January 1999:

1998 decommissioning activities at MYAPC were highlighted by two developments.  The first was the loss of the Texas Compact site as a possible location for MYAPC decommissioning-derived radioactive wastes, combined with the elimination of the Barnwell, South Carolina facility as a disposal site for the MYAPC reactor vessel with GTCC internals intact.  The state of Texas has suddenly and unexpectedly eliminated the Sierra Blanca site as a location of a low-level waste disposal facility; legislation now being considered in South Carolina would also close the Barnwell facility. At some time during 1998 the state of South Carolina affirmed a 50,000 curie limit for disposal of MYAPC wastes at Barnwell.  This information was provided by confidential sources within the bureaucracy of MYAPC to the editor of RADNET in the late fall of 1998. At no time did the state of South Carolina, the NRC or the state of Maine ever answer CBM's request for clarification of how the NRC's policy of concentration averaging for reactor vessel GTCC internals would impact the siting of the MYAPC reactor vessel at the Barnwell facility. It is still not clear how the state of South Carolina was able to over-rule the NRC and limit the radiological content of "low-level wastes" derived from the MYAPC decommissioning process to 50,000 curies, but the secrecy surrounding the issue of reactor vessel disposal with GTCC internals intact is consistent with the evasions and deceptions which have characterized so many aspects of the operation and decommissioning of nuclear power plants such as MYAPC. It is now even more likely that the GTCC reactor vessel internals as well as some of the class C internals will have to be kept on site at or adjacent to the new ISFSI facility that will be soon constructed at Wiscasset. The only remaining question is, will "decommissioning" leave 99%, 99.9% or 99.99% of MYAPC-derived radioactive wastes in a permanent defacto radioactive waste storage facility at Maine Yankee?

The second significant development in 1998 in the MYAPC decommissioning process was the Orwellian erasure of all news and public discussion of the March 30, 1984 nuclear accident at MYAPC in which reactor water storage tank (RWST) leaked at least 7,000 gallons of effluent into the environs of MYAPC. This accident was clearly documented in secret radiological survey 2401 at the end of volume 6 of the GTS Duratek Site Characterization Report, page 54. This was only one of numerous accidents documented by this report.  The cover-up of and evasion of responsibility for these nuclear accidents as well as of the financial legacy left by the establishment of a defacto radioactive waste repository at Wiscasset wouldn't be possible without the continuing corruption of language which characterizes most media coverage of the MYAPC debacle.  These omissions, evasions, manipulations of data, news spins and news speak are the basis of this Orwellian erasure from public consciousness of what MYAPC was, what it did, what it represented, what it will be in the future and the nature and costs of its radioactive legacy.  As the decommissioning process grinds to a halt because there is no place to put the radioactive waste which MYAPC created, a number of observations may be made about the current situation:
 

MYAPC has contracted with Stone & Webster and will pay this participant in the traffic in nuclear waste 250 million dollars to facilitate the establishment of the Wiscasset nuclear waste facility.  The use of the term "decommissioning operations contractor" continues the Orwellian tradition of manipulation of language to facilitate this profitable extension of MYAPC as a federally sponsored racketeering enterprise.  MYAPC is not actually being decommissioned at all, it's just being converted into a radioactive waste storage facility.

A Thursday, December 24, 1998, front page story in the Lincoln County Weekly about Maine Yankee increasing its annual collections from 14.9 million dollars to 33.6 million dollars to pay for "dismantling the plant and clean-up of the site"  is an excellent example of this process of erasure at work. Not only is the primary activity of the "decommissioning" process the construction of a  waste facility at MYAPC in the form of an ISFSI, it is unlikely that the extensive soil and sediment contamination in and around MYAPC will ever be fully remediated. Also the subject of evasive news reporting is the fact that the transfer of 130 million dollars collected via the mill rate fund for geological disposal of spent fuel to MYAPC for construction of the ISFSI (independent spent fuel storage installation) at Wiscasset ensures that this will be the final location for this fuel.

Texas has been eliminated as a destination for Maine's decommissioning-derived radioactive waste; Barnwell may soon also be eliminated by the South Carolina state legislature as a viable waste location. Beatty, Nevada remains as a viable location for the voluminous class A wastes and it is likely that numerous other vendors will appear who would be able to accept low-level wastes for storage or disposal. The problem of NRC misclassification of class B, C and GTCC wastes as "low-level wastes" will now come home to roost at MYAPC, where permanent on site storage of these not low-level wastes will be the only cost effective solution to the impasse created by the nuclear waste debacle.

The historic deficiencies in radiological surveillance procedures and documentation at MYAPC now manifest themselves in the form of the inability of the NRC to validate the new decommissioning site release criteria of 25 mrem/yr TEDE. Since no one, including Maine media, will admit there is a problem, its unlikely the problem will ever be addressed.

An important component of the Orwellian erasure of the impact and costs of MYAPC operations is the continuing cover-up of hot particle contamination in Montsweag Bay, the Sheepscot River basin and plant environs by past plant operations, accidental and deliberate discharges and accidents such as RWST leak of 1984.

Foremost among erased news topics by media such as the Lincoln County Weekly is the prospect of additional significant hot particle contamination of Montsweag Bay and the Sheepscot River basin if MYAPC decides to proceed with underwater segmentation of the reactor vessel internal components as part of the "decommissioning" process. Inevitable onsite safe storage of an intact reactor vessel is much safer and cost effective than pointless segmentation of reactor vessel internals that are not going anywhere.

When MYAPC constructs the ISFSI for its 1,440 spent fuel assemblies, the result will be 65 dry casks that weigh 150 tons each. It is neither cost effective nor practical to move these unwieldy casks to a final geological repository or an MRS facility even if the political squabbles accompanying these installations could be resolved. At 150 tons each, the multi-purpose dry casks are too heavy to move by road; the only viable option for transport is via rail.  There are presently no rail links to the proposed Yucca Mountain repository.  Political rather than physical obstacles ensure that it is unlikely that the MYAPC multi-purpose canisters will ever be moved anywhere, even by rail.  (Update:  The license presentation on the ISFSI at the January 21, 1999, CAP meeting included a redesigned ISFSI with a capacity for 72 casks, reflecting the necessity of onsite storage of GTCC reactor vessel components as well as control assembly elements (CEA) and of the high-level waste debris from operational mishaps -- see box labeled Spent Fuel Verification Program below.)

Insitu onsite storage, as allowed by the NRC site release criteria 25 mrem/yr TEDE, for the huge volumes of contaminated soil and Montsweag Bay sediments resulting from the numerous unreported nuclear accidents of the past at MYAPC will also be the likely cost effective alternative to transporting this contaminated material to a low-level waste repository such as that at Beatty, Nevada (class A low-level waste only).

The environs of Maine Yankee Atomic Power Company constitute a near surface radioactive waste disposal site which by law (CFR Section 10 Part 61) require analysis and characterization of all the isotopes destined for disposal. MYAPC and the NRC continue to be in noncompliance with federal law vis-a-vis accurately characterizing the land and sediment disposal of radioactive wastes derived from MYAPC operations, deliberate discharges, decommissioning discharges and undocumented accidents. For an excellent example of a more comprehensive environmental monitoring report which includes analyses of all the isotopes characterizing nuclear power plant operations see Radioactivity in Food and the Environment, 1997, RIFE-3, published by MAFF and SEPA, London.

January 5, 1999:

The following notice of violation was issued by the Center for Biological Monitoring after reviewing RIFE-3  (Radioactivity in Food and the Environment, 1997, issued by the Ministry of Agriculture, Fisheries and Food, UK and the Scottish Environmental Protection Agency.)

Cover letter:

Nuclear Regulatory Commission
Washington, DC  20555-0001
January 5, 1999

Dear Shirley Jackson:

Enclosed is 1) a summary of generic NRC and NRC licensee violations of 10 CFR Chapter 1, Part 60, especially 61.53 - 61.55 and 2) a copy of RIFE-3, Radioactivity in Food and the Environment, 1997, published by MAFF and the Scottish Environment Protection Agency (SEPA), the review of which occasioned this complaint.  It is my observation that the NRC has neither the intellectual nor financial resources needed to upgrade current radiological surveillance programs to meet the challenges of the new millennium.

Yours truly,

H. G. Brack
cc: NRC Commissioners

Notice:

January 5, 1999

Subject:  Generic NRC and NRC licensee (MYAPC) violations of 10 CFR Chapter 1, Part 60

10 CFR Chapter 1, Part 60 clearly mandates the systematic monitoring of all radionuclides contained in the wastes destined for near-surface land disposal (§61.53).  Isotopes listed in Tables 1 and 2 (§61.55) include long-lived radionuclides "whose potential hazard will persist long after such precautions as institutional controls, improved waste form and deeper disposal have ceased to be effective."  The Duratek Site Characterization Survey (1998) for the Maine Yankee Atomic Power Company (MYAPC) and a wide variety of historic licensee and other site assessments clearly document the environs of MYAPC as a radioactive waste disposal area.  MYAPC and the NRC failed to execute accurate environmental monitoring during reactor operations and during decommissioning activities that included discharge of 290,000 of the 300,000 gallons of radioactive water in the reactor water storage tank (RWST) during the spring of 1998, among other discharges.  These deficiencies have been exacerbated by the failure to evaluate, monitor or document the environmental impact of the 1984 accident also involving the RWST, and other inadvertent plant-derived liquid and hot particle discharges from 1972 - 1998.  MYAPC has been, in effect, the location of a small nuclear accident-in-progress.  As such, the environs of MYAPC, including Montsweag Bay and the Sheepscot River Basin, are clearly an unmonitored, undocumented radioactive waste disposal area.  The NRC and MYAPC, the licensee, are in habitual and generic violation of the requirements of 10 CFR Chapter 1, Part 60 et. al., especially that of §61.53 mandating environmental monitoring of the "impacts of ... operation ... of a land disposal facility."

Enclosed is a copy of RIFE-3, the third annual survey of radioactivity of food in the environment, published by Ministry of Agricultural Fisheries and Food (MAFF) and the Scottish Environmental Agency (SEPA), a review of which by the Center for Biological Monitoring prompted this citation.  The RIFE-3 report is sent to you as an example of a comprehensive radiological surveillance program which includes extensive analyses in a wide variety of media of long-lived radionuclides characterizing spent fuel and reactor operations.  The monitoring in the RIFE-3 report includes analyses for hard to detect (HTD) isotopes such as those listed in Tables 1 and 2 of §61.55 and includes ³H, ¹⁴C, ³⁵S, ⁶⁰Co, ⁶⁵Zn, ⁹⁰Sr, ⁹⁵Zr, ⁹⁵Nb, ⁹⁹Tc, ¹⁰³Ru, ¹⁰⁶Ru, ^110mAg, ¹²⁵Sb, ¹²⁹I, ¹³¹I, ¹³⁴Cs, ¹³⁷Cs, ¹⁴⁴Ce, ¹⁵⁴Eu, ¹⁵⁵Eu, ²³⁸Pu, ^239+240Pu, ²⁴¹Pu, ²⁴¹Am, ²⁴²Cm, ²⁴³Cm, and ²⁴⁴Cm (See page 74 as a typical example.)  The RIFE surveillance program clearly documents nuclear installation-derived plumes of many nuclides including ²⁴¹Am, ¹⁵⁵Eu, ²³⁸Pu, ²⁴¹Pu, the surprising and widespread uptake of ⁹⁹Tc by lobsters and the ubiquitous contamination of the environment by ¹³⁷Cs.

No such unclassified comprehensive monitoring program has ever been undertaken by the NRC, the DOE or the EPA in the vicinity of any U.S. reactor or weapons production installations.  The monitoring program in RIFE-3 provides a compelling and graphic contrast to the deficiencies in NRC surveillance programs discussed in Patterns of Noncompliance:  The Nuclear Regulatory Commission and the Maine Yankee Atomic Power Company: Generic and Site-Specific Deficiencies in Radiological Surveillance Programs issued by the Center for Biological Monitoring in June of 1998.

The deficiencies in NRC radiological surveillance programs are a component of a wider pattern of NRC licensee noncompliance and illegal activities (e.g. in Maine, the power uprate scam).  The failure to implement comprehensive 10-61 type monitoring, as exemplified by the enclosed MAFF and Scottish Environmental Protection Agency reports, is consistent with the ongoing failure of timely funding of radioactive waste storage and disposal costs or of accurate documentation of nuclear accidents of the type that occurred at MYAPC in 1984.

Citizen Advisory Panels (CAPs), such as the one now convened for MYAPC decommissioning, serve as facilitators of these evasions, omissions and illegal activities.  The current CAP at MYAPC serves as a buffer, ensuring that ratepayers pay the full cost of the "entitlements" derived from the traffic in nuclear waste.  MYAPC stockholders, who should be responsible for these liabilities (including upgraded radiological monitoring) up to the full value of their equity in the participating companies, are, consequently, protected from any loss of profits.  The fundamental purpose of federal oversight of the nuclear energy debacle is to perpetuate the omissions and evasions which maintain stockholder immunity from these liabilities.  Insufficient radiological monitoring is the first essential step in this program of institutionalized evasions.

The failure of the NRC and its licensees to comply with 10 CFR Part 60 et. al. by monitoring environments used as defacto radioactive waste disposal areas provides the legal bases for halting all reactor operations and decommissioning activities until a comprehensive monitoring program, such as that illustrated by the enclosed MAFF-SEPA report, is implemented.

January 21, 1999:
 

March 5, 1999:

There is growing evidence of the existence of a nuclear accident at the Maine Yankee Atomic Power Company (MYAPC) in Wiscasset, Maine.  The release phase of this accident, which has occurred in spurts over a long time frame (1973 to the present), will continue as the decommissioning process remobilizes fission and activation product contamination throughout the plant.

Item:  MYAPC released information about the contents of the spent fuel pool at the last Community Advisory Panel (CAP) meeting (February 18, 1999) in Wiscasset.  Of the 1,436 fuel assemblies, up to 298 are "nonstandard."  This is a deceptive way of acknowledging that over 20% of MYAPC has undergone fuel cladding failure at some time in the past.  Such failure releases substantial amounts of fission product into the primary cooling circulation water where it can spread to other areas of the plant.

The spent fuel pool also contains a variety of other equipment and items which may be further evidence of the nuclear accident that occurred at MYAPC.  These include control element assemblies and plugs, incore instrument thimbles, filter cartridges, neutron sources and, of particular interest, 22 storage baskets, the contents of which have not yet been made public.

Item:  On March 30, 1984, during a snowstorm, the reactor water storage tank (RWST) sprung a leak and released 7,000 gallons of radioactive water onto frozen ground.  The Licensee Event Report (84-004-00) indicates the water went into a storm drain and was diluted in the Forebay with no detectable radioactivity released.  The 1998 Duratek Site Characterization Report contradicts the NRC licensee event report by documenting significant soil contamination along the west side of MYAPC (Volume 6, Supplemental Survey 2501).  In a 10,000 sq. ft. area, which was frozen at the time of the release, Duratek site characterization data confirms fuel-rod-derived residual ¹³⁷Cs contamination of at least 3 million nanocuries.  There is no other reactor source for this isotope.  The maximum permissible concentration of ¹³⁷Cs in water released in the environment is 1 nanocurie/liter (10 CFR Part 20 Appendix B).  Seven thousand gallons of water = 26,600 liters; the MYAPC release limit for this quantity of contaminated water is therefore 26,600 nanocuries, far below residual contamination levels documented in the frozen soil in the 1984 accident. The contamination documented in Supplemental Survey 2501 is unlikely to be the only radiation released by this component of the accident.  (Portions of these reports have now been scanned and can be seen at these links: LER 84-004-00 and Survey 2501.)

Item:  The Duratek Site Characterization Report also documented high levels of radiocesium adjacent to and outside of the reactor containment and bioshield, with contamination as high as 156,000 pCi/kg ¹³⁷Cs in grid 103.  This is further evidence of systemic failure of fission product barriers at MYAPC. (Volume 6, Survey package R0100)

Item:  The Duratek report documents substantial activation product contamination outside of plant systems and equipment, with samples as high as 33,600,000 pCi/kg of  ⁶⁰Co in a hot particle (CRUD) on Bailey Point. (Volume 6, Survey package R0500).

Item:  Gamma spectroanalysis of smear samples (Duratek Site Characterization Report, Volume 3) document significant fission and activation product contamination throughout the pipes, drains, valves, steam generators and internal components of the plant outside of the containment and spent fuel pool.  Very limited Duratek smear sample spectroanalysis (48 smears in 15 systems) of removal contamination indicates:

• ⁶⁰Co contamination exceeding 2,000,000 pCi/kg in 15 of 48 smears.  Contamination peak value 86,400,000 pCi/kg.
• ¹³⁷Cs contamination exceeding 1,000,000 pCi/kg in 18 of 48 smears with peak values (PV) of 88,300,000 pCi/kg.
• Evidence of fission product contamination in all smear samples from drains, valves, piping and other water system components.

Item:  Pre-free release analysis of water in the reactor water storage tank (RWST) was taken as a non-representative grab sample of quiescent water and provides no information about fission and activation product contamination in tank sludge, sediments and scaling.  The NRC, the licensee and the state of Maine failed to provide CBM with the tank release data (including the neutron shield and other tank release data) when we requested it in the spring of 1998.  No specific public notification was provided by the NRC, the licensee or the CAP to area fishermen that the free release of the RWST was underway.

Item:  MYAPC did not release the last 10,000 gallons of water in the RWST during the time of this free release.  Data on fission product contamination of the remaining contents of the RWST is not contained in any NRC or licensee documents and has not been made available despite requests made by the Center for Biological Monitoring.

Item:  Significant fission product contamination remains within the reactor containment vessel.  The Duratek Site Characterization Report contains a complete activation product analysis of reactor internals (+3,000,000 Ci) but no information whatsoever about fission and activation product hot particles, "fuel fleas," and other contaminants in the reactor containment.  Underwater segmentation of the reactor vessel internals during the decommissioning process is a potential pathway for the release of spent-fuel-derived contamination within the reactor containment.

Item:  The Duratek site characterization documents high radiation fields remaining in and around the containment (removal of the spent fuel has been completed), as well as around the base and floor adjacent to the RWST, and in many other locations.  The question remains unanswered as to what extent these radiation fields derive from normally occurring shine from irradiated reactor internals versus radiation fields created by breach of the fission product barriers.  Contamination derived from the reactor water storage tank produced ground shine along the west side fence line which the licensee has always attributed to shine from normal reactor operations.

Spent fuel failure at MYAPC is an accident-in-progress.  The release of fission products in the 1984 RWST leak is one recently documented pulse of fission product contamination which has been followed by the undocumented free release of much of the remaining content of the RWST.  Decommissioning decontamination activities for the purpose of constructing a high-level waste repository at Wiscasset will result in the remobilization of fission product contamination which has already escaped the fission product barriers (containment bioshield, spent fuel pool) at MYAPC.

The NRC, the licensee, the CAP, the state of Maine and Maine media have either lied or provided misinformation about the status of the MYAPC facility.  The site is not clean as reported by MPBN, etc.  None of the above have had the integrity to report that a nuclear accident has occurred at MYAPC in the form of spent fuel cladding failure and that this accident has spread radioactive contamination throughout the environs of the MYAPC facility.  The fact that the release phase of this accident may resume with major decommissioning activities has been evaded.  The cover up of this relatively small nuclear accident involves numerous violations of federal law and NRC regulations by NRC and MYAPC staff.  Both the Maine State Nuclear Safety Advisor Uldis Vanags and Maine State Nuclear Safety Officer Pat Dostie participate in the avoidance of documentation of this breach of fission product barrier integrity at MYAPC.  We have requested the assistance of the Office of the US Attorney for Maine in reviewing the situation and intervening to prevent further releases of fission and activation products and hot particle contamination during the decommissioning process until a careful review and recharacterization of plant facilities and the environs clarifies the extent of spent-fuel-derived contamination.  It is important that the NRC provide an independent contractor, such as the GTS Duratek Co., to recharacterize spent-fuel-derived residual radioactivity and that the staff of MYAPC and the NRC have no further involvement with this process.  Public safety considerations mandate that a thorough recharacterization be completed before any further decommissioning activities begin.

This situation is particularly unfortunate because there is evidence for a similar and perhaps more serious nuclear accident, also involving fuel cladding failure, at the Haddam Neck, Connecticut, reactor.

Note to Media in Maine and elsewhere:

In the spring of 1998, you reported, as indicated by the licensee, that the site was "clean" with no contamination other than that expected from "normal" operations.  Would you please correct this misinformation and acknowledge that there has been a nuclear accident at the Maine Yankee Atomic Power Company, the release phase of which may not be over due to the remobilization of spent-fuel-derived contamination due to the decommissioning process?

Dear Helen, (etc.):

Thank you for conversing with me the other day.  I thought I would send you an inquiry concerning the topic of our conversation.  Would you like to continue participating in the contest described below?

Debris from a Fuel Cladding Failure Accident (FCFA) is now stored in the spent fuel pool of the Maine Yankee Atomic Power Company (MYAPC).  ( A FCFA  is not at all similar to a LORCA,  Loss of Reactor Coolant Accident.)  Some of the radiocesium (CS-137, CS-134) and other isotopes  from 200-300 damaged ("nonstandard") fuel assemblies have breached the fission product barrier (reactor containment, spent fuel pool) and spread throughout the facilities and environs of MYAPC.  Extensive soil contamination has been documented outside the bioshield at the base of the reactor containment.  A 1984 reactor water storage tank leak released +3,000,000 nanocuries of damaged fuel assembly-derived radiocesium into 10,000 square feet of frozen snow-covered soil.  The 1984 MYAPC Licensee Event Report (LER GDW-85-50) indicated that the licensee found no detectable radiation in plant environs and overlooked the soil contamination.   In 1998, a decommissioning activities release of 280,000 additional gallons of reactor water storage tank liquids remobilized an undetermined amount of accident-derived spent fuel isotopes.  Ten thousand gallons of RWST sludge and water remained to be characterized and "decommissioned."   Hot particle and activation product contamination documented by Hess, GTS Duratek , and others, may be correlated with accident debris in the MYAPC spent fuel pool.  Smear sample spectroanalyses of removable contamination documents the migration of high levels of radiocesium from damaged fuel assemblies throughout Maine Yankee Atomic Power Company plant water systems.  The reactor containment has been characterized by an activation product analysis, but not for accident-derived fission product debris and dross.   All fuel cladding failure accident debris and damaged fuel assemblies now in the MYAPC spent fuel pool will be indefinitely stored on-site in the new Independent Spent Fuel Storage Installation (ISFSI).  N.B. ISFSI is pronounced IsFahSee;  at the National Imagery Management Agency (NIMA), FCFA is pronounced "FicFah."  The NRC doesn't use an acronym for fuel cladding failure accidents.

Accident reconstruction and characterization of the remaining residual radiation resulting from this accident prior to accident site decommissioning is not required by any NRC or state of Maine regulations.  Any future accident characterization is purely voluntary on the part of MYAPC or its Decommissioning Operations Contractor (DOC), Stone and Webster.

The release phase of the MYAPC Fuel Cladding Failure Accident (FCFA) began in 1974 and will continue during the decommissioning process.  The largest releases in the future may occur as a result of underwater segmentation of reactor vessel internal components.  Hot particle contamination of Sheepscot River estuaries is not yet as pervasive as contamination from the Fuel Cladding Failure Accident (FCFA) in the vicinity of the Haddam Neck Connecticut Yankee Plant.

The public relations usefulness of euphemisms such as "licensee event" or  "unusual occurrence" as substitutes for "accident" is wearing thin.  Another new postmodern euphemism for "accident" is needed!  If you would like to play "Hide the Evidence," please me send a suggestion for an alternative euphemism.  First prize will be the MYAPC smear sample with the highest removable fission product contamination level.  The record to date is 88,000 picocuries per gram of accident-derived CS-137 (48 samples).  Second prize will be for the largest activation product hot particle found outside Radiation Contaminated Areas (RAC) of the MYAPC plant.  The record so far is 33,600 pCi/g  of Co-60 on Bailey's Point.  The federal government likes to use grams instead of kilograms as reporting units, so that contamination levels don't seem so obvious.

Anyway, Helen, (etc.), there has been a nuclear accident at the Maine Yankee Atomic Power Company in Wiscasset, Maine - a Fuel Cladding Failure Accident (FCFA).  Get used to it. Thank you for playing Hide the Evidence.   Hope you had a good time.

Yours truly,
Skip  [Fax (207)288-2725]
p. s. Do you "get it" yet?

Federal Bureau of Investigation
Augusta, ME  04330

Dear Dave Barry:

The U.S. Attorney's office for Maine (Don Clark) suggested I contact your office with respect to my request to his office for assistance in investigating one or more violations of 10 CFR Part 20, Appendix B.  My complaints involve gross failure by the Nuclear Regulatory Commission to document the source term (amount of radioactivity released during a nuclear accident), pathways and residual radiation from a fuel cladding failure accident (FCFA) at the Maine Yankee Atomic Power Company (MYAPC).  The accident began in 1973/74, and due to the spread of fission products beyond plant fission product barriers into the water systems and environs of MYAPC, additional undocumented releases of accident-derived fission products occurred during decommissioning activities in the spring of 1998, and will continue to occur during future decommissioning activities.  At the last MYAPC Community Advisory Panel (CAP) meeting, the licensee released details of its "spent fuel pool verification program" and provided information that indicates between 200 and 290 fuel assemblies are "nonstandard," raising the issue of how many becquerels of radioactivity (and of which isotopes) have been released by the fuel cladding failures now coming to light.  More details about this accident are contained in the accompanying pages.  Please note the enclosed faxes were originally sent to news media this week but, nonetheless, contain much of the basic information that I would like to share with the FBI.

Upon the suggestion of the U.S. Attorney's office in Maine, I have a number of requests:

1. There is a Community Advisory Panel meeting tonight (Thursday, March 11, 6:00 PM) at the Maine Yankee Information Center.  Even though it is late notice, I would like to request that someone from either the Bangor or the Augusta office please go to this meeting as an observer for the purposes of gathering background information about the NRC's failure to characterize both the size and duration of releases which have resulted from this (these) fuel cladding failure accident(s).

2. Please note the enclosure (Licensee Event Report 84-004-00) which alleges that a related event, 1984 leak in a reactor water storage tank containing abnormally high amounts of spent-fuel-derived radiocesium, does not represent a violation of technical specifications.  Data provided by the licensee in the 1998 GTS Duratek Site Characterization  Management Plan contradicts this report and indicates that a substantial amount of radioactivity was released by  this event.

3. The 1984 reactor water storage leak would not be as significant a violation of 10 CFR Part 20, Appendix B regulations were it not for the fact that the cursory site characterization which GTS Duratek executed clearly documents that a nuclear accident has occurred at the Maine Yankee Atomic Power Company facility.  The reactor water storage tank leak represents one among a series of undocumented releases of fission and activation products which have as their origin the fuel cladding failure accident (FCFA).  Since decommissioning activities are about to begin, it is particularly important that the source term (amount) and pathways of fission products released from damaged spent fuel now in the spent fuel pool be documented prior to any further decommissioning activities.

4. The licensee has also recently disclosed that debris other than damaged spent fuel assemblies from this fuel cladding failure accident(s) is also located in the spent fuel pool in the form of 22 baskets, the contents of which are as yet unidentified.  Control element assemblies and other items also in the spent fuel pool may have also played a role in this accident.

It is my contention that prior to any further decommissioning activities, the size and duration of this accident must be analyzed and characterized.  Significant quantities of accident-derived fission products still remains within the reactor containment, the reactor water storage tank, the plant water systems (which are about to be removed as part of the decommissioning process) and the environs of MYAPC.  Accident-derived contamination in all of these locations remains essentially uncharacterized.  I would further contend that the failure of the NRC to document the size and extent of this nuclear accident is a gross violation of federal law and that a number of state of Maine employees may also be sailing close to the wind as accessories to the ongoing cover-up of this fuel cladding failure accident.

As the director of research for the Center for Biological Monitoring (we collect and collate federal and other data, we don't do any monitoring), I have been in frequent contact with the NRC and their many professional employees for almost 30 years.  In making a controversial allegation that an accident other than normal operational "events" has occurred with respect to fuel cladding failure, I find the NRC in denial of the obvious.  The NRC has reached the point of psychic numbness; it is unable to act in a timely manner to document the extent of the fuel cladding failure accident at MYAPC.  Decommissioning activities which will remobilize accident-derived residual radiation are about to commence; the NRC, licensee and the state of Maine cannot be trusted to provide reliable data documenting what has occurred in the past not to mention what will occur in the future.  Will your office please get involved to review the violations of federal law which have and are taking place with respect to the cover-up of the extent of accident-derived contamination at MYAPC.

Yours truly,

H. G. Brack

1. What amount of radioactivity (how many becquerels of which isotopes) was released from the damaged fuel assemblies?

2. How much of this radioactivity was released beyond plant fission product barriers (e.g. 1984 reactor water storage tank leak (RWST), 1998 RWST decommissioning activities free release, other tank releases, other inadvertent releases via normal liquid discharges etc.)?

3. How much accident-derived radioactivity remains within the reactor containment?  What proportion of reactor containment residual radiation other than activated stainless steel components derives from normal plant operations and what proportion is derived from fuel cladding failure?

4. Is there any relationship between soil contamination documented at the base of the reactor containment outside the bioshield and the incidents of fuel cladding failure?

5. How many "bad batches" of fuel assemblies were noted, when were they noted and how many of the "nonstandard" ones now in the spent fuel pool are considered components of the "bad batches"?  (How many fuel assemblies are in a "batch"?)

6. What amount of accident-derived fission products remain within the steam generators, other plant tanks and reactor water systems after the decontamination flush?

7. Where is the documentation for the amount of plant-derived radioactivity contained within the decontamination flush; what amount of radioactivity was filtered out of the flush prior to dilution and free release; how does this data compare with decontamination flushes at other reactors undergoing decommissioning?

8. How much accident-derived radioactivity remains in the reactor water storage tank (RWST), both in tank sludge, and within the 10,000 gallons of radioactive water still in the tank?  Why was this amount of water withheld during the 1998 free release of the reactor water storage tank (RWST)?

9. What additional soil contamination exists in plant environs beyond that documented in GTS Duratek Supplemental Survey 2501?

10. Why was the soil contamination documented in Survey 2501 not mentioned in the Executive Summary of the GTS Duratek report?  Why was the MYAPC site represented as "clean" during the presentations made by the licensee at the Community Advisory Panel meetings in 1998, and so reported by Maine media?  Will Maine print and electronic media correct the misinformation previously reported?

11. How has accident-derived as well as normal-operation liquid emissions impacted the estuaries of the Sheepscot River including Montsweag Bay and Bailey Cove?

12. How much accident-derived radioactivity has been released into these marine environments after the cursory GTS characterization of contamination in Montsweag Bay.  Why did the NRC and the licensee wait until after cursory sediment sampling to discharge plant-derived liquids from the reactor decontamination flush, the reactor water storage tank (RWST) and other tanks?

13. What's the source of contamination on Bailey Point and how does it correlate with the fuel cladding failure accident (FCFA)?

14. What is the source of the hot particle contamination documented by Hess and the radiological information reports (RIRs) generated by the licensee, most of which are not available for public scrutiny?

15. What accident debris (other than the "nonstandard" fuel assemblies) remain in the spent fuel pool and what is their correlation with the fuel cladding failures?

16. Why would the licensee and the NRC utilize unreliable drive over gamma scans of soil contamination for environmental characterization when these drive over scans obviously failed to pick up surface contamination (+/- 10,000 sq. ft., +3,000,000 nanocuries ¹³⁷Cs) resulting from the 1984 reactor water storage tank leak (RWST)?

17. Who will implement an accurate characterization of the fuel cladding failure accident (FCFA) and will it be done prior to the resumption of additional decommissioning activities?

18. If the decommissioning operations contractor (DOC) Stone & Webster is responsible for this characterization, will the data be reliable?  Available for public scrutiny?  Subject to independent peer review from a nonbiased source other than the licensee or the NRC?  In this context, doesn't the DOC become a victim of the NRC's failure to document the incidents of fuel cladding failure at MYAPC?

19. Why are state of Maine site characterization split-samples not available for public scrutiny?

20. Why did the NRC failure to provide routine data pertaining to liquid discharges from plant tanks and water systems during 1998 MYAPC decommissioning activities?

21.  What steps does the decommissioning operations contractor (DOC) and the licensee intend to take during future plant decommissioning activities to document and then to limit additional releases of accident-derived fission and activation products and hot particles?

I'd like to share my concern that Friends of the Coast (FOC) and Citizens Awareness Network (see CAN's newsletter) have been thoroughly co-opted by Maine Yankee/Entergy/Stone & Webster (DOC - Decommissioning Operations Contractor).  The "settlement," whatever that was, including a cash $12,500 payment and establishment of a 200 acre park of some type, was the occasion of a lengthy diversion at the March Community Advisory Panel (CAP) Meeting.  Neither Ray Shadis (Friends of the Coast), nor anyone else questioned licensee assertions that fuel cladding failure accidents at MYAPC (20% failure rate) are part of "normal" operations and thus need no further documentation.  Also, not subject to FOC/CAP questions was the soil contamination outside the bioshield running twenty times higher than peak values in Yankee Rowe discharge bay sediments, an area of expected contamination.  The release phase of fuel cladding failure accidents at MYAPC is not yet over.  The site characterization report provides clear evidence of breaching of the fission product barriers at MYAPC - evidence confirmed by the high fuel cladding failure rate.  The source term of these failures must be documented prior to further decommissioning.  Diversion of attention by CAP (the cover-up advisory panel) and the licensee (MYAPC - Entergy) to public relations fluff ("the settlement") and secondary issues (e.g. plant security, noisy fans, etc.) serves to let the NRC and MYAPC off the hook.  Documentation to determine the size of the releases from fuel cladding failures, as well as their pathways and destinations, prior to further decommissioning activities is both a public safety and legal imperative.  In the context of the silence of Friends of the Coast on these issues, maybe it should consider a name change to Friends of the Cover-up.  How about CAN to CANT (can't focus on the necessity of source term documentation)?  If MYAPC and Connecticut Yankee fuel cladding failures are "normal," then operational reactor releases to the environment may be much higher nationwide than indicated by misleading and unreliable licensee annual effluent reports.

H.G. (Skip) Brack, Center for Biological Monitoring

Addendum:
On March 8, 1999, Ray Shadis of Friends of the Coast sent me the following comments about last week's CBM mailings:

"If you have not had adequate levels of success with the 'rub their noses' in it approach thus far, perhaps a change of approach is needed ... I am suggesting a different kind of self-discipline and self-sacrifice, each setting aside as much as we can, our ego, may be in order if one is to best serve the cause of protecting our environment and future generations."

In response to Ray's comments, I'd like to make the following statements:

• My compliments to Ray for his many successes in closing the MYAPC reactor, raising our awareness about many safety issues, and the long hours of uncompensated work he has put in at Friends of the Coast and on the CAP.  Unfortunately, the situation is now evolving where FOC, CAN, etc. and I may have a much more adversarial relationship than in the past, primarily due to what I consider to be very controversial and evasive presentations by the licensee at the CAP meetings.  The NRC and MYAPC have consistently and without FOC challenge misrepresented the environmental impact of plant operations and decommissioning.  The recent revelation that 20% of the fuel assemblies in the MYAPC spent fuel pool are "nonstandard" is a very controversial and newsworthy development.  The diversion of attention from this topic at the previous CAP meeting was unacceptable.
• With respect to Ray's comments, I would just like to point out in my defense, that CBM  has published in excess of a thousand pages of bibliographic citations, analyses and commentary and issued dozens of "polite" letters to regulatory authorities. With occasional exceptions, very little of the material we have posted on the Internet or published is of the inflammatory "rub their noses in it" type.  I agree with Ray that a change of approach from that I have taken as Editor of RADNET is now needed, but it won't be in the direction that you are suggesting.  Much more radical actions are needed to penetrate the veil of secrecy of the nuclear information gulag, of which the CAP is a startling example.  I am unconvinced that satire, humor, debunking, sarcasm, mockery and ridicule are any more or less egotistical than any of our conventional bibliographic citations in RADNET or of any of the past or present activities of the Friends of the Coast.
• The targets of most interest to me are not Friends of the Coast and other environmental organizations, but electronic and print media including MPBN, NPR, PPH, etc., and state of Maine and NRC participation in these evasions.  The Achilles' heel of spent fuel cladding accident cover-ups is that the decommissioning operations contractor (DOC), Stone & Webster, is now saddled with a legal responsibility to document the extent of fuel cladding failures at MYAPC prior to the commencement of decommissioning activities.  Particularly worrisome, is the conflict of interest inherent in the for-profit "discount" decommissioning of MYAPC and the appropriate and timely documentation of fuel cladding failures revealed by the site characterization report.  This documentation may never occur and the current charade will probably continue at the CAP meetings.  If this is the case, a much more confrontational approach is justified due to the near total throttling of public participation, dialogue or opportunity for questions at these meetings and any other forums.  If Friends of the Coast is going to be a party to the continuation of this cover-up, then I'm afraid that I'm going to be writing things that might make a lot of people angry.

March 30, 1999

Nuclear Regulatory Commission
Washington, DC  20555-0001

Dear Chairperson Jackson:

The Maine Yankee Atomic Power Company (MYAPC) has recently revealed that approximately 20% of the fuel assemblies now in the spent fuel pool are "nonstandard" and require special handling and dry cask packaging.  This information further confirms growing evidence of periodic loss of radiological controls at MYAPC.  Preliminary site characterization data gathered by GTS Duratek in 1998 constitute a predicator of this fuel cladding failure.

The NRC has no legal basis for proceeding with further decommissioning activities at MYAPC until source term analyses of the fuel cladding failure accidents which have occurred there are implemented and completed by some other more trustworthy entity than the NRC or the licensee.  Perhaps the Defense Nuclear Facilities Safety Board (DNFSB) or GTS Duratek could execute the source term analyses mandated by 10 CFR Part 20.  Nowhere in Part 20 are there any provisions that allow the NRC or its licensees to escape documentation of the fuel cladding failure that has been so graphically illustrated by the initial cursory site characterization of the MYAPC facility by GTS Duratek in 1998 and recently verified by the disclosure of the 20% fuel assembly damage rate.

Enclosed are copies of a Brief to the U.S. Attorney for Maine and a letter to the decommissioning operations contractor (DOC), Stone & Webster, summarizing the present position and intentions of the Center for Biological Monitoring.

How did the NRC end up in the untenable position of smugly asserting compliance with federal statutes when "under color of official right" it is in blatant noncompliance with these statutes?

Yours truly,

H. G. Brack
Director of Investigations
Radiological Surveillance Programs
Center for Biological Monitoring

Stone & Webster Construction Co., Inc.
Manager of Nuclear Decommissioning
245 Summer St.
Boston, MA  02210

Dear Mr. Nauman:

I am completing a review of the GTS Duratek Site Characterization Management Plan of the Maine Yankee Atomic Power Company (MYAPC) facilities.  A number of unexpected residual radiation anomalies are contained within the characterization report (eight volumes, Maine State Library.)  The licensee has recently announced the existence of 250 to 290 "nonstandard" fuel assemblies in the spent fuel pool which shed light on the anomalies in the characterization survey.  This represents a revision of previous (oral not written) licensee assertions that leaking fuel assemblies were associated with only a single "bad batch" (37 assemblies) in the early years of plant operation.  It is now clear that a series of fuel cladding failure accidents (FCFAs) have occurred at MYAPC and that this facility is, in essence, the location of a yet to be documented series of nuclear accidents.  Some of the damage to fuel assemblies may be the result of grid to rod fretting towards the end of reactor operations and debris now in the spent fuel pool may point to other events in addition to fuel cladding failure.  Fuel cladding failure, however, appears to be the primary source of residual radiation anomalies (fission products and hot particles) recently documented in reactor water systems and plant environs.

I would like to share the following observations with Stone & Webster:

1. Future decommissioning activities will likely extend the release duration of past fuel cladding failures.

2. Source term analyses (of isotope quantities, chemical and physical forms and release time) must be executed to determine the amount, pathways and destinations of fission products released during fuel cladding failures.

3. Much more extensive spectroanalyses of removable smear samples from plant equipment and water systems must be executed to document the pathways of fuel-derived fission products within the plant itself.  The 48 removable smear samples analyzed in the Duratek report for gamma-beta contamination, while showing a high percentage of anomalies, constitute a grossly inadequate database for decommissioning any type of reactor.

4. The equally cursory characterization of "unaffected" plant areas and adjacent off-site environs also provides graphic evidence of breach of fission product barriers.  A much more comprehensive program of spectroanalyses of soil and sediments as well as of selected bioaccumulators must be implemented as part of the fuel cladding failure (FCF) source term analyses. The pathways and destinations of fuel assembly-derived contamination that has breached reactor fission product barriers at MYAPC must be documented prior to any further decommissioning activities.

5. It is now clear that previous NRC licensee-generated event reports, annual effluent reports, reactor water systems and storage tank grab samples and other monitoring data are unreliable and cannot be used for source term analyses.  In fact, the licensee should and must be prohibited from supervising or controlling the documentation of these fuel cladding failures, etc.  Stone & Webster shares MYAPC's conflict of interest between profits and documentation.  Fuel cladding failure source term analyses must be executed by an entity without such conflicts of interest.

6. Resumption of decommissioning activities by Stone & Webster prior to accident characterization should result in the most vigorous possible prosecution of participants allowed by law, possibly including pursuit of Title 18 civil or criminal complaints (section §1964, etc.) (See correction in April 2 letter.)

I look forward to working with Stone & Webster to accurately document the source term for MYAPC fuel cladding failure accidents (FCFAs).  I have the following questions and requests:

· Please advise me who you think at Stone & Webster would be most effective in maintaining an open dialogue about this admittedly controversial subject?
· To whom should I address my questions about the progress of accident characterization efforts and the resulting database?
· Would any representatives from Stone & Webster come to join me for a meeting (or dinner) to review decommissioning procedures and data?
· Who at Stone & Webster, if anyone, is in charge of the fuel assembly verification program announced by MYAPC at a prior Community Advisory Panel meeting?

I would be interested in having one or more face to face meetings with Stone & Webster to discuss these issues, either in Boston, Portland or elsewhere.  Please advise me of the status of source term analyses of loss of radiological controls at the Maine Yankee Atomic Power Company.

Thank you for your attention in this matter.

Yours truly,

H. G. Brack
Director of Investigations
Radiological Surveillance Programs
Center for Biological Monitoring

cc. Dave Barry, Don Clark, Community Advisory Panel members, Scott Gray, Shirley Jackson, Mary Ann Lynch, Michael Masnik, NRC Commissioners, Michael Webb, John Zwolinski

· 10 CFR Chapter 1, Part 10.4 directs the NRC to "conduct its operations in a manner consistent with traditional American concepts of justice."
· 10 CFR Chapter 20, Part 20.103 mandates measurement of radiation levels and concentrations.
· 10 CFR 20.1302 requires surveys of radiation levels in unrestricted areas.
· 10 CFR 20.1402 sets site release criteria for residual radiation at 25 mrem/yr TEDE for members of the general public for all isotopes in all pathways.
· 10 CFR 20.1406 mandates minimization of contamination; 10 CFR 20.1501, surveys that are reasonable under the circumstances; 10 CFR 20.2103, record keeping; 10 CFR 20.2202, notification of incidents; 10 CFR 20.2207 reporting contamination exceeding regulatory limits.

At the Maine Yankee Atomic Power Company in Wiscasset, Maine, the NRC has clearly and consistently violated the letter and spirit of the Code of Federal Regulations through

1. Inadequate documentation of the environmental impact of plant operations including a general failure of historic documentation of the residual radiation levels and pathways of isotopes characterizing long-lived spent fuel wastes (LLSFW)

2. Failure to mandate a decommissioning activities environmental impact statement (EIS)

3. Premature acceptance of an inadequate and vague Preliminary Site Decommissioning Activities Report (PSDAR)

4. Tolerance of a cursory post-operational site characterization database (GTS Duratek)

5. Failing to adequately document the radiological profile of reactor water systems decontamination releases or to allow public discussion or review of this documentation

6. Failing to document the environmental impact of reactor water systems decontamination releases by allowing licensee scheduling of cursory marine sediment characterization prior to liquid effluent releases

7. Ignoring additional emerging evidence of loss of radiological controls and breaches of fission product barriers which graphically illustrate the necessity of additional site characterization prior to major decommissioning activities

8. Failure to adequately document the quantities, pathways and destinations of liquid effluent releases, including the 1984 reactor water storage tank (RWST) accident

9. a stubborn inability to recognize the necessity of upgrading obsolete radiological surveillance programs

10. Systematic avoidance of spectroanalyses of biologically significant radionuclides in abiotic and biotic media other than through cursory and misleading annual environmental monitoring reports

11. An over-reliance on inaccurate and inadequate "drive-over" gamma scanning technology for pre-decommissioning characterization in lieu of more costly spectroanalyses

12. Tolerance of a lack of public hearings, discussion, debate and documentation both during reactor operation and decommissioning in violation of "traditional American concepts of justice"

13. Encouragement of a licensee controlled Community Advisory Panel (CAP) that is both a conduit of misinformation and a forum for evasion, deception and obstruction of justice.

14. A refusal to acknowledge that the MYAPC facility has been the location of a series of fuel cladding failure accidents (FCFAs), 1974-1998

15. A concomitant refusal to recognize the statutory obligation of detailed post-accident source term analyses to determine the quantities, chemical and physical forms and release durations of contamination derived from the "nonstandard" fuel at MYAPC

16. Failure to conduct operations in a manner consistent with traditional American concepts of justice by the maintenance of secret records and databases, beginning with routine radiological incident reports (RIR) and extending to nuclear accidents not yet disclosed to the public, the MYAPC fuel cladding failure cover-up being indicative of a much broader pattern of NRC evasions and self-deception

In view of the anomalies in residual radiation levels at MYAPC plant systems and environs and a 20% fuel assembly damage rate, the NRC is not conducting itself in a manner that is "reasonable under the circumstances" or consistent with the statutory requirements in the Code of Federal Regulations

Nowhere in the Code of Federal Regulations does it suggest the Nuclear Regulatory Commission should join with the licensees to conduct for-profit reactor operations in the manner of a Banana Republic.  The NRC has demonstrated an exceptional inability to revise and upgrade its documentation of the environmental impact of reactor operations, accidents and decommissioning procedures not only to meet the statutory requirements of federal law but also to meet the challenges of radiological surveillance programs in the post-Chernobyl era.  The NRC has formed a closed society with its licensees and, in Maine, with state government and associated political supporters.  There has been no advance or reform in monitoring programs since the AEC was established in 1954.  With the promulgation of site release criteria of 25 mrem/yr TEDE for members of the general public, the NRC has shot itself once in each foot and then again in the head for good measure:  it lacks the database to validate the site release criteria.

There is now clear evidence of fuel cladding failure accidents at MYAPC and other New England reactors, coupled with an NRC failure to document the source term of these releases.  In effect, the NRC is facilitating a for-profit cover-up of instances of loss of radiological controls which are required by federal law to be documented.  Without this documentation, the NRC has no legal authority to allow decommissioning activities at MYAPC to proceed.  In fact, the inability of the NRC to observe or question the historic inadequacies in its radiological surveillance programs and the resultant lack of documentation of both routine emissions and accidental releases undermines the legal basis for any reactor operations in the United States.  If the NRC is unable to understand and enforce both the letter and spirit of 10 CFR Chapter 1, Part 10.4 or the monitoring and documentation requirements in 10 CFR Chapter 20, who will assume its oversight responsibilities?  Will the Department of Justice also serve as a facilitator of NRC noncompliance with federal law?

H. G. Brack
Director of Investigations
Radiological Surveillance Programs
Center for Biological Monitoring

Manager of Nuclear Decommissioning
Stone & Webster Co., Inc.
Boston, MA  02210

Dear Mr. Nauman:

I just wanted to correct a typographical error in my letter to you in section 6.  The sections of the U.S. Code which catch my attention are first and foremost 1961 and forward and also 371.  I also wonder if sections 101, 102 and 103, as well as 1505 could be applied to certain past activities of the licensee (MYAPC).  While I was away last week, I was also re-reading the Code of Federal Regulations and find 10 CFR Part 9 on public records and 10 CFR Part 13 on fraudulent claims and statements, as well as Part 21 on reporting defects and noncompliance to be relevant to the activities of the licensee.  I am realistic enough to realize that its very unlikely the Department of Justice would bring any charges against such well established and entrenched activities.  The failure to document the environmental impact of activities, which start at the beginning of the Cold War, is so ingrained, as to appear as normal behavior.  It will certainly be interesting to see what data Stone & Webster will provide to the public documenting the source term of fuel cladding failure, whatever its cause, at MYAPC.

Yours truly,

H. G. Brack

cc.  Don Clark
Shirley Jackson
Dave Barry

Date: Thu, 01 Apr 1999 08:02:11 -0500
To: dlochbaum@....
From: Raymond Shadis <shadis@....>
Subject: Re:Undocumented fuel cladding failures
Cc: "sbrack@acadia.net" <sbrack@acadia.net>

Dear Dave,
 I have a complete inventory of the contents of the MYAPS SFP. 20% is more
or less irrelevant, but they do have a lot of damaged fuel, some of which
was damaged during a pin-packing experiment in 1982-83-84. There is a lot
of stuff in baskets and special containers, including one fuel pin in a
concrete pipe. There are filters left from a SFP clean-up and fuel rubble
from the SFP bottom. All of this is documented in CONFIDENTIAL material
provided in our FERC discovery. I would break confidentiality rules and
give this to Skip, but he's acting like such an asshole, I can't trust that
he wouldn't betray MY confidence. It might be suggested to him that he (1)
Ask MYAPC for an inventory list of the SFP., or (2) Come seee me, sign a
confidentiality agreement w/MYAPC AND have a copy for himself subject to
our agreement which says these materials must be returned or destroyed
within 120 days of Jan.15, 1999.
 On another matter...

         Happy Easter,

                                                     Ray

The failure of Ray Shadis (Friends of the Coast) to challenge numerous instances of licensee misinformation and deceptions presented at monthly Community Advisory Panel (CAP) meetings, as well as Ray's comments in the above email, raise a number of important issues.  The fact that I have many questions and some criticisms of Ray's role in the CAP meetings should in no way detract from the value and the importance of the years of hard work by Ray and Friends of the Coast in shutting down MYAPC.

1. Under what legal authority can FERC or the NRC withhold information pertaining to the series of fuel cladding accidents which have occurred at the Maine Yankee Atomic Power Company from 1973 -1998?
2. What is the purpose of making evidence of a series of nuclear accidents subject to a confidentiality agreement?
3. If members of a Community Advisory Panel charged with facilitating communication between the licensee and the general public have access to confidential information not available to the public aren't these CAP members then a component of the ongoing cover-up?
4. Why must the materials cited in Ray Shadis's email be returned or destroyed within 120 days of Jan. 15, 1999?
5. Why shouldn't the information on the exact contents of the spent fuel pool be made available to the general public?
6. How and why did fuel assembly rubble come to rest on the spent fuel pool bottom?
7. Who benefits from the maintenance of confidentiality about the origins of nonstandard fuel assemblies and other debris in the spent fuel pool?
8. Now that Ray Shadis has been initiated and accepted within the closed society of the nuclear industrial complex, hasn't Friends of the Coast been effectively coopted?  Why shouldn't Friends of the Coast now be called Friends of the Cover-up?

• Defective fuel (what is defective fuel, how common a problem is defective fuel and what documentation exists pertaining to the use of defective fuel by NRC licensees?)
• Copper and other metal fragments in reactor water systems which damage the fuel assemblies (e.g. Connecticut Yankee experience major fuel cladding failure due to metal fragments - what other NRC licensee's have had major fuel cladding failure accidents as a result of loose metal fragments in the water systems?)
• Grid to rod fretting (MYAPC experienced at least one episode of grid to rod fretting just prior to closing - how common is grid to rod fretting at other NRC licensed reactors and what role did it play at MYAPC in generating the debris at the bottom of the spent fuel pool?)
• Fuel assembly consolidation, which Ray refers to as pin packing experiments, have occurred at a number of NRC licensed reactors including MYAPC.  To what extent did the futile attempts at fuel assembly consolidation lead to the generation of debris in the MYAPC spent fuel pool or the loss of radiological controls documented by the GTS Duratek site characterization report at MYAPC?

April 9, 1999, the Center for Biological Monitoring sent the following letter to five newspapers in the Wiscasset area:

Dear Editor:

At the last Maine Yankee Atomic Power Company (MYAPC) Community Advisory Panel (CAP) meeting, I made the observation that the elevated levels of soil contamination outside the reactor containment bioshield (up to 156,000 pCi/kg [picocuries per kilogram] of ¹³⁷Cs [cesium]) documented by GTS Duratek was highly unusual, may have originated from fuel cladding failure and was indicative of a loss of radiological controls.  I also pointed out that the elevated soil contamination levels at MYAPC were 20 times higher than the peak values of contamination in discharge bay sediments at the Yankee Rowe (CT) reactor, where contamination is to be expected.  Uldis Vanags, State Nuclear Safety Advisor and Mike Miesner, MYAPC President, indicated that these levels of soil contamination were a normal part of any reactor's operations.  They also made the same assertion with respect to the soil contamination along the west side fence line, where peak values exceed 50,000 pCi/kg of  ¹³⁷Cs and contamination extends over an area in excess of 10,000 square feet.  Can Uldis Vanags or Mr. Miesner back up their assertion of "normal" operations by citing even one U.S. reactor at which similar levels of soil contamination have been documented?  If these levels are a result of "normal" reactor operations, then we have many more problems at reactors which are continuing to operate than has ever been acknowledged by the nuclear industry.

Yours truly,

H. G. Brack

184 State Street
State House Station 38
Augusta, ME  04333

Dear Uldis Vanags:

With respect to the enclosed letter to the editor, can you back up your assertion that the elevated levels of ¹³⁷Cs in the soil outside the reactor containment bioshield is "normal?"  Can you cite any specific NRC, NRC licensee or licensee contractor spectroanalyses of any soil samples exceeding the 156,000 pCi/kg peak value noted in the GTS Duratek survey?  The same applies to the +/-10,000 ft² of soil contamination along the west side fence line and the hot particle found on Bailey Point.  I certainly would be interested in reviewing any publications or surveillance reports that would lead you to feel that these levels of contamination were "normal."

Yours truly,

H. G. Brack

cc. Don Clark
Michael Miesner

The NRC has sent us a number of inadequate responses to questions we had about documentation on the Maine Yankee site.  Below is a copy of the Center for Biological Monitoring's reply.

Quality Assurance, Vendor Inspection, Maintenance and Allegations Branch
Division of Inspection Program Management
Office of Nuclear Reactor Regulation
Nuclear Regulatory Commission
Washington, DC  20555-0001

Dear Chief Quay:

I have been dissatisfied with various formulaic replies I have received from the Nuclear Regulatory Commission (NRC) in response to my observations about the debacle at the Maine Yankee Atomic Power Company (MYAPC).  I'd like to summarize what I have been writing about.

· Gross inadequacies exist at MYAPC and other NRC licensed reactors in the record keeping of radioactive waste inventories, projections and characterizations.

· These inadequacies include long-standing deficiencies in radiological surveillance procedures, historical site assessment and pathway analyses.

· Annual licensee environmental reports are too cursory to provide a sufficient database for residual radiation criterion evaluation or to overcome the above deficiencies.

· Inventories and characterization of current MYAPC reactor vessel dross, CRUD, hot particles and fission and activation product residues are not available for public evaluation and may not be known to the NRC or licensee decommissioning operations contractors (DOCs).

· Excessive and illegal secrecy surrounds information and data ranging from routine radiological incidents to the sources of debris in the MYAPC spent fuel pool.

· The NRC's reluctance and inability to document the source term of fuel cladding failure at MYAPC -- including quantities, pathways and destinations of fission products released by these incidents is the most glaring example of the NRC's failure to document the ultimate impact of licensee activities.

· Knowledge of current onsite and offsite fission and activation product inventories and pathways, including marine ecosystem inventories, is minimal and insufficient for residual radiation criterion evaluation.

· The failure to maintain adequate record keeping of radioactive waste inventories, pathways and destinations is one component of a more pervasive generic pattern of violations of 10 CFR Part 1 Section 10.4 and is manifested in a lack of public hearings, environmental impact statements and restricted public oversight of decommissioning expenditures and procedures.

· As a result, expenditure of hundreds of millions of dollars (+/- $500,000,000) in public funds proceeds merrily along under the guise of secrecy, proprietary information and an "authorized" licensee controlled Community Advisory Panel (CAP) whose members sign confidentiality agreements to withhold information which should be in the public domain.

· The Community Advisory Panel serves to thwart public access to review or oversight of radioactive waste inventories, characteristics, pathways, destinations or decommissioning costs and procedures.  The role the CAP plays at MYAPC is particularly reprehensible because the decommissioning operation contractor, Stone & Webster, is not really decommissioning a nuclear reactor but further assisting in the construction of a poorly characterized radioactive waste storage facility.  The CAP assists the NRC and MYAPC in evading the documentation of the legacy of MYAPC.

Formulaic NRC responses to the above observations are no substitute for accountability, accurate record keeping or public participation in the documentation of the legacy of radioactive wastes left at Wiscasset, Maine, by NRC licensee activities.  Repeated assertions by the NRC that all federal regulations are being followed at the Wiscasset facility by the NRC and MYAPC cannot alter the statutory requirement that accurate record keeping be kept of the inventories, pathways and destinations of MYAPC-derived radioactive waste.  Neither the public nor the NRC know the current location of wastes released by fuel cladding failure and other "incidents" or "events" at MYAPC.  It is the NRC, mired in a culture of complacency and self-deception, that is unable to observe or acknowledge its own noncompliance with existing federal statutes.

Yours truly,

H. G. Brack

cc.  Shirley Jackson
John Zwolinski
Michael Webb
Michael Masnik
Seymour Weiss
Ron Bellamy
NRC Commissioners
CAP members

Today, CBM received the following email:

To: Skip Brack <sbrack@acadia.net>
From: Raymond Shadis
Subject: Re: fuel cladding - NRC response to MYAPC issues

Dear Skip,
 I asked Mary Ann to release a copy of the spent fuel pool inventory (w/caveats) I'm sending a copy of it to you. There is a lot of nasty and interesting trash in the pool. I believe some of it leads to criticality questions under some accident considerations. About the CAP. You are absolutely correct, the CAP is a essentially a public relations group. It's in the group's charter which I'm sure you have read. It is not an oversite group. Never was. That has to be made clear to everyone as it is NRC's
intention to substitute informal bodies and proceedings for adjudicatory processes and tests of truth. Except for those people (3) who reviewed some decommissioning contract bids in advance, there are no confidentiality agreements with CAP members. As a litigant, Friends of the Coast, is bound by certain confidentiality rules regarding discovery materials, as ordered
by the Federal Energy Regulatory Commission judge. One item I'd like to tell you about. It is an old  memo from a DC consulting firm to MYAPC which, in one section, chortles about the divisions, jealousies, territoriality, and competition among national environmental groups dealing with nuclear power questions. I think this is a parable for our local and New England-wide situation. Now, I personally, thrive on criticism, but I think you ought to find out what Friends of the Coast has on the agenda before you jump on us in public. I would be glad to meet with you or take a phone call most anytime. I truly appreciate your ongoing interest in the MYAPS decommissioning, and your work and generousity over the years. PLease
don't become discouraged ( or cranky with your allies) when it seems people aren't listening. It is, I'm afraid, the meat and potatoes of advocacy.Please, for the sake of fairness, circulate this response to whomever was served the letter below. Thanks for being there, Skip....................................................................................Ray

Today, CBM has posted a citation for the Maine Yankee Inspection Report 98-03 in RAD12: Maine Yankee: Section 2: Public Safety Issues.  Note there is documentation of an onsite area of contamination from a 1988 leak.  It is particularly interesting that the licensee has represented that the site is clean when in fact here is an area of residual radiation yet to be remediated.

April 26, 1999:

Today, CBM has posted a citation for the Proceedings of U.S. NRC Advisory Committee on Reactor Safeguards Meeting on Reactor Fuels, Onsite Fuel Storage, and Decommissioning, Friday, April 24, 1998, in RAD11 Section 4: Nuclear Power Plants: Spent Fuel Cladding Failure.  Included in the annotations is a list of observations which pertain to the current situation at MYAPC.

The Center for Biological Monitoring issued the following press release pertaining to the recent disclosure of the presence of 66 failed fuel assemblies in the Maine Yankee Atomic Power Company spent fuel pool.  The letters reprinted below discuss some of the issues involved in this discovery and were mailed to the recipients prior to this electronic posting.  As nuclear accidents go, the several episodes of fuel cladding failure, which the spent fuel pool inventory documents, may have little health physics impact. The significance of these failures lies instead with the inability of the Nuclear Regulatory Commission to understand and document these breaches of a fission product barrier (the fuel cladding) at the times that they occurred.  Even at the time of the compilation of the MYAPC spent fuel pool inventory (1998), it is clear from the documents released by the Community Advisory Panel that neither the NRC nor the licensee have any real understanding of the amount of radioactivity released into the reactor containment through loss of fuel assembly contents.  Even more significant is the Nuclear Regulatory Commission's reluctance to admit that fuel cladding failure is a form of a nuclear accident and the most significant probable risk (as in "probabilistic risk assessment") accompanying the day to day operations of a nuclear reactor.  LORCAs, reactor vessel embrittlement accidents, main line steam breaks and other forms of theoretical accidents may be more serious in their health consequences, but they are also more unlikely than the more ubiquitous fuel cladding failure accidents that can now be documented to have occurred at New England reactors in the last several decades.  The NRC itself has made a compelling argument for the prevalence of fuel cladding failure accidents (always called "leakage" by the NRC) in response to the Union of Concerned Scientist's 1998 petitions about fuel failure discussed in the letters and documents below.  The fuel cladding failures at MYAPC, Seabrook, Perry and River Bend are just little accidents, but the lies which accompany these losses of radiological controls hide the fact that there is a lot of similar fuel cladding failures that have happened, are happening or will happen at reactors outside of New England.  In the case of the Connecticut Yankee reactor at Haddam Neck, the cumulative losses from fuel cladding failures probably constitute the largest nuclear accident to happen in the United States since Three Mile Island.  We may conclude that the fuel cladding failure is normal but it is only normal in the sense that when you drive on an icy road you are likely to skid and have an accident.  It may not be a fatal accident, but it is still an accident.  In the case of the NRC, we need more truthful documentation about what happens to the long-lived spent fuel wastes once fuel cladding failure allows the spread of fuel pellets throughout the reactor containment.  The failure to document these small accidents, which in their cumulative impact as at Connecticut Yankee, can amount to more than just a small accident, is part of a larger NRC failure to document the environmental impact of reactor operations, decommissioning and "unusual events" under its federal jurisdiction.

Re:  Fuel cladding failure accidents at the Maine Yankee Atomic Power Company (MYAPC) in Wiscasset, Maine
(Also at Connecticut Yankee in Haddam Neck, CT and the Seabrook plant in Seabrook, New Hampshire)

Ray Shadis (Friends of the Coast), MYAPC staff and the Community Advisory Panel (CAP) should be commended for releasing for public review the MYAPC inventory of “spent fuel and other radioactive materials stored in the Maine Yankee spent fuel pool” MYPS 101, April 16, 1998, rev. 0.  This material has been up to now “confidential.”

This inventory contains the following information:  Out of 1,434 spent fuel assemblies now contained in the spent fuel pool, at least 15% are nonstandard and include the following:

· 66 fuel assemblies with “confirmed failure”
· 10 are consolidated or otherwise damaged
· 50 exhibit “physical damage”
· 18 have fuel rods replaced
· 80 have hollow rods (the present location of the spent fuel originally in these rods is not indicated in this inventory)
· 1 fuel rod is cemented into a pipe
· 1 fuel rod is stuck in a conduit
· 1 fuel rod was removed during a “1992 disposal campaign”
· in addition to this inventory of fuel assemblies in the spent fuel pool, this report indicates five filters “determined to be unsuitable for shipment due to dose rates” are in the spent fuel pool and contain loose fuel pellets derived from vacuuming up the debris released during the failure of the 66 fuel assemblies
· numerous other filters are within the fuel pool and also contain fuel pellets but as of 1998 the number of these is not known
· 61 additional filters are contained in trash baskets in the spent fuel pool which also contain solid wastes from thermal shield positioning pin repairs; these filters may also contain spent fuel pellets derived from the fuel cladding failure accidents at MYAPC

Summary:

Minor grid-to-rod fretting fuel assembly damage and pinhole leaks are a normal component of reactor operations, as the NRC has made clear to the Union of Concerned Scientists (UCS) in response to its petitions submitted to the NRC on September 25, 1998 and November 9, 1998, re: failed fuel assemblies at the River Bend, LA and Perry, OH, reactors.  The NRC response to the UCS petitions is dated April 18, 1999, and should be reviewed by all persons concerned with fuel failure.  The NRC is emphatic in insisting that fuel “leakage” is a normal part of reactor operations, but the NRC response to the UCS is also a model of equivocation and sophistry in that it does not differentiate between “leakage,” a word repeated dozens of times in the NRC response, and “failure,” the concern of the UCS petition.

In the case of MYAPC, 66 failed fuel assemblies with spilled spent fuel pellets throughout the containment; this is a radically different issue than the 50 leaky damaged fuel assemblies, where no fuel pellets may have escaped and where emissions are limited to noble gasses, tritium and ¹³¹I.  Each fuel assembly contains an excess of 100,000 curies (Ci) of long-lived spent fuel waste.  If 10% of this radioactivity was released during fuel cladding failure accidents, 660,000 Ci of spent fuel waste would have the following potential destinations:

· vacuuming and water system filters now in the spent fuel pool as noted above
· filters and resin beads shipped to Barnwell, SC as class B low-level waste
· spent fuel-derived pellets still lodged in inaccessible areas of the containment
· fuel pellets and pellet-derived fission products released outside of the reactor containment pressure boundary, but still within reactor water systems (piping, reactor water storage tank, other water system tanks, etc. as indicated by elevated fission product activity in the cursory GTS Duratek site characterization smear sample spectroanalyses)
· fuel cladding failure-derived radioactivity released through stack emissions (e.g. tritium, cesium iodide? etc.) and in water systems leaks 1984, 1988, etc.
· free released radioactivity during normal plant discharges to Montsweag Bay, during decommissioning reactor containment decontamination and water systems tank discharges

The actual amount of radioactivity released during fuel cladding failure accidents at MYAPC is unknown.  The NRC has demonstrated gross negligence in the documentation of the source term (quantities of accident-derived effluents) of fuel cladding failures at MYAPC including all of the above potential destinations in the rush to minimize MYAPC owner and stockholder liability for the costs of the radioactive legacy of the MYAPC reactor.  The NRC and the licensee have skipped the historical site assessment phase of reactor decommissioning in the hope that no one will request documentation of the accidents of the past.  The release of this proprietary information by MYAPC and the Community Advisory Panel is a giant step in confronting and documenting fuel cladding failure accidents at all US nuclear reactors.

4.0    Table A.2 contains a list of fuel with known failures. With the exception of assembly R033, the nature of the failures are considered to be gross cladding defects. Other fuel assemblies may also have failed fuel rods.

5.0    Table A.3 contains a list of those fuel assemblies including consolidated assemblies, that have vacancies in their arrays. This table also includes information on the consolidated assemblies.

6.0    Table A.4 contains a list of assemblies with known damage or physical alterations. None of the conditions is considered to be limiting for dry storage but may require additional review.

7.0    Table A.5 contains a list of assemblies that have been repaired. The original failed fuel pins were replaced with either fuel rods or dummy rods prior to continued exposure. Batch U assemblies did not receive additional exposure.

8.0    Table A.6 contains a list of assemblies that were modified to replace the original poison pins with hollow, floodable zirc rods. These assemblies received additional exposure after modification.

9.0    Maine Yankee has two failed rod containers. One is an designed container having roughly the same dimensions as a fuel assembly. The second is a fuel assembly cage used to store failed rods during early repair campaigns.

10.0    Several fuel assemblies have defective fuel rods stored in their guide tubes.

OTHER RADIOACTIVE MATERIAL

All or part of this material may be classified as greater than Class C radioactive waste.

1.0    Table A.7 contains information on the tri-nuke filters stored in the spent fuel pool. Not all of the filters believed to be stored in the pool have been enumerated.

2.0    Table A.8 contains information on solid material waste that is stored in the spent fuel pool.

3.0     Table A.9 and Figure A.2 provide information on 168 Control Element Assemblies (CEA) stored in the spent fuel pool.

4.0    Figure A.3 provides information on 8 CEA plugs stored in the spent fuel pool.

5.0    Figure A.4 provides information On 5 neutron sources (3 Pu-Be, 2 Sb-Be) stored in the spent fuel pool.

6.0    Table A.10 and Figure A.5 provide information on the 138 incore instrument thimbles stored in the spent fuel pool.

7.0    Table A.11 and Figure A.6 provide information on in-core instruments stored in the spent fuel pool.

8.0    Figure A.7 provides information on surveillance capsules stored in the spent fuel pool. Maine Yankee reserves the right to redirect some or all of the surveillance capsules as required to support decommissioning

9.0    Table A.12 provides the inventory of the trash baskets stored in the spent fuel pool.

10.0  Table A.13 provides information on nonfuel special nuclear material stored in the spent fuel pool.

11.0  Table A.14 provides information on each fuel cycle (core history).

The following filters were utilized with a TriNuke vacuum system at Maine Yankee. The filters were determined to be unsuitable for shipment due to dose rates during a disposal campaign in late 1992. Each filter is housed in a stainless mesh container. Efforts may be possible to consolidate the contents or repackage the filters for storage.

  Filter         Maximum Dose
 Number          Reading          Waste Stream and Comments

 1                  2000R       SFP floor clean up; may contain loose fuel pellets
 2                    100R       SFP floor clean up; may cantain loose fuel pellets
 3                  1000R       SFP floor clean up: may contain loose fuel pellets
 4                    200R       SFP floor clean up: may contain loose fuel pellets
 5                    200R       Machining debris from thermal shield repair
 6                      25R       SEP floor clean up: may contain loose fuel pellets

Four (4) specially designed filters were used to capture debris from Electro Discharge Machining (EDM) during repair of the thermal shield postioning pins. Dose rates on these filters were unavailable at the release of this document. These filters were designed to be stored in the SFP storage racks. Other filters containing radioactive material may also exist in the spent fuel pool.

     INVENTORY OF TRASH BASKETS IN MAINE YANKEE SPENT FUEL POOL

TRI-NUKE FILTERS, STORED IN SPENT FUEL POOL

Trash can in SFP           Source of Filters

BT2            5 filters on November1995 or cutup ICI's

BT4            5 filters from vacuuming upender pit and thermal shield repair Cycle 14 refueling [1994]

BT9            5 filters on November1995 or cutup ICl's (One cover bolt is stripped)

BT10          5 filters on November1995

BT13          5 filters on November1995

BT14          5 filters on November1995

BT15          5 filters on November1995

BT17          4 filters cycle 16 cavity purification and vacuuming on top of fuel (6/11/97)

BT19          5 filters on November1995

BT20          4 filters on November1995

BT21          4 filters on November1995, and debris bucket with 60 R/hr piece of metal
BT23          4 filters (1 from vacuuming, others from cavity upender pit vacuuming)
BT25          5 filters on November1995

Dear Governor Hodges:

I am enclosing a press release we have issued today containing information about two or more fuel cladding failure accidents at the Maine Yankee Atomic Power Company (MYAPC) in Wiscasset, Maine.  The first occurred in the first two cycles of reactor operation, 1/8/72 - 5/2/75, and the second occurred in the final cycle of operation, 1/15/96 - 12/ 6/96; the latter was probably responsible for the plant closure in 1997.

Please note in the enclosures that the licensee, in its confidential 1998 inventory of the spent fuel pool, lists 66 failed fuel assemblies in addition to 159 damaged or otherwise nonstandard fuel assemblies.

I have a query for your office and I was wondering if you would consider sending me a written response to the questions.

Please note that each of MYAPC’s fuel assemblies contain in excess of 100,000 curies (Ci) of long-lived spent fuel wastes, the six most ubiquitous of which are ¹³⁷Cs (half life [1/2 T] = 30 years), ⁹⁰Sr (1/2 T = 29 yr), ²³⁸Pu (1/2 T = 89 yr), ²⁴⁰Pu (1/2 T = 6,260 yr), ²³⁹Pu (1/2 T = 24,400 yr) and ²⁴¹Am (1/2 T = 458 yr).

If the 66 failed fuel assemblies leaked 10% of their contents then approximately 660,000 Ci of long-lived spent fuel wastes were released in the MYAPC containment, having escaped the first of three fission product barriers (the fuel cladding.)  The truth of the matter is that neither I nor the NRC or the licensee have the foggiest idea of the actual amounts of radioactivity released by these accidents, but a 10% dispersion rate seems reasonable for failed fuel assemblies.

The confidential MYAPC spent fuel pool inventory notes numerous filters still reside within the spent fuel pool which are too contaminated (the dose rate is too high) to be shipped to the Barnwell facility as low-level waste.  The 1998 inventory makes clear the fact that the licensee really has no idea how many filters are actually at the bottom of the spent fuel pool, nor do they have any idea of the radiological content of these filters.  The inventory does make clear, however, the fact that fuel pellets escaped the failed fuel assemblies and were spread throughout the reactor containment.  These pellets were then recovered by a combination of vacuuming and filtering the containment water.  Some of the lost pellets were actually vacuumed off the top of the fuel assemblies after one of the accidents.

The questions I have are:

· Does the state of South Carolina maintain a quantitative record of the radiological contents of filters and resins sent from MYAPC to the Barnwell facility (class B wastes in HICs - high impact containers)?  It is my understanding that none of these accident-derived wastes would qualify as class A wastes, though some may have been sent to Barnwell as class C wastes.
· It must be of interest to someone that low-level wastes being sent to Barnwell include filters containing significant quantities of MYAPC fuel cladding failure accident-derived long-lived spent fuel wastes.  Can the state of South Carolina give any estimate of the amount of radioactivity sited at Barnwell which is derived from the fuel cladding failure accidents at MYAPC, in contrast to the normal flow of operational low-level wastes (booties, gloves and the more innocuous everyday waste products of a nuclear reactor)?  Certainly, the main question during the decommissioning process here in Maine is:  What quantities of long-lived spent fuel wastes were released during the accidents at MYAPC, how much remain in the filters in the MYAPC spent fuel pool, and how much spent fuel wastes were sent to Barnwell as “low-level” wastes?
· During the upcoming decommissioning process Barnwell will be the recipient of a significant amount of fuel cladding failure accident-derived radioactivity.  If you don’t have records of past shipments, in view of the high radiological content of filters and resins which may arrive in the future, will you maintain record keeping of future waste inventories and will you make these records available to the public?
· The same question would also apply to the future shipment of the intact reactor vessel containment which will likely include a certain amount of dross including hot particles, CRUD and activation products.  If MYAPC is not successful in removing the remaining fuel cladding failure-derived spent fuel pellets from the containment during decommissioning, would you also share with us the inventories of dross and spent fuel pellets within the reactor containment after the GTCC internal components are segmented and removed?
· Are you aware that a much larger series of fuel failure accidents have occurred at Connecticut Yankee at Haddam Neck?  The potential source term (quantities of radioactivity released) of the fuel failure accidents at Haddam Neck is in the millions of curies, most of which were also vacuumed and filtered.  Do you have any data on the amounts of Connecticut Yankee fuel cladding failure accident-derived wastes which were sited at Barnwell?

Please be aware there has also recently been a fuel cladding failure accident at the Seabrook, New Hampshire, reactor in the summer of 1998.  Some of the long-lived spent fuel pellets and debris may also be destined for Barnwell.  I would just like to express my gratification that the state of South Carolina is willing to accept fuel cladding failure accident-derived long-lived spent fuel wastes for disposal at the Barnwell facility.  The NRC is emphatic in insisting that any and all such nuclear accidents, which can now be documented to have taken place in New England reactors, are well within the regulatory guidelines of 10 CFR Part 20, which apply to residents in New England as well as South Carolina.  The guideline for ¹³⁷Cs for members of the general public is that the annual limit of intake of ¹³⁷Cs not exceed 10,000 nanocuries.  There are no other quantitative or concentration-based guidelines other than for liquid effluents, which can be diluted by mixing, so that it is obvious that large quantities of fuel cladding failure accident-derived long-lived wastes can be generated at New England reactors and sited in low-level waste landfills such as that at Barnwell without violating any federal regulations.  Human curiosity nonetheless raises the question:  how many curies of spent fuel wastes from accidents at New England reactors have been sited at the landfill in Barnwell in the form of filters and resins contaminated with fuel assembly-derived isotopes?  I’d like to share your response to my questions with interested parties in Maine and with NRC staff who seem particularly reluctant to quantify the amounts of radioactivity released during fuel cladding failure accidents (not pinhole leakage, but cladding failure where spent fuel pellets are dispersed throughout the reactor containment).  Thank you for your attention in this matter.

Yours truly,
H. G. Brack

P. S. Most of the impact of the Chernobyl accident in the European community was well within the regulatory guidelines of 10 CFR Part 20.

Dear Congressman Markey:

I’d like to bring your attention to the enclosed press release and letter to Governor Hodges of South Carolina.  Both Maine Yankee Atomic Power Company (MYAPC) and NRC staff have insisted to me that elevated levels of soil contamination discovered during a cursory site characterization at MYAPC are absolutely normal results of reactor operations.  So, too, has the NRC claimed in response to the Union of Concerned Scientists (UCS) petition about fuel cladding failure that fuel cladding leakage is perfectly normal.  I agree with the latter assertion, but note that the NRC never really addressed the issue of fuel cladding failure, which is radically different from fuel cladding leakage, in that during fuel cladding failure accidents the fuel pellets spill out of the assemblies and move throughout the reactor containment.  Once they are spilled, they can only be retrieved via vacuum and water system filters which then are disposed of (in most cases) as “low-level wastes” at Barnwell, SC.  While the accident at MYAPC is relatively small (+/-600,000 Ci?) there has been a much larger accident at the Connecticut Yankee Haddam Neck facility which has been the subject of NRC historical site assessment review.  The startling fact emerges from NRC review of the Connecticut Yankee accident that any and all fuel cladding failure accidents and resulting emissions are always within the regulatory requirements of 10 CFR Part 20.  NRC reports are consistently characterized by a near total lack of nuclide-specific, media-specific data (e.g. Bq/kg) and a plethora of rhetoric.  It is now obvious that the NRC is totally incapable of executing comprehensive accurate assessments of the actual radiological impact of nuclear accidents at US reactors which are always called events or occurrences and are never documented in a straight-forward manner.  The NRC has thousands of employees and decades of experience in obsfucating the radiological impact of reactor operations, decommissioning and accidents such as the fuel cladding failures at New England reactors.  We now have the urgent need to delegate accurate, truthful and plain-spoken radiological surveillance to some independent entity which would be similar in its function (and also in its ethical independence from conflicts of interest in supervising a for-profit industry) to the Defense Nuclear Safety Board.  Please take a public stand on this issue and lead the way in Congress in establishing independent review and reform of the NRC’s failed oversight and inability to execute credible documentation of the radiological impact of the nuclear reactors under its supervision.

Yours truly,
H. G. Brack

Dear Ron Cole:

Would you be so kind as to provide to the Center for Biological Monitoring for public comment and review a description of your proposed methods and plans for documenting the inventories of radioactivity in materials removed from the Maine Yankee Atomic Power Company during the upcoming decommissioning process?  It would be helpful if in your descriptions you could use standard reporting units and express contamination in becquerels per kilogram (Bq/kg), becquerels per meter squared (Bq/m²) or dpm/100cm², rather than resort to the usual rhetorical device of indicating that the dose rate is well within federal regulations.  CBM is including this letter in a press release on fuel cladding failure accidents at New England reactors in the hope that Stone & Webster will be forthcoming, plainspoken and straight-shooting in its documentation of reactor-derived radioactivity encountered in the decommissioning process.  I do not suggest you use the Nuclear Regulatory Commission as a role model in this endeavor.

Thank you for your excellent presentation at the last CAP meeting on low-level waste transport.  The only point you didn’t mention was that 99.5% of reactor-generated radioactivity will remain onsite after the decommissioning is completed.  We all share the hope that the federal government will eventually resolve the waste storage and disposal issues which now make construction of independent spent fuel storage installations (ISFSIs) a necessity.

Yours truly,
H. G. Brack
cc. Don Clark

Dear Director Zwolinski:

Thank you for your May 4, 1999, letter.  I don’t have any questions or criticisms of your definition of nonstandard fuel; your explanation of what the licensee was referring to as nonstandard fuel is very helpful and I look forward to hearing more about what percentage of MYAPC fuel assemblies qualify for the UMS design once fuel inspection is completed.

I must point out, however, that I have spent several hours going over Samuel Collin’s response to the Union of Concerned Scientists about the issue of leaking fuel assemblies prior to receiving your second copy of his 39 page director’s decision.  You will note in the enclosed press release that I object strongly to Mr. Collin’s failure to differentiate between leaking fuel assemblies and failed fuel assemblies that then scatter fuel pellets throughout the reactor containment.  In my opinion, he never really satisfactorily addressed the Union of Concerned Scientists’ petition.

You will also note excerpts of the 1998 MYAPC spent fuel pool inventory which indicates 66 fuel assemblies have failed in addition to the numerous other damaged, altered and reconstructed fuel assemblies and related trash baskets in the spent fuel pool.  I was quite amazed to see the wide variety of equipment and debris stored in MYAPC’s spent fuel pool in addition to the “standard” fuel assemblies.  I would take exception to the last section of your letter:  clearly the collection of radioactive garbage and failed fuel assemblies in the MYAPC spent fuel pool is compelling and, in fact, absolutely incontrovertible evidence of periodic loss of radiological controls.  You imply in your letter that such loss of radiological controls has never occurred at MYAPC and that “the radiological monitoring programs required by the NRC are sufficiently comprehensive to provide an adequate assessment of the radiological impact of plant operation on the offsite environment.”  You could hardly provide a better illustration of why so many of the NRC’s assertions and claims about minimal environmental impact and nonexistent loss of radiological controls have zero credibility.  In view of the soil contamination documented outside the reactor bioshield and in supposedly unaffected areas in and around the Wiscasset reactor and the obvious problems with spent fuel pellets in reactor water system’s filters, it is now clear that the NRC cannot be trusted to document the environmental impact of reactor operations, decommissioning or “events” such as fuel cladding failure.  One can argue that both fuel cladding leakage and fuel cladding failure are a result of “normal” reactor operations but you cannot ignore federal law and assert that these failures and leaks do not need to be documented.

MYAPC leaves the citizens of the state of Maine with a costly legacy of nucle