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Division Spotlight
Fuel Cycle & Waste Management
Devoted to all aspects of the nuclear fuel cycle including waste management, worldwide. Division specific areas of interest and involvement include uranium conversion and enrichment; fuel fabrication, management (in-core and ex-core) and recycle; transportation; safeguards; high-level, low-level and mixed waste management and disposal; public policy and program management; decontamination and decommissioning environmental restoration; and excess weapons materials disposition.
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2024 ANS Winter Conference and Expo
November 17–21, 2024
Orlando, FL|Renaissance Orlando at SeaWorld
Standards Program
The Standards Committee is responsible for the development and maintenance of voluntary consensus standards that address the design, analysis, and operation of components, systems, and facilities related to the application of nuclear science and technology. Find out What’s New, check out the Standards Store, or Get Involved today!
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Bipartisan nuclear waste bill introduced in U.S. House
U.S. representatives Mike Levin (D., Calif.) and August Pfluger (R., Texas) have introduced the bipartisan Nuclear Waste Administration Act of 2024, which would establish an independent agency to manage the country’s nuclear waste.
In addition to establishing a new, single-purpose administration to manage the back end of the nuclear fuel cycle, the bill would direct a consent-based siting process for nuclear waste facilities and ensure reliable funding for managing nuclear waste by providing access to the Nuclear Waste Fund. According to Pfluger and Levin, the bill’s provisions are in line with recommendations from the Blue Ribbon Commission on America’s Nuclear Future.
Tsutomu Sakurai, Akira Takahashi, Niro Ishikawa, Yoshihide Komaki
Nuclear Technology | Volume 83 | Number 1 | October 1988 | Pages 24-30
Technical Paper | Fuel Cycle | doi.org/10.13182/NT88-A34172
Articles are hosted by Taylor and Francis Online.
The composition of NOx generated in the dissolution of UO2 has been described in different ways by earlier authors. Finding a way to determine the NOx composition in the dissolution included experiments concerning the reactions of NO and NO2 with 3 to 6 M HNO3. The following conclusions have been obtained for the dissolution: (a) of the NOx, NO is the direct product of the dissolution [3UO2 + 8HNO3 → 3UO2(NO3)2 + 2NO + 4H2O]; (b) part of the NO is converted quickly to NO2 by the second reaction, i.e., NO + 2HNO3→ 3NO2 + H2O (the equilibrium constant of this reaction determines the NOx composition); (c) the dissolution is therefore expressible as 3UO2 + 4(2 + x)HNO3→3UO2(NO3)2 + 2(1 — x)NO + 6xNO2 + 2(2 + x)H2O, (0 < × < 1) (some values of the × were obtained); (d) the amount of NO2 in the NOx is considerably smaller than that reported by earlier authors, e.g., 25% for 6.7 MHNO3 at 101°C; (e) UO2(NO3)2 coexisting in the solution tends to increase the NO component in the NOx.
