EIS-0113_Section_9 - Hanford Site

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Cn7 71d v^ 5 DOE/EIS-0113 (VOL. 5 of 5) PUBLIC COMMENTS FINAL ENVIRONMENTAL IMPACT STATEMENT HE Hanford Site Richland, Washington DECEMBER 1987 U.S. DEPARTMENT OF ENERGY ASSISTANT SECRETARY FOR DEFENSE PROGRAMS WASHINGTON, D.C. 20545
COYER SHEET RESPONSIBLE AGENCY: U.S. Department of Energy TITLE: Final Environmental Impact Statement, Disposal of Hanford Defense High-Level, Transuranic and Tank Wastes, Hanford Site, Richland, Washington - - CONTACTS: Additional copies or information concerning this statement can be obtained from: Mr. Tom Bauman, Communications Division, U.S. Department of Energy, Richland Operations Office, Richland, WA 99352. Telephone: (509) 376-7378. For general information on DOE's EIS process contact: Office of the Assistant Secretary for Environment, Safety and Health, U.S. Department of Energy, ATTN: Carol M. Borgstrom, Forrestal Building, 1000 Independence Avenue, S.W., Washington, D.C. 20585. Telephone: (202) 586-4600. ABSTRACT: The purpose of this Environmental Impact Statement (EIS) is to provide environmental input into the selection and implementation of final disposal actions for high-level, transuranic and tank wastes located at the Hanford Site, Richland, Washington, and into the construction, operation and decommissioning of waste treatment facilities that may be required in implementing waste disposal alternatives. Specifically evaluated are a Hanford Waste Vitrification Plant, L"V Transportable Grout Facility, and a Waste Receiving and Packaging Facility. - Also an evaluation is presented to assist in determining whether any additional action should be taken in terms of long-term environmental protection for waste that was disposed of at Hanford prior to 1970 as low-level waste (before the transuranic waste category was established by the Atomic Energy Commission but which might x= fall into that category if generated today). The following alternatives are considered in this EIS: 1) in-place stabilization and disposal, where waste is left in place but is isolated by protective and natural barriers; 2) geologic disposal, where most of the waste (by activity and to the extent practicable) is exhumed, treated, segregated, packaged and disposed of in a deep geologic repository; waste classified as high-level would be disposed of in a. commercial repository developed pursuant to the Nuclear Waste Policy . Act; transuranic waste would be disposed of in the 'Waste Isolation Pilot Plant near Carlsbad, New Mexico; 3) areference alternative, where some classes of waste are disposed of in geologic repositories and other classes of waste are disposed of by in-place stabilization and disposal; 4) the preferred alternative, in which double-shell tank wastes, strontium and cesium capsules, and retrievably stored TRU wastes are disposed of according to the reference alternative, and in which decisions are deferred on disposal of single-shell tank wastes and on further remedial action for TRU-contaminated soil sites and pre-1970 buried sus p ect TRUcontaminated solid wastes (except the 618-11 site) until additional information is obtained on waste characterization, retrieval methods, and performance of nearsurface disposal systems; and 5) a no disposal action alternative (continued storage).
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EIS-0113_Section_9 - Hanford Site

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