, in March 1998, the licensee discovered sources, used in bomb detection equipment, in a dumpster behind the maintenance building. The sources were exempt quantity sources with no measurable radiation levels. The incident inoicated weaknesses in control of radioactive material. The inspector noted that the licensee subsequently enhanced exempt source control. The inspectore discussed the surveys and t'onitoring of dumpsters from the station with longtime employees and did not identify any apparent instances where material, with significant levels of radiation had been released via the dumpsters to areas outside the protected area. The inspectors noted that the licensee also released contaminated video equipment from the station in February 1997. This matter was discussed in NRC inspection Report 50 213/97 01 and, in light of other programmatic weaknesses in the radiation protection program, was the subject, in part, of NRC Confirmatory Action Letter (CAL) No. 197 007, dated March 4,1997. As part of the radiation protection program commitments outlined to the NRC in the licensee's response to the CAL, the licensee significantly improved the radioactive material and contamination control programs, including elimination of the conditional release program. The inspectors noted that the likelihood of contaminated material being placed in dumpsters was significantly reduced, surveys were performed of the dumpsters prior to their removal from the protected area, and long term programmatic improvements in the routine survey and monitoring program are scheduled to be completed as part of the Phase 2 program enhancement initiative outlined in the licensee's Radiation Protection Program Improvement Plan,
i l The inspectors noted that the licensee continued to control release of all potentially ,
conte.minated material from the protected area in accordance with information contained in the licensee's November 13,1997, letter to the NRC. The inspectors made the following observation.
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- . . 6 - The likelihood of release of potentially contaminated material from the station via the dumpsters was considered significantly reduced due to enhancements in the contamination control program. Although materialleaving the protected area is to be evaluated and monitored,in accordance with licensee commitments outlined in its November 13,1997, letter, no formally defined survey program for the dumpsters was yet established, b.2 Protective Clothina Surveys As discussed above, two workers involved with cut out of the let down piping, received slight contamination, apparently attributable to slight residual contamination on previously laundered protective clothing. The inspectors subsequently reviewed this matter and determined that the licensee established maximum contamination limits with its laundry contractor for laJndered protective clothing. The licensee indicated that the monitoring capabilities of the laundry was reviewed by the licensee during an assessment in May 1997 and no anomalies were identified, in addition, the licensee provided for resurvey of a portion of the laundered protective clothing upon its return from the laundry vendor as a quality control check. The monitoring of a portion of the laundered articles was performed with a thin window GM type detector with a monitoring capability comparable to that provided by the vendor. The inspectors made the following observation. - Although monitoring was performed on returned laundry as a quality risurance check, there was no well defined program as to sample size to be monitored. Also, it was no clearly defined as to what actions were to be taken when contamination, above prescribed levels, was identified on laundered protective clothing. The licensee initiated a review of this matter. b.3 Monitorina of Personnel Exitina Process Buildinas The inspectors previously noted (Reference NRC Inspection Report No. 50 213/97- 08) that personnel exited proceus buildings without frisking. The buildings were not contaminated and floor surfaces were periodical!y monitored for detectable contamination. However, the inspectors noted that although survoys were performed it did not appear to be a good practice to exit process buildings without performing routine personnel monitoring upon exit. The inspectors noted that the licen *e had taken action to enhance the routine survey program to provide for improved monitoring of building exit points and building exits by direct monitoring.
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Notwithstanding the above, the inspectors noted that decommissioning activities could significantly challenge the contamination control program and that offective
I monitoring of personnel egressing process building during decommissioning <as en
important element of an effective contamination program to prevent inadvertent tracking of contamination into the environment (i.e., outdoor yard areas).
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During this inspection, the inspectors noted that the licensee was evaluating the , need to place personnel contamination monitors at building exits. c. Conclusion
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The licensee will evaluate and monitor, as appropriate, allitems removed from the protected area in accordance with its November 13,1997, letter to the NRC. The exempt source control program was improved. The survey and monitoring program for dumpsters was not well defined. The licensee plans to improve the routine , survey program during Phase il of its Radiation Protection improvement Plan. No r apparent instances of release M material with significant elevated radiation levels on contact was identified. The quality control survey and monitoring program, for > laundered protective clothing, was not vall defined. The licensee enhanced monitoring of building exit points and enhanced overall contamination and ' : radioactive material controls. RI.3 fladiation Surveys of Offsite Private Residences and Prooerty a. Insoection Scooe (84750,92904) The inspectors accon panied licensee staff to obsarve radiation and soil contamination surveys at offsite private residences, and properties. The surveys were completed during the period from September November 1997 at locations that received soils and fill from the Haddam Neck plant in the past. A representative from the State of Connecticut Department of Environmental Protection (DEP) was also in attendance to observe the licensee's survey and to conduct independent measurements. The NRC and the State of Connecticut obtained split soll samples for independent analysis. The NRC analysis results, completed and reviewed as of the date of this report, are provided, b. Observations and Findinas b.1 Backaround Various property owners previously advised the licensee that they had received soll from the plant, and general fill material (asphalt, concrete, soil) during plant constructen projects in the 1980s and 1990s. The fill was excavated from the site when CYAPCo constructed new buildings onsite (such as the emergency operations f acility and the radwaste reduction facility) and renovated a parking lot on the north side of the plant site. Although most excavated materials were taken to a plant landfill area on the south side of the site, a considerable amount of material was also released to the private sector. The fill materials came from both inside and outside the radiological controls area at the plant. NRC reviews were in progress to determine whether radiological surveys were conducted prior to release of the materials in each case.- Additional NRC reviews of this matter was ieported in inspections 97 05,97 07 and 97-08. . - . --. , ,. .- . - - - . - _ .
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8 b.2 Site Investination The offsite surveys began with the identification of locations where plant related fill may have been deposited. These areas were identified based on direct contact with property ownere by plant personnel, and based on public calls in response to CYAPCo and the CT Department of Environmental Protection following, various publicity and media reports. Areas to be investigated were assigned to a matrix to positively identify the area for follow up and to develop information on the time and circumstances under which the materials were received. The inspectors accompanied the licensee on a walk down of the subject properties to identify the areas potentially affected by plant related materials. The results of the site walk down were used to develop a specific survey and soil sampling plan of the "affected areas" at each location. The licensee also conducted surveys and soil sampling of areas onsite that were open for unrestricted public access, such as the north parking lot, the picnic areas, the boat launch access area, and the nature trails on the north and east side of the plant. The NRC provided independent oversight of the surveys at each location, with 100% coverage of the offsite areas, and coverage on a sampling basis for onsite areas accessible to the public. Unique Location numbers were assigned to each area to be investigated. Areas offsite were assigned a code in the *96xx" series, and onsite areas, accerible to the general public, were assigned a code in the *95xx" series. The NRC rrsuits, reported hereiri, use the licensee numbering and identification codes. The NRC analysis results, completed and reviewed as of the date of this report, are provided in Table 1. b.3 Survey Plan The licensee surveyed the properties using a combination of several techniques, depending on site specific circumstances. Very sensitive gamma survey instruments were used to provide radiation scans and dose rate measurements over the affected area of the property. The instruments were calibrated, and were source checked on the day of the survey. The radiation measurements were also taken over areas known to contain only indigenous material to establish background radiation levels nn the property. The inspectors verified that the instruments were within their calibration interval. The licensee obtained soil samples using a similar approach: a background soil sample was taken from an area known not to contain plant related fill; additional samples were taken from areas known to contain plant related fill. A water sample was collected from the site (house tap water) if a well was either in or potentially impacted by the affected area. Offsite soil and water samples were split with the NRC and the State of Connecticut. The NRC samples were analyzed at the NRC Radiation Laboratory in King of Prussia, Pennsylvania.
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b.4 Survey Method The survey instrumentation used was capable of detacting environmentallevels of radiation. The gamma scans were conducted with Eberline E600 survey instruments with SPA 3 sodium iodide (NAll probes. The saans were supplemented with fimJ point exposure rate measurements ushg E600 instruments with HP 300 Geiger Mueller probes. In situ scans using a gam ma spectroscopy instrument ware completed, as needed, to further ir"estigate areas showing potentialindications of elevated radiation levels above background levels. The gamma spectroscopy instruments readily differentiated between naturally occurring (background) radioisotopes (such as K-40, U 238, Bi 214), and those resulting from power plant operations, notably Cs 137 and Co 60. The radiation surveys were conducted by CYAPCo and contractor radiological controls technicians af ter the affected areas were measured and divided into grids to assure uniform coverage. The technicians scanned each area using a sweeping scan that overlapped as they traversed the ground in a slow walk. Tha technicians scanned the areas of interest in this manner. Special attention and investigation was directed to any areae indicating elevated count rates; areas that sppeared to have obvious plant related fill materials; and areas that were in an region of natural watei runoff from the areas of interest. The inspectors observed the technicians and monitored the scans while in progress to asture the surveys were conducted consistently using good scanning techniques. The surveys were completed in a careful and deliberate manner. The inspectors observed the survey instruments as the technicians scanned the site and took the readings. The inspectors independently confirmed the survey instrument readings and recorded the survey results. The results from independent instruments correlated well with the other, b.5 Soll Samoles Soil samples were taken with either an NRC or CT DEP representative present to assure samples were representative of the affected areas, and to maintain chain of custody of each sample for independent analysis. Soil samples were uniformly mixed prior to splits, and water samples were taken af ter drawing water through the reservoir (water tank or cistern) to assure fresh water from the well was taken. The licensee protocols were observed for water sample preservation. The analysis of the soil samples provided a very sensitive measure of radioactivity to levels below the licensee's lower level of detection (LLD) in the Radiological Environmental Monitoring Program (such as 0.15 picoCilgm for CO-60 and CS 137). The licensee also analyzed soil for the presence of Americium 241 (Am 241) as part of its assessment of the pra=ence of transuranic isotopes, b.6 Results The survey results showed no gamma exposure rate readings above typical ambient background levels at any of the sites surveyed. The representatives from the CT DEP reported comparable findings. Based on the direct radiation measurements, there were no anomalous dose rates identified at any site surveyed which had received plant reisted fill from Haddam Neck. Similarly, the soil sample results showed no detectable plant related radioactivity offsite, with the exception of two locations: Location 9608 and 9613. The results are shown in Table 1. The CT DEP reported comparable findings. As seen by a review of Table I, the NRC soil analyses compared favorably with the licensee soil analysis results. The licensee's ! measurements did not detect Am 241 at any location surveyed. _ _ - _ _ _ - _ _ _ _ _ _ _ - --_-___-___--_ __ _ ___ - _ _- -
. - _ - _ _- . . 10 TABLEI OFFSITE CONTAMINATION SURVEY RESULTS ~ ENVIRONMENTAL SAMPLES RESULTS' - HADDAM NECK AND VICINITY LOCATION TYPE SAMPLE NO. NRC CY
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CO-60 CS-137 CO-60 CS-137 9502 SOIL 9502CGOO8 <O.038 <O.059 <0.04 <O.05
, 9502CSOO9 <0.014 0.069 + /-O.006 <0.10 <O.14
, 9506 SOIL 9506CGOO1 <0.050 <0.037 <0.04 <0.05
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9506CSOO2 <0.018 0.038 + /-0.008 <0.06 <0.08
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9506CSOO3 <O.057 <0.063 <O.04 <0.05 9506CSOO4 <0.017 0.083 + /-0.007 <0.13 < 0.12 9512 SOIL 9512CGOO3 <0.034 <0.043 <0.04 <0.04 9512CSOO4 <0.018 0.125 + /-0.009 <0.12 0.170 + /- 0.041 9512COOO5 <0.014 0.070 + /-0.006 <0.07 <O.11 9512CSOO6 <O.029 <O.031 <O.01 <0.01 9512CSOO7 <0.014 0.345 + /-0.011 <O.11 0.290 + /- 0.060
9512COOO8 <0.076 0.11 + /-0.03 <0.05 <0.02 , 9512CSOO9 <O.015 <O.072 <O.05 <0.06 l: 9512COOO10 <0.096 <0.084 <O.02 <0.02 9601 SOIL 9601-1225 <O.019 0.033 + /-0.007 NRC NRC 9601-1240 <O.022 0.057 + /-0.010 Obtained Obtained
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9601-BKGD B67 <O.016 <0.015 a Split of a Split of j ; 9601-BKGD B78 <O.022 0.019 + /-O.009 10% of the 10% of the 9601-14,21-L12 <0.016 0.019 + /-0.007 Samples Samples 9601-14,21-L67 <O.018 0.0-49 + /-0.009 from this from this 9601-14,21-L78 <0.016 0.165 + /-0.008 Location. Location. 9601-17,17-L12 <0.026 0.123 + /-0.014 i
l 9601-17,17-L34 <O.018 0.070 + /-0.008 NRC & CY NRC & CY j
' 9601-17,17-L67 <O.018 0.018 + /-0.008 Results Results 9601-17,17-L78 <O.015 0.036 + /-0.007 Compared Compared 9601-10,17-L12 <0.015 0.023 + /-0.005 Favorably. Favorably. _ -- _. . _. . - . ... . _- ._-
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- 89799 6 096 81 95 4022 00000 0 224 01 00 6545 00000 0 000 0000 0000 00000 0 00O 0000 - - - - 0000 - - - - /- /- -/l - - / l - /- /- /- /I / / / / / I 7 +++++2+29 +++4976 + +++ ++++ 67 68 3 69362 9885 9207 1 73474 0. 6 0 049 543 0000 5734 3048 00 00 O0 S - 00000000 21 2.O 0 0 0 001 0 441 1 00 << << V C 00000<0< 000<<<< 0000 0000 C 0 4 Y 0 T I 0 N I / - C I V 0 2222221 2 4485746 221 2 . 7 +733 61 09 6- 000.00000 0000000 0000 4 01 1 01 1 0 D O 00000OOO O000O0O 000O 20O0 00 OO N A C <<<<<<<< <<<<<<< < <<< 0<<< << << K C 99688565 9486896 1 684 5424 68 44 E O0000000 01 00000 1 000 0000 00 00 N G.0 0 0 0.0 0 0 0000000 0000 0000 00 00 7 M 3 00O0O000 - - 00O0000 - - 0O00 - - - 0000 - - - - 00 O0 - - 1 I ///////- - - /- / ///// ////- /l/ / /- /- // A - ++++++++ +++++++ + +++ ++++ ++ ++ D S 0223 81 6O D C 1 667061 0 4649938 0209 935841 84 7760534 0963 2558 43 01 A 00000000 1 1 1 0000 1 01 0 541 1 00 00 H 0000000 0000 0000 00 00 1 - C 00000000 1 R 'S N 4444 T 0000 L U 0000 S 0 0000 E 6- /- -/ /- /- R O 81 887744 8381 806 2430 ++++ 58 41 S 1 21 1 1 1 1 1 1 21 1 1 21 21 1 1 1 1 1 1 E C 00000000 0000000 0000 6565 00 00 L 7772 P 0000000O 00O0000 0000 0000 00 O0 M <<<<<<<< <<<<<<< < <<< 0000 << << A S L A T . 1 2345678 1 346789 1 234 1 234 1 2 N O OOOO OOOO 55 OO E N OOOOOOOO OOOOOOO 01 OOOOOOOO OOOOOOO OOOO OOOO : : OO M E SSSSSSSS SSSSSSS SSSS SSSS 55 SS N L P CCCCCCCC CCCCCCC CCCC CCCC 1 1 - - CC O 22222222 4444444 7777 8888 99 1 1 R M 00000000 0000000 0000 0000 00 1 1 I V A 66666666 6666666 6666 6666 66 66 N S 99999999 9999999 9999 9999 99 99 E E L L L L l P I I I I IL i Y O O O O O O T S S S S S S N O I 2 4 7 8 9 1 T 0 0 0 0 0 1 A 6 9 6 9 6 9 6 9 6 9 6 9 C O L I
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. o . . 7 8 009 l 0 0 1 1 0 m 0 0 000 / i 0 0 C /- / - 400 / /- / - 5 u 7 + + + ++ 1 4 0 E- 87 61 4722 . 3 4 3 472 1 0 7 00 01 001 1 1 2 2 804 S - 1 1 1 21 O 0 3 7 O0 00OO00 Y C 0 0 000 < < H, < << <<<<<< C 3 6 2 0 0 0 Y 0 0 T I 0 0 O N I / - I- < C + + 7 1 I 0 1 22 0 0 4 69 488290 V 6- 3 2 3 3 000 1 0 2- 00 0001 1 1 D O 0 O00 0 O m O0 00OO00 N C. A C 0 0 <<< < < A << <<<<<< K C 4 1 6 5 67 28 82 E 1 1 1 2 00 1 0 01 N 0 0 202 0 00 00 00 7 M 3 0- 0- 0. 0 0 0 00 - - 00 - - 00 - - 1 / I 0- I- 0 /- // // // A - + + /+/ - + 5 1 7 ++ + 21 + D D S C 9 2 1 3 + 1 + 706 5 2 1 0 46 20- 81 34 67 +23+4 33 00.24 6 A 1 1 1 21 0 0 m0 00 0 0. O O 0 0 H < A< 00<<00 - C O 0 000 0 00 2 R 1 'S N 7- T L E U ) S 0 0 E 6- /- R O 0 667 9 4 1 94 774300 n C +2 42 3 332 0 1 f_im 01 222333 E 21 0 000 0 0 00 000000 L P 000 000 O 0 2 O./ i O0 00OO00 M 00< <<< < < H,2 Cu << ( <<<<<< A * S L A ) T . 1 1 N O 1 O 2 O 1 23 OOO 4 O O O O 8901 25 OO1 1 1 1 E N O O OOO O O OOOOOO M E S S SSS S W W SSSSSS N L P C C CCC C C C 4 1 2 CCCCCC O 3 3 888 1 1 888888 R M 1 1 1 1 1 0 0 0 7 hh 000000 I V A 6 6 666 7 8 9 ii ss 555555 N S 9 9 999 9 9( FF 999999 E R E D E L L L T H P I I I A N Y O O O S I O T S S S W F P N ) O I 3 8 1 8 1 4 T 1 1 0 0 0 A 6 9 6 9 7 9 8 97 E E C 9( T T O I I L S S l l ll llI lI llI If1lllll
. _ _ . . ___ ___ . . I 13 ENVIRONMENTAL SAMPLES RESULTS' - HADDAM NECK AND VICINITY , LOCATION TYPE- SAMPLE NO. NRC CY
,
CO-60 CS-137 C0-60 CS-137
'
SITE RIVER RiverOO1 <0.030 0.024 + /-0.009 <0.09 <O.10 RiverOO2-01 <0.028 0.126 + /-0.012 <0.13 < 0.13 .
4
RiverOO2-02 <0.029 <0.031 <0.08 <0.10 l ' SITE SITE 950801.ABC <O.028 0.016 + /-0.007 <O.06 <O.08 950802.ABC <0.027 0.048 + /-0.015 <0.07 <0.11 Notec, to Table 1. i 1. NRC and licensae sample results are reported in picocuries per gram (pCi/gm), with one standard deviation uncertainty, i unless otherwise noted. 2. Sample results less than or equal to two standard deviations are interpreted as including O or as not detected; further
-
analysis for this location was in progress at the end of the inspection. ' 3. Sample 9801 was subsequently relabeled as 9704.. t .
i
4 d . ,
'
I
{ _ . . , , . . . _ . . . . _ - _ _ __ _ _ _ ., _ . . . , _ , _
_ _ - - . _ _ _ _ _ _ . _ _ _ _ _ _ . . _ . _ _ _ .- _. ' , . 14 , b.7 Dose Assessment The analyses identified apparent plant related radioactivity at two locations offsite (i.e., locations 9608 and 9613). The soil concentrations of Co-60 detected were below the REMP environmental LLDs. The licensee follow up and assessment of the two locations was in progress at the conclusion of this inspection. At 9608, the licensee had completed a full scope characterization survey udng techniques l similar to that described in NUREG/CR 5849 to better define the extent and degree of soli contamination. A similar characterization survey was planned for Location 9613. NRC review of both sites was in progress at the conclusion of the inspection. The licensee used the results from the soll characterization to perform a dose assessment of the plant related material at Location 9608. The assesstnent was completed using the calculational methodologies of RESRAD Version 5.0, an -environmental assessment tool provided by the Argonne National Laboratory. The dose assessment considered the distribution of plant related radioisotopes measured using the soil charact6tization, and accounted for isotopic decay for the period that the fill was present at the location. The assessment also considered occupancy and use factors at the location for the exposed population. The licensee's calculation estimated that the maximum dose would be less that 1.0 mrem per year
l (0.63 mrem) using realistic occupancy and use factors. The inspectors completed
an independent RESRAD calculation for Location 9608 and found comparable results (maximum dose less than 1.0 mrem per year). Licensee actions were in progress at the conclusion of the inspection to develop a site remediation plan, as appropriate, with the property owner for Location 9608.
! NRC review of the licensee activities offsite and the completion of independent NRC i
analysis of the offsite areas remained in progress at the conclusion of the inspection.
l The inspectors noted that the licensee was particularly interested in locating '
concrete blocks which workers may have been authorized to remove from the site.
l
The inspector noted that the licensee developed an action plan to locate, characterize, remediate, and return the concrete blocks to the station. The licensee was assessing and planned to remediate, as ne,:essary, offsite areas affected by plant radioactivity. The circumstances surrounding the release of the
j material, is considered an NRC unresolved item pending further review by the NRC
(URI 9710-01). c. Conclusions
l Some plant related radioactivity was released from the site and was deposited with l till material at two offsite locations. NRC review of licensee actions to assess and ,
remediate the offsite areas remained under NRC review at the end of the inspection
!- period.
. _ . - - -. - - . _ - - - . - - - _ ~ . . _ . - _ . - ~ _ - - - _ _ - * I t * I : 15 } : Licensee activities were effective relative to the identification of offsite areas that i had received plant related fill material, and the conduct of follow up surveys and , assessment at each location. l.icenses surveys of the offsito and public accessible areas onsite were thorough and sufficient to assess the radiological conditions present. , Based on review of radiological survey data obtained by the end of the inspection period, independent sampling and analysis of environmental samples, and performance of independent radiological surveys, no apparent significant residual radioactive contamination, that would pose and immediate health and safety concern to the public was identified. However, an unresolved item was identified associated with the circumstances surrounding the release of contamination to the environment. i R7 Quality Assurance in RP&C Activities , a. insoection Scope 192904) ' The inspectors selectively reviewed the licensee's radiation protection oversight activities, b. Observations and Findinas ' The licensee has significantly enhanced the independent oversight of the radiation protection program. The inspectors noted that numerous surveillances of station activities were performed during which radiation protection activities were reviewed. The licensee was aggressively tracking and monitoring the identified - issues. The inspectors reviewed the August 7,1997, Contamination Control Program Assessment, and noted it to be comprehensive. Findings identified via audits and
,
assessments were included in the licensee's Radiation Protection improvement Plan. The inspectors also reviewed the findings of the October 1997, Radiation Protection , ' Program Audit. The audit identified a number of program areas for enhancement and a number of program deficiencies. The licensee issued Adverse Condition Reports for the findings, took immediate corrective actiona, established a
I plan / schedule for long term corrective actions, and included the corrective actions
as part of the Radiation Protection improvement Plan, c. - Conclusion The licensee improved its oversight of radiation protection activities and programs.
,
Audit and assessment findings were being incorporated into the Radiation Protection
'
improvement Plan.
l l
: ,,A._ .,_;-_, __ . _ . _ . _ . _ . . _ - - - . . .._. . . _ , . . . . .
. .
16 R8 Miscellaneous Matters R8.1 Confirmatorv Action Letter Review a. Scope The NRC issued Confirmatory Action Letter (CAL) No. 1 97-007, dated March 4,1997, to confirm the licensee's actions and commitments to identify and of fectively resolve weaknesses and deficiencies in the implementation of its radiological controls program. The licensee's response to the CAL, dated May 30,1997, provided for implementation of corrective actions in three phases (i.e., Phases I, ll, and 111). Phase I items were those items considered to have some potential risk of affecting public or worker health and safety or compliance with regulations and were scheduled to be completed by July 31,1997. Phase ll Items were items associated with general program enhancement and were identified as items necessary to implement the program to fully meet or exceed industry radiation protection good practices. Phase lll program efforts involved review and evaluation of the program in order to ensure that the program was capable of effectively supporting primary system chemical decontamination. The implementation of the CAL was previously reviewed during NRC Inspection Nos. 50 213/97-06and 97 08. During the previous inspections, the inspector determined that the licensee was implementing its commitments to the NRC. By letter dated September 10,1997, the licensee indicated that it had completed Phase I of its Radiation Protection improvement Plan. The inspectors reviewed all Phase I items to determine their status and adequacy. b. Observations and Findinos b.1 Previous issues During NRC Inspection 50 213/07 08,the inspector identified several concerns associated with the Phase I program. The concerns and the licensee's actions on these matters are discussed below. - The inspectors questioned the adequacy of the verification of the effectiveness of the training of personnel on new procedures and procedures changes. It was not apparent that the means employed to determine the effectiveness of personnel training was adequate and that personnel were fully cognizant of requirements in the new and/or revised procedures. The inspectors observed that the licensee implemented enhanced verification of procedure knowledge through development and administration of written exams and implementation of enhanced procedure guidance in response to this matter.
. . 17 - The inspectors questioned several program aspects that did not appear to have been addressed within the scope of Phase I program improvements as follows: - The inspectors questioned the adequacy of guidance for performing internal dosn assessments in that program procedures allowed for limited evaluation of apparent minor intakes by person.ael of gamma emitting radioactive material detet.ted by whole body counting. The licensen modified procedures to provide for enhanced review of apparent minor intakes of radioactive material to account for and evaluate potential undetected radionuclides (e.g., transuranics). - The inspectors noted that the licensee's dose assessment program provided for evaluation of diver tritium exposure in derived air concentrations hc,urs (DAC-hrs) even though airborne activity would not be the likely cause of a tritium exposure. The licensee revised procedures to provide for calculation of dose equivalent d'se to potential tritium intake. - There was a need to evaluate the adequacy and effectiveness . .adiological contamination control practices within the radiological controlled area. The licensee performed a stand alone audit of contamination controls. The audit was comprehensive. The audit finding were included in the licensee's performance enhancement program. - The inspectors noted a review of the adequacy and effectiveness of radiography practices should be performed. A review was performed which indicated current controls for radiography
! practices were appropriate.
- The inspectors noted that, in response to the CAL, the licensee had developed a list of areas with potential alpha emitters. The inspector. noted that the list did not contain the residual heat removal sump. The licensee initiated a review of this matter, b.2 NRC Review of Phase l Item Comoletion The inspectors reviewed the licensee's implementation of its Phase I radiation protection improvement plan. The inspectors reviewed the Phase 1 items and selectively reviewed non Phase I items to evaluate whether any individual items, with a potential of affecting public or worker health and safety or compliance with regulations, should be classified as Phase I items and completed on an earlier time schedule. As of October 1997,the Radiation Protection improvement Plan included 439 corrective action items of which 192 were Phase I items.
- -_- _ - - . - - - . - - - - - . - . - - _ - - _ _ - . - - . -
, .
. i 18 - The licensee developed and implemented a comprehensive plan to review and address programmatic issues considered Phase I items. The items were tracked, reviewed, and approved by the Radiation Protection Manger as part of the item 4 closure process. The inspectors did not identify any significant matters that should ! be reclassified as Phase iItems. The inspectors noted that the pinn was developed I and monitored by experienced radiation protection professionals including Certified l Health Physicists and was consistent with commitments made by the licensee to ; the NRC in its May 30,1997, letter. i ' The inspectors' review indicated the licensee implemented its Phase l Radiation Protection improvement Plan as outlined in its letter to the NRC. The inspectors noted that in some cases (e.g., work planning and control, and the ALARA program), the licensee took interim corrective actions to enhance the program pending long term program enhancements scheduled for completion as Phase ll ; items. The inspectors reviewed the licensee's independent assessment of the radiation protection program to verify whether all appropriate assessment findings were included as action items within the Radiation Protection improvement Plan. The " licensee addressed the following specific findings, as indicated: - There did not appear to be a well defined transition plan from the recovery i organi.'ation to the decommissioning organization. The licensee defined the organization, identified roles and responsibilities for personnel, and initiated action to develop a procedure for formal turnover of responsibilities for personnel leaving the f acility.
'
- It was not apparent that the determination of resource requirements adequately addressed the functional responsibilities of the radioactive waste group. The licensee did review the resource loading and based on limited work . activities, no additional personnel resources were considered needed. The licensee has since initiated a review of requests for decontamination support
'
perwnnel to support decommissioning activities. - The training coordinator was not identified as a member of the organization,
- - nor were his responsibilities identified.
The licensee provided interim responsibilities, Identified the individual ori an , organization chart, and initiated action to revise procedures to identify training responsibilities. - Training program guidance did not provide well defined guidance for level of training required on new procedures and procedure changes. The licensee initiated revisions of procedures to address this matter, , .. - ,,r, _ , _ , , , , _ . _ . . , . - ,. ,_ ._ r. , , . , . , _. ,,
. .
19 - The routir e survey program frequencies, identified in the survey matrix, may not achieve the expectations of early identification of contarnination control problems and implementation of corrective actions. The licensee implemented a revised sample matrix and was developing a Contamination Control Program document as a Phase ll Item. - Radwaste shipping procedures did not define assumptions for dose conversion f actors or provide sign offs to verify assumptions wore appropriate for ear:h shipment. Procedures were revised to require the Radioactive Materials Supervisor to obtain factors from corporate radiation protection group or the station engineer to ensure calculations are appropriate and the isotope mix used was accurate, c. Conclusion The licensee completed Phase I of its Radiation Protection improvement Program consistent with commitments made to the NRC, Overall quality, monitoring, and review of Phase I program improvement items was considered good. R8.2 (Closedl URI 9612-01.02: Exoosure Assessment. Dose Calculations a. insocction Scope (92904) On No mmber 2,1996, the licensee experienced an airborne radioactivity conter.unation event in the fuel transfer canal and adjoining reactor cavity due to work in the fuel transfer canal. The event resulted in unplanned intakes of radioactive material by personnel working within the fuel transfer canal and the reactor cavity. The event and its causes were detailed in NRC Inspection Report No. 50 213/9612, dated December 19,1990. The event was subsequently discussed in NRC Information Notice No. 97 36, Unplanned Intakes by Workers of Transuranic Airborne Radioactive Materials and External Exposure Due to inadequate Control of Work, dated June 20,1997. As part of the previous inspection, the inspactors reviewed the licensee's dose calculations for the workers who entered the fuel transfer canal on November 2,1996. Subsequently, during NRC Inspection 50 213/97 01, dated May 7,1997, the inspectors performed a comprehensive evaluation of the maximum dose to the workers. The inspectors noted that the licensee was reviewing potential doses to other personnel who supported the work activity, in light of recognition of the potential for intake of transuranics airborne radioactive material. During this inspection, the inspectors reviewed the calculation of the committed dose equivalent to the two involved workers as well as the licensee's dose estimates, attributable to potentialintakes of radioactive material, for other personnel who were in the area during and following the event.
_ _ _ _ - _ _ _ _ _ . _ . _ _ _ . _ _ -_._. . . _ _ _ _ . _ _ . _ _ . _ _ ._ _ ' . . 20 b. .Qhtervations and Findinat I i b.1. Dose Estimates for Two involved Workers l l The licensee performed comprehensive dose assessments for the two workers j (Worker A and Worker B) who were involved in work activities in the fuel transfer l canal on November 2,1996. The licensee used the services of a contractor to i evaluate the dose attributable to radioactive materials and also to review the dose I assessments attributable to radiation sources external to the workers' bodies. The l' dose assessments, as indicated above, were contained in a December 26,1996, , dose estimate. The inspectors summarized the licensee's dose estimates in NRC l Inspection Report No. 50 214/97 01. The inspectors had no significant questions on the dose estimates attributable to radiation sources external to the body. The dose assessment for the two workers, for intake of radioactive material, was j provided to the NRC in a letter dated February 28,1997, and previously reviewed ; by the inspectors at the site. The inspectors reviewed the licensee's dose assessment and assumptions used, and
. performed independent calculations using various assumptions to verify the
adequacy of the assessment. Further, the NRC used the internal dose assessment . ' services of the Oak Ridge institute of Science and Education (ORISE) to review the licensee dose assessment as well as perform independent dose assessments. As - part of this effort, the licensee's dose assessment was validated, using its selected model and assumptions. The inspectors noted that there were a variety of possible dose assessments for - these iniakes based on pr'ameters that could affect the calculation. These , parameters included particle size of radioactive material, solubility or transportability class of the material, selection of a respiratory tract model (i.e., ICRP 30 or the , newer ICRP 66 model), applicable dosimetry system (i.e., ICRP 30 or the newer ICRP 60 model) and other parameters such as fraction of materialinhaled or ingested. In addition, because the potentialintake of transuranics was not , recognized until about five days af ter the event, initiation of indirect bloassay sampling and analysis (e.g., fecal analysis) was delayed, and resulted in loss of
l Information relative to modeling and subsequent dose assessment, i
" The licensee contractor dose assessment indicated that, based on modeling, a large fraction of the intake was via an ingestion pathway which resulted in relatively low committed doses that were well within applicable NRC regulatory limits. The ; licensee contractor assessment assumed a one micron particle size for purposes of - analysis since 10 CFR Part 20 annuallimits of Intake for particulates were based on i one micron particle size. The licensee contractor assessment results, using a combined inhalation / ingestion model, appeared to show a reasonable comparison to actual bloassay data and no exposure in excess of NRC limits. . - ., . - .. - __, -- - - . . - _ . - . - - . - _ . - . - - .- - ,
__ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ -__ . - - _ _ _ _ . _ _ _ _ __ __ _ _ _ - - _ _ _ _ _ . - _ . . 21 Notwithstanding the above licensee calculation, the inspectors noted that other assumptions also provided reasonable comparisons of actual bloassay results to calculated radionuclide intakes /bloassay results. In particular, the inspectors noted that the particle size of the material as well as the route of Intake could significantly ; affect the dose estimates. Further,10 CFR Part 20, Appendix B, specifies different annual limits of intakes (Alls) of radioactive material for these different routes of intake, i i
<
As part of the evaluation, the inspectors and the NRC ORISE contractor evaluated the potential intakes via modeling using the computer code CINDY (Version 1.4), which uses ICRP 30 dose methodology and the ICRP 30 lung model, and using the computer code LUDEP (Version 2.4), which uses ICRP 60 dose methodolgy and the ICRP 66 lung model. The ICRP 60/66 methodology was used, in part to validate the ICRP 30 calculations, and also to evaluate the intakes relative to the newer ICRP * lung model. In particular, based on the understanding of work performed, and the : bioassay results, it appeared that the intake may have oc. curred due to an inhalation of larger particles that were rapidly cleared from the lung, as compared to an ingestion of a large portion of the material. As part of the evaluation, the inspectors and NRC ORISE contractor performed assessments and intercomparisons of calculm wi versus actual bloassay data, as the particle size of the material was varied. 7he analysis results indicated an improved fit to actual bloassay data when assuming an inhalation of larger particles in the 15 to 20 micron range. Based on the analysis, the following doses were calculated using the ICRP 60/66 models which provided an improved lung model for calculation of CDE in conjunction with ICRP 30 organ dose weighting factors provided in 10 CFR 20.1003 for use in calculation of CEDE. The licensee's results are provided for comparison purposes. Teble 2 Licensee Worker Dose Ast,essments (Comparison of NRC/ Licensee Results) Worker Licensee NRC Licencee NRC CEDE (rem) CEDE (rem) CDE (remj CDE (rem) Worker A 0.25 0.77 3.00 13.2 Worker B 0.44 0.34 5.40 5.85 Note it Definitions -
I CDE = Committed Dose Equivalent (CDE is the dose equivalent that an organ or tissue will
receive, from an intake of radioactive material by an individual, during the 50 year period following the intake.) . -- ,,r- - ~ ,we , , , - . . - - , . - . , - , - - - . - . , , - - - - < - - - , , - - - - , , , - , . . - - - , , , , - - - , - ,~ , e-
_ .. . . . . .
- I
l
. l
22 CEDE = Committed Effective Dose Equivalent (CEDE is product of the CDE for an organ or tissue and a weighting factor applicable to each of the organs or tissues that are irradiated.) DDF.= Deep Dose Equivalent (DDE is the dose equivalent at a tissue depth of I centimeter i (1000 milligrams per square centimeter) and applies to external whole body exposure.) TEDE = Total Effective Dose Equivalent (TEDE is the sum of the DDE and the CEDE.) TODE= Total Organ Dose Equivalent (TODE is the sum of CDE and DDE) Note 2: Worker A (above) is the same worker identified in NRC Inspection Report No. 50 213/97 01 as Worker A and as Individual A in NRC Inspection Report No. 50 213/96- 12. The licensee's contractor and the NRC contractor refer to this individual as Worker 2 in their dose assessments. Worker B (above) is the same worker identified in NRC Inspection Report No. 50 213/97 01 as Worker 8 and as Individual B in NRC Inspection Report 50-213/9612. The licensee's contractor and NRC contractor refer to this latter - individual as Worker 1 in their dose assessments.) Regarding the above dose estimates, the inspector noted that use of ICRP 60 organ weighting factors v/ould result in lower calculated committed doses; however,10 CFR 20.1003 requires the use of ICRP 30 weighting factors, codified therein, when calculating CEDE. In addition, use of ICRP 30 dose assessment methodology, using the indicated larger particle size, would result in a higher estimate of both CEDG and CDE for both workers, however, the ICRP 66 lung modelis believed to provide an improved assessment of potential doses due 'o inhalation of larger particles. , The inspectors noted that the dose assessments made with any of the various models did not indicate an occupational exposure in excess of NRC annuallimits (i.e., the 5 rem TEDE limit or the 50 rem TODE limit specified in 10 CFR 20.1201). Based on the NRC contractor assessment, the assumption of inhalation of larger particles, and modeling of that assumption, using an improved lung model, appears to provide an improved fit to actual bloassay data and consequently resultant dose estimates. As a result, based on the above analysis and previous NRC analysis discussed in NRC Inspection Report No. 50-213/97 01,the maximum annual TEDE dose to Worker A may be best estimated as 1.16 rem for 1996 (i.e., the summation of 0.77 rem CEDE as a result of the event plus the total 1996 ODE of 0.306 rem). This estimated dose is approximately 23% of the NRC annuallimit. Similarly, the maximum dose (i.e, Total Organ Dose Equivalent (TODE)) to an organ (bone) of * Worker A may be best estimated as 13.6 rem for 1996 (l.e.,13.2 rem CDE as a result of the event plus the total 1996 DDE of 0.396 DDE). This latter exposure is approximately 27% of the NRC annual limit. As depicted in Table 2, the estimate of Worker B's exposure was not appreciably different than originally determined by the licensee. _ _ . _ . _ - . _ .
- _____.___ _ .____ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ . - _ _ _ . . _ _ _ _ _ .. ' e O 23 b.2 Dose Estimates for Other Personnel As discussed above, the inspectors reviewed the licensee's revised dose estimates for personnel, other than the above discussed two workars, involved in work and support activities in an't atound the fuel transfer canal and reactor cavity during and following the November 2,1996, altborne radioactivity event. The inspectors noted that whole body counts for these workers indicated minimal or less than minimal , detectable quantities of radioactive material within the body. The re evaluation was performed by the licensee in light of identification of airborne transuranic radionuclides. The inspectors reviewed the dose evaluations, as appropriate, for seven individuals who were known to have been in the area or may have been in the area. The dose evaluations reviewed were committed dose equivalents (CDE) to bone surfaces (as compared to the 50 rem annuallimit) and committed effective dose equivalents (CEDE) (as compared to the 5 rem annual total effective dose equivalent (TEDE), which consists of the deep dose equivalent (DDE) plus the CEDE). The inspectors noted that the licensee's calculations relied principally on direct evaluation of intakes by scaling actual whole body counts or whole body count minimum detectable activities to laboratory analysis results of airborne radioactivity samples and debris samples. The intakes were determined by use of NUREGICR 4884, Interpretation of Bioassay Measurements. The inspectors' review indicated that in general, the dose assessments appeared conservative in nature and no unplanned exposures in excess of regulatory limits was identified. Maximum committed effective dose equivalent (CEDE) to any one individual as a result of the event was 150 millirem resulting in a 1996 TEDE for this individual of approximately 2.08 ram. The maximum estimated committed dose equivalent (CDE) was 2.89 rem resuitig in a 1996 TODE (for this same individual) of approximately 4.8 rem. The additional doses were included in personnel exposure records, c. Conclusion The licensee performed generally comprehensive dose t,sessments following identification of potentialintakes of transuranics by personnelinvolved in work or support activities during and following the November 2,1996, airborne radioactivity event. No occupational exposures in excess of applicable NRC limits were identified. The unresolved item is closed. R8.3 (Uodate) URI 97-01 11: Contamination Controls Calculations This unresolved item involved release of contaminated material from the Haddam Neck site. Licensee efforts in the area of contamination control are discussed in Section R1.2 of this report.
, , .
r _ _ _ _ _ _
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24 R8.4 Liccasee Actions to Review NRC Bulletin 8010 a. Inspection Scope (92904) During NRC Inspection Nu. 50123/97 08,the inspectors observed that the licensee had identified contamination in normally non-radioactive systems (e.g., turbine sumps and the closed loop cooling water). During the previous inspection, the inspectors noted that the licensee had established a task force to review all plant systems which have the potential to f all under NRC Bulletin 8010, conducted safety evaluntions in accordance with the bulletin, and develop a comprehensive NRC Bulletin 8010 program for decommissioning. During this inspection, the inspectors reviewed the status of the licensee't, actions on NRC Bulleth 0010. b. Observations and Findinas The licensee developed and implemented a three phase program to re evaluate plant systems relative to NRC Bulletin 8010 criteria. The program included review of all systems including current systems in operation and abandoned systems. The licensee performed a comprehensive review of the systems relative to criteria contained in NRC Bulletin 8010 and was establishing a sampling program to monitor those systems, as appropriate, to ensure detection of potential cross- contamination of normally non radioactive systems. The review was completed on November 14,1997. The review of known radioactive systems was for purposes of evaluating system interf aces with typically non-radioactiva systems. The review of non-radioactive systems included review of system interfaces and past known contamination history. The licensee developed a safety evaluation status summary for affected or potentially affected systems and was performing safety evaluations on those systems considered high priority (i.e., those systems known to contain or had contained radioactive material or had a high potential for contamination. The licensee had also esta'lished o a sampling and analysis matrix for use in ivaluating proposed changes to the chemistry sampling program. The licensee revised analysis methods to establish lower limits of detection to meet environmentallower limits of detection. The licensee was also initiating action to review and revise the radiological environmental monitoring program and the offsite dose calculation manual to provide for sampling of alternate release paths (e.g, storm drain system) as appropriate. The potential changes to the offsite dose calculation methods included addition of the external containment sump and RCA yard drain system as a continuous release pathway. The inspectors noted that although several systems were identified that exhibited low level contamination (e.g., closnd loop cooling, heating and condensate steam component cooling water, turbine sumps) no apparent immediate safety concerns were noted. The licensee had posted the turbine building with information signs indicating the need to contact radiation safety personnel when planning work in the turbine building on a potentially contaminated system.
. e
25 The inspectors made the following observation. - The licensee's analysis indicated that no monitoring would be recommended for low priority systems that were abandoned or non operational, these systems would be surveyed by the characterization group in support of decommissioning, and no safety evaluation would be performed since the systems were not operational. The inspectors noted it was not clear whether non-operational or abandoned system were contaminated and if so, what the bases was for not monitoring these systems for potentialleaks to the environment if such leaks were possible. Also, it was not clear as to the bases for not performing a safety evaluation of such systems if they are contaminated, particularly if the UFSAR identifies them as non-contaminated systems. The licensee initiated a review of this matte.r. c. Conclusion The licensee established and implemented a task f rce to re reviuw plant systems, relative to NRC Bulletin 80-10, that could result in unmonitored releases to the environment. This was considered a very good initiative to improve management oversight of station systems that cou!d become cross contaminated and result in an unmonitored release to the environment. However,it was not clear as to the bases for not monitoring contaminated non operational or abandoned systems or the bases for not performing a safety evaluation of such systems,if they area contaminated, particularly if the UFSAR identifies them as non contaminated systems. R8.5 UFSAR A recent discovery of a licensee operating their f acility in a manner contrary to the Updated Final Safety Analysis Report (UFSAR) description highlighted the need from a special focused review that compares plant practices, procedures and/or parameters to the UFSAR description. While performing the inspection discussed in this report, the inspectors reviewed the applicable portions of the UFSAR that related to the areas inspected. The inspectors selectively verified that the UFSAR wording was consistent with the observed practices and procedures and/or parameters. VI. Manaaement Meetina X1 Meeting Summary The NRC Region 1 Deputy Regional Administrator, and other NRC personnel met wit 5 licensee representatives at the Connecticut Yankee Station on October 31,1997, lhe meeting was open to the nublic and members of the public were in attendance. The attachments t's iii;;,eport r,rovide the summary material provide by the licensee at the meeting. Attachment 1 (three pages) provides a summary of licensee onsite environmental
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! 26 - sampling and dose projections. Attachment 2 (eleven pages) provides a summary of health physics department performance measures and results. Attachment 3 (two pages) provides a summary of apparent causes of health physics related adverse condition reports. Attachment 4 (twenty seven pages) provides the licensee's summary of the Confirmatory Action letter status and actions taken. X2 Exit Meetings The inspectors presented the inspection results to members of licensee management at the f conclusion of the onsite portion of the inspection on October 10 and 17, October 31, and November 28,1997. The licensee acknowledged the findings presented. PARTIAL LIST OF PERSONS CONTACTED > Licensen T. Feigenbaum, Executive Vic;, President and Chief Nuclear Officer R. Mellor, Director Site Operations and Decommissioning G. Bouchard, Work Services Director R. Gault, Radiation Protection Supervisor S. Herd, Chemistry Manager G. van Noordonnen, Licensing Manager R. Sexton, Radiation Protection Manager R. Shippee, Site Characterization L. Raybum Silvia, Health Physicist M. Sweeney, Radiation Protection Services Supervisor J. Warnock, Quality Assurance Manager NflG W. Axelson, Deputy Regional Administrator, NRC Region 1 J. White, Chief, Radiation Safety Branch, NRC Region i State of Connecticut K. McCarty, Director, Department of Environmental Protection M. Firsick, Health Physicist INSPECTION PROCEDURES USED IP 71707: Plant Operations - IP 83728: Contamination Control IP 84750: Effluent Monitoring IP 92904: Follow-up - Plant Support
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* 27 ITEMS OPEN, CLOSED, AND DISCUSSED .QDa0 97 10-01 URI Contaminated Material Identified Offsite Discussed 97 01 11 URI Review Release of Contaminated Material Closed 96 12 01 URI Maximum estimated Doses to Worker A 96 12 02 URI Maximum estimated Doses to Worker B (Note: URI 9612 02 was inadvertently opened and ider.tified in NRC Inspection Report No. 50 213/o7 01.This item was not opened in NRC Inspection Report 50 213/9612a~nd is closed for administrative purposes.) LIST OF ACRONYMS ACR Adverse Condition Report CAL Confirmatory Action Letter CCPM corrected counts per minuto CFR Code of Federal Regulations CYAPCo Connecticut Yankee Atomic Power Company FSAR Final Safety Analysis Report GL Generic Letter GM Geiger Mueller HP Health Physics ICRP International Commission on Radiological Protection IFl inspection Follow up item IR Inspection Report LAS large area smear NMSS Nuclear Materials Safety and Safeguards NOV Notice of Violation NRC Nuclear Regulatory Commission NRR Nuclear Reactor Regulation PAB Primary Auxiliary Building PCF personnel contamination form QA Quality Assurance OAS Quality Assurance Surveillance OC Quality Control RCA Radiologically Controlled Area REMP Radiological Environmental Monitoring Program UFSAR Updated Final Safety Analysis Report URI Unresolved item VIO Violation WCM Work Control Manual
. _ . . . - . - . . . . -_. . _ _ _ _ _ ____ _ _ _ . _ . _ _ _ _ _ _ ATTACHMENT 1 SCOPING SURVEY STATUS - - (1 OF 2) I AREA AROUND CENTRAL MOUNTAIN SIDE TRAll No Detectable Activity Auxiliary Exit f Road PARKING LOT ' / STORM DRAIN No Detectable , CORE BORES ~ - - No Detectable j RUNOFF Activity Activity ; Asphalt 10mRlyrl J Avg 11mR!yr e . . - __ ~ _. _s q _ . . - h p ,)J .=, y_1@.. -. ~\% -p :g- . I = gTT~ ' l! .: \ i ~~
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I i i l INDICATES AREAS OF THE SITE THAT HAVE BEEN SURVEYED / SAMPLED FOR RADIOACTIVE MATERIALS - NO DETECTABLE ACTIVITY FOUND } { INDICATES AREAS OF THE SITE THAT HAVE BEEN SURVEYED / SAMPLED FOR RADIOACTIVE MATERIALS - MEASLHABLE ACTIVITY FOUND i COMMENTS: Areas Evaluated by Scanning. Soil Sampling and Exposure Rate Readings i ! Revision #510/28/97 ) --
t . . _ _ . . ._ __ __ _ ,____ . , _ _ _ _ - _ ._. ___l
- . . . . : Revision #510/28As7 SCOPING SURVEY STATUS } \ (2 0F 2) A 1 . . . - ,- ... . - .- ~ ,, _;:. , e ,- . -.- _ y - - - ,, -;1.:. . . ..- : . .: . - . . .- w . * g * / , ,s ' . - ~~+'. ,- . s,s - . .-a .-: . .- : - I . . . .. . - s', . .. . -:- . , , . , ., l n . - 3- l * * ..,,- . : . < w .s,e' V - ., ,, , \ ,,r' -:-z g- ,. -, _; ,g f SOUTHEAST a"e' ' : s , .- N, SITE LANDFILL .- ~ jJ /g 23 mR/yr .' T- ,e = = = s 4. :. . .d' ] - .- ,f ,1 7 ;' _ ' . " RIVER ' ~~), / '__ ' '::* * SEDIMENT i ', \ * / '/ No Detectable .- / . Activity i * N N , - ? * NATURE TRAILS PUBLIC FISHING ho Detectable ' Activity AREA 9 _ -- No Dt.tectablo N j , ~ ' - - - " Activity / . ' y 7 N ' ., , ' ' : - : [,/ . , .- _ _, .-.. , , , . :r. .. - - * , - /. -_ % _ _ *: . -jM - = , . a_:sman - - . * * -,L *4y , CENTRAL AND SOUTH PENINSULA Samples Being Evaluated Spot Check Scan ShowS: No Detectable Activity [ INDICATES AREAS OF THE SITE THAT HAVE BEEN SURVEYED / SAMPLED FOR RADIOACTIVE MATERIALS - I } INDICATES AREAS OF THE SITE THAT HAVE BEE!I SURVEYED / SAMPLED FOR RADIOACTIVE MATERIA
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. . SOIL SAMPLING STATUS . , ..,..... Jc ,,m., . .... . . .... . 7; J:.,- . . :. - . .
I O
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! '!!l"l.7"!72NhljlI".',",!"ll,3 T N ~~ I og i,anonounm.,n.n.nnaa,a,g $ - :- ' -- -o- w 0 o g mano.mn ..m. m m m ,mi gg .' .p __ gg u- zyn- \, , = , . - , ' 1, /} u -- o id" h4 cb C L o ] ,anmnnmimmn ni_nnnunn[]!::::.:::Md PM g. 0 s/M" INDICATES AREAS OF THE SITE THAT SOIL HAS BEEN SURVEYED / SAMPLED FOR RADIOACTIVE MATERIALS .NDICATES AREAS OF THE SITE THAT SOIL HAS BEEN SURVEYED / SAMPLED FOR RADIOACTNE MATERIAL INDICATES AREAS OF THE S!TE THAT SOIL HAS BEEN SURVEYED / SAMPLED FOR RADIOACTIVE MATERI Revision #410/30/97 - - . , .
-___ :... ATTACHMENT 2 . - . . ., . . ,. '." - .: . - ,,- Perfor,m.anceMe.;.,cy asures ' [' = =;..' ?:a,. L:; . , ' ' ' ' .o . ' ' Health Physics DepartmdntG $' ' :"> Ociober 30,1997? '!i f' . , , , , ., . . - 'f. "- > . E Connecticut Yankee Atomic Power Company Haddam Neck Plant
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. . Rcta of Pcrsonnti Contcminction Ev nts (HPPM 97-3) . Events RWP Hours Running 12 Mo. Avg. Nov 96 7 14,599 0 Dec 96 6 8,128 0 Jan 97 0 8,573 0 Teb 97 0 7.609 2,858 Mar 97 * 8,806 2,961 Mar 97 2 10,627 2,963 May 97 0 8.o47 2,977 Jun-97 12 9,204 2,448 Jul97 4 8,741 2,421 Aug 97 1 8,828 2,709 Sen-97 3 7,714 2,844 Oct 97* 2 7,001 2,860 , Total: 38s ' 108,677.24 Bunning 12 Month Avg. (RWP Hours Per Event) Goal: 83000 Current: 2860 Trend of 12 Month Average (Up Shows Improvement) 3g .t , - . ,... _ .i . . a . 2.th#;. a4 ic@vQ; $, - +. . 3g ',' E an htn:n.:WCOLc6;.39fh2: df.dsI; ;.g. c .. , , ,,,. -2 ~,, v . . y w, glg/g 4 g.e pg s. .y j. .- ,a,, 4 ., -. , . . . g p. - c , w- cc u , 2500 g . .g y m y y y . _ _ ' y ;; - s .) Qt Q,, J. j , 3 . 3L g ', ,7: ;% u ,s ..~ o % m - .a ', , g 2000 y g ' .g w gy , "g , g3 3 , j r.q . v _ t - i ..w 'y s; i p 11 y," k ,. M / ,; n t a- : t W% ; ph - ' y ) y D h c,: y : g +'~ jf( t :, t e< w p - l . , 4,. 6 e cc yy ,m . $ m g: ..', . g. z " {iid;6 { :1;p 4 y; jj . %' g+ , r, .q'- Q. s g' . .. q ,w * #' ',, 7 % [6 - rw,e ...g e. 3, . . ; +. . 4 9, , .L J) 1 +J A .. w . $.. i ,.: - , , , +y t. -. .. t g' ' ,,' , . #s .. t. m r , . 3'- 500 ' % ' $ .g 4 '"- fg - y% g; ' 'i j . _ . ' h j, % eM @ % $ MG# $ w $ m y$,, k u x x g . :4 ; .:we q,wg- y - sgn.s a g :en . c. w- ~. , u. a . a , 9 4 - 2 4 m , Month * *=> Mor.th-to-date 10/30/97 8.46 AM PerCon Report _ _ - _ _ _ _ _ _ - _ _ _ _ _ - _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ - _ _ _ _ _ ._. _ _ _ - _ _ _ _ _ _ _ _ _ - - _ _ - _ _ _ _ _ _ - _ _ _ _ _ - -
_ _ _ .. .. . _ . _ _ _ - , , Pcrccntcg3 of Survoys Maating Qu Ilty Standards On First Submittal (HPPM 97 02) . Week Ending Unacceptable . Total Percent Acceptable 13-Sep 21 74 72 % 20-Sep 27 151 82 % 27 Sep 17 177 90 % 4-Oct 19 130 85 % 11-Oct 20 124 84 % 18-Oct 22 118 81 % ~ 25-Oct 7 147 9W. . Note: For data to be valid, total number of surveys should 150/ week. - - Running Weekly Average Goal: >98% Current: 84% Weekly Trend (Up indicates improvement) 100 % ** ~ .,-]h % ,. s 4.J -- : ?' f,, I ' 80% < .. , - s.3 11 ,: * , 70% . W- g ";m .Ja . n). . . , : r;.. 3 3, Lu . - ? -f! p ,v . g . m 60% - ;y4 N(4)) ;rl jyj,;. .: Q jplyp H. .&. ; , :' , :. ', , L . . , as .g, 50% - .;*<< .j., ; q J:s(;,a l .r ene,. s o < 40% - dd *o3 %W. 7 id? t ". 1.4n Q+#f. , . . $ , y" y. . *t s r 'y 'y J 30% - - ?lQ *:: ,^ y. * < s.. . .: ,' J,46 .; JC'; p I.&py} , . . . 20% * ,a .n .p . Qb * i,g>: y_. ,q +9y n; a ', Q o.e j(+yy' . ;j 7 : .e; b 3.y * ' .dp . ' ' ' l' e , ,; ; t . 1Mep 20 Sep 27-Sep 4-Oct 11-Oct 16-Oct 25-Oct Week Ending 10/30/97 9.11 AM Survey Quality
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_ - _ _ _ _ _ _ _ _ .. .. . . . . . . .. . _ . . Performance Measure Davelopment Record
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Functional Area Crrrical Activ ' Lower Level (Department Only) HP Operations Survey Documentation - What is the percentage of total survey records submitted each week that meet established quality expectations? Goalfor Critical Activity . . - > 98% acceptance rate Desenation of stessure This measure will express the number of survey records submitted each week that are acceptable as a percentage of total surveys submitted for that week. Acceptable surveys will meet the criteria of the Survey Documentation Guideline. ' Wow wito themeasure be determined? . ' ~ The measure will be calculated as follows for each week in which 50 or more surveys are performed: total number of survey records each day - number of unacceptable survey records each day x100 total number'of survey records each day This measure will be recorded in an electronic databate and reported !n the form of a trending graph. ' RawDanRenadred . 1. date of each day on which surveys have been submitted 2. number of unacceptable surveys per date 3. total number of surveys per date , Location (s) of Raw Data - Date information is recorded on each survey record. Unacceptable survey records will be uniquely marked by the HP Operations Supervisor following review, This will allow data collection when the records are being filed. _ Upon filing survey records, administrative support personnel will record the required data. Upon filing. Norma"y multiple times per week, but Weekly always once per week, as a minimum HP administrative support personnel. Radiation Protection Supervisor - Operations Date: 1 I HPPM97 .' DOC Revision 0 _ _ _ _ _ _ _ - _ - _ _ _ _ _ _ _ _ _ - _ _ _ _ _
_ _ _ . _ _ _ _ . _ _ _ _ _ _ _ _ _ . _ _ _ _ . _ _ _ _ _ . ._ ., ! ACRs Attributable to Work Practices of RP Personnel ' ACR CausalFactor 1F
, (HPPM 97-4) .
Month - ACR's Jul-9' 10 - Aug-97 6 Sep-97 3 Oct-97* 2
, 4 i Running Monthly Averagg
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j Goal: <1 i Current: 5.25
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Monthly Trond (Down Shows improvement) 12 :wmn.e-n m& r ym ;- x~,.wa>y~ arc c+ thg &.4.u.$,Wi,%*GiW;;lMa.%{np4'Q R , w,,&ymc. .?]: ,%:-~; n -- ,q ;w,.a:Qy mne on wag<m.,,;,c,;u%;;1,Q..u?.a 3 t . o, , e.t%%&.A.ix.w a,yr,, : m, t to ,d e t x,m s... m . .m . _ . . p n,v,,n- u ad.. mv. m . a- wg*.s. eApu. %wxwehm n-e . - n trp,&e:..q<pm. .m n.c.,ri,e.g=.A,w _. #,e.
- 44 / WuuTWWA:;d.q%wesisuMiG~uTWM@idJsed?
8 y 'anw, n. e- 0 "~? TO'3t . % straw +y %s.nep m@Q ynr*I?g m * t ~ $>P@* Td .~1 Mf'nXEs w a N: tTTM if # , * 4 .fd: hEf.%%s,-4 ~'igb'sW > .b4w,ltshX Yd ,Tl'M ?.p uA i% n; k: M .:c,$r5d f +; X ,' M & 5 6- sM .. :- 1x ' ~ um' . ' oer . :., .. go f e. ... 5
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i M y' op!!$p;m?, &ph bt:x '* .s.A.Dt#MWflid1W * s.a murmsp, :.y%4 '0%+p,t ~ i% nkM * 4 ' '3% X &,, %.. k * A $ $ ?& & 4 m +"h WvO. w w aW84 2- %. o. -1sd. .w an%nd n. - s@duw r (l,t.)qnu.s. y; ',','mg. -y m.u- p;faydi.g, , %hm -.. . .f,.f.n;.4p . a y;g -w &[y. . - p - u. IM3 +w, Av kn!!p iin wnuf> k% gp+ . c sp n 0 t - . JuM7 Aug 97 Sep 97 Oci97* Month :
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*=> Month-to-date 1Cf30/97 9:12 AM Work Practices . ACR 1F - - _ - . _
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, , ACR0 Attributabla to RP Proccdura Dcficicnclos
ACR CausalFactor 3A (HPPM 97-5) . Month : ACR's Jul-97 10 . Aug-97 7 Sep-97 1 Oct-97* O Running Monthly Average .s . Goal: <0.5 Current: 4.50 . . Monthly Trend (Down Shows improvement) 12 . .*: . s. .- .,v,.. .,.:.:c.s;w;t ,...- .,ik. .y ,-. e.::.,- , rv 1- , , :.:w .. , , - . . - . < . a ..: :a . .:x;- *g". w. y;,. ,q. . . ,s ~;O . * * ~ y'y" * " .. -,. ,,,c . ,~, e - . " " ' to m,, .s,. .. Aia2 ; ,m s - +, - . ,. n . ,+. , v.~ ,:e ca : .s , .- y . 4 wr u - < . - .. e: s .w 4,..g+WvLc a y,A W h % M . . W,a-v.- #s.i#2 6- ,-: , .a n ~ . 4 , :n. .1.. a.mu e y. . . -. mv,, .wa > . .s. p . .r s y , , 4w: ;.n. + , N- .(s; - - 4 z , .5,,6, emag :>1 g ,-* A. ., - . v': . a 7.*% - . j' s . , ~ ., j'4 /* 4.., ... .k.e' W ** Q f_H.J.,jy -s, . .m %.? ~ a *i;,f e -, .., %2 ;'q~ . . . - . . w <.u < 6 g %, , p39 Q R g,6! n;f7 w, - 4 d ii.a W W p.n l2 W :,z. . 4 team,e ,n- ,s - - . r n.y:, yx ?9Q^A?)a+W~5.;<Q*Vf 4- - ;c . c.g; :: u . q r ;-::,:; y,WQk -* : ', )-O4;* ' j ;- nypl p1 .y ". JQ:y' ' . k v h e * ey e; m9*. Q'? vt...y: ; 2- . .,bi, 4c.;C. . bo,&,.. lbu W:.,.W ... ' W ,r .- .w,, , :v; i .d e5 w n% yJ,p..v.n.. ..w,- - .w q . ,i. s , ., i g. . . i. w;., ,y ,s a. -- og v- e ya . s *' - Qhs . .,l,.r , N,* ^*G -.~.c+ % <1 & .i -d :g ' . . cv s- , c L'Jui-97;Wie ';(y,K. Aua-9T%y.s;.>5lyj% sses :gQfj;p44@mf6.W.;.#iL%; v.i;Ny@Mit;y;? W;a w Oct-97* :La 1M;,F,~ , -2 Month . * *=> Month-to-date . . , 10/30/97 k15 AM Procedure Derciences . ACH 3A - _ _ _ _ . _ _ _ - _ _ - - _ _ - . _ _ _ _ _ _ _ - _ - _ _ _ _ - _ - _ _ - - _ _ . _ _ _ _ _ _ _ _ _.___ - _ _ -__- _ _ ._
. . - . . -- . - -- .. - . - . . - - - . _ _ . - - . - - = -. - , -. f . Pcrccnt of ACRs Self-identified by MP Department (HPPM 97-6)
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. 4 s Month: < internal-- External # Total n %3 elf-ID Jul-97 13 14 27 48% Aug-97 17 6 23 74 % r Sep-97 - 7 4 11 64 % Oct-97* 5 4 9 56 %
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I Running Monthly Average
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.. . Goal: >90% Current: 60%
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Monthly Trend (Up Shows improvement) 100 % H Q iXUffi W ?A*;9** W e.? $OE?ffQi W klll$5 QTT% W T&: 90 % - , w ~# j~d' ~p'.:i: < ~ ' 'm ' 'R ' ':;c#q .u" *%? .J: * 3 3 a'?"y 2*p' *s 1,3 W s f y' 'a.+> ' ~ ~m.s*,g . '.+ : ~ . , ' ' ""
i' B0%
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70% .ilEF8$,466(4 [W * *MTWWMCRff8A$ljd2dErj0Rd ,1krtnkc " wgaa . .".'.' p & -.- .'**...y - t' 60% - . . ,'. '.,'~.,'~N*'M ...s F z : ... . -_' '~ #"9cwg# "s-".,,...,,g'
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* M $$'[M . %,yT/ ${f'2Y),? h .a 3 40% - g 30% - 'AUi $l0%n N30%\ 1if E3T QN 7 eJ , , , , , , , , , . ,_
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0% i . Juk97 Aug-97 Sep 97 Oct-97' Month s * *=> Month-to-date
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, W30/97 9:36 AM sew-ID of Problems _ _ _ . .__ , ., . . _ _ . . _ _ . . _ . .
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. . . . ACR0 Attribuv Ma to In:daquata RP Tr:Ining ACR . cusalFactors 11 and 1J (HPPM 97-7) . , t . Month ACR's. Jul-97 A ' Aug-97 1 , Sep-97 0 Oct-97* 2 Running Monthly Averagg . , . Goal: <0.5 * Current: 1.75
. 4
. Monthly Trend (Down Shows improvement) ,
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b * hy . $ 3 % B : M s tu d s a&:;.! 4 % g~4a J a g u s a tg y , m 5 25' 19 E ., ,, ,.E,mE "N_,' '"'",' *m ..d b ' } 2- " * *'~ * *r-r-+ . _.,,,_C % _, @,_,. _- ~u2'd e **'_J
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c . g ,, _.-, m .,. ~g..Ng . . _ , _ . . . 1.5 - **7 " - T . - '9 M @,"f M $iQ M'$#@@igjjgj@fjf +,. , 0.5 - Yb'Y' b Y b $$ us yp'gyvma ,.., .,.fg. 9:g ,m s ng. _ m ..m , pp,# m s y 11pp* Jul-97 Aug-97 - Sep-97 Oct-97'
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= . * - *=> Month-to-date .
- 1000/97 9.37 AM Trainnig . ACR 11 & 1J
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. . __. . __ _ .. . ._. ._ _ _ . _ _ . _ _ ._ . 1 J \ ' HP Related ACRs :
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,
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Week HP Related Ending ACRs 16-Aug 5 23-Aug 3 30-Aug 3 *
.
6-Sep 3 13 Sep 3
'
20-Sep 3 27 Scp 4
- 4-Oct 3
11-Oct 4 18-Oct 3 25-Oct 1 .r - 1-Nov '1 4 Average Weekly Number of HP Related ACRs
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. Current = 3.25 Goal < 2hvk
i. 4
. Number of HP Related ACRs . 5 ,w a.,n,,w 9u r7e.c < -vv-, n: a;c,: 2z .;,~. ~. , c . , . u.y 2,y. 4.5 p n a, v .v. , ': ast-u m. ';' :;+.,A y + ni:9 -y:rv. m.v+?;t,*. . p gx A _,g g., - e e , .- , .,.r.'< . ;; q u, , , . vA 3 ; o ..- w. D ,, , .. ;;. _y
,
4 3 g ; g[_ ' v ~ )r ' .- g -- g - - g c- g-g g .y .c < -., *, .- p, e;: . s,1 f,;- , ; , s t g- 3 - . IL$ . Y' ^ ..' ?$$ h '4 , 'N , ~-l . V ' ?* SE?: i 1 3 t_ ' t :w 1 :- ' . 70'; ev :.. ;-d im *, p . < , :% ,. % % cvs a - a. x.. .e we. 4 -s_ .q. ~u f ~* .t, ;^ ; _s .u- " ' ' + 16- 23- 30- 6- - 13- 20- 27- 4- 11- 18- 24 1- * Aug Aug Aug Sep Sep- Sep Sep Oct Oct Oct Oct Nov
, Week Ending
,
4 A
8 t 10/306,7 8:33 AM HP ACRs _- . _ . -
.-, _ _ . _. .- .- __ - - * l ' . An Explanation ofPerfonnance Measures . Performance measures, in one form or another, are recognized as an important element of effective management programs. Managers and supervisors directing the efforts of an organization or a group can be sensibly implement changes with appropriate knowledge. The goal of performance measurement is to arrive at sound decisions about actions affecting the product or process and its output. The attached flow chart provides guidance on developing and revising performance measurements at any level within an organization. The development of performance measurements for a specific process should involve as many cognizant employees as possible to stimulate ideas and reinforce the notion that this is a team effort requiring buy-in from all involved in order to succeed. Individuals get an opportunity to receive a broadened perspective of the organization's functions, rather than the more limited perspective of their own immediate scan of control. As a process, performance measur ament ic not simr,1y concerned with collecting data associated with a predefined performa.ma goal or standard. Performance measurement is better thought of as an overs 1 management system involving prevention and detection aimed at achieving conformance of the work product or service to customer's requirements. Additionally, it is concerned with process optimization through increased efficiency and effectiveness of the process or product. These actions occur in a continuous cycle, allowing options for expansion and improvement of the work process or product as better techniques * are discovered and implemented.
,
. 1 3 . , - , .
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Start . V Identify Process V ' Identify Critical Activities V > Establish Goals V Establish Measurements Document measurement y i l and file data Identify Responsibilities AL V c 3 > Collect Data > Database , , V l No i Analyze and i 4 ___ Yes a Report ggw v';bi>)Mti&MM> V Tf)h[[ =7 Compare to Goals Yes JL y ,; . ,1.k ?: & . $%% cNsT s y ggi om~;pr mm*%ggy , 3 JL yYes L Implement l T Corrective Actions l _ _ _ . - _-_ _ __- - ___-__ _-__-________- _________ - _ __O
j \ll l i lj 1!\l * * ' 's Em P M% R N1 C 7 R1 A 9 d 9 e ) y w d 1 1 ( t e c n o e R M e N o t E t gc i F a T O% o nn s - t O1 e e l R e R A L1 NinD - a l i t ai e a r o , o o N i t c c U . a s - Q . . d= . DTw f f nw ,d P r i c D n% 1 1 n . * e a ood e . , e gc kr < .n kkc s N e = cco o ,or o h y O o E=aar LLP PP W P C E , h S t n MOT F l o NOOD N P a c ELLP P W e H f o e s u a C - 3 T N E M H C A T T A % 4 2 E% P0 ) 8 9 ( 7 9 7 9 9 1 R 9 1 R : E T R ) E T R : A U 1 ( A U Q : Q m- T S N D R -* s R I um R I H T ,5% F
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<l1lL
a 1 . . HP ACR'S COMPARED TO SITE ACR'S 450 : -- >422 . 400 ------- - ----------- -- - -- - - --- ---- -- ---- - - - - -- - - ---------~~-------- -- ----- - 350 - - - --- - -------------------- ----- ------ ------- --------------- 300 ---------- - - - - - - - - - - - - - - - - - - - ----------- - ----- ------- i+ SITE ACRs ! ' I i - - - --- -- - - --- -- - -- - - --- - - -- - -- -- ---- --- -- --- -- L_G-. _HP AC;b _. * 250 - - - -- - 22 -------------------------------- -----------------------------------------------------------------------------
I
200
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N - - - - - --- --- ------- -- -- ---- - -- 150 -- -- -- - - - - - - --- -- -- - - - - - ---- -
i i l
- --------- 100 ---------- --- - - ---- --- - ------ ---- - ------------------~~------------------ --------------------------- -- ------------- -- --- --- -- ----- ------- --- --- -- - yta ---- - ---- 50 -- ------- --- ----------------- - -------- ---- _ . - ~ ,,, 0 "' SEPT. JUNE MAR.
. . . .. -... . .. .. . . . -. . . -- . - . - . . .-. - - . - -.. . . . ... . .. ATTACHMENT 4 i Connecticut Yankee Atomic 2 Power Company .) Confirmatory Action Letter
- Meeting
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~ October 31,1997 t - 4 h i . _ .~. . . . _ _I
- . . . . .. Aaenda _ a introduction Ted Feigenbaum - Overview Russ Mellor * Confirmatory Action Letter Gary Bouchard - Administrative Controls Gary Bouchard a Radiation Monitoring System improvements Gary Bouchard - Health Physics Program improvements Dick Sexton ' - Confirmatory Survey Dick Sexton * Corrective Action Feedback John Haseltine/ Gary Bouchard * Oversight Perspective Joe Bourassa * Summary Russ Mellor - - Concluding Remarks Ted Feigenbaum
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2 $
.. Introduction Ted C. Feigenbaum Executive Vice President and Chief Nuclear Officer a Of ,
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. . . .. .. . . .. : C'verview :
Achieved Improvements in Radiation Protection -
Performance Indicators and Feedback Mechanisms Working
Radiological Work Performance Has improved i
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No Major Decommissioning Work Until Programs Ready
Some Radiological Tasks Necessary To Prepare for Decommissioning . - . . _ .
. . . ., Confirmatory Action I etter
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* Background
l - Refueling Canal Personnel Contamination
- Contaminated Video Equipment - Radiation Monitoring System Calibration * Initial Actions - Administrative Controls Put in Place - Independent Assessor Contracted - Extensive Confirmatory Survey initiated - RMS Declared inoperable . - Root Cause investigation initiated s , . 8 I
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Causal Factors
l * Refueling Canal Personnel Contamination l -Pre-Job Brief l
-Scheduling
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-Surveys -RWP -HP Job Coverage - Air Sampling - -Radworker Practices m e D _
. - . . Causal Factors (Cont.) * Contaminated Video Equipment -Lack of Sufficient Control Procedures - Personnel Performance -Release Facility Logistics . G
-___ - ._ _ _ _ _ . - _ _ _ _ - - . - - - _ _ _ _ _ - _ _ _
_ . .-. --- - _ - - - - . . . . ~ Causal Factors (Cont.) . . .
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Radiation Monitoring System Calibration -Management involvement -Decision Making -Engineering Practices -Follow-up on Safety Concerns -PORC Review . i __ _. _ _ - _ _.__.____ _ . _ __ ____ _ _ l -
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Administrative Controls -* . Administrative Controls for Radiological Work -
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* E xisting Controls Successful . * 1 Work Performed H - Service Water Piping NDE and Repairs - New Fuel Shipping - Spent Fuel Inventory , -- Spent Fuel Shuffle ' - RWST Draining
- - RCA Ventilation Testing
- . , - Spent Fuel Pool Filter Replacements . , * Continuing Controls . 6 . - __ _ _ _ _ _ - _ _ - . . , . - . - . _ . - - . - - . . - . . _ , . . - - . - - - _ - . , _ .--
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Administrative Controls (Cont.) ' ' .
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- Radiological Work Activities Prior to Major Decommissioning
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- Site Surveys - Remove Artifact - Repair RWST Tank Bottom
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- Ship Control Rod Drive Shafts - Repair Spent Resin Facility Steam Leak
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- Repair Polar Crane
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- Test Containment Smoke Detection - Repair and Load Test Containment Elevator - Replace Spent Fuel Pool Purification Filter - - Overhaul Spent Fuel Pool Cooling Pump
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, . ,m . -. - .-
. . . Radiation Monitoring System Improvements * The RMS is Operable and Working Well
l -Background , '
- Problem
e
-Causal Factors - Actions Taken -Current Status
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' t l Radiation Protection
Improvement Plan j
. l Schedule
-: * Phase I - Required improvements Completed j
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* Phase ll - Program Enhancements End of 1997
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. * Phase ill - Effectivness Review / Continuous Prior to RCS Improvement Decon. 12 h
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Phase I Accomolishments
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* Standards and Expectations Established . .
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Cultural Changes initiated - 192 Corrective Actions Completed * Planning, RWPs, and Pre-Job Briefings 1 Strengthened , * Contamination / Radioactive Material Contro: i Enhanced - . , ! 13 . ________s_ - - _ _ _ _ . _ _ _ _ _ _ . _ _ _ _ . _ _ _ . _ _ _ . _ .
. Phase I Accomplishments (Cont.)
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* Instrumentation Program improved ~ * Improved Accuracy and Corapleteness of Radiological Surveys * Alpha W;onitoring Enhanced - Staff Training Conducted ; * Enhanced Radiation Worker Training - . 'l _
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HP Organi7ation & Expectations * Positive Culture Change "We can fix it" * Self-critical Attitude (HP Generated ACRs increasing) * Improved Sense of Near-Term and Long-Term
l Direction for the Program
* Expectations Established * Appropriate HP Resources Applied * . . . I
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Procedure Compliance - Management Reaffirmed Strict Procedure Adherence as a Policy - Staff Focusing on Correcting Procedure !ssues Rather Than Procedure Wo -Arounds - Procedures Revised to Achieve Compliance During Phase I - Procedure Integration During Phase II . .
. .e . Training . * - Increased Training Resources - ! * Release Surveys - Alpha Monitoring and Controls * Phase i Enhancements * Intemal Dosimetry Program improvements * New Instrumentation . . O
h...
-- - -- ._. - _ . _ - . . _ Confirnlatorv Survey
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* Confirmatory Survey Completed
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* Over 186,000 Items Surveyed ^
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* 435 Items or 0.24% Had Detectable Activity
l -70% (307 items) Had <100 ccpm L L
l' * Conclusions
! -Improvement in Material Release Process
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-No Significant Health or Safety Concem - . 18
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. . Maior Phase II Actions * Radiation Protection Plan * Comprehensive Program and Process Integration * Performance Measures * Increase Self-assessments * Systematic Contamination Control Monitoring * Decommissioning ALARA Program
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* Decommissioning Radioactive Material Shipping Program
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* Training for HP Personnel . 19 . - . .
.. Corrective Action Program l Improved Process - * - Lower Threshold * Have Trending Programs to Evaluate and Monitor * Work Observation Program
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. 20 Gr _ ..
.. Corrective Action Proararn (Cont.1 . , , ) - Health Physics Program ACR Data -Corrective Action Program improving -Problems Self-identified -Emphasis is on Procedure Compliance and Quality -Problems Identified Are of Low Significance - . .
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Oversight Perspective * Strengthened QA Organization with Radiological Expertise
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a improved Nuclear Safety Assessment Board
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-- CY Specific : '
! - Extensive Decommissioning and Radiation Protection Experience I -
Increased Surveillance and Audit of Activities * Corrective Actions From Refueling Canal Personnel Contamination Have Been implemented * Implementation of Radiological Aictivities .l - RMS - :: - Confirmatory Survey l! !l N ,
4
.. - . _ _ _ --- . ._ ..__----o
.. ; Oversiaht Persoective (Cont 3, - . , ' . -RPIP Excellent Technical Resources Extensive Program Improvement Initiatives improved Training
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Areas For Improvement identified and are Being Pursued * Corrective Action Program is Improving . . 23 I , i
., Oversight Perspective (Conty * Overall Performance Has Improved Primarily Due to: -Improved Planning . -Heightened Expectation and Standards -Increased Management involvement -Better Communications * Process Enhancements are Still Required and are
- Being Pursued Through Phase Il RPIP Implementation
- Oversight of Radiological Activities Will Continue ~ Through Audits, Surveillances and Assessments.
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! -H l Summary
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CY ls Readv To Perform Additional - , Radioloaical Activities . * - The Culture Has Changed -Team Building
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-Standards And Expectations -Corrective Action Program -Prejob Briefings, Planning And Scheduling -Work Observations, Self-Assessments ' * Outside Expertise Brought in . 2s h ..- - . ..,. . . - - . . ... . .. -,_...-.,....--.--...-----,.-_]' .
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., ' Summarv. ? cont.1 . . * Responsive To issues in the CAL ~ ' -Corrective Action -Radiation Protection
- -Program Changes
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-Effective Administrative Controls - Our Health Physics Department and Radworker
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Performance Has improved - Therefore, Confident We Can Perform - Radiological Work -@ .
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. m . @ M L ' @ E o . T o> ._ C -, o C O O 4 4 e i . . _ _ _ _ _ _ . _ . _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _
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Summarv. f cont.1 . - Responsive To issues in the CAL . -Corrective Action , -Radiation Protection -Program Changes -Effective Administrative Controls - Our Health Physics Department and Radworker Performance Has improved
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* - Therefore, Confident We Can Perform - Radiological Work 2s h .- e . A k_ .____
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