FINAL PROGRAMMATIC ENVIRONMENTAL IMPACT STATEMENT for the URANIUM MILL TAILINGS REMEDIAL ACTION GROUND WATER PROJECT Volume I
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DOE/EIS-0198 FINAL PROGRAMMATIC ENVIRONMENTAL IMPACT STATEMENT FOR THE URANIUM MILL TAILINGS REMEDIAL ACTION GROUND WATER PROJECT Volume I October 1996 TABLE OF CONTENTS SUMMARY 1.0 INTRODUCTION 2.0 ALTERNATIVES 3.0 AFFECTED ENVIRONMENT 4.0 ENVIRONMENTAL IMPACTS 5.0 UNAVOIDABLE ADVERSE ENVIRONMENTAL IMPACTS OF THE PROPOSED ACTION 6.0 SHORT-TERM USES AND LONG-TERM PRODUCTIVITY 7.0 IRREVERSIBLE AND IRRETRIEVABLE COMMITMENT OF RESOURCES 8.0 REFERENCES 9.0 GLOSSARY 10.0 ABBREVIATIONS AND ACRONYMS 11.0 PREPARERS OF THE FINAL PEIS 12.0 ORGANIZATIONS CONSULTED DURING PEIS PREPARATION 13.0 AGENCIES, ORGANIZATIONS, AND PERSONS RECEIVING COPIES OF THE PEIS Appendices Appendix A - Comments and Responses Appendix B (electroic copy is unavilable) SUMMARY This programmatic environmental impact statement (PEIS) was prepared for the Uranium Mill Tailings Remedial Action (UMTRA) Ground Water Project to comply with the National Environmental Policy Act (NEPA). This PEIS provides an analysis of the potential impacts of the alternatives and ground water compliance strategies as well as potential cumulative impacts. On November 8, 1978, Congress enacted the Uranium Mill Tailings Radiation Control Act (UMTRCA) of 1978, Public Law, codified at 42 USC '7901 et seq. Congress found that uranium mill tailings ". may pose a potential and significant radiation health hazard to the public, and that every reasonable effort should be made to provide for stabilization, disposal, and control in a safe, and environmentally sound manner of such tailings in order to prevent or minimize other environmental hazards from such tailings." Congress authorized the Secretary of Energy to designate inactive uranium processing sites for remedial action by the U.S. Department of Energy (DOE). Congress also directed the U.S. Environmental Protection Agency (EPA) to set the standards to be followed by the DOE for this process of stabilization, disposal, and control. On January 5, 1983, EPA published standards (40 CFR Part 192) for the disposal and cleanup of residual radioactive materials. On September 3, 1985, the U.S. Court of Appeals for the Tenth Circuit set aside and remanded to EPA the ground water provisions of the standards. The EPA proposed new standards to replace remanded sections and changed other sections of 40 CFR Part 192. These proposed standards were published in the Federal Register on September 24, 1987 (52 FR 36000). Section 108 of the UMTRCA requires that DOE comply with EPA's proposed standards in the absence of final standards. The Ground Water Project was planned under the proposed standards. On January 11, 1995, EPA published the final rule, with which the DOE must now comply. The PEIS and the Ground Water Project are in accordance with the final standards. The EPA reserves the right to modify the ground water standards, if necessary, based on changes in EPA drinking water standards. Appendix A contains a copy of the 1983 EPA ground water compliance standards, the 1987 proposed changes to the standards, and the 1995 final rule. Under UMTRA, DOE is responsible for bringing the designated processing sites into compliance with the EPA ground water standards and complying with all other applicable standards and requirements. The U.S. Nuclear Regulatory Commission (NRC) must concur with DOE's actions. States are full participants in the process. The DOE also must consult with any affected Indian tribes and the Bureau of Indian Affairs. Uranium processing activities at most of the inactive mill sites resulted in the contamination of ground water beneath and, in some cases, downgradient of the sites. This contaminated ground water often has elevated levels of constituents such as but not limited to uranium and nitrates. The purpose of the UMTRA Ground Water Project is to eliminate or reduce to acceptable levels the potential health and environmental consequences of milling activities by meeting the EPA ground water standards. The first step in the UMTRA Ground Water Project is the preparation of this PEIS. This document analyzes the potential impacts of four alternatives for conducting the Ground Water Project. These alternatives do not address site-specific ground water compliance strategies because the PEIS is a planning document only. It assesses the potential programmatic impacts of conducting the Ground Water Project, provides a method for determining the site-specific ground water compliance strategies, and provides data and information that can be used to prepare site-specific environmental impacts analyses more efficiently. Participation by affected states, tribes, and local government agencies will be encouraged during preparation of this PEIS, and during implementation of the alternative selected in the Record of Decision. This PEIS differs substantially from a site-specific environmental impact statement because multiple ground water compliance strategies, each with its own set of potential impacts, could be used to implement all the alternatives except the no action alternative. In a traditional environmental impact statement, an impacts analysis leads directly to the defined alternatives. The impacts analysis for implementing alternatives in this PEIS first involves evaluating a ground water compliance strategy or strategies (Figure 1), the use of which will result in site-specific impacts. This PEIS impacts analysis assesses only the potential impacts of the various ground water compliance strategies, then relates them to the alternatives to provide a comparison of impacts. DESCRIPTION OF THE PROPOSED ACTION (PREFERRED ALTERNATIVE) AND ALTERNATIVES Table 1. Ground water compliance strategies that apply under each alternative Alternative Active remediation Strategy Passive Proposed action No actiona to background remediation levels Active ground water remediation methods % %b Natural flushing C % % No ground water remediation % % Sites that qualify for supplemental standards d or alternate concentration limitse. Sites that meet maximum concentration limits or % % background levels (no impacts).f aThe analysis of the no action alternative is required by the CEQ and DOE. bActive remediation methods would not be used at sites where contamination does not exceed background and likely would not be used at sites that qualify for supplemental standards based on the existence of limited use ground water. cNatural flushing means allowing the natural ground water movement and geochemical processes to decrease contaminant concentrations. dSupplemental standards applicable for certain site conditions, as identified in the EPA standards, that are protective of human health and the environment, and may be applied in lieu of prescriptive levels. eConcentrations of contaminants that may exceed the maximum concentration limits; or, limits for those constituents without maximum concentration limits. If DOE demonstrates, and NRC concurs, that human health and the environment would not be adversely affected, DOE may meet an alternate concentration limit. f"No remediation" at sites that do not exceed maximum concentration limits or background levels is not the same as "no action" because these sites would require activities such as site characterization to show that no remediation is warranted. The PEIS considers four programmatic alternatives for implementing the UMTRA Ground Water Project: 1) the proposed action (DOE's preferred alternative), 2) no action, 3) active remediation to background levels, and 4) passive remediation. A Record of Decision will identify the alternative that will become the programmatic foundation for conducting the Ground Water Project at all sites. All the alternatives listed except the no action alternative would use one or more ground water compliance strategies to meet the EPA ground water standards. Table 1 shows the alternatives and the strategies that are described below. 1) Proposed action (Preferred Alternative) The proposed action which is DOE's preferred alternative would use ground water compliance strategies tailored for each site to achieve conditions that are protective of human health and the environment. The proposed action would consider ground water compliance decisions in a step-by-step approach, beginning with consideration of "no remediation" strategy and proceeding, if necessary, to the passive strategy, such as natural flushing with compliance monitoring and institutional controls, and to a more complex, active ground water cleanup method, such as pump and treat or other engineered approaches to cleaning up contaminated ground water. For example, under the proposed action, if a site risk assessment and site observational work plan indicate that the strategy of "no remediation" would still be protective of human health and the environment, a more complex and potentially disruptive strategy involving active cleanup methods would not be necessary. The proposed action is intended to establish a consistent risk-based framework for implementing the UMTRA Ground Water Project and determining appropriate ground water compliance strategies at the UMTRA Project former processing sites. The determination of site-specific ground water compliance strategies would take into account site-specific ground water conditions; human and environmental risks; participation of the tribes, States and local communities; and cost. This approach is sufficiently flexible to allow for interim actions, such as alternate water supply systems, should these activities be necessary in order to reduce risk and/or support institutional controls.