Appendix 1 : Staff Responses to Public Comments on Addendum 1 and the Proposed Rule

THE SCOPING PROCESS

The proposed amendments to 10 CFR 51.53(c)(3)(ii)(J) and (M) were published in the Federal Register on February 26, 1999 (64 FR 9884-88), and a 60-day comment period that ended on April 27, 1999, was provided. A Notice of Availability for NUREG-1437, Vol. 1, Addendum 1 appeared in the same issue of the Federal Register (64 FR 9889) and included a solicitation for public comments through April 27, 1999.

Thirty-one comment letters were received on the proposed rule from power reactor licensees, State and local Government agencies, the nuclear power industry and its legal affiliations, a public interest group, and an individual. Most of the comments were from the State of Nevada, Clark and Nye Counties, Nevada, and local government entities in Nevada. These comments focused on the NRC not involving Nevada in scoping and designing the study in Addendum 1 and on perceived deficiencies in the scope and thoroughness of the analysis in the Addendum. The State of Utah also submitted extensive comments that focused on concerns with the scope and thoroughness of the supporting analysis in Addendum 1, including the lack of consideration of the proposed Private Fuel Storage Facility at Skull Valley, Utah. Industry comments focused on clarifications in the rule language.

Written comments were received from the following agencies, organizations, and individuals:

RESPONSES TO COMMENTS

The written comments have been summarized and grouped into issue categories. As a result of the NRC staff's review of all written comments, some modifications and clarifications have been incorporated into Addendum 1--notably, the use of more conservative assumptions in the analyses and a fuller explanation of those analyses. In addition, the rule language has been edited for clarification. The NRC staff has also prepared responses, given below, to the issues raised by the commentors.

Issue 1--Public Notice

Comment: The titles of the notices published in the Federal Register were inaccurate and misleading because they do not clearly indicate the subject matter of the proposed rule and Addendum 1 that addresses transportation of spent nuclear fuel.

Response: The NRC believes that the titles properly reflect the regulatory action being taken. As required by NRC regulations,(1) a notice of the proposed rule and a Notice of Availability of Addendum 1 were published in the Federal Register (64 FR 9884 and 64 FR 9889, February 26, 1999). While the notice's title did not include the specific term "transportation" the titles define the subject matter of the regulation to be affected; the title of the proposed rule is "Changes to Requirements for Environmental Review for Renewal of Nuclear Power Plant Operating Licenses." The title of the Notice of Availability is "Changes to Requirements for Environmental Review for Renewal of Nuclear Power Plant Operating Licenses, Availability of Supplemental Environmental Impact Statement." Addendum 1 supplements specific sections of NUREG-1437, Generic Environmental Impact Statement for License Renewal of Nuclear Plants (May 1996). This limited function is indicated by the title of Addendum 1, Generic Environmental Impact Statement for License Renewal of Nuclear Plants: Main Report Section 6.3--`Transportation,' Table 9.1 `Summary of findings on NEPA issues for license renewal of nuclear power plants,' Draft Report for Comment.

The rule change and the supporting Addendum 1 affect only the plant-specific environmental analysis required to be submitted in the Environmental Report of an applicant for the renewal of a nuclear power plant operating license and the plant-specific supplemental environmental impact statement prepared by the NRC. Even though the analysis in Addendum 1 focuses on spent-fuel shipments converging on the proposed repository at Yucca Mountain, Nevada, that analysis and the resulting rule affect only the review requirements for renewal of an individual nuclear power plant operating license. It is not intended that Addendum 1 or the revised rule support any other regulatory decision by the NRC.

Issue 2--Communications

Comment: NRC failed to consult with Nevada State agencies, Nevada local governments, and with Nevada Indian Tribes.

Response: As discussed above, a variety of organizations and government agencies submitted substantive comments in response to the proposed rule. The NRC has considered these comments and, in many cases, altered its analysis as a result of this input. Prior to issuance of the proposed rule for comment, however, the NRC did not seek any pre-publication input from Nevada state agencies, Nevada local Governments, and Nevada Indian Tribes for the following reasons. First, the rule involves a narrow aspect of the environmental review of individual nuclear power plant license renewal decisions, which is a regulatory decision completely separate from the regulatory requirements that will guide the NRC licensing review of a HLW repository and from the decision process leading to a DOE site recommendation on Yucca Mountain, Nevada, the site DOE currently has under study. This rule amends the December 18, 1996, rule with respect to two questions not adequately answered:

1. Are the current environmental impact values in Table S-4, based on several destinations, still reasonable to incorporate in a license renewal review that assumes a single destination for spent fuel at Yucca Mountain, Nevada?

2. Are the current environmental impact values in Table S-4 (which are based on fuel enriched to no greater than 4 percent, the average level of irradiation of spent fuel not exceeding 33,000 MWd/MTU, and shipment no less than 90 days after discharge from the reactor) still reasonable to incorporate in a license renewal review of plants that may use fuel enriched up to 5 percent and potentially ship spent fuel with a burnup of up to 62,000 MWd/MTU?

The amendment has no direct regulatory impact on any entity within Nevada. The selection of Yucca Mountain for the generic evaluation of transportation impacts was made because that site is currently the only one under consideration for a high-level-waste (HLW) repository. Before HLW is actually transported to Yucca Mountain, Nevada, the State, local Governments, Indian Tribes, and the public have the opportunity to provide input on site-specific transportation impacts by commenting on DOE's draft EIS for the proposed repository at the Yucca Mountain site, which was made available for a 180-day comment period beginning on August 13, 1999 (http://www.ymp.gov/).

Also, the need for and scope of the current rule amendment were identified within the context of a preceding rulemaking that specified the plant-specific content of the environmental review of applications for the renewal of individual nuclear power plant operating licenses. The previous final rule was published in the Federal Register first on June 5, 1996 (61 FR 28467), and again with minor modifications on December 18, 1996 (61 FR 66537). The Commission stated in the December Federal Register notice, "as part of its efforts to develop regulatory guidance for this rule, the Commission will consider whether further changes to the rule are desirable to generically address: (1) The issue of cumulative transportation impacts and (2) the implications that the use of higher burn-up fuel have for the conclusions in Table S-4. After consideration of these issues, the Commission will determine whether the issue of transportation impacts should be changed to Category 1."

Issue 3--Transportation Analysis

Comment: NRC failed to consult relevant Yucca Mountain transportation risk and impact studies.

Response: The publications cited by commentors have been reviewed for information that may be of direct use within the limited focus and purpose of the current rule. Most of the information in these documents was found to be potentially more relevant to a detailed site-specific review of Yucca Mountain than to the generic analysis for this rule. That information has been brought to the attention of those organizational units within the NRC responsible for activities relating to DOE's study on the Yucca Mountain site so they can appropriately consider the information in any future prelicensing activities involving Yucca Mountain. Specific to the current rule, the demographic data used as inputs to the RADTRAN computer code, which was used to generate the impact analysis in Addendum 1 were more current than data used in many of the studies cited by the commentors.

Comment: NRC failed to consult the full spectrum of transportation mode and route scenarios.

Response: The purpose of this rule and associated analysis is to reach conclusions regarding the likely environmental impact of license renewal. As noted above, this amendment is an addition to generic assessments of license renewal environmental impacts already codified in the Commission's regulations at 10 CFR Part 51, Subpart A, Appendix B. It is not an environmental impact statement for a repository at Yucca Mountain for which DOE is responsible and, as such, does not delve into the expansive range of different transportation modes and route scenarios that would be considered in the context of a decision on Yucca Mountain as the possible site for the facility itself. Instead, the NRC has sought to determine a conservative estimate of the likely impacts from transporting fuel and waste generated, during the license renewal term, in the vicinity of a potential repository. In doing so, the NRC considered only those transportation modes and route scenarios that would likely result in the greatest impacts. For the proposed rule, the NRC staff--in consultation with the DOE staff--determined that truck shipments through densely populated areas of Clark County, Nevada, would have the highest potential impacts among the alternative transportation scenarios and modes that would receive serious consideration in decisions relating to the suitability of the site undergoing study for a repository at Yucca Mountain. The NRC continues to believe that using these route scenarios and modes to generate conservative estimates is reasonable for the purpose of this rulemaking.

Comment: There was insufficient consideration of routine transportation radiological risks due to use of an average dose rate lower than the regulatory limit.

Response: The RADTRAN analysis reported in the final Addendum 1 has been modified to use the most conservative assumption that the radiation levels for all shipments are at the regulatory limit of 0.1 mSv/hour [10 mrem/hour] at 2 m [6.6 ft] from the shipment vehicle surface. As noted in Section 2.2.3 of Addendum 1, this assumption is sufficiently conservative to bound the analysis of routine transportation radiological risk and allow a reasonable assessment of that risk. Actual average radiation levels and associated doses would be much lower because shipments must be designed so that the regulatory limits are not exceeded. The use of the regulatory limits in the revised analysis results in higher dose estimates for incident-free transportation. However, these revised estimates are still small as defined in 10 CFR Part 51, Subpart A, Appendix B. Consequently, the conclusion regarding the radiological risks of routine transportation remains valid.

Comment: There was insufficient consideration of routine transportation radiological risks to members of the public residing, working, or institutionally confined at locations near shipping routes.

Response: The analysis encompasses members of the public residing, working, or institutionally confined at locations near shipping routes by assuming that the resident population along the transportation routes is exposed to every shipment. The text of Sect. 2.3 of Addendum 1, has been revised to state this assumption and its effects on the revised analysis more clearly. In addition, more conservative assumptions of truck speed have been used in the revised RADTRAN analysis conservatively thus extending the exposure time to individuals along the transportation route. These assumptions further ensure that members of the public cited by the commentors would be encompassed by the dose and risk assessments. As expected, the use of these more conservative assumptions leads to higher estimates of radiation dose to the public. However, these revised dose estimates remain well below regulatory limits for members of the public and small compared to natural background and other sources of radiation exposure.

Several commentors indicated that Addendum 1 should focus on unique and location-specific circumstances of the transportation routes and population centers. However, the analysis in Addendum 1 is generic and was designed to support only the limited scope of the decision regarding this rule change. The NRC believes that the routes chosen represent a conservative analysis due to the higher number of people who live along these routes. Because the purpose of this rule is to provide a generic analysis for the limited purpose of determining the likely impact of transportation during the license renewal term, the large analytical effort required for the identification of specific population locations and traffic circumstances is not warranted within the context of the current rule. Although the comments raise valid issues, those concerns should be resolved within the context of studying, and making decisions concerning, the suitability of the candidate repository site at Yucca Mountain and regulatory requirements governing transportation of spent fuel.

Comment: There was insufficient consideration of radiological risks resulting from traffic gridlock incidents.

Response: Traffic gridlock incidents are not specifically analyzed in NUREG-1437 because of the limited scope and generic nature of the analysis (see response to comment on consideration of risks to members of the public, above). However, the revised RADTRAN analysis includes approximately two hours of stationary time in Clark County (during a 100 to 140 mile trip depending upon the route) for each truck shipment; and traffic gridlock could be one of the reasons for the truck being stationary.

To a limited extent, the incorporation of more conservative assumptions of truck speed into the revised RADTRAN analysis compensates for an analysis of traffic gridlock by allowing for increased exposure time at any given point during transport. As noted earlier, these revised assumptions lead to higher but still small dose estimates. In addition, the routes used in the analysis in Addendum 1 were deliberately chosen to maximize estimated dose. Actual routes would be less likely to have significant areas where traffic gridlock occurs. The selection of the actual routes, for example, would comply with the U.S. Department of Transportation's Federal Highway Administration regulations (49 CFR Part 397, Subpart D) that require minimizing the time in transit (i.e., avoiding periods of great traffic congestion) for routing radioactive shipments.

Comment: There was insufficient consideration of routine transportation radiological risks to vehicle inspectors and escorts.

Response: The RADTRAN analysis in the revised Addendum 1 conservatively uses the regulatory dose rate limit of .02 mSv/hour (2 mrem/hour) for the vehicle crew. In addition, a discussion of potential doses to escorts has been included in Addendum 1, Section 2.2.3. In the analysis, both the escorts and drivers are assumed to be exposed to the regulatory limit, although the dose to the escorts would realistically be less than that to the drivers. Even with these more conservative assumptions, the estimated dose and risk to the crew are small and below regulatory limits.

The risk to vehicle inspectors would be encompassed by the addition of stationary time for the transport truck in Clark County (see response to comment about traffic gridlock, above). Again, the estimated dose and risk are increased by the use of more conservative assumptions; but they remain small and below regulatory limits.

Comment: There was insufficient consideration of severe transportation accident risks.

Response: The Commission has evaluated the potential radiological hazards of severe transportation accidents involving truck and rail spent nuclear fuel (SNF) shipments (NUREG/CR-4829, " Shipping Container Response to Severe Highway and Railway Accident Conditions" February 1987, commonly referred to as the modal study). The modal study evaluated SNF shipping casks certified to NRC standards against thermal and mechanical forces generated in actual truck and rail accidents. This evaluation included an assessment of cask performance for a number of severe transportation accidents, including the Caldecott Tunnel fire. The modal study concluded that there would be no release in 994 of 1,000 real accidents, and that a substantially lower fraction of accidents could result in any significant release. These results when combined with the probability of a severe accident involving a shipment of SNF, demonstrate that the overall risk associated with severe accidents of SNF shipping casks is very low. The results of the modal study were factored into the analysis for this rulemaking, as an input to the RADTRAN computer code. Additional analyses were performed to address the possible impacts of accidents involving higher burnup fuel.

The consequences associated with an individual SNF shipment have an upper bound, based on the amount of material in the package, the availability of mechanisms to disperse the radioactive contents, the locations and number of receptors, and post-event intervention than would occur. Further, this upper bound in transit might reasonably be expected to be less than that at the origin or destination points (where more SNF would be stored), and some events themselves might be expected to have greater consequences than the damage they cause to the SNF cask. The NRC recognizes that there are some conceivable events (not necessarily traditional 'transportation accidents'), that might be hypothesized to occur to a SNF cask while in transport. Even though these events have an extremely low probability of occurring, they might result in high consequences if they were to occur. The NRC considers these events to be remote and speculative and thus, does not call for detailed consideration. Because the NRC traditionally considers risk to be the product of the probability of an event and its resultant consequences, events with such low probability of occurring have a negligible contribution to the overall risk. In addition, as the probabilities of the events become very low, the value of insights to be gained, for use in regulatory decisions, is not apparent.

Comment: The study underestimates Clark County's residential population and growth rate. In addition, the study does not account for the large nonresident population, resulting in underestimates of risk and impacts.

Response: In keeping with the generic nature and limited intent of the analysis, the original analysis used best available data and best estimates of existing population and population growth rates. In response to commentors' concerns and to reflect the potentially large population growth rate of Clark County, the NRC staff has incorporated higher population estimates into the analysis to provide conservative (higher than best estimate) assessments of potential impacts. However, as indicated by the comment, the task of estimating the impacts on the area population is more complex than assuming a population growth rate. Both the rate of growth of the population and changes in location of the population within the county are important. As stated in Addendum 1, populations within a half mile of the transportation route are the most affected by the transportation activities. Therefore, in order to ensure that the size of the affected population is conservative, the NRC staff's analysis not only increases over time the existing population densities along the assumed transportation routes, but also forecasts increased residential, business, and transient/tourist populations in the areas of likely development.

Issue 4--Cumulative Impacts

Comment: NRC failed to consider cumulative impacts of all spent fuel, HLW, and low-level-waste shipments.

Response: Table S-4 shows the environmental impacts of transportation of fuel and waste directly attributable to one nuclear power plant. The current rulemaking was narrowly focused on the question of whether the impact values given in Table S-4 would be different with spent fuel shipments converging on one destination, Yucca Mountain -- the candidate site under study by DOE for a repository, rather than several destinations. Table S-4 does not consider non-commercial power reactor shipments of fuel and waste. Nevertheless, a discussion of the cumulative impacts of transporting spent fuel, HLW, and low-level waste through southern Nevada has been added to Addendum 1 (Section 2.4). To estimate the potential cumulative effects of DOE shipments of LLW to the Nevada Test Site as well as shipments of HLW to a possible repository, the NRC staff used information published in DOE's Waste Management Programmatic EIS (DOE/EIS-0200-F) May 1997. To ensure that cumulative impacts are not underestimated, the NRC staff selected alternatives in the EIS that led to the highest numbers of shipments to the Nevada Test Site and Yucca Mountain. The results of the analysis indicate that the cumulative doses and expected cancer fatalities resulting from the civilian SNF and the DOE shipments are small compared to the risk of cancer from other causes.

Comment: Commentors stated that cumulative impacts along the Wasatch Front must be considered.

Response: The State of Utah maintains that a study similar to the one conducted for Las Vegas and Clark County must be conducted for the cumulative impacts along the Wasatch Front that would originate from the proposed Private Fuel Storage Facility to be located at Skull Valley, Utah. Such an analysis is beyond the scope of this generic rulemaking because the Commission directed that cumulative impacts attributed to transportation be analyzed only in the vicinity of Yucca Mountain. However, the NRC is currently reviewing a site-specific application for construction and operation of the proposed Private Fuel Storage Facility at Skull Valley in a separate regulatory action. A site-specific study of the cumulative impacts of transportation is part of that review. The study will be reported in a draft Environmental Impact Statement to be published for public comment. Its availability will be noticed in the Federal Register.

Issue 5--Legal Requirements

Comment: NRC failed to conduct a legally sufficient risk assessment. Use of a model such as RADTRAN is not in and of itself sufficient to meet the requirements of the National Environmental Policy Act. The NRC must consider consequences of low-probability, high-consequence accidents not included in RADTRAN, including unique local conditions, unforeseen events, sabotage, and human error in cask design. The NRC should adopt the comprehensive risk assessment approach for SNF and HLW transportation described in Golding and White, Guidelines on the Scope, Content, and Use of Comprehensive Risk Assessment in the Management of High-Level Nuclear Waste Transportation (1990).

Response: See the response above regarding consideration of severe accident risk (low probability, high consequence accidents) during transportation.

The NRC's regulatory program will continue to ensure that the risk of severe transportation accidents are minimized. Physical security for spent fuel transportation is regulated under 10 CFR 73.37. The regulatory philosophy is designed to reduce the threat potential to shipments and to facilitate response to incidents and recovery of packages that might be diverted in transit. Although the analysis supporting the current rule does not account for the potential for human error, activities related to the design, fabrication, maintenance, and use of transportation packages are conducted under an NRC-approved Quality Assurance Program. This helps to provide consistency in performance and helps reduce the incidence of human error. While a location-specific transportation risk assessment is included in the DOE EIS for the decisions relating to a possible Yucca Mountain repository, the NRC staff believes that the analysis conducted for this rulemaking provides an adequate consideration of the impacts from license renewal. Further, through its regulatory, licensing, and certification functions, the NRC has tried to ensure that transportation of SNF is performed safely with minimum risk to the public, and that vehicle crashes while transporting SNF do not result in severe accidents. Similarly, DOE is expected to ensure that the routes and procedures chosen for SNF transport to the repository provide ample protection of the public health and safety and the NRC reviews and approves the selected routes .

The analysis in Addendum 1 shows that even with conservative assumptions, the cumulative radiological and non-radiological accident risks of SNF transport in Clark County are small. However, there are a number of opportunities to further reduce human health impacts. These include transporting SNF by rail rather than by truck. This would reduce human health effects by reducing the number of shipments and the likelihood of accidents. In addition, shipping SNF via the proposed beltway would reduce health impacts compared to shipping via the current interstate highway system. The implementation of such mitigative measures must await future decisions that fall well outside of the scope of this rulemaking. In addition, for the purposes of individual license renewal rule decisions, no plant specific mitigation measures were found appropriate for addresses the impacts identified in the Addendum. The NRC staff notes that DOE addresses transportation impacts, mitigation measures, and alternative transportation modes in its EIS for the proposed repository at Yucca Mountain .

Issue 6--Socioeconomics

Comment: NRC failed to consider socioeconomic impacts .

Response: Several commentors raised an issue of public perception of risk of waste shipments and its effect on tourism and property values. Under the National Environmental Policy Act (NEPA), the NRC is obligated to consider the effects on the physical environment that could result from the proposed action. Effects that are not directly related to the physical environment must have a reasonably close causal relationship to a change in the physical environment. The Supreme Court ruling in Metropolitan Edison Co. v. People Against Nuclear Energy, 460 U.S. 766 (1983) has narrowly circumscribed, if not entirely eliminated, an agency's NEPA obligation to consider impacts arising solely from the public's perception that an agency's action has created risks of accidents. Accordingly, it is not necessary to consider the impacts on tourism and property values from the public's perception of risk.

The socioeconomic impacts of plant refurbishment and continued operation during the renewal period are discussed in the plant-specific supplement to the GEIS for each individual license renewal applicant. The NRC recognizes that there will likely be increased costs in the unlikely event of an accident. However, for the majority of transportation accidents that may occur, the associated costs are small. For the most severe accidents analyzed by the RADTRAN computer code, the costs could be substantial. Given the low probability of such accidents, the socioeconomic impacts of transportation of SNF do not alter the Commission's conclusions regarding the impacts of this issue.

Issue 7--Higher Burnup Fuel

Comment: There was insufficient consideration of extended fuel burnup issues.

Response: Section 3 of Addendum 1 addresses the issues associated with extended fuel burnup in detail. The NRC staff's analysis of higher burnup fuel examined the issues of radiation doses due to higher dose rates during shipment, higher radiation doses in the event of transportation accidents, and the potential for a criticality in the very unlikely event that high burnup fuel geometry is altered during a transportation accident.

The analysis done by the NRC staff concluded that higher burnup fuel would likely cause higher dose rates during transportation and that dose rates following transportation accidents with radiological releases would also increase, all other things being equal. However, despite the increased dose rates the potential impacts on the transport crews and the affected members of the public would still be acceptably small. The analysis of the potential for criticality following a change in fuel geometry as the result of a transportation accident determined that such an event was not a concern.

Issue 8--Environmental Justice

Comment: NRC failed to consider Environmental Justice.

Response: The analysis suggests that the routes through downtown Las Vegas, Nevada may run through areas containing a higher proportion of low-income and minority groups than the beltway routes. However, as discussed in Sections 2.3 and 2.4 Addendum, the radiological and nonradiological impacts of transportation of SNF are small. In addition, these small impacts are dispersed throughout the entire routes and do not appear to fall disproportionately in any one area. Based on the analysis performed the NRC staff concludes the overall impacts of transportation of SNF will not likely be disproportionately high or adverse for any minority or low-income population.

Issue 9--Regulatory Text

Comment: Several suggestions for clarifying the regulatory text were offered.

Response: The rule has been revised to make it clear that the environmental impact values in Table S-4 (10 CFR 51.52) may be used to account for the environmental effects of transportation of fuel and waste to and from a nuclear power plant at repository such as Yucca Mountain, Nevada, which is under consideration as a HLW repository. If, in the future, Yucca Mountain is removed from consideration as a HLW repository, the Commission will evaluate whether the generic analysis performed for the current rule is applicable to other sites that are considered. If fuel enrichment greater than 5 percent Uranium-235 and fuel burnup of greater than 62,000 MWd/MTU are approved by the Commission, the Commission will consider a rulemaking to assess the continuing generic applicability of Table S-4 to environmental reviews for license renewal.

Comment: The addition to the rule of local transportation impacts associated with continued operation of a plant during the license renewal period needs further clarification in the rule language and in the Supplementary Information.

Response: The rule was revised to clarify that the issue of "Public services, Transportation" in Table B-1 of Appendix B to Subpart A of 10 CFR Part 51 involves the contribution of highway traffic directly attributable to refurbishment and continued operation of a plant during the license renewal period to changes in the service levels of highways in the vicinity of the plant. The majority of traffic directly attributable to a plant is commuting plant workers.

Comment: Paragraph (M) of 10 CFR 51.53(c)(3)(ii) should be deleted.

Response: The rule language has been amended and Paragraph (M) has been deleted. This change from the proposed rule was necessary in order to provide consistency with 51.53(c)(3)(ii), as this section only deals with Category 2 issues. Since the cumulative impacts of transportation of SNF in the vicinity of Yucca Mountain is no longer a Category 2 issue, inclusion in 51.53(c)(3)(ii) is no longer necessary.

Other Comments

This section addresses the comments that are not encompassed by the issue summaries and responses given above. In addition, some comments were received after the close of the comment period. These comments were reviewed, and most were found to be similar to comments already addressed by the issue summaries and responses. However, the comments that raised new ideas relevant to Addendum 1 are also presented in this section. For these late comments, revisions to Addendum 1 were necessarily minimal.

Comment: Addendum 1 assumes that truck transport would have the highest doses. This assumption is not necessarily valid. Also, a different route that avoids Las Vegas should be addressed. (A route through Nellis Air Force Base and down US-95 is being considered by DOE and it has been shown to have higher risks of accident fatalities and to increase the radiological risk.) Routes chosen in Addendum 1 do not bound the analysis properly.

Response: The transportation and route scenarios and their underlying assumptions were designed to reflect situations that most likely would result in highest doses in order to bound the analysis properly as the routes chosen for this analysis were the most populated routes in the state of Nevada. Also, as noted in an earlier response, the NRC staff consulted DOE in determining that truck shipments through densely populated areas of Clark County, Nevada, would have the highest potential impacts among the alternative transportation scenarios that would be given serious consideration in decisions relating to the suitability of the site undergoing study for a repository at Yucca Mountain.

The comment that a route from Nellis Air Force Base down US-95 is higher risk than those selected by the NRC staff provided no specific details concerning that assertion. In the NRC staff's view, any route that bypasses major centers of population will have significantly lower radiological impacts. With regard to traffic accident rates, while it may be true that certain routes will have accident rates that are higher than average, the average rates are low enough that modest increases from the average will not significantly change the staff's conclusions.

Comment: SNF from California would go through Las Vegas twice (in route to Skull Valley and subsequently to Yucca Mountain), resulting in increased risk.

Response: If the proposed SNF storage facility is licensed and built, some SNF may go through Clark County on the way to Skull Valley, Utah. The NRC staff has not analyzed this possible impact because it is not clear at this time that the proposed Skull Valley facility will be licensed or that the SNF would go through Las Vegas if the facility were built. In addition, SNF from California makes up only a small fraction of the SNF that would be shipped. The NRC staff concludes that the conservative assumptions used in the analysis more than compensate for minor changes in transportation plans that may develop for that fraction of the total SNF.

Comment: The NRC should provide affected parties with some statement of the regulatory effect of the interrelationships between the numerous other similar analyses.

Response: As a general matter, the National Environmental Policy Act (NEPA) requires all Federal agencies to perform an environmental review for certain actions they propose to conduct. In the context of nuclear waste management, several agencies have regulatory and operational responsibilities which may involve various proposed actions that, in turn, require the preparation of environmental impact statements (EISs). Inevitably, there may be a degree of overlap in the types of impacts discussed in these various EISs. However, the analysis developed by the NRC for the purposes of license renewal is not binding on future actions and associated environmental impact analyses.

The NRC proposed action that has triggered the preparation of this rulemaking and the associated analysis of environmental impact is the agency's responsibility to review applications for the renewal of nuclear power plant licenses. In light of the discrete purpose of this rulemaking, the NRC has sought to gauge the impacts of license renewal given the information currently available on those impacts including the transportation of spent fuel. Even though these impacts do not occur at the plant site during license renewal, the NRC has considered them here pursuant to its NEPA responsibilities.

Future EISs prepared by other agencies on proposed actions in the waste management arena (e.g., any recommendation by DOE on approval of the Yucca Mountain site for development of a repository) will undoubtedly address some of the same impacts covered by the analysis described in this notice. Some of these other impact statements are anticipated to be more detailed given their purpose and the availability of additional information in the future. This, however, does not diminish the adequacy of the NRC's action. This analysis is sufficient for the purpose it serves and it provides the Commission with the information needed to weigh the likely environmental impacts of SNF transportation for individual license renewals applications and reach informed decisions regarding the acceptability of these applications. The rule does not, however, dictate any particular result for future actions taken with regard to a waste repository or other waste management matters. Specifically, any generic conclusions by the Commission concerning the cumulative environmental impacts of transportation associated with nuclear power plants would in no way affect any DOE decision concerning the suitability of Yucca Mountain or any consideration that DOE may give to transportation impacts in making that decision.

Comment: Addendum 1 is not meaningful to the public. For example, it is impossible to determine if the spent fuel isotope inventory shown in the sample pages of the RADTRAN printout matches the fuel considered in the Addendum.

Response: In preparing Addendum 1, the NRC staff has attempted to write to a broad and diverse audience as much as possible. The NRC staff acknowledges that this rulemaking involves complicated, technical issues. However, the NRC staff has attempted to present these matters in the most clear manner possible. Addendum 1 has been revised and Table 2 provides the fuel isotope inventory that can be compared to the sample pages of the RADTRAN computer code printout.

Comment: The study area is inaccurately defined and the location of some cities is incorrectly stated.

Response: During the preparation of Addendum 1, the initial study area selected for analysis emphasized the urban areas in and near Las Vegas. Route selections were based in part on their proximity to those areas, not to county borders. However, in response to public comments, the study area was expanded to include the entire county. Consequently, the "entry" point for SNF shipments shifted to cities such as Mesquite.

Comment: Addendum 1 should discuss potential mitigation measures, not rely on the DOE Yucca Mountain EIS for that discussion.

Response: The analysis in Addendum 1 shows that, even with conservative assumptions, the cumulative radiological and non-radiological accident risks of SNF transport in Clark County are small. However, there are a number of opportunities to further reduce human health impacts. These include transporting SNF by rail rather than by truck. This would reduce human health effects by reducing the number of shipments and the likelihood of accidents. In addition, shipping SNF via the proposed beltway would reduce health impacts compared to shipping via the current interstate highway system. The implementation of such mitigative measures must await future decisions that fall well outside of the scope of this rulemaking. In addition, for the purposes of individual license renewal rule decisions, no plant specific mitigation measures were found appropriate for addressing the impacts identified in the Addendum. The NRC staff notes that DOE will addresses transportation impacts, mitigation measures, and alternative transportation modes in its EIS for the proposed action to develop a repository at Yucca Mountain .

Comment: Addendum 1 does not mention that the proposed repository which is the destination for shipments of spent nuclear fuel is in Nye County.

Response: A statement noting that the proposed Yucca Mountain repository is in Nye County has been added to Addendum 1.

Comment: No statements of baseline conditions are given in Addendum 1.

Response: Addendum 1 uses background and natural radiation levels as the baseline conditions against which dose estimates can be compared. Both are presented in Addendum 1 and are based in large part on information published by the National Council on Radiation Protection and Measurements.

Comment: The analysis in Addendum 1 is limited to human health effects. Other potential impacts should be considered.

Response: Addendum 1 was prepared to provide information regarding a proposed rule to determine whether the transportation of higher enriched, higher burnup fuel to a single destination is consistent with the values of Table S-4. Because the pertinent section of Table S-4 concerns impact values for human health effects, Addendum 1 concentrates on potential cumulative impacts to human health. However, Section 2.3 of Addendum 1 has been revised to look at the potentially most significant non-human health effect which is the potential increase in traffic volume in Clark County as the result of the transportation of SNF. The NRC staff conclusion is that the impacts are small.

Comment: The analysis assumes the use of the large-capacity GA-4/9 truck cask, which has not been certified and must be used in combination with specially designed trucks that have not been tested. It also assumes that these cask and truck systems will be available in sufficient quantity for the shipments. The commentor seeks assurance that the assumed truck cask system is feasible and that DOE's proposed regional service contractor approach would feasiblely result in the use of such a system for all shipments in the potential truck shipment campaign.

Response: The analysis done by the NRC staff assumes that an adequate number of certified casks would be available. Addendum 1 used extremely conservative assumptions regarding SNF shipments and casks to ensure that the analysis would lead to maximum dose estimates. For example, the analysis of incident-free transportation impacts assumes the use of legal-weight trucks for shipment of the SNF, which results in more and smaller shipments. For the accident analysis, the use of the largest-capacity casks was assumed in order to maximize the amount of SNF that would be involved in the accident. These parameters were intended to bound the parts of the analysis, not to describe parts of the actual SNF shipment protocol such as the specific casks that will be used.

Comment: The analysis appears to assume that oldest spent nuclear fuel would be shipped first to the repository. If so, how will institutional measures achieve this sequencing? If they do not, how will the maximum potential radioactive risk in shipment and storage or disposal be addressed?

Response: The spent fuel will be shipped in casks certified by the NRC. In fact, the current practice of NRC issuing certificates of compliance for casks used for shipment of power reactor fuel is to specify 5 years as the minimum cooling period in a certificate.

Comment: Addendum 1 uses national accident rate statistics. State and/or local rates would be more appropriate.

Response: For the analysis of radiological accidents, data specific to Nevada were used in the RADTRAN computer code runs. However, for the analysis of non-radiological accidents, the NRC staff required data regarding not only accident rates but also injury and fatality statistics. Those data were not available except from the U.S. Department of Transportation.

Comment: Water resource supplies within boundaries of the State of Nevada belong to the public. All waters are subject to appropriation for the beneficial use only under state law.

Response: The water resources of the state will be unaffected by the transport of SNF through Clark County.

Comment: Report failed to provide conditions for informed consent which requires disclosure to those affected, their understanding , and voluntary acceptance.

Response: NRC regulations already contain values that the NRC considers to be acceptable environmental impacts from the shipment of SNF and other radioactive waste. In Addendum 1 the NRC staff is, in part, ensuring that the overall impacts of the transportation of the additional SNF that will be generated as the result of nuclear power plant license renewal are bounded, given the best information the NRC staff has at this time, by those values previously found acceptable. The values specified in the regulations are supported by analysis and were adopted into the regulations only after providing opportunity for public comment as part of the NRC's rulemaking process. As such, the NRC has followed all applicable legal requirements and appropriately carried out its responsibility to consider the environmental impacts of its license renewal decision.

Comment: The NRC staff uses "flawed" science as evidenced by factors including a questionable definition of risk which fails to account for severe accidents, use of misleading if not false average radiation dose rates, manipulation of dose rate data to obtain acceptable results and lack of empirical data especially that applicable to transportation of SNF.

Response: The decision before the Commission is whether the impacts of license renewal are so severe that they should preclude the option of license renewal. As such, the Commission has considered a reasonable estimate of impacts and not included remote and speculative scenarios that do not add to our regulatory decision (see also response to comment on severe accidents, above).

In the analyses described in Addendum 1 the NRC staff uses dose rates that reflect the applicable regulatory limit rather than average dose rates. Even with these very conservative assumptions for dose rates, transportation modes, transportation routes, and a number of other factors, radiation impacts on the transport crews and the general public were not only found to be within all regulatory limits but small as well and there was no need to adjust the assumptions.

Throughout Addendum 1 the NRC staff discusses the assumptions that were made and where applicable the empirical data used to support those assumptions is referenced. With respect to making judgements about the shipment of spent fuel the NRC staff has the benefit of data from over 40 years of experience in shipping SNF in this country as well as overseas.

Comment: High level waste management and transportation should not be a generic issue and Yucca Mountain should not be used for the study as DOE is behind schedule and it is not an approved site for SNF.

Response: Given that the potential environmental impacts of the transportation of SNF resulting from license renewal are similar for all nuclear power plants who seek to renew their operating licenses, and that the NRC staff's analysis contained in Addendum 1 concludes that the impacts are likely to be small, the Commission feels it is appropriate to reclassify the issue as a Category 1 issue. Use of Yucca Mountain, Nevada for purposes of the staff's analysis, as the destination of the SNF is appropriate as it is the only site presently under study. It must be emphasized that this generic environmental impact statement is required to make use of the best information available and at this time the assumption that Yucca Mountain is the destination is reasonable for purposes of the staff's analysis. If in the future, conditions change, the assumption made for this analysis may need to be reevaluated.

Comment: Need to consider the intermodal option being considered by Congress for Caliente, Nevada.

Response: Rather than speculate on which transportation option or options will ultimately be selected, the NRC staff has chosen a mode and routes to Yucca Mountain which in its judgement will have the greatest potential environmental impacts in order to do a bounding analysis for the purpose of this rulemaking.

Comment: The analysis needs to address the impacts of above ground nuclear weapons testing being done at the Nevada Test Site.

Response: For the purposes of considering the environmental impacts of license renewal, there does not appear to be a relevant connection between transportation impacts from civilian SNF and defense related weapons testing at the Nevada test site.

Comment: The analysis relies on assumptions that are 25-30 years old and that have a number of problems including omission of important radionuclides (Iodine-129, Chlorine-36 and Cobalt-60), unrealistic RADTRAN assumptions including inadequate consideration of severe accidents, outdated assumptions from NUREG-0170 and WASH-1238 including the failure to consider the degradation of cladding during extended dry storage, and failure to consider the rail-heavy haul truck option.

Response: With regard to the radionuclides, as indicated in Table 2 of Addendum 1, Cobalt-60 is considered. While both Iodine-129 and Chlorine-36 are long lived, neither is a significant contributor to overall dose. Iodine-129 has a very low specific activity and Chlorine-36 is a beta emitter.

The issue of the severity of accidents considered in the NRC staff's analysis was addressed in an earlier response to comment. The assumptions that are used in the NRC staff's analysis have been periodically reviewed and found adequate. The hypothetical accident conditions of 10 CFR 71.73 have been evaluated against actual conditions encountered in highway and railway accidents and were found to be bounding as documented in NUREG/CR-4829, February 1987, "Shipping Container Response to Severe Highway and Railway Accident Conditions." As noted in Table 3 of Addendum 1, the version of RADTRAN used is updated to March 1999.

Section 3 of Addendum 1 does consider the possible effect of cladding degradation on criticality in the context of increased burnup. That analysis would be equally applicable to any cladding degradation that might occur during prolonged dry storage of the SNF.

With regard to what is asserted to be inadequate consideration of the potential radiological impacts of the rail-heavy haul truck option, the NRC staff has analyzed the radiological impacts of the truck mode along various routes through and around Las Vegas and concludes that they are the limiting scenarios. The largest doses in the incident-free conditions are now to the public. If the rail-heavy haul transport scenario was adopted, a substantial portion of the public exposure would be avoided, since in this scenario, the slow moving heavy haul truck transport would not move through a major population center.

Comment: NRC must consider potential Indian Tribe claims of authority to regulate shipments across reservation lands.

Response: This analysis is a generic study that assumes certain routes for the purpose of evaluating environmental impacts. Because the purpose of this study is neither to propose nor approve routes, the NRC does not need to consider tribal claims of authority to regulate shipments in the context of this analysis.

Comment: The beltway is a county road, not part of the Federal highway system; it is not clear it can be used for shipments.

Response: The DOT regulations do not require that SNF shipments only use federal highways. Therefore, the NRC assumed that the beltway is a possible route around Las Vegas.

Comment: The NRC should address the implications of higher enrichment, higher burnup fuel for consequences of radiological sabotage, as NRC has done so far for the increase in burnup from 33,000 MWd/MTU to 40,000 MWd/MTU (see 49 FR 23867, Proposed Revisions to 10 CFR 73, Modification of Protection Requirements for Spent Fuel Shipments, 6/8/84).

Response: The NRC has not quantified the likelihood of the occurrence of sabotage in this analysis because the likelihood of an individual attack cannot be determined with any degree of certainty. Nonetheless, the NRC has considered, for the purposes of this environmental impact statement and rulemaking, the environmental consequences of such an event. In the determination of the consequences of such an event, higher burnup is only one factor. Based on the staff's study of higher burnup fuel (NUREG-1437, Vol.1, Addendum 1, Table 2), the consequences of a sabotage event involving such fuel could be larger than those in the studies referenced by the commentor. However, given that the consequences of the studies referenced by the commentor were small, even modest increases due to the effects of higher burnup fuel would not result in unacceptably large consequences. Because burnup is not the only factor that could affect the consequences of a sabotage event, the staff continues to study this area. Should new and significant information result from the further study, actions addressing such information will be considered.

Nevertheless, the extensive security measures required by NRC regulations make sabotage events extremely unlikely. Moreover, the casks required to be used to transport spent fuel are designed to withstand very substantial impacts during transport without loss of containment integrity. The cask designs should serve to further reduce the likelihood of release of radioactive material in the extremely unlikely event of sabotage. In view of the fact that NRC safeguards regulations make sabotage events extremely unlikely, and the fact that the cask designs themselves should make a release of radioactive material unlikely even were sabotage to occur, and based on our judgement that, in the extremely unlikely event that sabotage and releases did occur, the consequences from higher burnup fuel would not be unacceptably large, we have concluded that a more extensive study of higher burnup fuel consequences is not warranted for this environmental impact statement and rulemaking.

On June 22, 1999, the Nevada Attorney General filed a petition with the Commission which requested the NRC to amend regulations governing safeguards for shipments of spent nuclear fuel against sabotage and terrorism and to initiate a comprehensive assessment. In particular, the petition indicated that NRC should factor into its regulations the changing nature of threats posed by domestic terrorists, the increased availability of advanced weaponry and the greater vulnerability of larger shipping casks traveling across the country. If, as a result of reviewing this petition, the NRC reaches conclusions that are inconsistent with the results or assumptions in the present rulemaking, the Commission will need to revisit the analysis presented here.

1. 10 CFR 2.804, "Notice of proposed rulemaking" and 10 CFR 51.117, "Draft environmental impact statement-notice of availability."