Invited Presentations
Public Comments
Invited Presentation
Presentations by Washington River Protection System’s Contractors
FFRDC Team’s Presentations
Stakeholders’ Presentations
Public Comments
Submitted Written Comments at the Public Meeting
Submitted Written Comments to the National Academies of Sciences, Engineering, and Medicine Darryl Siemer, a consulting scientist who is retired from the Idaho National Laboratory, submitted a number of comments via e-mail.
Invited Presentations
Committee Members’ Presentations
Stakeholder Presentation
FFRDC Team’s Presentations
Stakeholder Presentation
Public Comment
Submitted Written Comment to the National Academies
Invited Presentations
Committee Member’s Presentation
Stakeholders’ Presentations
FFRDC Team’s Presentations
There were no formal presentations. The FFRDC team and the National Academies committee had a 3-hour long discussion about the FFRDC’s incomplete draft report and next steps toward completing the report.
Invited Presentations
Committee Member’s Presentation
Stakeholder Presentation
FFRDC Team’s Presentations
Public Comment
Comments received at this meeting from stakeholders and members of the public are included in the congressionally mandated comment period.
Invited Presentations
Committee Member’s Presentation
FFRDC Team’s Presentations
Stakeholders’ Presentations
Public Comment
that the cleanup “challenges tilts decision making towards faster, cheaper solutions at the expense of environmental protectiveness and human health and safety”; efforts to find alternatives to vitrification “have all ended with the conclusion that nothing proposed is ‘as good as glass’”; “firmly believes that waste containing long-lived radioactive toxins that will take millions of years to decay should not be buried at Hanford above an aquifer that feeds into the Columbia River” and “that cost savings should not be the dominating factor that drives cleanup decisions … and can often be deceptive”; for example, “if further research shows that the getters are not guaranteed to confine the technetium-99 and iodine-129 in grout form and pretreatment is required to remove these radionuclides prior to putting it in grout form, those cost savings could quickly disappear”; expresses concern about DOE’s “enthusiasm” for grout for SLAW, “despite the need for further research and development” and “seems premature to declare that there is a clear scientifically defensible path forward for grout … under the assumption that further study and research will confirm the best-case scenarios”; their technical concerns include: that “the grout form proposed by the FFRDC report is itself toxic and a potential threat to the environment”; “long-term integrity of grout is untested”; grouting “will not effectively bind residual high-level waste components such as iodine-129 and technetium-99”; “Hanford’s climatic and soil environments are particularly harsh for grout monoliths”; “Grout performance and the rate of groundwater flow through the grout monolith is critically dependent on near-perfect, fracture-free, installation”; “Future use scenarios assume continuous institutional controls over the entire life of the project, including unrealistic restrictions on land uses”; “Climatic scenarios exclude dam failures, Columbia River flooding, concentrated rainfall events, glacial flooding/damming, and climate change-induced alterations in evapotranspiration/rainfall, all of which are plausible and even predictable events for this region,” October 25, 2019.
[and] was perplexed that the study did not include an obvious alternative involving pretreatment, [in particular] an alternative with Tc-99 removal pretreatment using ion exchange resin, as described in Section 3.1.2.3 [of the FFRDC report], and separate waste stream management. That alternative, combined with enhanced grout with an iodine getter (e.g., layered bismuth hydroxides, in a Portland cement-based grout formulation) would eliminate the chemical competition to maintain a reducing environment to Tc-99 retention within an otherwise oxidizing environment”; (3) “While the research results for enhanced grout and ceramic waste form FBSR since the 2012 Tank Closure and Waste Management Environmental Impact Statement (TC&WM EIS) are encouraging, the State considers these two waste forms in the research and development stage … [and] still require additional development and long-term testing before they can be considered proven”; (4) “the figure in Appendix F [of the FFRDC report] presents the data in a way that makes it appear vitrified waste, rather than the secondary waste from the vitrification process, contributes most of the I-129 to groundwater. The State believes that this should be corrected. … since the 2012 TC&WM EIS it has been known that “some of the secondary waste would have to be treated with improved grout formulations. Vitrification alternatives analysis should not be unfairly penalized by treating the secondary waste with lesser performing grout”; (5) “while it may be possible to control future releases of chromium, nitrate, Tc-99, and I-129 from IDF (by controlling the waste forms, limiting [what] is disposed of in IDF, or both), there is little to no possibility of controlling the future release of [these contaminants] from waste already disposed of to the soils across the Hanford Site. These additional contributions are why the State is looking for results that are significantly lower than the EPA drinking water MCLs”; (6) “agree that the term [‘as good as glass’] needs to be objectively defined. A detailed approach to this definition was developed in 2003 timeframe when the ‘as good as glass’ term was first coined and agreed to between Ecology and the United States Department of Energy (DOE). The State would welcome an opportunity to rekindle the discussion around a comprehensive working definition with DOE and DOE’s selected technical community representatives”; (7) “would have appreciated it if the FFRDC had estimated the quantity of low activity waste that might require Land Disposal Restriction (LDR) pretreatment for LDR organics and LDR metals” and what are the fractional amounts of various types of waste considering the different potential waste forms that may need additional treatments to be compliant with LDR requirements; (8) Review #3 “appeared to advocate consideration of enhancing the disposal facility design to enhance the performance of each waste form.… If there is a proven basis for considering these kinds of disposal facility enhancements in relation to long term performance, (e.g., substantially greater than 1,000 years), the State asks that the Committee refer that basis. If there is none, the State asks that these comments be removed from the NAS’s review”; (9) “The most significant new element that could change SLAW technology selection is the potential availability of an out-of-state commercial disposal facility, Waste Control Specialists (WCS) in Texas. The state of Washington is cautiously optimistic about the WCS facility and its potential as a disposal site for Hanford’s SLAW”; (10) agree with the committee that the specifics on the Performance Evaluation “analysis were not transparent, and would require disclosure of more specific information prior to State acceptance”; (11) “concur with the Committee’s comments regarding the consideration of risk in the FFRDC report” and particularly appreciated the comments that “the cost estimates did not include consideration of identified risks, e.g., increasing the estimate uncertainty range, and the risk induced by funding uncertainty” and that “the study does not consider the legal regulatory documents that would need to be changed and the cost and schedule risks if a technology other than vitrification is used”; (12) there might be significant delays—at least a decade—in the need for SLAW facilities because of the September 4, 2019, DOE notification that the High Level Waste (HLW) Facility and Pretreatment (PT) Facility could be delayed beyond the milestones contained in current version of a consent decree,” the pending results of DOE’s analysis of alternatives, discussions about the continued need for sludge washing, and the potential for Direct Feed LAW operations creating additional available tank volume in the time before startup of HLW processing; (13) “While this FFRDC study might be a valuable first stepping stone toward
selection of a SLAW treatment technology other than vitrification as a general proposition, it is not sufficient to be acceptable as the basis for selection of a SLAW treatment technology other than vitrification for on-site disposal. This is because the enhanced grout and FBSR waste forms have not yet proven to have long-term performance”; (14) “was heartened that NAS included the ‘Considerations for Decision-Makers’ in their review”; highlights that there has been one double-shell tank failure, AY-102, and three years were required to retrieve the contents; four more double-shell tanks are in similar condition; in addition, double-shell tanks’ availability will further decrease during DFLAW operations and due to Tank Side Cesium Removal pretreatment; therefore, the state of Washington wants to avoid “any technology that will require additional research and development where possible, because the evidence is mounting that the existing tank infrastructure is running out of capacity and time,” October 31, 2019.
ion that the R&D will be an ongoing need during development and operation of the treatment facilities, and that the current investment in directly supporting R&D is insufficient”; “encourages the Committee to recognize that Hanford also competes for resources across the entire DOE Environmental Management mission, and greater expenditures at Hanford will likely slow progress at other sites”; believe that it would be incomplete for the committee “not to include analysis of options for SLAW disposition using the current HLW definition adopted by the Department” [in the Federal Register notice in June 2019], but they note that this definition has yet to be implemented at Hanford; highlights that Review #3 “begins with the premise that there is a ‘perceived agreement’ that the final waste form for tank SLAW will be vitrification or another final waste form that is ‘as good as glass’”; “DOE has not entered into any such agreement, and CRESP urges that this error in [Review #3] be corrected” and “should make clear that the Hanford Federal Facility Agreement (FFA), which is the legally binding agreement, … contains no such agreement”; Review #3 “does not address the important issue of regulatory authority over mixed waste, and its implications for regulation of SLAW. RCRA regulators have the authority to regulate the chemically hazardous aspects of mixed waste, whereas regulators with nuclear regulatory authority—here DOE—have authority over the radioactive components. Under this allocation, RCRA regulators do not have authority to impose different regulatory requirements depending on the radioactivity of mixed wastes unless those differences affect the chemically hazardous character of the wastes”; “Developing an adequately protective and cost-effective treatment plan for non-HLW SLAW wastes requires that DOE, Washington state, and EPA fully and carefully consider the potential applicability of all available LDR flexibility mechanisms…. The analysis should evaluate the prospects for each major category of non-HLW SLAW waste stream to meet the criteria required for regulatory approval for use of each of the RCRA LDR flexibility mechanisms.… If the analysis is not possible for this Report, we strongly recommend that it be considered for a follow-on NAS study”; there is the need for a more accurate inventory of RCRA tank wastes and that the current operating assumption is that all of the tanks contain all of the hazardous materials under RCRA, thus substantially increasing the costs for cleanup; there is a need to understand the impact of RCRA tank closure requirements on SLAW volume; the report “should evaluate a full range of disposal site options, both on-site and off-site” and in particular, should consider “the Nevada National Security Site (NNSS) as a potential disposal site for Hanford SLAW”; underscores the noncompliance with the Federal Facility Compliance Act (FFCA) at the IDF such that the FFCA provides that requirements to federal facilities apply “in the same manner, and to the same extent” as requirements applicable to private parties and to “impose on Hanford a requirement that LAW be vitrified or the equivalent, when no such requirement is imposed on private LAW disposal sites, could constitute a violation of the parity requirement of FFCA,” October 31, 2019.
the process duration is compressed that means the tank waste feed is being treated at a rate much faster than was used as the basis for design of the WTP LAW Off-Gas treatment system, or the tank waste effluents management system. The promise of an easy fix with good glass must be evaluated in terms of the concentrations in the off-gas effluents, and whether the increased off-gas burden creates equipment capacity problems, including at ETF, or equipment corrosion problems, due to higher concentrations of halides, for example. It may be premature to suggest relying on better glass as a basis for deleting secondary LAW treatment. This will be especially true if the DFLAW off-gas and effluents systems do not perform as advertised,” November 6, 2019.