Determination of U3O8 in UO2 by Infrared Spectroscopy
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The Role of Pe, Ph, and Carbonate on the Solubility of UO2 and Uraninite Under Nominally Reducing Conditions
Geochimica et Cosmochimica Acta, Vol. 62, No. 13, pp. 2223–2231, 1998 Copyright © 1998 Elsevier Science Ltd Pergamon Printed in the USA. All rights reserved 0016-7037/98 $19.00 1 .00 PII S0016-7037(98)00140-9 The role of pe, pH, and carbonate on the solubility of UO2 and uraninite under nominally reducing conditions 1 1 1 1 2 2 3, IGNASI CASAS, JOAN DE PABLO, JAVIER GIMENEZ´ , M. ELENA TORRERO, JORDI BRUNO, ESTHER CERA, ROBERT J. FINCH, * and 3,† RODNEY C. EWING 1Department of Chemical Engineering, Polytechnic University of Catalunya, Barcelona 08028, Spain 2QuantiSci SL, Parc Tecnolo`gic del Valle`s, Cerdanyola 08290, Spain 3Department of Earth and Planetary Sciences, University of New Mexico, Albuquerque, New Mexico 87131, USA (Received August 14, 1997; accepted in revised form March 26, 1998) Abstract—Experimental data obtained from uranium dioxide solubility studies as a function of pH and under nominally reducing conditions in a 0.008 mol dm23 perchlorate medium and in a 1 mol dm23 chloride solution are presented. The solubility of extensively characterized uraninite samples from Cigar Lake (Canada), Jachymov (Czech Republic), and Oklo (Gabon) was determined in a solution matching the composition of a groundwater associated with granitic terrain. The redox potential of the test solution was monitored throughout the experimental period. The results obtained were modeled using aqueous formation constants compiled by the NEA, using stability constants corrected to appropriate ionic strengths. The solubility curves have been adjusted by calculating the 1 N value of Ks4 (UO2(s) 2H2O U(OH)4(aq)) that gave the best fit with the experimental data. -
Depleted Uranium Hexafluoride: Waste Or Resource?
UCRGJC-120397 PREPRINT Depleted Uranium Hexafluoride: Waste or Resource? N. Schwertz J. Zoller R Rosen S. Patton C. Bradley A. Murray This paper was prepared for submittal to the Global ‘95 International Conference on Evaluation of Emerging Nuclear Fuel Cycle Systems Versailles, France September 11-14,1995 July 1995 This isa preprint of apaper intended for publication in a jaurnal orproceedings. Since changes may be made before publication, this preprint is made available with the understanding that it will not be cited or reproduced without the permiasion of the anthor. DISCLAIMER This document was prepared as an account of work sponsored by an agency of the United Stat= Government. Neither theunited States Governmentmor theuniversity of California nor any oftheir employees, makes any warranty, express or implied, or assumesanylegalliabilityorrespomibility forthe accuracy,completeness,orusefuin~ of any information, apparatus, pduct, or process disdosed, or represents that its use wouldnotinfringe privatelyowned rights. Referencehemin to anyspe&c commercial prodocis, proms, or service by trade name, trademark, manufacturer, or otherwise, does not necessarily constituteor imply its endorsement, reconunendation, or favoring by the United States Government or the University of California. The views and opinions of authors expressed herein do not necessady state or reflect those of the United States Government or the University of California, and shall not be used for adveltising or product endorsement purposes. DISCLAIMER Portions of this document may be illegible in electronic image products. Images are produced from the best available original document . DEPLETED URANIUM HEXAFLUORIDE: WASTE OR RESOURCE? N. Schwertz, J. Zoller, R. Rosen, S. Patton LAWRENCE LIVERMORE NATIONAL LABORATORY P. -
Depleted Uranium Technical Brief
Disclaimer - For assistance accessing this document or additional information,please contact [email protected]. Depleted Uranium Technical Brief United States Office of Air and Radiation EPA-402-R-06-011 Environmental Protection Agency Washington, DC 20460 December 2006 Depleted Uranium Technical Brief EPA 402-R-06-011 December 2006 Project Officer Brian Littleton U.S. Environmental Protection Agency Office of Radiation and Indoor Air Radiation Protection Division ii iii FOREWARD The Depleted Uranium Technical Brief is designed to convey available information and knowledge about depleted uranium to EPA Remedial Project Managers, On-Scene Coordinators, contractors, and other Agency managers involved with the remediation of sites contaminated with this material. It addresses relative questions regarding the chemical and radiological health concerns involved with depleted uranium in the environment. This technical brief was developed to address the common misconception that depleted uranium represents only a radiological health hazard. It provides accepted data and references to additional sources for both the radiological and chemical characteristics, health risk as well as references for both the monitoring and measurement and applicable treatment techniques for depleted uranium. Please Note: This document has been changed from the original publication dated December 2006. This version corrects references in Appendix 1 that improperly identified the content of Appendix 3 and Appendix 4. The document also clarifies the content of Appendix 4. iv Acknowledgments This technical bulletin is based, in part, on an engineering bulletin that was prepared by the U.S. Environmental Protection Agency, Office of Radiation and Indoor Air (ORIA), with the assistance of Trinity Engineering Associates, Inc. -
Dissolution of Uranium Dioxide in Nitric Acid Media: What Do We Know?
EPJ Nuclear Sci. Technol. 3, 13 (2017) Nuclear © Sciences P. Marc et al., published by EDP Sciences, 2017 & Technologies DOI: 10.1051/epjn/2017005 Available online at: http://www.epj-n.org REGULAR ARTICLE Dissolution of uranium dioxide in nitric acid media: what do we know? Philippe Marc1, Alastair Magnaldo1,*, Aimé Vaudano1, Thibaud Delahaye2, and Éric Schaer3 1 CEA, Nuclear Energy Division, Research Department of Mining and Fuel Recycling Processes, Service of Dissolution and Separation Processes, Laboratory of Dissolution Studies, 30207 Bagnols-sur-Cèze, France 2 CEA, Nuclear Energy Division, Research Department of Mining and Fuel Recycling Processes, Service of Actinides Materials Fabrication, Laboratory of Actinide Conversion Processes, 30207 Bagnols-sur-Cèze, France 3 Laboratoire Réactions et Génie des Procédés, UMR CNRS 7274, University of Lorraine, 54001 Nancy, France Received: 16 March 2016 / Received in final form: 15 November 2016 / Accepted: 14 February 2017 Abstract. This article draws a state of knowledge of the dissolution of uranium dioxide in nitric acid media. The chemistry of the reaction is first investigated, and two reactions appear as most suitable to describe the mechanism, leading to the formation of monoxide and dioxide nitrogen as reaction by-products, while the oxidation mechanism is shown to happen before solubilization. The solid aspect of the reaction is also investigated: manufacturing conditions have an impact on dissolution kinetics, and the non-uniform attack at the surface of the solid results in the appearing of pits and cracks. Last, the existence of an autocatalytic mechanism is questionned. The second part of this article presents a compilation of the impacts of several physico-chemical parameters on the dissolution rates. -
Needs for Large Mass Phototype Corium Experiments
NEEDS FOR LARGE MASS PROTOTYPIC CORIUM EXPERIMENTS: THE PLINIUS-2 PLATFORM Christophe Journeau, Laurence Buffe, Jean François Haquet, Pascal Piluso, Guy Willermoz CEA DEN, Cadarache, SMTA, 13108 St Paul lès Durance, France [email protected]; [email protected]; [email protected]; [email protected]; [email protected] ABSTRACT Corium is the molten material formed after meltdown of a nuclear reactor core during a severe accident. In order to improve the understanding and modelling of corium behavior, experiments are needed both for LWRs and GenIV fast reactors. Experiments using low temperature simulant materials, thanks to lower costs and constraints, allow the testing of a larger number of configurations and the determination of correlations. But some crucial corium phenomena cannot be reproduced at low temperatures such as the importance of radiation heat transfer or the presence of a large (up to 1000 K) liquidus-solidus interval. Consequently, some experiments are performed with high temperature simulant materials: alumina thermite as well as refractory oxides. However, it is not feasible to simulate all the aspects of corium phenomenology, especially its high temperature physico-chemistry. Therefore, even though the use of depleted uranium implies a series of protective and regulatory measures, the need for prototypic corium experimented is supported through several examples Another important aspect of experiment design deals with scaling. Small or medium scale corium experiments are easier to operate and only a few large scale (>100 kg) facilities have been built. Several effects are only visible with significant masses, as for instance, the formation of a corium cake during FCI or all the phenomena controlled by crust strength, such as underwater spreading or corium jet ablation. -
Inventory for Geological Disposal Main Report October 2018 DSSC/403/02
DSSC/403/02 Inventory for geological disposal Main Report October 2018 DSSC/403/02 Inventory for geological disposal Main Report October 2018 DSSC/403/02 Conditions of Publication This report is made available under the Radioactive Waste Management Ltd (RWM) Transparency Policy. In line with this policy, RWM is seeking to make information on its activities readily available, and to enable interested parties to have access to and influence on its future programmes. The report may be freely used for non-commercial purposes. RWM is a wholly owned subsidiary of the Nuclear Decommissioning Authority (NDA), accordingly all commercial uses, including copying and re publication, require permission from the NDA. All copyright, database rights and other intellectual property rights reside with the NDA. Applications for permission to use the report commercially should be made to the NDA Information Manager. Although great care has been taken to ensure the accuracy and completeness of the information contained in this publication, the NDA cannot assume any responsibility for consequences that may arise from its use by other parties. © Nuclear Decommissioning Authority 2018 All rights reserved. ISBN 978-1-84029-584-9. Other Publications If you would like to see other reports available from RWM and the NDA, a complete listing can be viewed at our website www.nda.gov.uk, or please write to us at the address below. Feedback Readers are invited to provide feedback on this report and on the means of improving the range of reports published. Feedback should be addressed to: RWM Feedback Radioactive Waste Management Ltd Building 587 Curie Avenue Harwell Campus Didcot OX11 0RH UK email: [email protected] ii DSSC/403/02 Preface Radioactive Waste Management Limited (RWM) has been established as the delivery organisation responsible for the implementation of a safe, sustainable and publicly acceptable programme for the geological disposal of the higher activity radioactive wastes in the UK. -
DEPLETED URANIUM HEXAFLUORIDE (Current Situation, Safe Handling and Prospects)
DEPLETED URANIUM HEXAFLUORIDE (current situation, safe handling and prospects) 2020 Authors: Alexander Nikitin, Head of Bellona Foundation Oleg Muratov, nuclear physicist, Head of Radiation Technology Dept., TVEL JSC Ksenia Vakhrusheva, Cand. Sci. Econ., Expert, BELLONA International Foundation Editor: Elena Verevkina Design: Alexandra Solokhina This Report was prepared with support and participation of Environmental Board of the Public Council of Rosatom State Atomiс Energy Corporation Publishers: Bellona Foundation Environmental Protection NGO ‘Ecopravo’ Expert and Legal Center TABLE OF CONTENTS Abbreviations ............................................................................................................................. 4 Foreword ..................................................................................................................................... 5 Introduction ................................................................................................................................ 6 Chapter 1. A few words about nuclear physics and radioactivity for non-specialists............... 8 Chapter 2. Uranium hexafluoride and its properties ..................................................................... 11 2.1. Physical properties of uranium hexafluoride .................................................................. 12 2.2. Chemical properties of uranium hexafluoride ................................................................ 13 Chapter 3. What is DUHF .................................................................................................................. -
Fifth Canadian National Report for the Joint Convention
Canadian National Report for the Joint Convention on the Safety of Spent Fuel Management and on the Safety of Radioactive Waste Management © Canadian Nuclear Safety Commission (CNSC) 2014 PWGSC catalogue number CC172-23/2014E-PDF ISSN 2368-4828 Extracts from this document may be reproduced for individual use without permission provided the source is fully acknowledged. However, reproduction in whole or in part for purposes of resale or redistribution requires prior written permission from the Canadian Nuclear Safety Commission. Également publié en français sous le titre: Rapport national du Canada pour la Convention commune sur la sûreté de la gestion du combustible usé et sur la sûreté de la gestion des déchets radioactifs Document availability This document can be viewed on the CNSC website at nuclearsafety.gc.ca. To request a copy of the document in English or French, please contact: Canadian Nuclear Safety Commission 280 Slater Street P.O. Box 1046, Station B Ottawa, Ontario K1P 5S9 CANADA Tel.: 613-995-5894 or 1-800-668-5284 (in Canada only) Facsimile: 613-995-5086 Email: [email protected] Website: nuclearsafety.gc.ca Facebook: facebook.com/CanadianNuclearSafetyCommission YouTube: youtube.com/cnscccsn Publishing history October, 2011 Fourth Report October, 2008 Third Report October, 2005 Second Report October, 2002 First Report ii Preface Information in this report covers the period up to March 31, 2014. However, in some instances the reporting period extends beyond this to the time of writing the report: July 31, 2014. Examples include the current status of the Canadian Nuclear Safety Commission’s regulatory documents, the Nuclear Waste Management Organization’s (NWMO) Adaptive Phased Management (APM) approach, and Ontario Power Generation’s (OPG) Deep Geologic Repository (DGR). -
09 Fr0200361
09 FR0200361 ^r.^r IQ 34. IMPORTANCE OF PROTOTYPIC-CORIUM EXPERIMENTS FOR SEVERE ACCIDENT RESEARCH P. PILUSO, C. JOURNEAU, G. COGNET, D. MAGALLON*, J.M. SEILER** CEA Cadarache 13108 St Paul les Durance cedex, France *: detached from the Joint Research Centre of the European Commission ** CEA Grenoble KEY WORDS: Severe accidents, Nuclear materials, Experiments Introduction: In case of a severe accident in a nuclear reactor, very complex physical and chemical phenomena would occur. Parallel to the development of mechanistic and scenario codes, experiments are needed to determine key phenomena and coupling, develop and qualify specific models, validate codes. Due to lower costs and constraints, experiments using low temperature simulant materials (such as CORINE [1] or Scaled Simulant Spreading Experiments (S3C) [2] for spreading or BALI [3,4] for in-vessel pools) allow the testing of a large number of configurations and the determination of correlations. But some crucial corium phenomena and behaviours such as the importance of radiation heat transfer or the presence of a large liquidus-solidus interval (up to 1000 K) are not reproduced in low temperature experiments. Consequently, it is attempted to simulate real corium with high temperature simulant materials: alumina, thermite, widely used (e.g. KATS [5] or COMET [6] facilities); high temperature salts or mixtures with zirconia and/or hafnia. However, it is not feasible to simulate all the aspects of corium phenomenology, especially its high temperature behaviour. Therefore, experiments with prototypic material are performed to check the results obtained with simulants and identify possible differences. In this context, CEA has undertaken a large program on severe accidents with prototypic corium [7]. -
Fuel Cycle Processes Directed Self-Study Course! This Is the Third of Nine Modules Available in This Directed Self-Study Course
MODULE 3.0: URANIUM CONVERSION Introduction Welcome to Module 3.0 of the Fuel Cycle Processes Directed Self-Study Course! This is the third of nine modules available in this directed self-study course. The purpose of this module is to be able to discuss the NRC regulations of and describe conversion facilities; identify the basic steps of the dry fluoride volatility conversion process and contrast with the wet acid digestion conversion process; identify sampling and measurement activities for the dry conversion process and the radiological and non-radiological hazards associated with the dry conversion process. This self-study module is designed to assist you in accomplishing the learning objectives listed at the beginning of the module. There are five learning objectives in this module. The module has self-check questions and activities to help you assess your understanding of the concepts presented in the module. Before you Begin It is recommended that you have access to the following materials: ◙ Trainee Guide ◙ Sequoyah Fuels Accident Slides (on CD accompanying course manual) ◙ “Release of UF6 from a Ruptured Model 48Y Cylinder at Sequoyah Fuels Corporation Facility: Lessons-Learned Report," U.S. Nuclear Regulatory Commission, NUREG-1198, June 1986. ◙ “Assessment of the Public Health Impact from the Accidental Release of UF6 at the Sequoyah Fuels Corporation Facility at Gore, Oklahoma," U.S. Nuclear Regulatory Commission, NUREG-1189, Vol. 1, March 1986. Complete the following prerequisites: ◙ Module 1.0: Overview of the Nuclear Fuel Cycle How to Complete this Module 1. Review the learning objectives. 2. Read each section within the module in sequential order. -
Preparation and Characterization of Uranium Oxides in Support of the K Basin Sludge Treatment Project
PNNL-17678 Preparation and Characterization of Uranium Oxides in Support of the K Basin Sludge Treatment Project SI Sinkov CH Delegard AJ Schmidt July 2008 DISCLAIMER This report was prepared as an account of work sponsored by an agency of the United States Government. Neither the United States Government nor any agency thereof, nor Battelle Memorial Institute, nor any of their employees, makes any warranty, express or implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed, or represents that its use would not infringe privately owned rights. Reference herein to any specific commercial product, process, or service by trade name, trademark, manufacturer, or otherwise does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States Government or any agency thereof, or Battelle Memorial Institute. The views and opinions of authors expressed herein do not necessarily state or reflect those of the United States Government or any agency thereof. PACIFIC NORTHWEST NATIONAL LABORATORY operated by BATTELLE for the UNITED STATES DEPARTMENT OF ENERGY under Contract DE-AC05-76RL01830 Printed in the United States of America Available to DOE and DOE contractors from the Office of Scientific and Technical Information, P.O. Box 62, Oak Ridge, TN 37831-0062; ph: (865) 576-8401 fax: (865) 576-5728 email: [email protected] Available to the public from the National Technical Information Service, U.S. Department of Commerce, 5285 Port Royal Rd., Springfield, VA 22161 ph: (800) 553-6847 fax: (703) 605-6900 email: [email protected] online ordering: http://www.ntis.gov/ordering.htm This document was printed on recycled paper. -
Uranium, from Mine to Mill
Milling Uranium production and resources Uranium history Simplified flow chart of uranium ore processing from Uranium • In 1789, Martin Klaproth, a German chemist, isolated 2016 mining to the production of concentrate. These processes Country resources (tU)* an oxide of uranium while analyzing pitchblende 2017/18 production (tU) are commonly known as milling and the product – <US$130/kg samples from silver mines in Bohemia. Pocket Guide uranium oxide concentrate – is the raw material for making nuclear fuel. Australia 6315 1,174,000 • For over 100 years uranium was mainly used as a colorant for ceramic glazes and for tinting in early Brazil 44 155,100 photography. Uranium was produced in Bohemia, Open pit Underground Cornwall (UK), Portugal and Colorado and total mining mining Canada 14,039 357,500 production amounted to about 300-400 tonnes. Crushing • The discovery of radium in 1898 by Marie Curie led & grinding China 1616 120,000 to the construction of a number of radium extraction Czech Republic 138 1300 plants processing uranium ore (radium is a decay product of uranium). Leaching India 385 Not available • Prized for its use in cancer therapy, radium reached a price of 750,000 gold francs per gram in 1906 (US$10 Kazakhstan 24,575 285,600 Tailings disposal Separate solids million). It is estimated that 754 grams were produced Recycle Malawi 0 8200 worldwide between 1898 and 1928. Uranium itself was barren liquor treated simply as a waste material. In-situ Extract U Namibia 3507 248,200 • With the discovery of nuclear fission in 1939, the leach mining in liquor uranium industry entered a new era.