ML110540570
ML110540570 | |
Person / Time | |
---|---|
Site: | Davis Besse ![]() |
Issue date: | 02/23/2011 |
From: | Beyond Nuclear, Citizens Environmental Alliance of Southwestern Ontario, Don't Waste Michigan, Green Party of Ohio |
To: | NRC/SECY |
SECY RAS | |
References | |
RAS 19635, 50-346-LR, ASLBP 11-907-01-LR-BD01 | |
Download: ML110540570 (74) | |
Text
February 23, 2011 UNITED STATES OF AMERICA NUCLEAR REGULATORY COMMISSION Office of the Secretary In the Matter of: ) Docket No. 50-346 FirstEnergy Nuclear Operating Company )
Davis-Besse Nuclear Power Station, Unit 1 )
(Regarding the Renewal of Facility )
Operating License NPF-003 for a 20-Year Period) )
)
JOINT INTERVENORS COMBINED REPLY IN SUPPORT OF PETITION FOR LEAVE TO INTERVENE (CORRECTED VERSION)
Now come Beyond Nuclear, Citizens Environment Alliance of Southwestern Ontario, Dont Waste Michigan, and the Green Party of Ohio, (hereafter Petitioners) and hereby make their CORRECTED reply in support of their Petition for Leave to Intervene submitted on December 27, 2010 in this proceeding in accordance with the ASLBs 2/17 /2011 order.
REPLY TO FENOC ASSERTION OF PETITIONERS UNTIMELY SUBMISSION At pages 11-13 of its Answer, FENOC accuses Petitioners of not timely filing their Petition for Leave to Intervene. Significantly, FENOC makes no credible argument of prejudice to its interest as a result of the shortly before, and shortly after midnight submission by Petitioners on December 27-28, 2010. Moreover, the NRC staff does not challenge the timeliness of Petitioners filing.
As detailed in the attached Declaration of Kevin Kamps, Petitioners experienced major difficulties with NRCs Electronic Information Exchange system on the night of the December 27, 2010, despite their good faith efforts to attain compatible computational status, and having earlier obtained assurances from the EIE Help Desk that everything was in good order. Joint petitioners pro se point person for this proceeding is Kevin Kamps of Beyond Nuclear. He contacted the EIE Help Desk a week in advance of the December 27, 2010 filing deadline, and spent an extended period of time on the phone and his computer with the EIE Help Desk obtaining his EIE digital certificate for the Davis-Besse proceeding, making sure that it was in good order.
On the evening of the December 27, 2010 deadline, Kevin Kamps again contacted the EIE Help Desk at 7:00 p.m., ahead of its closure at 8:00 p.m., to make sure that his digital certificate was in good order and that everything would function smoothly for the filing due before midnight. He spoke with Debra at the EIE Help Desk, who assured him that the certificate was fine and that the filing should proceed smoothly.
Once Kamps had the petition and request in final form, and all exhibits in order and ready to submit, he began the process of submission at 11:00 p.m. It quickly became apparent that the EIE system was not working properly. Kamps was only able to get up to the signature page of the EIE system, but was unable to get beyond it, no matter how he tried to.
As an emergency contingency, Kamps contacted his co-worker Paul Gunter, who also had a digital certificate for the Davis-Besse proceeding. Fortunately, Gunter was able to submit Petitioners documents into the system after racing to the Beyond Nuclear office (on Christmas holiday; Beyond Nuclear takes the Christmas to New Years time window as holiday) after 11 p.m. in order to do so. Kamps transmitted the complete filing, including all exhibits, to Gunter via email, then called the NRC Secretarys office and the EIE Help Desk to leave timely mes-sages about the problems he experienced in filing. Gunter handled the filing through the NRC EIE as quickly as he was able.
It should also be noted that all of the exhibits, as well as Dr. Al Compaans curriculum vitae and declaration, were embedded as links in the Microsoft Word version of the Request for Hearing and Petition for Leave to Intervene, which FENOC itself admits (FENOC Answer p.
- 11) was submitted before the midnight deadline.1 Thus, all exhibits, as well as Dr. Compaans supporting documents, were available to FENOC in a timely fashion.
Kamps spent hours the next day, as delineated in his Declaration, working with EIE Help Desk staff, who verbalized their own frustrations with the system and who questioned whether there was a software problem that had corrupted Kamps electronic certificate. After noon on December 28, Kamps submitted two exhibits that the EIE system had earlier rejected, after the Help Desk staff identified the filing problem.
Notably, shortly after 8:00 a.m. on December 28, Kamps spoke to NRC staffer Rebecca Gitter, who apologized to him for the difficulties with the EIE system, saying, This is something others have experienced. She added that this is a common problem others have had at the submission stage. Kamps Declaration, p. 2.
Obviously, the EIE Help Desks assurances to Kevin Kamps on December 21 and 27, 2010 that his digital certificate was in good order and he would be able to submit documents to 1
The text of the Petition itself, the standing declarations, and eight exhibits (Exhibits 1, 2, 5-7, and 9-11) were submitted by the requisite deadline on December 27, 2010.
the EIE system were incorrect. Kamps made good faith attempts to file before the midnight deadline, followed by Paul Gunters successful filing of several key documents ahead of midnight and Gunters submission of 73 items in all, one at a time, into the EIEs Davis-Besse docket. Kamps immediately followed up the next day at the commencement of NRC business hours to straighten out the glitch and filed the remaining two exhibits as soon as the problems were identified and solved by the Help Desk. Kamps Decl. pp. 2-3.
Petitioners submit that they have demonstrated good cause to have their Petition deemed timely submitted and filed. The first factor of those specified in 10 C.F.R. § 2.309 (c)(1), the timeliness rule, is whether there exists "good cause, if any, for the failure to file on time." Cincinnati Gas and Electric Co. (William H. Zimmer Nuclear Power Station), ALAB-595, 11 NRC 860, 862 (1980). In considering the "good cause" factor, a strong excuse for lateness will attenuate the showing necessary on the other factors of 10 C.F.R. § 2.309 (c). Puget Sound Power & Light Co. (Skagit Nuclear Power Project, Units 1 and 2), ALAB-523, 9 NRC 58, 63 (1979). See also Florida Power and Light Co. (St. Lucie Nuclear Power Plant, Unit No.
2), ALAB-420, 6 NRC 8, 22 (1977), affirmed, CLI-78-12, 7 NRC 939 (1978). While a satisfactory explanation for failure to file on time does not automatically warrant the acceptance of a late-filed intervention petition, because those additional factors specified under 10 C.F.R. § 2.309(c) must also be considered, it remains that where a late filing of an intervention petition has been satisfactorily explained, a much smaller demonstration with regard to the other factors of 10 C.F.R. § 2.309 (c) is necessary than would otherwise be the case. Wisconsin Public Service Corporation (Kewaunee Nuclear Power Plant), LBP-78-24, 8 NRC 78, 83 (1978).
Finally, petitioners proceeding pro se will be shown greater leeway on the question of whether they have demonstrated good cause for lateness than petitioners represented by counsel.
Maine Yankee Atomic Power Co. (Maine Yankee Atomic Power Station), LBP-03-23, 58 NRC 372, 378 (2003). That principle should be applied to the facts here.
Against Petitioners account of what went wrong with the filing - most of which can be verified through NRC Help Desk records and the Secretarys phone log - FENOC can make no credible showing of prejudice. Unless, that is, FENOCs legal staff awaited the filing at 12:01 a.m. December 2010 in order to immediately begin work on their response to the Petition for Leave to Intervene. FENOCs objection is frivolous, hypertechnical, and rote. There is no issue as to the genuine efforts by Petitioners to timely file through an inexperienced, pro se coord-inator in his first adjudicatory filing situation. This is a non-issue, and Petitioners pray the ASLB ignore the Applicants pointless objection.
REPLY TO CLAIMED LACK OF STANDING OF CITIZENS ENVIRONMENT ALLIANCE OF SOUTHWESTERN ONTARIO In an argument which disrespects the workload facing the ASLB, both FENOC and the NRC Staff contrive to object to the standing of Citizens Environment Alliance of Southwestern Ontario, a Windsor, Ontario organization. They claim (FENOC Answer p. 9; Staff Answer p. 6),
that the CEAs two declarants, Rick Coronado and Derek Coronado, live at a Windsor address that according to respondents measurement is 300 feet outside of the 50-mile radius (that is, 50.024 miles) , hence outside the radius of proximity which is customarily presumed to establish standing to petition the NRC in license extension cases.
FENOC claims to have measured (FirstEnergys Answer p. 9 fn. 31) from an aerial map of the Davis-Besse site by first locating the Davis-Besse site address . . . and then manually moving the location marker to the containment building, which is clearly visible using the Hybrid . . . viewer. FENOC does not state whether it measured from the precise center of the containment building. And FENOC makes no demonstration that the 50-mile proximity pre-sumption is not, in fact, measured from the boundary fence at Davis-Besse. Nor do the Staff or FENOC address the issue of whether being inside a 50 mile radius from the Davis-Besse water outflow pipe, which easily extends several hundred feet into Lake Erie and which in some accident scenarios could dump prodigious amounts of highly-radioactive water into the Lake which would evaporate into the air, would not confer standing on CEA under the proximity presumption.
The hairsplitting implicit in the respondents global positioning overkill postulates a reading of the proximity presumption to which the Commission does not subscribe. In Calvert Cliffs 3 Nuclear Project, LLC and Unistar Nuclear Operating Services, LLC (Combined License Application for Calvert Cliffs, Unit 3), CLI-09-20, the Commission stated:
In practice, we have found standing based on this proximity presumption if a petitioner (or a representative of a petitioner organization) resides within approximately 50 miles of the facility in question. (Emphasis supplied)
Id. at 5.
Pertinent emergency preparedness documents on which the proximity presumption is based refer to the 50-mile radius as approximate. See Davis-Besse Nuclear Power Station Emergency Plan Implementing Procedure, RA-EP-02245, Protective Action Guidelines, Revision 01 (2003), ADAMS #ML030220458, p. 4, Definitions:
3.5 EMERGENCY PLANNING ZONE(S) -The two zones that are established around a nuclear power station in which predetermined protective actions plans are needed.
3.5.1 The first zone has an approximate radius of 10 miles for the plume exposure pathway.
3.5.2 The second zone has an approximate radius of 50 miles for the ingestion exposure pathway. (Emphasis supplied)
See also December 21, 1979 letter, NRC to licensees (ADAMS #ML073521046):
Briefly, the proposed rule would . . . (3) Require extending emergency planning considerations to the emergency planning zones (i.e., within the approximate 10 and 50 mile radii around the plant). (Emphasis supplied)
It bears noting that the CEA office in Windsor is located at 1950 Ottawa Street,2 and using the same calculator as FENOC did, when the Coronados are at work or meeting in that office, they are within 49.751 miles of the containment building at Davis-Besse. The proximity presumption applies if the petitioner lives within, or otherwise has frequent contacts with, the zone of possible harm from the nuclear reactor. Paina Hawaii, LLC, LBP-06-4, 63 NRC 99, 105 (2006), (citing Fla. Power & Light Co. (Turkey Point Nuclear Generating Plant, Units 3 and 4),
LBP-01-6, 53 NRC 138, 146 (2001), affd on other grounds, CLI-01-17, 54 NRC 3 (2001).
Indeed, the NRC has entertained a proximity presumption of greater than 50 miles.
Philadelphia Electric Co. (Limerick Generating Station, Units 1 and 2), LBP-82-43A, 15 NRC 1423, 1447 (1982) (residence more than 75 miles from a plant will not alone establish an interest sufficient for standing as a matter of right), citing Dairyland Power Cooperative (LaCrosse Boiling Water Reactor), ALAB-497, 8 NRC 312, 313 (1978); Public Service Co. of Oklahoma (Black Fox Units 1 and 2), ALAB-397, 5 NRC 1143, 1150 (1977).
Rick and Derek Coronado have produced sufficient evidence to warrant their being allowed to intervene on behalf of Citizens Environment Alliance of Southwestern Ontario.
REPLY AS TO CLAIMED LACK OF GERMANENESS OF DONT WASTE MICHIGAN FENOC maintains (Answer p. 10) that Dont Waste Michigan fails to demonstrate that 2
http://www.citizensenvironmentalliance.org/about_cea.html the interests it seeks to protect are germane to its purpose, arguing that Dont Waste Michigan does not explain how seeking to intervene in this license renewal proceeding for a facility located outside of Michigan falls within its organizational interests or purpose.
FENOC is wrong. The complete corporate purpose statement of Dont Waste Michigan, as stated in its articles of incorporation, is as follows:
A statewide coalition of concerned individuals, citizens groups, and environ-mental organizations dedicated to educating the public about the dangers nuclear contamination poses to human health and the environment.
Taking these broad goals of DWM together with the proximity presumption that hundreds of thousands of Michigan residents live within 50 miles of Davis-Besse, it is indisputable that DWM claims a valid stake on behalf of its members for purposes of this relicensing case.
Where a showing of germaneness needs to be made, as a requirement, it is undemand-ing. The germaneness requirement mandates mere pertinence between litigation subject and organizational purpose. Humane Society of the United States v. Hodel, 840 F.2d 45, 58-59, 268 U.S.App.D.C. 165 (D.C. Cir. 1988). Other courts agree: showing germaneness is unde-manding. See, e.g., National Constructors Association v. National Electrical Contractors Association, 498 F.Supp. 510, 521 (D.Md.1980) (germaneness standard allows suits by groups whose purposes are "pertinent or relevant to" claim at issue); American Insurance Association v.
Selby, 624 F.Supp. 267, 271 (D.D.C.1985) (stating that "an association's litigation interests must be truly unrelated to its organizational interests before a court will declare that those interests are not germane"); Medical Association of Alabama v. Schweiker, 554 F.Supp. 955, 965 (M.D.
Ala.1983) (germaneness test requires that "the injury to [an association's] members has some reasonable connection with the reason the members joined the organization and with the objectives of the organization").
Petitioners have demonstrated the requisite mere pertinence between litigation subject and organizational purpose enunciated in Hodel. Dont Waste Michigan clearly deserves to be accorded standing to participate as one of the Joint Petitioners.
REPLY IN SUPPORT OF CONTENTIONS ONE, TWO AND THREE A. Dinosaur Denial Both FENOC and NRC Staff assert that neither Wind nor Solar provide baseload power and that neither Wind nor Solar comprise a single, discrete electric generating source.
It gainsays FENOC and the Staff nothing to assert that the future of Wind and Solar is remote and speculative when their data dates from 1986 (wind-power classification of Class 3 or higher necessary for production,, ER p. 221-2); 1996 (GEIS says 214 square miles of land needed to replace 910 MW ; 12,740 acres of photovoltaic solar collectors to replace 910 MW);
and 2009. The ER neither notes nor discusses active plans for deployment of Solar and Wind in the near Great Lakes demonstrated by Joint Petitioners in their initial filing. When FENOC trvializes the current status of alternatives as emerging and under development, it is well to understand that the utility critiques technologies which have experienced a double-digit explosion of deployment in the same decade of a nuclear revival that has produced zero new nuclear power plant capacity additions. According to the U.S. Department of Energy (DOE), the U.S. has gone from 2,472 MW of wind-generated electricity in 1999 to 36,698 MW in 2009.3 In the present baseload generation market, Wind and Solar are competing head-on with 3
http://www.windpoweringamerica.gov/wind_installed_capacity.asp nuclear and beating it badly in the cost per installed kilowatt. FENOCs and the Staffs dinosaur denial of the onslaught of Wind and Solar is studiously misleading, and that misdirection violates NEPA straightaway.
NRC regulations at 10 C.F.R. § 51.92(a)(2) obligate the NRC staff to supplement a final environmental impact statement where [t]here are new and significant circumstances or information relevant to environmental concerns and bearing on the proposed action or its impacts. Reliance on inaccurate data, coupled with word play aimed at minimizing and trivializing these highly-competitive alternatives threatens to "defeat the purpose of an EIS by
'impairing the agency's consideration of the adverse environmental effects' and by 'skewing the public's evaluation' of the proposed agency action." Hughes River Watershed Conservancy v.
Glickman, 81 F.3d 437, 446-48 (4th Cir. 1996).
B. The Baseload Mislead FENOC and the NRC Staff consider Davis-Besse to be a baseload power source. The concept of baseload power implies continuously-available power to the grid, but the actual facts of the record of power delivery from both Davis-Besse and Perry (FENOCs other Ohio nuclear plant), show otherwise. Data from the U.S. Energy Information Agency4 (EIA) for the twenty years from 1989 through 2008 show that the capacity factor for the combination of the two plants is only 75%. In 2010, the Union of Concerned Scientists published a report, Walking a Nuclear Tightrope: The Unlearned Lessons of Year-Plus Reactor Outages, in which Davis-Besse was 4
http://www.eia.doe.gov/cneaf/nuclear/state_profiles/ohio/oh.html accorded attention for some of the longest outages in the domestic industrys history.5 Thus, baseload power, at least as FirstEnergy uses the term, certainly does not mean 100% availability. As between Perry and Davis-Besse, the latter has the notably worse record of performance over 30 years, with many major outages lasting more than 12 months, including more than one summer during which time the demand for electricity reached its maximum.
During these long outages, FirstEnergy has had to bring alternative generating sources online or to purchase power.
Contemporary energy storage schemes, such as pumped hydro or compressed air energy storage (CAES) do not have the storage capacity to replace the long-duration outages that are common with nuclear power. Even under the best of conditions, a nuclear refueling event will exhaust these energy storage resources. Hence even baseload nuclear power is, itself, not always available as baseload, indeed, is unavailable fully one-quarter of the time. The capacity factor of Solar is about 20%, while Wind is about 30%. The comparison between the 75%
capacity of nuclear and 30% for wind or 20% for solar is a much lower hurdle than the myth of baseload productivity for nuclear posed by FENOC and the NRC Staff.
Considered together, or even discretely, Solar and Wind could provide a credible and reliable electric power baseload. The nature of Solar and Wind in the territory of FirstEnergy is such that complete outages will never occur, especially during the peak demand summer months.
This critical insight, which is missing from the Environmental Report, contains great significance. Petitioners do not claim 100% availability for solar or wind power; but the 5
http://www.ucsusa.org/nuclear_power/nuclear_power_risk/safety/walking-a-nuclear-tightrope.ht ml, pp. 22-23, 26, 32, 34, 36.
distinction between Solar or Wind discretely or in combination vs. Nuclear is quantitative, not dispositive. It does not legitimately support dismissal of the alternatives contentions.
C. Nuclear Is Not Discrete Contrary to the implication of FENOCs and the NRC Staffs Answers, nuclear is not truly a single, discrete electric generating source. Petitioners have noted above that 25% of the time, according to the historical record, Davis-Besse has required back-up power. In this sense, it cannot truly be considered a single, discrete electric generating source. But beyond this obvious difficulty due to refueling, unexpected events and hole in the head crises, nuclear power is coupled with energy storage. A good example of this is the operation of the Ludington Pumped Storage Plant, operated jointly by DTE Energy and Consumers Energy. [brochure 62-5117, 15607 5M 12/06]. This hydro plant uses excess power from nighttime baseload generators when the demand is low, and produces power during the day when the demand is high. Some of this power is drawn from large nuclear and coal plants as far away as Monroe, about 200 miles away from Ludington, MI. Consequently, even large nuclear power stations cannot truly be considered as single and discrete sources of power.
Just as nuclear power can be coupled with energy storage such as pumped hydro, Petitioners have proposed the coupling of energy storage with Solar or Wind to compose a viable alternative to a twenty-year license extension of Davis-Besse. Again, the distinction is quantitative and not dispositive. Recently, Milligan, et al. [Michael Milligan, Kevin Porter, Edgar DeMeo, Paul Denholm, Hannele Holttinen, Brendan Kirby, Nicholas Miller, Andrew Mills, Mark OMalley, Matthew Schuerger, and Lennart Soder, Wind power myths debunked, IEEE Power & Energy Magazine, Nov-Dec 2009 pp. 89-996] discussed the fact that storage has been widely used in the electrical grid network, even before wind or solar became widely used.
They state:
Storage is nearly always beneficial to the grid, but this benefit must be weighed against its cost. With more than 26 GW of wind power currently operating in the United States and more than 65 GW of wind energy operating in Europe (as of the date of this writing), no additional storage has been added to the systems to balance wind. Storage has value in a system without wind, which is the reason why about 20 GW of pumped hydro storage was built in the United States and 100 GW was built worldwide, decades before wind and solar energy were considered as viable electricity generating technol-ogies. Additional wind could increase the value of energy storage in the grid as a whole, but storage would continue to provide its services to the grid - storing energy from a mix of sources and responding to variations in the net demand, not just wind.
Nuclear power and other conventional sources of power use energy storage to facilitate smooth grid operation. There is considerable expense and instability caused to the grid if a large so-called baseload coal or nuclear plant departs it suddenly.
Petitioners contend that the combined resource of Solar and storage or Wind and storage, or both together + storage, will form a viable alternative to Davis-Besse. The particular example chosen by Petitioners in their initial filing to illustrate this contention was the proposed Norton Energy Storage Project for underground CAES announced by First Energy. According to a FE press release, the Norton facility could easily handle power production equal to or greater than the 900 MW of Davis-Besse. In contrast with the use of the Ludington energy storage by DTE for power plants, including nuclear, near Detroit, 200 miles distant, the Norton facility is only 85 miles from the Davis Besse site. Shorter transmission lines contribute to greater economy of operation of the combined resource. In fact either the Solar or the Wind resource (or the 6
http://www.ieee-pes.org/images/pdf/open-access-milligan.pdf combination) would be distributed somewhat across Northern Ohio and/or other parts of the FE distribution territory, much of which is even closer to the Norton storage location.
Nuclear power is in-discrete in yet an additional aspect. A long, complex uranium fuel chain is required for Davis-Besse to operate and generate electricity. This includes such far-flung front-end activities as: uranium mining, milling, processing, conversion, enrichment, and fuel fabrication, with all the transportation in between. And it requires such far-flung back end activities as: on-site irradiated nuclear fuel storage in the waste storage pool and dry casks, perhaps followed by: off-site irradiated nuclear fuel storage in dry casks in "centralized interim storage facilities" -- surface parking lots often targeted at Native American communities, an environmental justice violation; dirty, dangerous, and expensive reprocessing, as at Department of Energy facilities; and ultimate disposal of irradiated nuclear fuel at a permanent geologic repository. Also included in back-end nuclear fuel chain activities are various forms of so-called "low-level" (but not low-risk) radioactive waste "management" activities, from deconversion of depleted uranium at enrichment facilities, to disposal in shallow dirt trenches, to incineration, to so-called "recycling" in common use products, an issue that will grow much worse when Davis-Besse is decommissioned, its radioactive facilities dismantled and its radioactively contaminated soil, groundwaters, and Lake Erie sediments "cleaned up" (if that's even possible) someday, a task that will grow more daunting the longer Davis-Besse operates. Without this far-flung nuclear fuel chain complex, with its radiological, toxic chemical, and even greenhouse gas emissions at each step, Davis-Besse could not operate to generate electricity. Davis-Besse is cannot in any respect be considered discrete.
The misconception that neither Wind nor Solar represent single, discrete electric generating sources, while nuclear power does, projects a faux apples-and-oranges comparison.
Petitioners legitimately seek an apples-to-apples comparison between their postulated alter-natives and Davis-Besse to see who holds the lemon.
D. The Replacement Power of Wind and Solar The NRC Staff states (Answer pp. 15-16) that Joint Petitioners have not provided sufficient information to show a genuine dispute with the ERs conclusions that solar power and wind power cannot replace Davis-Besse as a source of 910 MWe of baseload power by the commencement of the relicensing period, 2017. The Staff suggests that neither solar nor wind can be implemented by 2017.
- 1. Wind If there is no massive installation of wind across the near Great Lakes between now and 2017, it will be anomalous. On December 1, 2010, the National Wildlife Federation issued a report on Eastern seaboard wind power potential offshore entitled Offshore Wind in the Atlantic: Growing Momentum for Jobs, Energy Independence, Clean Air, and Wildlife Protection.7 The rates of dispersion of commercial-grade wind generators, present and projected, is accelerating. Altogether, 908 MW of dependable wind could be installed in time; it's not a technical impossibility, but it requires the political will to get it done.
The European Union is projected to have 40,000 MW of wind power installed by 2020, 9 years from now; China is projected to have 30,000 MW of wind power installed by 2020, 9 years from now (in 2007, China had 1.5 MW, which increased to 102 MW by 2010). Id., p. 19. Even 7
www.nwf.org/News-and-Magazines/Media-Center/News-by-Topic/Global-Warming/2010/12-0 1-10-Offshore-Atlantic-Wind-is-Next-Clean-Energy-Wave.aspx. Petitioners submitted this report as Exhibit 12 along with their December 27, 2010 petition.
DOE projects that the US can and will have 10,000 MW of win power installed by 2020, 9 years from now. Id. If China can grow wind that fast, why can't 2,700 MW be installed in FENOC's service area to completely replace D-B in the next 6 years? 2,700 MW. Even assuming a 30%
capacity factor, such an aggregation of windmills would still generate 900 MWe, replacing Davis-Besse.
Europe has experienced remarkable growth in wind as well: 2,300 MW in 2010; 40,000 to 55,000 MW by 2020; 150,000 MW by 2030. Id. p. 20.
Approximately 6 GW of offshore wind projects have been proposed along the US Atlantic Coast and many are advancing (2.84 - 3.25 GW proposed, another 2.47 - 3.22 GW advancing, for a total of 5.32 - 6.47 GW proposed and advancing. This total is 6,000 MW, versus David-Besses 908 MW. Id. p. 20. Maine proposes 5,000 MW of offshore wind by 2030.
5,000 MW in 19 years averages to 263 MWe per year. If OH matched that rate of growth of offshore wind power, as in Lake Erie, it could install 1,578 MWe of offshore wind power capacity by 2017. Even at 30% capacity factor, that would still be 473.4 MWe, replacing over half of D-B's output. Combined with onshore wind in OH, and solar PV, D-B would be replaced by 2017. Similarly, at p. 36, the report documents that Massachusetts established a goal in 2009 to go from zero to 2,000 MW of onshore and offshore wind power by 2020. 2,000 MW in 11 years averages to 181.8 MW per year. So, if Ohio were to match that rate of growth, from 2011 to 2017, Ohio would see installation of 1,090 MW of wind power. Even at a 30% capacity rate, this would replace one-third (1/3) of Davis-Besse's output -- the other two-thirds (2/3) could be replaced by solar PV.
In MA, the Cape Wind project alone will be 468 MWe of offshore wind, installed between now and 2013. Even accounting for a 30% capacity factor, in two years, a dependable 140 MWe of electricity will be generated by Cape Wind in the next two years. Even tiny Rhode Island plans to install 384 MWe of offshore wind by 2014. And at a 30% capacity factor, that will be over 100 MWe of dependable wind power. Ohio has much more potential than that, if it chooses to tap it!
- 2. Solar One of the worlds largest photovoltaics manufacturers has a plant located in the FE service area. In calendar year 2009, First Solar was the worlds largest manufacturer, producing 1,200 MW of solar panels. It is disingenuous to argue that appropriate PV installations could not be accomplished in the next six years. Paula Mints of Navigant Consulting8 reported in August 2010 that the manufacturing capacity of PV modules in 2010 was 35,000 MW. Even with a capacity factor of 20% this would represent 7 GW of continuous power in one years production of solar panels at the 2010 capacity. Mints also demonstrates that the historical growth rate of module production over the past 35 years has been 42%. Preliminary figures by Mints for 2010 indicate that the growth over 2009 was 100%!9 But even at a pessimistic 30% growth rate, production will have expanded by another factor of 4.8 in six years to a capacity of 168,000 MW.
The adequacy of supply of state-of-the-art photovoltaic collectors for the installation of 900 MW equivalent of PV power by 2017 simply cannot be used to dismiss this contention.
E. Solars Is the Lesser Carbon Footprint 8
http://www.electroiq.com/ElectroIQ/en-us/index/display/Photovoltaics_Article
_Tools_Template.articles.Photovoltaics-World.industry-news.2010.august.strong-d emand_in_2009.html 9
http://www.electroiq.com/index/display/photovoltaics-article- display/3067170607/
articles/Photovoltaics-World/industry-news/2011/1/the-12-step_solar.html At p. 23 of its Answer, NRC Staff maintains that Joint Petitioners also argue that solar power has a much smaller footprint than nuclear power, and that use of solar energy would meet Ohios mandates for renewable energies. Petitioners made no such claim. Solar power has a carbon (CO2) footprint that is much smaller than the full fuel chain of nuclear. The carbon footprint refers to CO2 emissions to the atmosphere per unit of power generated over the life of a power plant.
As to the physical footprint of solar, the Staff is also incorrect where it argues (Answer
- p. 25) that Since buildings sit on land, Joint Petitioners have not demonstrated that rooftop installations can reduce the amount of land needed for 910 MWe baseload power generation by 2017. It is true that large land areas are necessary for solar power to be a viable alternative to Davis-Besses license renewal. But the notion of required land area for a power facility relates to reassignment of land use such that it cannot be used for other purposes. When PV is placed on rooftops, it certainly does not prevent normal usage of the land beneath the installation. This argument may be quickly disregarded.
Petitioners offer the following illustrative consideration. The Davis-Besse facility occupies 954 acres. The Norton underground storage facility occupies an additional 92 surface acres. The combined area is 4,233,000 square meters. If this land area were covered by solar panels the power production would be 550 MW, assuming a modest 13% efficiency from the panels. This is already a significant fraction of the Davis-Besse generation capacity. When one considers PV installations on rooftop spaces, the supposed problem of permanently tying up land for solar disappears. Maya Chaudhari, Lisa Frantzis, Dr. Tom E. Hoff have analyzed the availability of rooftop space across the U.S. suitable for PV.10 Their analysis concludes that there is easily sufficient rooftop space for solar to provide a very large fraction of the U.S. electricity generation (in addition, there is a large amount of land that is unavailable for other uses such as landfill covers, roadside and railroad right-of-ways, etc.):
The state-by-state analysis, the first of its kind, concludes that the potential U.S.
market for grid-connected solar rooftop PV could reach 2,900 MW per year by 2010, assuming that the solar industry can achieve a breakthrough price of $2.00-$2.50 per installed watt. Rooftop space is not a constraining factor for solar development.
Residential and commercial rooftop space in the U.S. could accommodate up to 710,000 MW of solar electric power (if all rooftops were fully utilized, taking into account proper orientation of buildings, shading from trees, HVAC equipment, and other solar access factors). For comparison, total electricity-generating capacity in the U.S. today is about 950,000 MW. (Emphasis supplied)
Even limiting the rooftop space converted for solar only to commercial rooftops that are suitable for PV, Paul Denholm and Robert Margolis of NREL have written:11 For commercial buildings, we used the CBECS database to estimate the dis-tribution between flat and pitched roofs (DOE 2003). The CBECS data indicates that about 37% of commercial buildings (corresponding to about 31% of roof area) use shingles, wood, or slate; and it assumed that these roof materials are used on pitched roofs, with the remainder flat. For the orientations of pitched roofs, we assume a uniform distribution. Total roof area was then translated into usable area using an availability factor, which accounts for shading, rooftop obstructions, and other constraints.
Applying the data of Denholm and Margolis, including these constraints of shading and ori-entation, etc., for the flat commercial rooftops in the Cleveland-Akron-Youngstown-Toledo metro areas - all FE territory - to obtain the solar generation potential, the commercial roof space can reasonably be estimated to yield 4,400 MW of solar electricity. Considering a capacity 10 PV Grid Connected Market Potential in 2010 Under a Cost Breakthrough Scenario, September 2004. http://www.ef.org/documents/EF-Final-Final2.pdf.
11 Supply Curves for Rooftop Solar PV-Generated Electricity for the United States, Technical Report, NREL/TP-6A0-44073, November 2008, p. 4, http://www.nrel.gov/docs/fy09osti/44073.pdf .
factor of about 20% for solar, these two sources, commercial rooftops and the Davis-Besse plus Norton land area, would yield 990 MW of baseload generating capacity. This demonstrates that the generating capacity of solar, together with the storage capacity of Norton, can readily provide a very viable alternative to Davis-Besse, without impacting any additional land area.
F. FENOC Surrounded by Nonspeculative Solar Ferrets FENOC asserts (Answer p. 25) that An environmental review need not ferret out every possible alternative, regardless of how uncommon or unknown that alternative may have been at the time the project was approved. Rather, NEPA only requires consideration of reasonable alternatives, (i.e., those that are feasible and nonspeculative). FENOC maintains that Peti-tioners have not met four criteria. Taking these criteria, however, as supported by the foregoing observations in this Reply, Petitioners have conclusively met them:
a) That the solar generation option (which includes an integrated storage unit, not unlike the storage regularly used by conventional power sources such as nuclear and coal) will accomp-lish the purpose of the proposed project (908 MWe of grid power);.
b) That the solar option is both technically feasible now; and c) commercially deliverable today from an industry which has grown annually at a rate of 40% per year for the past 30 years. And the largest manufacturer of PV modules in the world in 2009 had its only U.S. manufacturing facilities located in the FE service area ((Perrysburg, OH);
d) That this power is supplied from a single source, solar panels that could be located if desired in the Ohio region of the FE service territory, with no impact on land usage. This source would utilize storage to provide continuous supply in conceptually the same way that storage, whether pumped hydro or compressed air or other storage, is used to smooth out the day/night load variations on large conventional power plants such as nuclear and coal.
And a nearly-identical profile could be depicted for Wind.
G. CAES: Its More Than a Concept FENOC claims (Answer, p. 38) that compressed air energy storage (CAES) is only a concept. But the Electric Power Research Institute (EPRI) has identified pumped hydro and compressed air energy storage as the two best choices for energy storage.12 FE acknowledges this wisdom, as signified by its purchase of the Norton underground CAES facility. Compressed air storage is not just a concept. Large CAES systems have been in operation since 1978 in Bremen, Germany (Huntorf), where there is a 290 MW plant,13 and since 1991 in Alabama (McIntosh plant), a 110 MW facility.14 H. NRC Finally Takes NEPAs Alternatives Requirements Seriously Even as Solar and Wind have become very serious market competitors with which the nuclear industry has to contend, when combined with storage or supportive conventional power sources, they are receiving increasingly serious scrutiny as alternatives during the NEPA phase of power plant licensing.
In Environmental Law & Policy Center v. NRC, 470 F.3d 676 (7th Cir. 2006), the NRC was considering an early site permit for a new nuclear plant. Environmentalist intervenors asserted that the applicant utility failed to adequately consider energy efficiency or combinations of wind or solar power with fossil fueled plants. Id. at 680. The ASLB Board acknowledged the 12 http://www.greentechmedia.com/articles/read/epri-on-renewable-energy-compressed-air-energy-storage 13 http://coen.boisestate.edu/WindEnergy/resources/ER-07-001.pdf 14 http://www.caes.net/mcintosh.html environmental groups' contention that Exelon had failed to consider combining wind or solar power with fossil fueled facilities and had used potentially flawed and outdated information regarding wind and solar power generation methods. After the ASLB admitted the contention, the utility, Exelon, provided a report evaluating facilities that combined wind or solar power with fossil fuel which concluded that coal-fired facilities, gas-fired facilities, or facilities using a combination of these alternatives were not environmentally preferable to the proposed nuclear facility, because the combination would produce environmental impacts greater than or equal to a new nuclear facility. Id. at 680. The Staff issued a draft Environmental Impact Statement (DEIS), concluding that individual wind and solar facilities were not sufficient on their own to generate baseload power and that, from an environmental standpoint, the nuclear facility would be preferable or equivalent to a combination facility using wind or solar power and fossil fuel. The utility moved successfully for summary disposition on the issue and the environmental groups appealed. Id. at 680.
On appeal, the Seventh Circuit affirmed that the NRC had taken the requisite hard look under NEPA, and ducked. Noting that the need for power issue might be premature since the early site permit opened a window for Exelon to apply for permit to construct a nuclear plant anytime during a 40-year window, the Court of Appeals opined that The need for power could vary considerably over that time period, so any analysis at this stage is speculative at best. Id. at 684. From Environmental Law & Policy Center, it is evident that consideration of wind and solar alternatives in combination with other forms of energy has a history dating back at least to 2005. In the six (6) years since then, they have only become more formidable competitors with nuclear power.
Far more recently, the NRC considered the adequacy of a utilitys discussion of alternatives to a new nuclear plant at Calvert Cliffs and found the summary rejection of wind and solar disconcerting. Calvert Cliffs 3 Nuclear Project, LLC and Unistar Nuclear Operating Services, LLC (COLA for Calvert Cliffs Unit 3), LBP-10-24, Docket No. 52-016-COL (December 28, 2010). In Calvert Cliffs, the intervenors sought admission of Contention 10C, which stated: The DEIS Discussion of a Combination of Alternatives is Inadequate and Faulty.
The intervenors asserted that the NRC Staff grossly underestimated the contribution from all wind power sources, that additional wind power which would be produced off the nearby coasts of Delaware and New Jersey was not mentioned in the DEIS; that the NRC staff did not consider a DOE assessment of offshore wind potential in Maryland; and that the DEIS significantly underestimated the potential contribution of wind power to a combined alternative of wind and solar photovoltaic-generated electricity. The intervenors contended that a feasible combination of alternatives might well include a considerably smaller natural gas plant than contemplated in the DEIS, along with a much larger contribution from renewable sources of power and demand-side programs to produce reliable baseload power with lower environmental consequence and possibly reduced economic cost. Id. p. 48.
The ASLB agreed, holding:
Intervenors have provided sufficient information to show that there is a genuine dispute concerning the appropriate composition of the combined alternative described in the DEIS and its environmental consequences. This dispute is material to the licensing decision. In order to issue the license, the NRC Staff must prepare an EIS that complies with NEPA. As we have explained, the alternatives analysis is the most critical part of an EIS. Intervenors maintain that the comparison in the DEIS between a new nuclear power plant and the combined alternative violates NEPA because it is inaccurate and incomplete. They have identified information indicating that the NRC Staff might have significantly underestimated the potential contribution of wind power and solar power to the combined alternative. If Intervenors are correct, then the DEISs comparison of alternatives might well be incomplete or inaccurate because, by underestimating the contribution of power sources that produce little or no air emissions, it overestimates the air emissions the combined alternative would produce. The estimated level of air emissions influenced the DEISs comparison of the combined alternative to the construction of a new nuclear power plant.
Id. pp. 48-49. Respecting the matter of whether, having identified serious factual flaws in the DEIS, what the duty of the NRC Staff under NEPA was, the Board further ruled as follows:
If Intervenors contention is upheld on the merits, they will have shown that the DEIS violates NEPA even if they have not shown precisely how the DEIS should be revised or what ultimate conclusion it should reach. Federal courts have held that inaccurate, incomplete, or misleading information in an EIS concerning the comparison of alternatives is itself sufficient to render the EIS unlawful and to compel its revision. As the court of appeals explained in Animal Defense Council v. Hodel, The Council alleges that the EIS was so filled with misinformation and incorrect cost figures that the Bureau must revise its EIS to adequately provide the public with an informed comparison of alternatives. Where the information in the initial EIS was so incomplete or misleading that the decisionmaker and the public could not make an informed comparison of the alternatives, revision of an EIS may be necessary to provide a reasonable, good faith, and objective presentation of the subjects required by NEPA. Johnston v. Davis, 698 F.2d 1088, 1095 (10th Cir. 1983) (revision of EIS necessary where use of artificially low discount rate resulted in unreasonable comparison of alternatives to proposed project); see also National Wildlife Federation v. Andrus, 440 F.Supp. 1245, 1254 (D.D.C. 1977)
(EIS deficient where several alternatives were not treated in the EIS and the EIS did not set forth reasons why these alternatives were rejected).
Thus, if the DEISs analysis of the combined alternative significantly underestimates the potential contribution of wind and solar power, as Intervenors maintain, then the EIS fails in one of its essential functions - to provide the public and the decision maker with accurate information comparing the proposed action and its alternatives - and, as such, it cannot support an agency decision to issue the license. (Emphasis supplied)
Id. p. 50.
Conceding that Calvert Cliffs involves a COLA for a new power plant, Petitioners urge, nevertheless, that NEPA applies as fully to the consideration of alternatives in a supplemental EIS - the NEPA document to be produced for these license extension proceedings. Even when the 1996 GEIS has resolved a Category 1 issue generically, the applicant must still provide additional analysis in its Environmental Report if new significant information may bear on the applicability of the Category 1 finding at the particular plant. Intervenors may seek a waiver to a rule if they possess information that may show that a generic rule would not serve its purpose at the specific plant; or they may use the SEIS notice and comment process to request that the NRC forgo use of the suspect generic finding and suspend license renewal proceedings, pending a new rulemaking or update of the GEIS. Entergy Nuclear Generation Co. And Entergy Nuclear Operations, Inc. (Pilgrim Nuclear Power Station), LBP-06-24, 64 NRC 257, 294-95 (2006). An applicant is required to address new and significant information for either Category 1 or Category 2 issues in its ER for an LRA. Entergy Nuclear Operations, Inc. (Indian Point, Units 2 and 3),
LBP-08-13, 68 NRC 43, 189 (2008).
Accordingly, the NRCs own interpretations of its obligation to consider alternatives under NEPA requires a greatly-expanded scrutiny of Solar and Wind power as a possible baseload replacement of Davis-Besse in this license extension proceeding. The existence of a viable, but unexamined alternative renders an environmental impact statement inadequate.
Idaho Conservation League v. Mumma, 956 F.2d 1508, 1519-20 (9th Cir. 1992). Agencies must study. . . significant alternatives suggested by other agencies or the public. . . . DuBois v. U.S.
Dept. of Agric., 102 F.3d 1273, 1286 (1st Cir. 1996), cert. denied, 117 S.Ct. 1567 (1997). Even an alternative which would only partially satisfy the need and purpose of the proposed project must be considered by the agency if it is "reasonable," Natural Resources Defense Council v.
Callaway, 524 F.2d 79, (2nd Cir. 1975), because it might convince the decision-maker to meet part of the goal with less impact, North Buckhead Civic Assn v. Skinner, 903 F.2d 1533, 1542 (11th Cir. 1990).
I. Conclusion:
Contentions One, Two and Three Should Be Admitted FENOC claims (Answer p. 27) that the evaluation of the relicensing application must not be "based on speculation about alternatives that may be technically feasible or commercially viable sometime in the future." If that is the case, then the relicensing application itself must be immediately denied. By applying for relicensing so many years before the current operating license expires, FENOC is speculating that large, discrete power sources such as Davis-Besse will still be commercially viable.
There are many plausible scenarios under which this speculation could be false. A large scale accident could lead to the banning of nuclear power. The regulatory response to the current status of tritium leaks could be additional regulation or remediation mandates that make nuclear power too expensive to be commercially viable. FENOC may argue that these postulates are not "feasible and reasonable," but it cannot be denied that the relicensing application itself is the result of speculation on market, environmental, and technological conditions six years into the future. FENOC is also speculating that the wind, solar, and combined wind and solar technol-ogies advocated as alternatives by the Petitioners will not be commercially viable or technol-ogically feasible in the future, knowing full well that the real-world evidence, today, reveals otherwise. Wind, solar, and combined wind and solar are technically feasible and commerically viable in their current status. FENOC's claim that wind, solar, and combined wind and solar can not provide baseload generation are belied by the fact that they are currently doing so in many European countries. The petitioner's contentions are backed, not by speculation, but by data collected from currently functioning electrical grids in other countries.
The NRCs NEPA regulation found at 40 C.F.R. § 1502.14(a) obligates the NRC to
[r]igorously explore and objectively evaluate all reasonable alternatives, FENOC cannot credibly argue that reliance on the 1996 factual conclusions of the GEIS, and to not mention 2010 Wind and Solar market analyses, nor to assess serious contemporaneous plans to commercialize Wind and Solar comprises rigor. Wind power has experienced a surge in technological development over the past fifteen years. Wind turbines are more economical, larger, and technologically feasible than they were when the boilerplate language FENOC used was written.
The reasons for elimination of an alternative must, themselves, be reasonable. To simply claim repeatedly that wind, solar, and combined wind and solar can not provide baseload power is unreasonable in light of the fact that they are doing so in many countries including Germany, Denmark, Spain, and China. FirstEnergys Environment Report has so briefly discussed the wind and solar energy alternatives, relying upon significantly dated information compounded by its own omission of significant expert and expert agency documents for its distribution jurisdiction as to leave its discussion of the alternative significantly incomplete, uninforming, inaccurate and misleading for the purpose of preparing the Environmental Impact Statement. Wind and Solar, either as baseload or in some combination, constitute reasonable alternatives, the more so when other far less attainable alternatives, such as geothermal, were identified and considered in the Environmental Report.
The ASLB must take pains to avoid the losing proposition of blindly adopting the applicant's goals, because it does not allow for the full consideration of alternatives required by NEPA. Simmons v. Corps of Engineers, 20 F.3d 664, 669 (7 Cir. 1997). NEPA requires an agency to "exercise a degree of skepticism in dealing with self-serving statements from a prime beneficiary of the project" and to look at the general goal of the project rather than only those alternatives by which a particular applicant can reach its own specific goals. Id.
The Environmental Report is plainly inadequate on Solar, Wind, and a combination of Solar and Wind as alternatives which would obviate the need for a 20-year license extension.
Our combined reply regarding CONTENTION FOUR: SEVERE ACCIDENT COST UNDERESTIMATED In Contention Four of their December 27, 2010 Petition and Request (Page 100), Joint Petitioners assert that:
The Environmental Report (ER) is Inadequate Because It Underestimates the True Cost of a Severe Accident at Davis-Besse in Violation of 10 C.F.R. 51.53 (C)(3)(II)(L) and Further Analysis by the Applicant, FENOC, Is Called For.
INTRODUCTION FENOC acknowledges, under E.1.2 REQUIREMENTS at page E-15 of its Environmental Report, that NRC regulations state and require:
10 CFR 51, Subpart A, Appendix B, Table B-1, Issue 76 (Severe Accidents)
The probability weighted consequences of atmospheric releases, fallout onto open bodies of water, releases to ground water, and societal and economic impacts from severe accidents are small for all plants. However, alternatives to mitigate severe accidents must be considered for all plants that have not considered such alternatives.
As context for considering Severe Accidents and their mitigation at Davis-Besse, it should be borne in mind that Davis-Besse has had numerous near-misses with severe accidents.
Joint Petitioner Beyond Nuclear has summarized these numerous close-calls in a November 2010 backgrounder (corrected December 2010) entitled Davis-Besse Atomic Reactor: 20 MORE Years of Radioactive Russian Roulette on the Great Lakes Shore?! This backgrounder has been submitted along with this Combined Reply to the NRC EIE Hearing Docket for this proceeding, and is also viewable online at
http://www.beyondnuclear.org/storage/Davis_Besse_Backgrounder.pdf. As Davis-Besse has had so many brushes with severe accidents, it is remarkable that FENOC has identified no severe accident mitigation alternatives that it considers cost-beneficial at its problem-plagued reactor.
[Note, per ASLB MEMORANDUM AND ORDER dated February 18, 2011, which ruled in favor of FENOCs Motion to Strike dated February 7, 2011, this attachment has been stricken. It is now not attached to this revised Combined Reply.]
FENOC and NRC staffs objections to Joint Petitioners CONTENTION FOUR:
SEVERE ACCIDENT COST UNDERESTIMATED are similar. Thus, Joint Petitioners comments regarding FENOCs objections may be applied to NRC staffs objections, as appropriate.
FENOC and NRC staff seem to have forgotten at least three basic principles.
First, a proceeding, including before this ASLB, has at least three distinct phases:
Pleading, Summary Disposition, and Hearing.
The issue at the Pleading stage is whether, taking all of the facts pleaded as true, Joint Petitioners contentions provide sufficient alleged factual or legal bases; or, as said in the Federal Rules of Civil Procedure, state a claim upon which relief can be granted.
Intervenors are not asked to prove their case at the contention stage, or to provide an exhaustive list of possible bases, but simply to provide sufficient alleged factual or legal bases to support the contention, and to do so at the outset. (NRC staff Practice and Procedure Digest (NRC Digest), Prehearing Matters, page 16). Commission Rules of Practice make no provision for motions for orders of dismissal for failing to state a legal claim. However, the Federal Rules of Civil Procedure do in Rule 12(b)(6), and ASLBs occasionally look to federal cases interpreting
that rule for guidance. In the consideration of such dismissal motions, which are not generally viewed favorably by the courts, all factual allegations of the complaint are to be considered true and to be read in a light most favorable to the nonmoving party. Sequoyah Fuels Corp. and General Atomics (Gore, Oklahoma Site Decontamination and Decommissioning Funding), LBP-94-17, 39 NRC 359, 365 (1994) (NRC Digest, Hearings, 80)
Similarly, the issue at this stage is not whether summary disposition should be granted.
There are plainly material facts in dispute, and summary disposition is proper only after giving Joint Petitioners the opportunity to present all pertinent material. Further, even after discovery is completed, the material facts must be undisputed. If there is any possibility that a litigable issue of fact exists or any doubt as to whether the parties should have been permitted or required to proceed further, the motion must be denied. (NRC Digest, Hearings 64, 65, underlining added; see also, 10 C.F.R. § 2.710(d)(2)).
Even more clearly, the issue now before the Board is not whether, after both discovery and hearing, all of those disputed facts should be decided in favor of the Applicant and the NRC.
And it is FENOC, not the Joint Petitioners, that has the burden of proving that it is entitled to a 20 year license extension. (See NRC Digest, Hearings, pages 82-83)
Second, NRC practice is not a law or rule, and is open to challenge on numerous grounds: e.g., it does not provide the required protection to the public, it is not reasonable, and that it is not supported by proved facts applicable -- not in the past - but rather to whether, in the here and now, Davis-Besse should be granted a license extension. Similarly, NRC NUREGs and Regulatory Guidance documents are routine policy pronouncements that do not carry the binding effect of regulations. International Uranium (USA) Corp., CLI-00-1,51 NRC 9,19 (2000);
Southern Nuclear Operating Co. (Early Site Permit for Vogtle ESP Site), LBP-07-3,65 NRC 237,254(2007). PHM 105. Adjudicatory decisions must be supported by evidence properly in the record. Pacific Gas & Electric Co. (Diablo Canyon Nuclear Power Plant, Units 1 & 2),
ALAB-580, 11 NRC 227, 230 (1980); Philadelphia Electric Co. (Limerick Generating Station, Units 1 and 2), ALAB-836, 23 NRC 479, 499 n.33 (1986).
Third, the decisions in the prior proceedings to which FENOC and NRC staff refer are essentially irrelevant. Those decisions were dependent on exactly what the intervenor(s) there did, or did not, plead or prove. A decision that an issue was not part of an intervenors contention, for example, that Pilgrim Watchs original contention (Pilgrim nuclear power plant license extension proceeding) did not specifically include health or clean-up costs, or that Riverkeepers contention (Indian Point license extension proceeding) did not raise whether the choice of source term was proper, has nothing to do with whether the issues that are raised by the Joint Petitioners here must be considered. A prior decision that an intervenor did not prove an admitted contention similarly has nothing to do with whether a contention should be admitted here.
The NRC Commission has long said (Fed. Register, Vol. 63, No. 150, August 5, 1998, repeated in the 2010 Edition of the NRC Digest) that:
the Commission's objectives are to provide a fair hearing process...and to produce an informed adjudicatory record that supports agency decision making on matters related to the NRC's responsibilities for protecting public health and safety, the common defense and security, and the environment, and that the opportunity for hearing should be a meaningful one that focuses on genuine issues and real disputes....
The most recent edition of the NRC Digest says that Public participation through intervention is a positive factor in the licensing process and Intervenors perform a valuable function and are to be complimented and encouraged. (Prehearing Matters, 11)
Joint Petitioners trust that the NRC means what it has said, and that the Petitioners here will be permitted to perform their indisputably valuable function, and help insure that the NRC will fulfill its responsibilities for protecting public health and safety, the common defense and security, and the environment, or, as NRCs website homepage (http://www.nrc.gov/) so elegantly puts it, Protecting People and the Environment.
FENOCS ADMISSIBILITY ARGUMENT FENOC first incorrectly argues that Contention 4 is inadmissible for three fundamental reasons, and then attempts to challenge each material dispute raised by the Joint Petitioners in six subparts, the Petition and Request designated as:
(1) FENOCS USE OF PROBABILISTIC MODELING UNDERESTIMATED THE TRUE CONSEQUENCES OF A SEVERE ACCIDENT (Joint Petitioners Petition and Request, December 27, 2010, beginning on Page 104);
(2) THE SAMA ANALYSIS FOR DAVIS-BESSE MINIMIZES THE POTENTIAL AMOUNT OF RADIOACTIVE RELEASE IN A SEVERE ACCIDENT (Page 108);
(3) THE SAMA ANALYSIS FOR DAVIS-BESSE USES AN OUTDATED AND INACCURATE PROXY TO PERFORM ITS SAMA ANALYSIS, THE MACCS2 COMPUTER PROGRAM (Page 115);
(4) USE OF AN INAPPROPRIATE AIR DISPERSION MODEL, THE STRAIGHT-LINE GAUSSIAN PLUME, AND METEOROLOGICAL DATA INPUTS THAT DID NOT ACCURATELY PREDICT THE GEOGRAPHIC DISPERSION AND DEPOSITION OF RADIONUCLIDES AT DAVIS-BESSES GREAT LAKES SHORELINE LOCATION (Page 116);
(5) USE OF INPUTS THAT MINIMIZED AND INACCURATELY REFLECTED
THE ECONOMIC CONSEQUENCES OF A SEVERE ACCIDENT, INCLUDING DECONTAMINATION COSTS, CLEANUP COSTS AND HEALTH COSTS, AND THAT EITHER MINIMIZED OR IGNORED A HOST OF OTHER COSTS (Page 135);
(6) USE OF INAPPROPRIATE STATISTICAL ANALYSIS OF THE DATA, SPECIFICALLY THE APPLICANT CHOSE TO FOLLOW NRC PRACTICE, NOT NRC REGULATION, REGARDING SAMA ANALYSES BY USING MEAN CONSEQUENCE VALUES INSTEAD OF, FOR EXAMPLE, 95TH PERCERNTILE VALUES (Page 149).
FENOCs Summary of FirstEnergy Response to Contention 4 (FENOC Answer, Page
- 80) alleges that Contention 4 suffers from several pervasive flaws that render all of its six subparts, and therefore the contention in its entirety, inadmissible under 10 C.F.R. § 2.309(f)(1).
FENOCs three fundamental objections are: (1) numerous issues that plainly are beyond the proper scope of this license renewal proceeding; (2) lack of adequate support in the form of alleged facts or expert opinion; and (3) failure to demonstrate that any of its SAMA contentions raises a genuine, material dispute with the Applicant.
FENOC concludes its summary by stating For these reasons, and as explained more fully below, none of the six subparts of Contention 4, whether viewed independently or cumulatively in combination with other subparts of the contention, is admissible. Thus, Contention 4 should be rejected in its entirety for failing to meet the requirements of 10 C.F.R. § 2.309(f)(1)(iii)-(vi). (FENOC Answer, Page 83)
FENOC assertions that Contention 4 is inadmissible are incorrect, and their arguments fundamentally flawed, including that Joint Petitioners have ignored NEPAs rule of reason, and failed to present a genuine dispute by not proving issues raised with facts supported by expert testimony. In so doing, FENOC has repeatedly attempted to support its mistaken arguments by
citing opinions and decisions made at other license extension adjudicatory proceedings -- out of context and not applicable here.
NEPAS RULE OF REASON Both FENOC (pages 24, 71, and 76) and NRC staff (page 37 and 84) bring forward the rule of reason in their arguments so that the discussion below applies to both, as appropriate.
FENOCs (pages 82, 112, and 115) and NRC staffs (pages 69) arguments are seriously flawed. Joint Petitioners did not argue that there were plainly better methods to determine offsite consequences; instead we correctly stated that FENOCs methods were plainly outdated, inappropriate for Davis-Besses location, and significantly flawed. FENOCs choice of methods served to severely underestimate consequences so that offsite costs appeared to not justify mitigations to reduce risk and better protect the health and safety of the public.
Joint Petitioners, unlike FENOC, fully understand the rule of reason. NEPA does not allow, or find reasonable, the Applicants decision to use outdated methodologies and assumptions in their analyses. Joint Petitioners alternative methods are available, in use by other federal agencies, industries and parties, and are both reliable and applicable to Davis-Besses SAMA cost-benefit analyses.
One example involves issues surrounding the meteorological plume model. FENOC labels its treatment of the meteorological plume model issue as referring to Joint Petitioners Contention 4d: Use of the Gaussian Plume Model in the ATMOS Module of MACCS2 (FENOC Answer, Pages 105-115). Joint Petitioners designated this contention as USE OF AN INAPPROPRIATE AIR DISPERSION MODEL, THE STRAIGHT-LINE GAUSSIAN
PLUME, AND METEOROLOGICAL DATA INPUTS THAT DID NOT ACCURATELY PREDICT THE GEOGRAPHIC DISPERSION AND DEPOSITION OF RADIONUCLIDES AT DAVIS-BESSES GREAT LAKES SHORELINE LOCATION (Petition and Request, December 27, 2010, beginning at Page 116). FENOC (at its Answer, page 23) and (NRC staff, and its Answer, page 38) state that an environmental impact statement is not intended to be a research document. We do not necessarily disagree. However, the statement is not applicable to the issue at hand.
The plume modeling that Joint Petitioners present as appropriate for Davis-Besses SAMA analysis, instead of FENOCs decision to use the straight-line Gaussian plume model, are not techniques that require research. They are, in fact, established methods that are publically available, routinely used, and appropriate for quantifying atmospheric dispersion of contaminants. Although an effort may be required to adapt them for SAMA analyses, this would be very straightforward - research would not be required.
Appropriate meteorological data or modeling methodology is available. There is no shortage of appropriate meteorological data for a licensing model application. Alternative modeling methods that would use more extensive meteorological data are also available.
FENOC chose to use only one year of onsite data collected at the Davis-Besse site.
Meteorological data is also available from the nearby Toledo Express commercial airport (FENOCs Environmental Report at Section 2.10, Meteorology and Air Quality, and Table 2.10-1, Summary of Local Climatology Data (Toledo), cites meteorological data from the Toledo Express Airport, but does not utilize it in its SAMA analyses) and, importantly, processed data on a gridded basis can be obtained from NOAA (the U.S federal National Oceanographic and
Atmospheric Administration) to augment Davis-Besses limited onsite meteorological data relied upon for the SAMA analyses that have been provided by FENOC. Also there are several publically available meteorological modeling methods that can simulate variable trajectory transport and dispersion phenomena. MM5 is one which is routinely used nationally and internationally. There are other options as well. The present state of the art for an appropriate meteorological model would use multi-station meteorological measurement data as input to the meteorological model. The numerical computations, based upon numerical weather prediction techniques, would compute wind fields appropriate for modeling dispersion over a much larger geographic area than the a single measurement site at Davis-Besse itself can appropriately provide for.
A second reasonableness criterion is that the modeling method must be reliable. The outputs from such meteorological models that are used to produce inputs for the dispersion models are well accepted and form the basis for weather predictions provided by NOAAs National Weather Service (or NWS, cited by Joint Petitioners at pages 117, 120, 121 of their December 27, 2010 Petition and Request as experts on the phenomenon of Great Lakes sea breeze effect), as well as analyses of air pollution impacts of concern to regulatory agencies.
These techniques have been proven to be reliable and acceptable for air quality permitting and policy applications in complex terrain - such as that surrounding Davis-Besse -- and over long distances for the U.S. Environmental Protection Agency (EPA), the U.S. National Park Service (NPS), as well as internationally. Joint Petitioners argued with sufficient particularity in their Petition and Request that for complex meteorological situations such as exist at the Davis-Besse site and its surrounding region, these techniques would be more reliable than using the straight-line Gaussian plume model.
The third reasonableness criterion is that the modeling methods be applicable to SAMA analyses. The methods Joint Petitioners recommended are applicable because with straightforward modifications to incorporate nuclear radioisotope decay rates, they can produce the fields of concentration values and deposition rates needed for radiation dosage calculations.
The fourth reasonableness criterion is that the modeling methodology be adaptable for evaluating SAMA analysis cost-benefit conclusions. There is nothing inherent in variable trajectory models that would prohibit the output concentration and deposition fields from being applied to SAMA analyses.
None of the criteria cited would make the use of alternative models unreasonable to apply to FENOCs Davis-Besse SAMA analyses.
Further, there is no basis to the argument that there may be no way to assess through mathematical or precise model-to-model comparisons, how alternative meteorological models would change the SAMA analysis results. Some assessments may necessarily be qualitative, based simply upon expert opinion. But this argument seems to undercut the very value of mathematical simulation models in general as a method to assess the impacts of atomic reactor radioactivity emissions.
It is worth noting that any notion that the use of advanced models would be computationally too expensive and/or burdensome to use is not justified by the actual run time shown in Joint Petitioners review of MACCS2 output files. With modern computers, the use of inappropriate models on the basis of differences of computational costs is indefensible.
Invoking the rule of reason to the present disagreement about the most appropriate modeling methodology for application to FENOCs Davis-Besse SAMA analyses is blatantly dismissive of the concept that the present methods are inappropriate and outdated and that there are indeed alternative modeling methods that would be quite reasonable to use.
Another example involves issues surrounding the Modular Accident Analysis Program, or MAAP code. This contention is discussed by FENOC in its Answer to Contention 4b:
FirstEnergys SAMA Analysis Minimizes the Potential Amount of Radioactive Release in a Severe Accident, pages 92 to 98; by NRC staff in its Answer at i. Joint Petitioners Claim that MAAP is Inappropriate Does Not Raise a Material Issue, beginning at its Answer on page 79; and by Joint Petitioners under the designation THE SAMA ANALYSIS FOR DAVIS-BESSE MINIMIZES THE POTENTIAL AMOUNT OF RADIOACTIVE RELEASE IN A SEVERE ACCIDENT (Petition and Request, Page 108).
Joint Petitioners explained that the source terms used by FENOC to estimate the consequences of severe accidents (radionuclide release fractions generated by the Modular Accident Analysis Progression, MAAP) are consistently smaller for key radionuclides than the release fractions specified in NUREG-1465 and its recent revision for high-burnup fuel.
The radioactivity source term used results in lower consequences than would be obtained from NUREG-1465 release fractions and release durations. New research is not required. Joint Petitioners alternative model is reliable. Instead, independent studies and a study by the Brookhaven National Laboratory, cited in Joint Petitioners contention, showed use of the MAAP code is unreliable due to significantly underestimating collective dose. (J. Lehner et al.,
Benefit Cost Analysis of Enhancing Combustible Gas Control Availability at Ice Condenser and
Mark III Containment Plants, Final Letter Report, Brookhaven National Laboratory, Upton, NY, December 23, 2002, p. 17. ADAMS Accession Number ML031700011, cited on page 113 of Joint Petitioners December 27, 2010 Petition and Request)
We would demonstrate this at the hearing. Joint Petitioners alternative model is applicable to SAMA analyses and adaptable for evaluating the SAMA analysis cost-benefit conclusions. The effect of alternative source codes for evaluating SAMA analysis cost-benefit conclusions has been demonstrated at other sites. As an example, Dr. Edwin Lyman, Senior Scientist at the Union of Concerned Scientists (UCS), has performed such an alternative analysis for Entergys Indian Point nuclear power plant (Units 2 and 3) near New York City, which has also been the subject of an ongoing license extension proceeding before an NRC ASLB since April 30, 2007.
Yet another example involves issues surrounding the MELCOR Accident Consequence Code System, or MACCS2 risk consequence code. This contention is discussed by FENOC at Contention 4c: The MACCS2 Code Used in FirstEnergys SAMA Analysis Is Outdated and Inaccurate, pages 98 to 105 of FENOCs Answer; by NRC staff between pages 58 to 79, including issues of the MACCS2 code being outdated or obsolete from page 58 to 61; and by Joint Petitioners under the designation THE SAMA ANALYSIS FOR DAVIS-BESSE USES AN OUTDATED AND INACCURATE PROXY TO PERFORM ITS SAMA ANALYSIS, THE MACCS2 COMPUTER PROGRAM (Page 115).
The Applicants SAMA analysis uses MELCOR Accident Consequence Code System (MACCS2) computer program. Joint Petitioners stated the plain fact that there is no NRC
regulation requiring the use of that code, or any other particular code. It was FENOCs choice.
There are other consequence computer codes in use for nuclear accidents around the world.
Again, research is not necessary.
Further, Joint Petitioners explained that it is reasonable to require FENOC to update the code if, as we shall demonstrate, it provides the wrong answer by significantly underestimating offsite consequence costs.
The user (FENOC is this instance) controls what is put into the consequence code - the meteorological data, decay chain data, the dose conversion factor file data, the population input file data, and the data that go into the COMIDA 2 model. The MACCS2 codes OUTPUT file does the averaging and ranks the data into a cumulative distribution function (CDF) - the mean, 50th quartile, 90th quartile, 95th quartile, peak consequence, peak probability, and peak trial.
FENOC chose to take the mean value; and, there is no NRC rule requiring the mean. The mean is the wrong choice, as it underestimates consequences. A mean divides the sum by the number of entries. There are thousands of individual data entries so that dividing the sum by so many entries unreasonably dilutes the results. Further, FENOC multiplied the mean by its estimate of the probability of the accident scenario.
The point is that FENOCs choices - inputs and choice of averaging and probability -
resulted in significantly underestimating costs. It is not unreasonable to require further analysis using different data and parameters.
Lastly, it is obvious that FENOC has time to do a proper analysis; Davis Besses license does not expire for over six more years, so they clearly have time to do so.
MOTIONS TO INTERVENE - REQUIREMENTS Joint Petitioners largely covered this issue in the foregoing Introduction to this section of its Combined Reply regarding CONTENTION FOUR: SEVERE ACCIDENT COST UNDERESTIMATED.
However we shall take this opportunity to address points raised by FENOC. FENOC argues that Contention 4 lacks adequate support in the form of alleged facts or expert opinion, in contravention of 10 C.F.R. [Part] 2.309(f)(1)(v). (FENOC Answer, Page 80)
Joint Petitioners quite clearly met this standard. Joint Petitioners provided genuine disputes and did not rest upon mere allegations or denials; rather disputes raised were supported by ample references to experts, government documents and site specific studies.
Expert testimony is not required at this stage in the proceeding. If it were so, most members of the public, non-profit public interest groups, and local governments would be unable to file due to lack of resources. The very limited resources of these groups necessarily must be preserved for expert witnesses required at the summary disposition and hearing stage of these proceedings. Surely it is not the intent of the NRC Commission to restrict initial participation only to insiders with deep pockets?
What FENOC forgets is that we are at the initial stage of the proceeding (not the summary disposition or hearing stage) and are following requirements to introduce with sufficient particularity areas that the Applicant must defend against.
UNCERTAINTY
An example of FENOCs attack on Contention Four for [lack of] adequate support in the form of alleged facts or expert opinion, in contravention of 10 C.F.R. [Part] 2.309(f)(1)(v) is its allegation that Contention 4f Lacks Adequate Factual or Expert Support(FENOC Answer, Page 131). FENOC makes this claim against Joint Petitioners challenge to its treatment of uncertainty in its SAMA analyses.
In defense of its treatment of uncertainty, FENOC argues that it performed a number of sensitivity analyses to account for uncertainty. At FENOCs Answer, Page 132, Footnote 567, it states:
With regard to the cost-benefit evaluation, seven sensitivity cases were investigated. These cases examined: (1) the impacts of assuming damaged plant equipment is repaired and refurbished following an accident, (2) a lower discount rate, (3) a higher discount rate, (4) higher on-site dose estimates, (5) higher total on-site cleanup costs, (6) higher costs for replacement power, and (7) a higher non-internals event hazard groups multiplier. Further details on the sensitivity cases are provided ER Appendix E, Section E.8.
However, Joint Petitioners have clearly refuted the value of these studies, as they relied on the exact same flawed methodology. Repeating the same mistakes over and over does not provide the correct answer or, in this case, demonstrate that they properly accounted for uncertainty.
Joint Petitioners fully appreciate that there is uncertainty. For example, source term, meteorological conditions and evacuation (protective action measures cannot be definitively predicted to be occurring at any given time and must be addressed probabilistically in SAMA analyses). But NEPA requires an honest probabilistic analysis based on available, reliable and up-to-date models. FENOC failed to do so, the dispute that forms the very heart of this contention.
Further, there is no basis to the argument that there may be no way to assess through mathematical or precise model-to-model comparisons, how alternative models would change the SAMA analysis results. Some assessments may necessarily be qualitative, based simply upon expert opinion. But this argument seems to undercut the very value of mathematical simulation models in general as a method to assess the impacts of nuclear reactor radioactivity emissions offsite in a severe accident. Surely the ASLB does not believe this.
Finally, FENOC questions (at its Answer, Page 131) why Joint Petitioners cited Dr.
Edwin Lymans testimony in the Indian Point (Units 2 and 3) license extension proceeding, and how it applies to this Davis-Besse license extension proceeding. Joint Petitioners cited Dr.
Lymans testimony to emphasize the importance of scientific conservatism, as embodied in 95th percentile confidence levels as opposed to mean values. Joint petitioners insist that such confidence levels are necessary to adequately protect people and the environment against the hazards of radioactivity, to successfully mitigate against severe accidents.
SECTION-BY-SECTION REBUTTAL FENOC and NRC staff make similar arguments; therefore Joint Petitioners reply to NRC staffs Answer would be applicable here below, as appropriate.
FENOCs Arguments Against Contention 4a: Use of Probabilistic Risk Assessment Techniques, (Pages 83 to 92 of FENOCs Answer); Joint Petitioners FENOCS USE OF PROBABILISTIC MODELING UNDERESTIMATED THE TRUE CONSEQUENCES OF A SEVERE ACCIDENT (Joint Petitioners Petition and Request, December 27, 2010, beginning on Page 104)
In this contention, Joint Petitioners assert that FENOCs use of probabilistic modeling underestimated the deaths, injuries, and economic impact likely from a severe accident by
multiplying consequence values, irrespective of their amount, with very low probability numbers, making the consequence figures appear minimal. FENOCs claim that this contention is inadmissible is incorrect.
At Page 89 of its Answer, FENOC states:
Petitioners citation to a 1985 decision involving Indian Point also is inapposite.
Specifically, Petitioners note that the Board stated that the Commission should not ignore the potential consequences of severe-consequence accidents by always multiplying those consequences by low probability values. But the Boards statement is taken out of context. In that decision (which pre-dates the SAMA analysis requirement in Part 51 by more than a decade), the Board noted that, due to the high population density near Indian Point, a low probability accident at Indian Point may result in greater consequences than the same accident at another site. The Board did not hold that it is inappropriate to consider the probability of a severe accident in assessing the associated risk. In fact, in that proceeding, the Commission instructed the Board to consider serious accidents with equal attention to both probabilities and consequences. This is consistent with the definition of risk articulated by the Commission and used in numerous nuclear regulatory contexts, including SAMA analysis. [FENOCs reference to footnotes removed by Joint Petitioners]
Joint Petitioners take issue with several aspects of FENOCs argument. First is its apparent attempt to downplay population density risks at Davis-Besse. Davis-Besses neighbors include: Detroit, Michigan; Toledo and Cleveland, Ohio; and Windsor, Ontario. These major metropolitan areas are all located within 50 miles of Davis-Besse. Given such population density, a severe accident at Davis-Besse, certainly one involving a radiological release, would likely result in large, not small, consequences.
In addition to population density, Davis-Besses Lake Erie shoreline location raises additional risks. Lake Erie serves as the headwaters for the drinking water supply for many millions of people downstream, not only in the U.S. and Canada, but also in numerous Native American and First Nations. Toronto, Ontario and Montreal, Quebec - two of the largest metropolitan areas in all of Canada, are downstream of Davis-Besse on the Great Lakes and St.
Lawrence River. A severe accident at Davis-Besse, especially one involving a radiological release, would result not in small, but rather large, consequences of an international scope to downstream drinking water supplies. Such large consequences of international scope to downstream drinking water - and also agricultural irrigation water -- supplies would also extend, of course, to the northern shore of Lake Erie itself.
Due to such risks of an international incident involving a catastrophic radiological release into the Great Lakes (drinking water supply for 40 million people altogether in both countries, engine for one of the biggest regional economies on the entire planet, and heart of one of the worlds largest trading partnerships between the U.S. and Canada), FENOC and NRC itself must much more seriously address the risks of an intentional terrorist attack at Davis-Besse, as opposed to the flippant bureaucratic dismissal embodied by FENOCs response to Alleged Need to Consider Intentional Acts at its Answer, Page 86. To do otherwise is to risk unimaginable peril. FENOCs argument, and NRCs policy position, effectively assumes that the risk of a terrorist attack at Davis-Besse is zero. As shown by the events of September 11, 2001, such a risk calculation is dead wrong. As alluded to by the title of Dr. Edwin Lymans report, Chernobyl on the Hudson? The Health and Economic Impacts of a Terrorist Attack at the Indian Point Nuclear Plant, (Union of Concerned Scientists, September 2004, available at http://www.ucsusa.org/nuclear_power/nuclear_power_risk/sabotage_and_attacks_on_reactors/im pacts-of-a-terrorist-attack.html), Joint Petitioners are determined to do prevent a Chernobyl on the Great Lakes - as by intervening in this proceeding, and demanding that accurate SAMA analyses be carried out by FENOC in order to prevent a severe accident - or attack - from ever taking place at Davis-Besse. And of course, an element of Joint Petitioners Contentions One (Wind), Two (Solar), and Three (Solar and Wind Combined) is that those renewable energy
alternatives to Davis-Besse would not incur the risks of severe accidents or attacks unleashing catastrophic amounts of radioactivity into the Great Lakes Basin to blow with the wind and flow with the water to fallout downstream and downwind over vast areas.
Joint Petitioners do not disagree with the reasoning behind the cited Commission instruction to the ASLB in the 1980s Indian Point proceeding cited above, that regarding serious accident risk, equal attention should be paid to both probabilities and consequences. In fact, that is the very definition of risk itself.
However, FENOC misconstrues Joint Petitioners challenge. Joint Petitioners are not enemies of probability determinations. But Joint Petitioners are enemies of FENOCs systemic underestimation of risk probabilities due to its flawed models and methodologies.
FENOC has consistently underestimated risk in its SAMA calculations by inappropriately and improperly underestimating probability values, as Joint Petitioners have shown in Contention Four. FENOC has then multiplied consequences by improperly and inappropriately low probability values to arrive at seemingly low overall risk values. In fact, FENOC determined that not a single one of the Severe Accident Mitigation Alternatives it had considered in its ER SAMA analysis proved to be cost-beneficial.
In refuting Joint Petitioners dispute regarding probabilistic modeling, FENOC cites from the Pilgrim license extension proceeding. That ASLB deemed such a challenge inadmissible because the use of probabilistic risk assessment and modeling is obviously accepted and standard practice in SAMA analyses. (FENOC Answer, Page 85, Emphasis added) However, this is Davis-Besses license extension proceeding, not Pilgrims. Further, we underscore the key word practice. It is a practice, not a rule.
Joint Petitioners agree that probability must be taken into consideration, but with due caution. That is why we referenced Kamiar Jamalis (DOE Project Manager for Code Manual for MACCS2) Use of Risk Measures in Design and Licensing Future Reactors (an attachment to our Petition and Request). Jamali made clear that PRA (probabilistic risk assessment) uncertainties are so large and unknowable that it is a huge mistake to use a single number coming from them for any decision regarding adequate protection. Examples of these uncertainties include probabilistic quantification of single and common-cause hardware or software failures, occurrence of certain physical phenomena, human errors of omission and commission, magnitudes of source terms, radionuclide release and transport, atmospheric dispersion, biological effects of radiation, dose calculations, and many others. (Jamali, Page 935, Emphasis added)
Also, human error is not considered in PRAs. PRAs project into the future and come up with some very small number that an accident scenario only is likely to occur in so many hundreds-to-thousands of years. But no U.S. commercial reactor has operated for more than 42 years (Oyster Creek, 1969 to 2011), so actual experience is absent from which to base predictions. Uncertainty must be respected by making certain that appropriate and up-to-date methods and assumptions are used in the analysis. FENOC has not done so.
FENOCs argument misinterprets the GEIS. FENOC argues that This challenge to NRC regulations is impermissible under 10 C.F.R. [Part] 2.335, as the NRC has determined As a general matter[in Part 51]that the probability weighted consequences of atmospheric releases fallout onto open bodies of water, releases to ground water, and societal and economic impacts from severe accidents are small for all plants, but that alternatives to mitigate severe accidents must be considered for all plants that have not considered such alternatives. (FENOC,
Answer, Page 84, citing 10 C.F.R. Part 51, Subpart A, App. B, Table B-1, emphasis added by FENOC). FENOC surmises that Any contention asserting that this supplemental site-specific mitigation analysis must ignore risk and focus only on accident consequences necessarily implies that the NRCs underlying codified impact analysis improperly considered risk. (FENOC, Answer, Page 84)
However, FENOCs conclusion is wrong. FENOC misinterprets what the GEIS says. The GEIS says not that accident consequences are small, but after going through the probability weighted consequences, that they then appear small. Therefore, we conclude that the GEIS supports our dispute regarding FENOCs choice to multiply the mean by the weighted probability in the MACCS2 OUTPUT file.
Finally, FENOC argues that Joint Petitioners claim that the use of probabilistic modeling is improper for considering intentional malevolent acts (such as terrorist attacks) because the Commission concluded that NEPA imposes no legal duty on the NRC to consider intentional malevolent actsin conjunction with commercial power reactor license renewal applications.
(FENOC, Answer, Page 87, citing Oyster Creek and Pilgrim). And, further, that the GEIS concluded that the core damage and radiological release from such acts would be no worse than the damage and release expected from internally initiated events. (FENOC, Answer, Page 87, citing Oyster Creek) However, that argument fails in that the consequences of an accident scenario must be analyzed, to determine the potential severity; nothing excludes severe accidents that happen to result from a terrorist attack, or other malevolent intentional act.
Absent a site specific PRA at Davis-Besse to determine its specific vulnerabilities and potential accident consequences, the actual risk at Davis-Besse is unknown.
FENOCs Arguments Against Contention 4b: FirstEnergys SAMA Analysis Minimizes the Potential Amount of Radioactive Release in a Severe Accident (FENOC Answer, Page 92 to 98), Joint Petitioners THE SAMA ANALYSIS FOR DAVIS-BESSE MINIMIZES THE POTENTIAL AMOUNT OF RADIOACTIVE RELEASE IN A SEVERE ACCIDENT (beginning on Petition and Request, December 27, 2010, Page 108)
In this contention, Joint Petitioners assert that FENOCs SAMA analysis for Davis-Besse minimizes the potential amount of radioactive release in a severe accident. FENOCs claims -
that This contention also is inadmissible because it raises issues beyond the scope of this proceeding, lacks adequate factual or legal support, and fails to raise a genuine dispute on a material issue of fact or law, in contravention of 10 C.F.R. [Part] 2.309(f)(1)(iii)-(iv) (FENOC Answer, Page 92) - is incorrect.
Irradiated Nuclear Fuel Pool Accidents FENOC (Page 92) argues that no mitigation analysis is required for irradiated nuclear fuel pool accidents, an argument similar to its one above regarding terrorist attacks/malevolent acts. Joint Petitioners have clearly established the dispute.
We noted specifically that although 10 C.F.R. [Part] 51.53(c)(3)(ii)(L) does not provide a definition of severe accidents, the GEIS, which provides the factual background for the SAMA requirement in the regulations, does define a severe accident. According to Section 5.2.1 of NUREG 1437 General Characteristics of Accidents, the term accident refers to any unintentional event outside the normal plant operational envelope that results in a release or the potential for release of radioactive materials into the environment and severe[includes]
those involving multiple failures of equipment or function and, therefore, whose likelihood is generally lower than design basis accidents but where consequences may be higher
(Emphasis added). This section recognizes the potential for a severe accident in which there are releases substantially in excess of permissible limits for normal operation.
The term accident refers to any unintentional event outside the normal plant operational envelope that results in a release or the potential for release of radioactive materials into the environment. Generally, the U.S. Nuclear Regulatory Commission (NRC) categorizes accidents as design basis (i.e., the plant is designed specifically to accommodate these) or severe (i.e., those involving multiple failures of equipment or function and, therefore, whose likelihood is generally lower than design-basis accidents but where consequences may be higher), for which plants are analyzed to determine their response. The predominant focus in environmental assessments is on events that can lead to releases substantially in excess of permissible limits for normal operation.
Normal release limits are specified in the NRCs regulations (10 C.F.R. Part 20 and 10 C.F.R. Part 50, Appendix A). GEIS, 5.2.1, Italics added by Joint Petitioners.
Section 5 focuses on potential consequences to determine whether or not a potential accident is severe - and thus within the scope of a Severe Accident Mitigation Analysis. The question is not whether the source of the Severe Accident is the first or second largest inventory of radioactive materials. Perhaps FENOC confused Section 6 of the GEIS with Section 5.
Section 6 deals with normal operations (see, for example, Section 6.1, Accidental releasescould conceivably result in releases that would cause moderate or large radiological impacts. Such conditions are beyond the scope of regulations controlling normal operations (Emphasis added)
Section 5, not Section 6, deals with severe accidents. Nothing in Section 5 excludes severe accidents involving what is, at Davis-Besse, the largest inventory of radioactive materials
- the irradiated nuclear fuel storage pool. Due to 40 years of operations by 2017, the inventory of radioactive materials in Davis-Besses irradiated nuclear fuel storage pool will be many times that contained in its reactor core.
FENOC dismisses the fact that interactions between the irradiated nuclear fuel storage pool and the reactor need to be studied in the context of severe accidents. Its argument is foolish on its face. FENOC says, at Answer Page 93, that Petitioners reference to a study prepared by Dr.
Gordon Thompson [Risks of Pool Sabotage of Spent Fuel at Pilgrim Nuclear Power Station and Vermont Yankee, A Report for the Massachusetts Attorney General, by IRSS, at 12, 16, May 2006, available at ADAMS Accession No. ML061630088] and the Shearon Harris license amendment proceeding lend no support to their contention that FirstEnergy must examine interactions between the reactor and the spent fuel pool in its SAMA analysis. First, it is not the Joint Petitioners responsibility to demonstrate proof at this state of the proceeding; and second, the interactions between the reactor and the pool apply at Davis-Besse - one does not need to have a nuclear engineering degree to figure that out. FENOC has raised the issue of a single, discrete electric generation source time and time again in its Answer to challenge Joint Petitioners contentions that renewable sources of electricity such as solar PV and wind power -
especially in combination together, and interconnected, as well as connected to storage devices (Joint Petitioners Contentions One, Two, and Three). However, if Davis-Besse nuclear power plant itself is to be considered a single, discrete electric generation source, must not the irradiated nuclear fuel storage pool be included in that definition? The reactor could not operate without somewhere to discharge its thermally hot and radioactively lethal irradiated nuclear fuel every 18 to 24 months, so that it can thermally cool and radioactively decay for at least five years. Thus, interactions between the reactor and the pool must be addressed, including in FENOCs SAMA analysis.
FENOC also states Petitioners also argue, without any factual or expert support, that the offsite cost risk of a pool fire is substantially higher than the offsite cost of a release from a
core damage accident. FENOC must be familiar with such studies as Robert Alvarez, Jan Beyea, Klaus Janberg, Jungmin Kang, Ed Lyman, Allison Macfarlane, Gordon Thompson, Frank N. von Hippel, Reducing the Hazards from Stored Spent Power-Reactor Fuel in the United States, Science and Global Security, 11:1-51,
[January] 2003; Technical Study of Spent Fuel Pool Accident Risk at Decommissioning Nuclear Power Plants (NRC, NUREG-1738, 2001); and many others. To put this dispute in some context, around 200 tons of nuclear fuel in the Chernobyl Unit 4 core exploded on April 26, 1986, and then - along with its graphite moderator - burned for ten days. But there were already 557 tons of irradiated nuclear fuel stored at Davis-Besse by spring 2010, according to the U.S.
Department of Energys February 2002 Final Environmental Impact Statement for the Yucca Mountain, Nevada dumpsite. DOEs FEIS went on to project that if Davis-Besse operates for a total of 50 years (that is, till 2027), it will generate over 900 tons of irradiated nuclear fuel. But of course, FENOC has applied to NRC for permission to operate not 50 years, but 60. Given that Davis-Besse generates from 20 to 30 metric tons of irradiated nuclear fuel every year it operates, another decade of operations would add yet another 200 to 300 metric tons of irradiated nuclear fuel stored on-site. Altogether, well over 1,000 tons of irradiated nuclear fuel could accumulate at the Davis-Besse site over the course of 60 years of operations. Despite the presence of a growing number of dry storage casks (which have their own problems), Davis-Besses pool remains filled to capacity (well beyond the original design capacity, due to multiple re-rackings) with many hundreds of tons of irradiated nuclear fuel. Given that irradiated nuclear fuel discharged from Davis-Besses core every 18 to 24 months during refueling outages must be stored in the pool for a minimum of five years, accident and attack risks involving Davis-Besses pool will continue to be a significant safety and security issue for as long as Davis-Besse
operates, and in fact longer - until the pool is emptied of its ultra-hazardous contents (at which time the risks will shift over to problematic dry casks, risky transport by road, rail, or waterway, etc.) The Chernobyl nuclear catastrophe that began nearly 25 years ago, but will continue to unfold for centuries and millennia due to the radioactive contamination of vast regions, has shown how much damage 200 tons of nuclear fuel exploding and burning for ten days can do.
Thus, an even greater quantity of irradiated nuclear fuel stored in Davis-Besses pool cannot be dismissed as having zero risk whatsoever, or even as having less risk than Davis-Besses operating reactor core, containing as it does less nuclear fuel than the pool (albeit significantly higher in many shorter-lived hazardous radioisotopes that have yet to radioactively decay).
MAAP Code FENOC incorrectly found inadmissible Petitioners dispute regarding its use of the MAAP code to generate source terms. FENOC improperly and incorrectly alleges that Petitioners have provided no facts or expert opinion to establish that FirstEnergy has used the MAAP code improperly, or that the use of alternative source terms would have resulted in the identification of additional potentially cost-beneficial SAMAs for Davis-Besse. (FENOC Answer, Page 97)
Joint Petitioners are not required to prove our case at this juncture - this is not summary disposition.
Joint Petitioners referenced multiple sources in their contention. Examples included NRC, Brookhaven National Laboratory, and J. Schaperow.
FENOCs objection that Petitioners failure to meet their burden in this regard is particularly glaring given the widespread use and acceptance of MAAP code in the nuclear industry. (FENOC Answer, Page 98) But two wrongs dont make a right. Strength in numbers is not a valid defense of a flawed code. Groupthink, a word coined in the early 1950s, was
modeled after Orwells doublethink from his novel 1984. Groupthink is defined by the World English Dictionary as meaning a tendency within organizations or society to promote or establish the view of the predominant group. Just because MAAP is broadly used does not necessarily mean that it is free from the flaws we allege. In fact, closed-mindedness is not a healthy attitude to criticism, especially in realms as significant to public safety as the nuclear power industry.
NRC staffs Answer (at Page 80) agrees with Joint Petitioners position that the MAAP code has not been formally reviewed and approved by NRC. NRC staff says:
The Staff recognizes that Joint Petitioners have provided some support for the argument that MAAP may lead to lower consequences when compared to source terms generated by NRC Staff. Id. at 114. Specifically, the studies Joint Petitioners reference indicate that MAAP may lead to lower consequences when compared to the source terms in NUREG-1465. Id. Joint Petitioners also note that
[i]t has been previously observed that MAAP generates lower release fractions than those derived and used by NRC in studies such as NUREG-1150, id. At 113, which uses the Source Term Code Package [NRCs state-of the art methodology for source term analysis at the time of NUREG-1150] and MELCOR. Id. at 113 (quoting a Brookhaven National Laboratory study that independently analyzed the costs and benefits of one SAMA in the Catawba and McGuire license renewal proceeding).
NRC staff also expresses agreement that Joint Petitioners are correct that the MAAP code has not been formally reviewed and approved by the NRC, (Answer, Page 80) thus, that its use is not required.
FENOCs Arguments Against Contention 4c: The MACCS2 Code Used in FirstEnergys SAMA Analysis Is Outdated and Inaccurate (FENOCs Answer, Pages 98 to 105), Joint Petitioners contention designated THE SAMA ANALYSIS FOR DAVIS-BESSE USES AN OUTDATED AND INACCURATE PROXY TO PERFORM ITS SAMA ANALYSIS, THE MACCS2 COMPUTER PROGRAM (Joint Petitioners Petition and Request, December 27, 2010, beginning at Page 115)
Petitioners assert that the SAMA analysis FENOC uses for Davis-Besse utilizes an outdated and inaccurate proxy, the MACCS2 computer program.
FENOC incorrectly argues that this contention is inadmissible because it lacks an adequate factual basis, and that Petitioners fall short of establishing the materiality of their claims or a genuine dispute with FirstEnergy on a material issue of law or fact. (Answer, Page
- 98) It is clear that FENOC, like NRC staff, forgets that this is the preliminary pleading stage of these proceedings and that we are neither in the summary disposition nor hearing stage, as explained above.
For example, one material dispute of law or fact that we clearly establish is that The cost formula and assumptions contained in the MACCS2 underestimates the costs likely to be incurred as a result of a severe accident, explained in greater detail further below. (Petition and Request, Page 116) And, most certainly, we fulfilled our pledge to provide greater detail in the Petition further below.
For example, in the following section of our Petition and Request, we dispute the straight-line Gaussian plume model that is embedded in the ATMOS module of the code.
This model calculates air and ground concentrations, plume size, and timing information for all plume segments as a function of downwind distance. FENOC acknowledges (Answer, Page 108) that the straight-line Gaussian plume is inextricably embedded in the MACCS2 model when it states: the straight-line Gaussian ATMOS model cannot be replaced without replacing the MACCS2 code itself. In that particular section of our SAMA related contention, we dispute the assumptions regarding cleanup and health costs embedded in the code. In yet another section of our SAMA related contention, we dispute the averaging performed in the MACCS2 output file.
Joint Petitioners devoted separate sections to these subparts because each subpart contributes to the whole or fundamental dispute that FENOCs Environmental Report is inadequate because it underestimates the true cost of a severe accident at Davis-Besse in violation of 10 C.F.R.51.53 (C)(3)(II)(L) and further, and more accurate, analysis by FENOC is called for.
It is telling that even FENOC admits that there is no specific legal requirement that an applicant use the MACCS2 code in its SAMA analysis (Answer, Page 99)
FENOC argues, opposing Joint Petitioners assertion that the MACCS2 code is not quality assured and was developed for research purposes and not licensing purposes, that the contention also lacks a sound factual basis. (Answer, Page 100) However, Joint Petitioners key and relevant factual dispute was provided by an article written by David I.
Chanin. Mr. Chanin wrote the FORTRAN for the MACCS and MACCS2 codes. He specifically wrote the referenced paper because, as described in an endnote:
The QA distinctions between an NQA-1 "licensing code" and a "research code" like MACCS2 have been emphasized in light of the fact that MACCS2 calculations are being used to support the Severe Accident Mitigation Alternatives (SAMA) analyses required for the license renewal of commercial nuclear power plants. It seems to me that the code's QA shortcomings and the lack of input justifications are again being ignored, just as they were prior to DNFSB TECH-25 and the veritable firestorm that soon followed. D.C.]
FENOCs criticism of Petitioners statement that there is no explanation of exactly how [MACCS2] works - that the contention is spurious and reflects Petitioners failure to meet their pleading obligation, (Answer, Page 101) is incorrect. They argue that the MACCS2 Users Guide explains how it works and that Joint Petitioners must have known that because they reference the Users Guide. However, what Joint Petitioners know is what is and what is not in the Guide - information, and lack thereof, that FENOC apparently has missed.
FENOCs Arguments Against Contention 4d: Use of the Gaussian Plume Model in the ATMOS Module of MACCS2 (Answer, Page 105 to 115), Joint Petitioners Contention Designated USE OF AN INAPPROPRIATE AIR DISPERSION MODEL, THE STRAIGHT-LINE GAUSSIAN PLUME, AND METEOROLOGICAL DATA INPUTS THAT DID NOT ACCURATELY PREDICT THE GEOGRAPHIC DISPERSION AND DEPOSITION OF RADIONUCLIDES AT DAVIS-BESSES GREAT LAKES SHORELINE LOCATION (beginning on Page 116 of Petition and Request, December 27, 2010)
In this Contention, Joint Petitioners challenge the use of an inappropriate air dispersion model, the straight-line Gaussian plume, and meteorological data inputs that did not accurately predict the geographic dispersion and deposition of hazardous radionuclides at Davis-Besses Great Lakes shoreline location.
FENOC properly acknowledges that Joint Petitioners pled a number of disputes that include: the straight-line Gaussian plume model; sea breeze; plumes remaining concentrated over water resulting in hot spots; terrain effects; input data restricted to one year; and input data from one source, the onsite meteorological tower. FENOC does not take issue with Joint Petitioners dispute that the meteorological input data came solely from the onsite meteorological tower. Therefore, we can conclude that they agree with Joint Petitioners that disputes on these various issues exist.
FENOC, like NRC staff, forgets that requirements for a Petition to Intervene and Request for a Hearing are very different from those at summary disposition or a hearing. It is clear that these issues have been pled and that FENOC has been properly forewarned of what to expect at hearing. Examples abound.
FENOC incorrectly states, at Answer Page 106, that Petitioners scattershot references to the technical literaturewholly unsubstantiated by any expert opiniondo not constitute adequate factual support for the contention. Not true. Joint Petitioners provided more than adequate support for a pleading, including a plethora of citations to government studies, site specific studies, and more general but applicable research published in prestigious journal articles.
FENOC argues that Petitioners again provide no factual or expert support for their assertion as to why data collected at the Davis-Besse site meteorological tower would not reflect any sea breeze present in the site vicinity. (Answer, Page 114) FENOC likewise argues that Petitioners argument that the MACCS2 code is inappropriate because it fails to account for the behavior of plumes over water similarly falters for lack of adequate support. (Answer, Page 110) In addition, FENOC argues (Answer, Page 111) that our dispute that the straight line model
is inappropriate and cannot account for changes in terrain simply referred to an EPA Guidance that does not address radiological modeling for a severe reactor accident, but Instead, it addresses modeling of air pollution dispersion under the Clean Air Act. Are we to believe that gaseous and particulate radionuclides are not hazardous air pollutants? A common thread to FENOCs various arguments above is that they forget the central issue at this stage of the proceeding - what is and what is not required at the pleading stage.
FENOC in its arguments makes repeated reference to commentary and decisions in prior proceedings, especially to the on-going SAMA adjudicatory contentions in the license extension proceeding at Pilgrim Nuclear Power Station in Massachusetts (Answer, Pages 107-112, and 115). However these references are irrelevant. Those decisions were dependent on exactly what the intervenor(s) there did or did not plead or prove, and have nothing to do with whether a contention should be admitted here.
For example, at its Answer Page 112, FENOC cites the Commission as noting the relevant inquiry is not whether there are plainly better atmospheric dispersion models, but rather, whether the SAMA analysis resulted in erroneous conclusions on the SAMAs found cost-beneficial to implement (Pilgrim, CLI-10-11, slip op. at 37) But the above reference refers to the Commissions Remand of the SAMA contention back to the ASLB on March 26, 2010. That Petitioners (Pilgrim Watchs) Motion to Intervene was filed in May 2006, and was admitted by the ASLB in October 2006. It should have been clear to FENOC that pleading requirements are far less than at the remanded hearing stage.
Next, regarding FENOCs allegation that the document that Petitioners (sic) cite to support their terrain effects claim actually shows that the straight-line modeling limitation serves to increase conservatism, (FENOC Answer, Page 113, Emphasis in original) we find it telling that FENOC, in its repeated citations from the Pilgrim license extension proceeding, chose only to very selectively quote from intervenor Pilgrim Watchs SAMA filings; but avoided, for example, Pilgrim Watchs Brief in Response to CLI-09-11, at 11, that responded to the Commissions request for briefing on whether the straight-line Gaussian plume model was conservative. It is unnecessary to respond here. Suffice it to say, we will provide evidence at the
required stage here and, like at Pilgrim, present factual evidence that indeed the straight-line Gaussian plume is NOT conservative.
The core issue in Joint Petitioners contention is the FENOC did not choose a reasonable methodology, and there are models that are appropriate, up-to-date, reliable, and suitable to Davis-Besses site that would be reasonable - examples were provided.
At (5) on Page 113 of its Answer under Meteorological Monitoring Data, FENOC refutes our dispute that one year of meteorological data from a single collection point is insufficient. FENOC argues Petitioners again provide no factual or expert support for their assertion as to why data collected at the Davis-Besse site meteorological tower would not reflect any sea breeze present at the site vicinity. (Answer, Page 114) Petitioners are not required to defend or prove our case here. However we will provide a short response for the benefit of the ASLB - an appetizer. Seasonal wind distributions can vary greatly from one year to the next.
The simple fact is that measurements from a single anemometer will not provide sufficient information to project how an accidental release of a hazardous material would travel. For example, a sea breeze (or lake breeze given Davis-Besses Lake Erie shoreline location) effect will not be identified by a single onsite meteorological tower in cases when the sea breeze is just developing and for cases when the onshore component winds do not reach entirely from the ground to the anemometer height; instead, the anemometer would likely indicate an offshore wind indication. Further, in MACCS2 Guidance Report June 2004 Final Report page 3-8:3.2 Phenomenological Regimes of Applicability, it says that basing wind direction on the single on-site meteorological tower data ignores shifting wind patterns away from the site including temporary stagnations, re-circulations, and wind flow reversals that produce a different plume trajectory.
FENOCs Arguments Against Contention 4e: Assessment of the Economic Consequences of a Severe Accident, Including Decontamination, Cleanup, and Health Costs (Answer, Pages 115 to 130), Joint Petitioners contention designated USE OF INPUTS THAT MINIMIZED AND INACCURATELY REFLECTED THE ECONOMIC CONSEQUENCES OF A SEVERE ACCIDENT, INCLUDING DECONTAMINATION COSTS, CLEANUP COSTS AND
HEALTH COSTS, AND THAT EITHER MINIMIZED OR IGNORED A HOST OF OTHER COSTS (beginning on Page 135 of the Petition and Request, December 27, 2010)
In this contention, Joint Petitioners challenge the use of inputs that minimized and inaccurately reflected the economic consequences of a severe accident, including decontamination costs, cleanup costs and health costs, and that either minimized or ignored a host of other costs.
FENOC, like NRC staff, mistakenly believes that we are at the Summary Disposition stage of this process. Not so. Please refer again to the initial discussion of what is required, above.
FENOC argues that Contention 4e is inadmissible. They could not be more mistaken.
Decontamination and Cleanup Costs:
It is apparent that FENOC does not want to touch this issue any more than NRC, EPA or DHS want to take responsibility for cleanup, or industry to admit/advertise that Price-Anderson does not cover cleanup costs, only damages. It is the big Elephant in the Room. These revelations came to public light for the first time thanks to reporter Doug Guarino at Inside EPA, who uncovered the truth in November 2010 via the Freedom of Information Act.
However FENOCs arguments are ludicrous and disjointed on their face. Again we were not required to prove our case at this contention stage, or to provide an exhaustive list of possible bases, but simply to provide sufficient alleged factual or legal bases to support the contention and do so at the outset. We did - ample references, for example, were provided to government documents and the FENOC license extension applications ER SAMA section.
Inexplicably, FENOC believes that we are at summary disposition and says (at 91) that, Petitioners arguments lack sufficient specificity, lack adequate factual or legal support, and do not establish a genuine material dispute. (Answer, Page 116)
It is clear that FENOC either does not want to understand the issue or that they understand it only too well and base their argument upon misrepresentations of Joint Petitioners motion. For example:
FENOC spends considerable time muddying the waters about the differences between plutonium dispersal from weapons versus reactor accident. FENOC states at Page 117:
The Site Restoration Study indicates only that certain decontamination data may not be applicable to a plutonium dispersal accident. For example, it states that
[a]lmost all of the prior work in the U.S. and abroad on methods and effectiveness of radiological decontamination has been focused on fission products, and on time frames and conditions that have limited applicability to decontamination after a plutonium-dispersal accident. That document makes no such assertion with respect to a reactor accident. (Emphasis by FENOC)
It is clear that we did not ask for FENOC to base its analyses on plutonium dispersal in a nuclear weapons accident; instead, we made plain that a large problem with the MACCS2s code was that it, like its predecessor WASH-1400, assumes that the same methodology used to clean-up weapons events will be used after a severe nuclear reactor accident. The methods in MACCS2 (fire hosing and plowing under fields) are modeled assuming that they will be used to clean-up nuclear reactor accidents. Joint Petitioners explained why this is not acceptable for Davis Besses site. Radionuclides from reactor accidents differ from those released by a nuclear bomb explosion; therefore, they could not be cleaned up in the same manner, as quickly, or cheaply.
Further, because plowing under fields and fire hosing does not cleanup the radionuclides, but simply moves them into the groundwater or deeper into the soil to once again reappear (as in food crops and drinking water) and contaminate the area and its living beings, this method will not be acceptable to local officials and the public.
FENOC has a most interesting definition of conservatism. They claim, at Page 118, that moving contamination from one place to another in the same geographical, contaminated area adds conservatism to the MACCS2 code and justifies its use, disputing Petitioners.
FENOC misinterprets Petitioners reference to SAND-96-0957 (beginning at Answer, Page 116). They imply that we were advocating basing cleanup on a plutonium event. To the contrary, Joint Petitioners properly referenced the DOE document simply to point out that there were alternative models for cleanup and that DOE had moved far beyond NRC to improve methodology.
FENOC (Answer, Pages 123-125) misconstrues decontamination issues. They avoid the point by failing to say what they put into the MACCS2 code. Did FENOC take the Users Guides suggestion; and did FENOC use the sample problem data? These are questions to answer as we go forward in this proceeding.
FENOC apparently chooses to misunderstand Joint Petitioners references to Luna and Reichmuths referenced RDD studies for the US Department of Homeland Security. They were provided in the Petition and Request as a yardstick to indicate that if cleanup were properly assessed by FENOC in their SAMA, as required, that costs would be considerably higher, adding additional SAMAs as cost-beneficial. The studies provided likely costs per kilometer in urban to rural areas. Joint Petitioners thus logically concluded that a severe accident at Davis-Besse is likely to result in huge costs; costs not accounted for by FENOC, because of the type and magnitude of radionuclides released in comparison with a RDD type device. (Petition and Request, Page 140, December 27, 2010)
Health Costs:
Joint Petitioners dispute health costs used in the analysis - they were underestimated. The population dose conversion factor of $2,000/person-rem used by FENOC to estimate the cost of the health effects generated by radiation exposure is based on a deeply flawed analysis and seriously underestimates the cost of the health consequences of severe accidents. Joint Petitioners supported its dispute with reference to government documents, the National
Academies of Sciences, and independent research reported in respected technical journals. We fully satisfied requirements at this pleading stage.
Petitioners argue that FENOCs evacuation time input data into the code were unrealistically low and unsubstantiated; and that if correct evacuation times and assumptions had been used, the analysis would show far fewer numbers in the affected population will evacuate in a timely manner, increasing health-related costs. Petition and Request at Page 147. FENOCs claim that our dispute is inadmissible does not stand up.
FENOC refers to a sensitivity study on Page 124 of its Answer. However, their sensitivity studies, actually referred to throughout their Answer in addition to this Contention 4e relevant instance, simply entered different inputs into the same flawed model. To paraphrase Einstein, repeating the same mistake many times does not give a reliable answer. We supported our dispute as required at this stage and thereby satisfied our pleading. We are not required to prove our case at this time. Joint Petitioners note that once more FENOC referenced Pilgrim findings at Answer, Page 125. We remind the ASLB that a prior decision, that an Intervenor did not prove a contention at another reactor in another license extension adjudication process, has nothing to do with whether a contention should be admitted here.
FENOC dismisses the relevance of the CRAC-2 study cited by Joint Petitioners, stating (at Answer, Page 128): Petitioners also do not explain the relevance of this almost 30-year old studywhich used 1970 census data and the CRAC2 computer code It is certainly not Joint Petitioners fault that NRC has not published an update to CRAC-2 since 1982. Significantly, NRC attempted to keep the information in CRAC-2 from the public - it took Congressman Ed Markey of Massachusetts to force NRC to make the report public in the first place. We must also hasten to add that we have tremendous concerns that the update NRC is undertaking, State of the Art Reactor Consequence Calculations, so-called, raises serious concerns, yet again, that flawed modeling will lead to serious underestimates of radiological risks to the public. Joint Petitioners cited CRAC-2 to emphasize the very serious consequences that could result in Detroit/Windsor,
Toledo, or Cleveland - depending on which way the wind happened to be blowing when the catastrophic radiological release at Davis-Besse takes place - and hence the importance of preventing such a release in the first place, as through doing accurate SAMA analyses and taking the appropriate cost-beneficial actions in response, as FENOC is supposed to do.
Myriad Other Economic Costs Joint Petitioners allege that FENOC failed to include a myriad of other economic costs including the business value of property; loss and/or damage to infrastructure; costs of job training, unemployment costs, and litigation; and underestimated the value of farm land, for example, by not considering the value of the farm property for development purposes as opposed to agricultural, and farm land assessments are intentionally very low to encourage farming and open space. Contrary to FENOC, the issue is properly pled, and provides sufficient notice to them that this is a dispute to prepare for further down the road in this proceeding.
FENOCs Arguments Against Contention 4f: Statistical Analysis of Data (Answer Page 130 to 134), Joint Petitioners contention designated as USE OF INAPPROPRIATE STATISTICAL ANALYSIS OF THE DATA, SPECIFICALLY THE APPLICANT CHOSE TO FOLLOW NRC PRACTICE, NOT NRC REGULATION, REGARDING SAMA ANALYSES BY USING MEAN CONSEQUENCE VALUES INSTEAD OF, FOR EXAMPLE, 95TH PERCERNTILE VALUES (beginning on Page 149 of Petition and Request, December 27, 2010).
In this contention, Joint Petitioners challenge the use of inappropriate statistical analysis of the data - specifically the Applicant chose to follow NRC practice, not NRC regulation, regarding SAMA analyses by using mean consequence values instead of, for example, 95th percentile values. Thereby this important dispute is raised at the outset.
As Joint Petitioners have previously explained, the MACCS2 codes OUTPUT file does the averaging and ranks the data into a cumulative distribution function (CDF, not to be confused with Core Damage Frequency) - 50th quartile, mean, 90th quartile, 95th quartile, etc. FENOC chose to take the mean value; and, there is no NRC rule requiring the mean. The mean is the
wrong choice, for it underestimates consequences. A mean divides the sum by the number of entries. There are thousands of individual data entries so that dividing the sum by so many entries unreasonably dilutes the results. Further FENOC multiplied the mean by their estimate of the probability of the accident scenario. The point is that FENOCs choices - inputs and choice of averaging and probability - resulted in significantly underestimating costs.
In summary, Joint Petitioners satisfied pleading requirements for Contention 4 and we look forward to proving our case at the appropriate stages in the process ahead.
Final Miscellaneous Points FENOC more than once raised the issue that Joint Petitioners had copied their Contention Four from work done by other intervenors in earlier license extension proceedings. But this was certainly no secret - Joint Petitioners announced this at the very beginning of Contention Four, thanking New England Coalition and Friends of the Coast for their groundbreaking work at the Seabrook proceeding. Joint Petitioners were remiss in not thanking Pilgrim Watch and Riverkeeper for their even earlier groundbreaking work at Pilgrim and Indian Point, for it too was cited by Joint Petitioners.
At Page 82, FENOC charges that Joint Petitioners may not fully understand their own contention, portraying it thus as frivolous. What FENOC needs to fully understand is that Joint Petitioners, and area residents they represent, will not silently accept the serious radiological risks that the aging and deteriorating Davis-Besse atomic reactor inflicts on the region. Hence our Petition and Request.
At Page 85, Footnote 357, FENOC obfuscates the meanings of risk and consequence.
If a severe accident in fact does happen, that is, probability of risk equals 100%, then the consequences of course will not be small. The definition of risk is probability multiplied by consequence. 100% probability times consequence equals risk.
At Page 87, FENOC cites NRCs GEIS conclusion that the core damage and radiological release from such [intentional] acts would be no worse than the damage and release expected from internally initiated [accidental] events. FENOC adds that the U.S. Court of Appeals for the Third Circuit affirmed this conclusion. But Joint Petitioners must agree with Dr.
Ed Lyman of UCS, whose report Chernobyl on the Hudson? we cited. Intentional acts of terrorism targeted at a nuclear power plant would be designed to maximize radiological releases.
Equating this with accidents seems to us a fallacious assumption.
At Page 90, FENOC argues that New York Citys dense population raises different risk considerations at Indian Point than the population density surrounding Davis-Besse. However, Joint Petitioners insist that the dense populations represented by Detroit/Windsor, Toledo, Cleveland, etc. require that the utmost precautions be taken to prevent radiological releases at Davis-Besse, whether due to accidents or attacks, as by accurate SAMA analyses and appropriate cost-beneficial actions in response.
FENOC accuses Joint Petitioners of copying, nearly verbatim, from intervenor Riverkeeper in the Indian Point proceeding. Joint Petitioners freely admitted, as already mentioned, at the very beginning of their Contention Four, that New England Coalition and Friends of the Coasts Petition at Seabrook formed the model for its SAMA contention at Davis-Besse.
At Page 98, FENOC states Petitioners failure to meet their burden in this regard is particularly glaring given the widespread use and acceptance of the MAAP code in the nuclear industry. Joint Petitioners must point out that widespread use and acceptance does not necessarily mean it is correct, conservative, or protective of safety and environment. Joint Petitioners have mentioned the risks of groupthink above. The widespread use and acceptance of flammable fire barriers across the nuclear power industry does not make that practice right or acceptable or safe. Likewise, the deployment of irradiated nuclear fuel dry casks across the industry that violate basic quality assurance principles does not make that practice right, safe, or acceptable. Also, widespread use and acceptance of the illusion that Yucca
Mountain would solve the 54 year old problem of what to do with forever deadly commercial irradiated nuclear fuel did not make it so, as the projects recent cancellation has revealed. These are but three of countless examples from the nuclear power industry that could be mentioned, including flaws with the MAAP code, as Joint Petitioners have here contended.
This same reasoning applies to FENOCs citation, on Page 107, of a recent Commission ruling that the straight-line Gaussian plume model used in the ATMOS module of MACCS2 has been an accepted analytical approach for plume dispersion analyses in the nuclear industry for several decades. Again, long-time, widespread acceptance does not necessarily make something right. Hence Joint Petitioners contention. By the way, FENOCs reference to the Commission recently confirmed that MACCS2not AERMOD or CALPUFFis the most current, established code for NRC SAMA analysis is troubling to Petitioners. A several-decade-old, flawed code being the most current, established code for NRC SAMA analysis is troubling.
Similarly, FENOCs dismissal of Joint Petitioners concerns about lack of quality assurance on the MAACS2 code is reflective of a dangerous attitude apparent across the nuclear establishment regarding the safety significance of QA. QA problems, as mentioned just above, have been identified with dry cask storage, as by industry whistleblower Oscar Shirani, and NRC inspector Ross Landsman. But they have also been identified repeatedly at DOEs Yucca Mountain Project, by the GAO. Beyond Nuclear, Citizens Environment Alliance of Southwestern Ontario, and Dont Waste Michigan - Petitioners in this proceeding - have contended serious QA problems with the Fermi 3 new reactor proposal 30 miles northwest of Davis-Besse at Detroit Edisons Fermi nuclear power plant site, an issue that will now be heard by the ASLB. FENOCs dismissal of QAs significance - as by its implication at Page 100 that
NRC can do a lesser job of QA than DOE (that a SAMA analysis is to be held to a lesser standard than a DOE Documented Safety Analysis) - is reflective of a troubling trend apparent across the nuclear power industry and its regulatory agency. The fact that FENOC identified not one single SAMA that proved cost-beneficial seems to echo this trend.
FENOCs assertion at Page 101 that A SAMA analysis is not safety-related perplexes and troubles Joint Petitioners. It seems to indicate a perilous disregard by FENOC of the safety significance of SAMA analyses, and may explain why and how FENOC found not a single SAMA to be cost-effective. Of course the public bears the ultimate risk of such decisions by FENOC, while FENOC saves money at the expense of public risk.
Beginning on Page 108, FENOCs dismissal of experts cited by Joint Petitioners regarding the Great Lakes sea breeze effect is unacceptable. Joint Petitioners re-affirm that the NOAA NWS and Dr. Heidorn should be recognized as the experts that they are on this significant Great Lakes meteorological dynamic. It should also be emphasized that, whereas New England Coalition and Friends of the Coast at Seabrook, as well as Pilgrim Watch at Pilgrim, identified the significance of sea breeze effect for the dense population of metro Boston, in this proceeding, Joint Petitioners point to the significance of Great Lakes sea breeze dynamics for the dense populations in metro area such as Detroit/Windsor, Toledo, and Cleveland.
At Page 112, FENOC complains that Joint Petitioners did not include as an exhibit or provide with a reference link DOEs MACCS2 Guidance. But NRC and DOE were at one time the same agency (AEC), and are still closely affiliated, so we assumed that NRC had instant access to this document, and thus so does FENOC, which must work with its regulator NRC on an ongoing basis to fulfill NRC regulations.
Regarding Footnote 512 on Page 117 of FENOCs Answer, about 1% of irradiated nuclear fuel is comprised of plutonium that has built up during the course of the nuclear chain reaction in Davis-Besses reactor core. Likewise, even reactor fuel in the core undergoing fissioning will contain some quantity of plutonium, which builds up over time to that 1% level.
Any plutonium is significant because its various istopes are ultra-hazardous. As Joint Petitioners have mentioned earlier, Davis-Besse had 557 metric tons of irradiated nuclear fuel stored on-site, in both the pool and dry casks, as of spring 2010. If Davis-Besse operates for a total of 50 years, that amount will grow to over 900 metric tons. And if operated a decade beyond that, as FENOC has applied to NRC for permission to do, the amount of irradiated fuel at Davis-Besse could grow to more than 1,000 metric tons. 1% of 1,000 metric tons is 10 metric tons of plutonium, or 10,000 kilograms of plutonium. Typical nuclear weapons contain only several kilograms of plutonium, at most. Thus, the amount of plutonium at Davis-Besse would represent thousands of nuclear weapons worth. It would be available for release to the environment in the event of a severe accident. This establishes clearly the significance of a potential plutonium release from Davis-Besse in the event of a severe accident. However, it must be kept in mind that plutonium isotopes represent just a handful of the hundreds of hazardous radioactive isotopes that would be released by Davis-Besse in the event of a severe accident, isotopes that are not even present in undetonated nuclear weapons.
FENOC at Page 120 of its Answer cites a Commission statement claiming that acknowledged difficulties of the Chernobyl clean-up may largely have been due to poor training, lack of equipment, and a nearly complete break-down in leadership. Petitioners would point to the U.S. experience in the aftermath of Hurricane Katrina as an example of how such difficulties could be experienced right here at home in the aftermath of a nuclear power plant
disaster as well. Inside EPAs November 2010 revelations about ongoing disputes between NRC, EPA, and FEMA over which agency would lead a post accident clean up, and where funding would come from to do the clean up, show that authority in this country is indeterminate. And if FENOC and NRC assume that the U.S. military could be called upon to take part in dealing with a severe nuclear accident at Davis-Besse and its aftermath, it should be kept in mind that, as with the USSR in 1986, the U.S. military is stretched thin due to its current war in Afghanistan, not to mention its additional current war in Iraq.
At Page 122-123 of its Answer, FENOC charges that Petitioners here do not furnish any alleged facts, documentary support, or expert opinion - i.e., anything beyond pure assertion - for their loss of economic activity argument. Petitioners are surprised by FENOCs ignorance of economic activity in northwest Ohio where Davis-Besse is based. This includes not only the recreation and tourism associated with the Lake Erie Islands, the abundant fisheries to be found in Lake Erie, but also the industrial base represented by the combined Detroit/Windsor, Toledo, and Cleveland metro areas, including, as mentioned elsewhere in this filing, the largest factory for solar PV panel production in the world, FirstSolar in Perrysburg, Ohio. In fact, the Great Lakes region, of which northwest Ohio is a part, is one of the biggest regional economies on the planet. The loss of economic activity at risk if Davis-Besse suffers a severe accident is self-evident.
In response to FENOCs repeated complaints that Joint Petitioners merely copied, or cut and paste, their Contention Four from other intervenors in other proceedings, we must respond that those living in glass houses should not throw stones. The NRC OIG in 2007 reported that, in the context of reactor license extensions, NRC staff had copied, at times nearly verbatim, from nuclear utility ERs, in preparation of NRC environmental documents presented as independent
analyses. Later, NRC OIG also documented that NRC staff had destroyed working documents that led up to, and supposedly justified, their decisions to grant license extensions. Nuclear utilities receiving license extensions after such NRC staff cut and paste performances benefitted, of course, by receiving the license extensions despite less than independent NRC staff safety and environmental analyses. It should be kept in mind that NRC is a federal agency, with a billion dollar plus annual budget, and over 4,000 staff at its disposal. Joint Petitioners, on the other hand, are small non-profit organizations, whose total annual budgets, if added together, represent much less than what FENOC makes in a single day, in net profit, at Davis-Besse.
Therefore, yes, groups like ours do work with similar groups across the country to pool resources and not recreate the wheel unnecessarily, such as we did on our SAMA contention.
We are also surprised at FENOCs complaint at Page 128 of its Answer, in regards to Joint Petitioners citation of CRAC-2, that This document is not attached to the Petition as an Exhibit, and counsel has been unable to locate a document with this title, author, and date that is readily available in the public domain. Nor do Petitioners identify the relevant pages of this document. Petitioners failure in this regard deprives the Board and other participants of the ability to readily evaluate the accuracy (or inaccuracy) of Petitioners characterization of the referenced document. CRAC-2 is a well known report within the nuclear power establishment.
It is an NRC document. Its findings are clearly identifiable within the report.
February 23, 2011 UNITED STATES OF AMERICA NUCLEAR REGULATORY COMMISSION Office of the Secretary In the Matter of: ) Docket No. 50-346 FirstEnergy Nuclear Operating Company )
Davis-Besse Nuclear Power Station, Unit 1 )
(Regarding the Renewal of Facility )
Operating License NPF-003 for a 20-Year Period) )
)
CERTIFICATION OF SERVICE I hereby certify that a copy of the foregoing JOINT INTERVENORS COMBINED REPLY IN SUPPORT OF PETITION FOR LEAVE TO INTERVENE (CORRECTED VERSION) was sent by me to the following persons via electronic deposit filing with the Commissions EIE system this 23rd day of February, 2011:
Administrative Judge Office of the Secretary William J. Froehlich, Chair U.S. Nuclear Regulatory Commission Atomic Safety and Licensing Board Panel Rulemakings and Adjudications Staff U.S. Nuclear Regulatory Commission Washington, DC 20555-0001 Washington, DC 20555-0001 E-mail: hearingdocket@nrc.gov E-mail: wjf1@nrc.gov Office of the General Counsel Administrative Judge U.S. Nuclear Regulatory Commission Dr. William E. Kastenberg Mail Stop O-15D21 Atomic Safety and Licensing Board Panel Washington, DC 20555-0001 U.S. Nuclear Regulatory Commission Brian G. Harris Washington, DC 20555-0001 Megan Wright E-mail: wek1@nrc.gov Emily L. Monteith E-mail: Brian.Harris@nrc.gov; Megan.Wright@nrc.gov; Emily.Monteith@nrc.gov Office of Commission Appellate Adjudication U.S. Nuclear Regulatory Commission Mail Stop: O-16C1 Washington, DC 20555-0001 E-mail: ocaamail@nrc.gov Michael Keegan Dont Waste Michigan 811 Harrison Street Monroe, MI 48161 E-mail: mkeeganj@comcast.net Stephen J. Burdick Morgan, Lewis & Bockius LLP 1111 Pennsylvania Avenue, N.W.
Washington, D.C. 20004 Phone: 202-739-5059 Fax: 202-739-3001 E-mail: sburdick@morganlewis.com Respectfully submitted,
/s/ Kevin Kamps & submitted by Digital Certificate pro se on behalf of Petitioners Kevin Kamps Radioactive Waste Watchdog Beyond Nuclear 6930 Carroll Avenue, Suite 400 Takoma Park, MD 20912 Tel. 301.270.2209 ext. 1 Email: kevin@beyondnuclear.org Website: www.beyondnuclear.org