GLOBAL MODEL for IODINE BEKAVIOUR FN REACTOR Contaayment

Total Page:16

File Type:pdf, Size:1020Kb

GLOBAL MODEL for IODINE BEKAVIOUR FN REACTOR Contaayment GLOBAL MODEL FOR IODINE BEKAVIOUR FN REACTOR CONTAaYMENT Anandhi Narayanan A thesis submitted in conformity with the requirements for the degree of Master of Applied Science Graduate Department of Chemical Engineering and Applied Chemistry University of Toronto @ Copyright by Anandhi Narayanan 2000 National iibrary Bibliothèque nationale I*I of Canada du Canada Acquisitions and Acquisitions et Bibliographie Services seivices bibliographiques 395 Wellington Sheet 395. rue Wellington Ottawa ON K1A ON4 Ottawa ON K1A ON4 Canada Canada The author has granted a non- L'auteur a accordé une Licence non exclusive licence allowing the exclusive permettant à la National Library of Canada to Bibliothèque nationale du Canada de reproduce, loan, distn'bute or sell reproduire, prêter, distribuer ou copies of ths thesis in microform, vendre des copies de cette thèse sous paper or electronic formats. la forme de microfiche/tilm, de reproduction sur papier ou sur format électronique. The author retains ownership of the L'auteur conserve la propriété du copyright in this thesis. Neither the droit d'auteur qui protège cette thèse. thesis nor substantial extracts kom it Ni la thèse ni des extraits substantiels may be printed or othenirise de celle-ci ne doivent être imprimés reproduced without the author's ou autrement reproduits sans son permission. autorisation. Global Model for Iodine Behaviour in Reactor Containment Master of Applied Science, May 2000 Anandhi Narayanan Graduate Department of Chernical Engineering and Applied Chemistry University of Toronto ABSTRACT The objective of this thesis was io develop a mechanistic model to simulate iodine behaviour within the containment structure of a nuclear generating station. The model included both aqueous and gas phase radiolysis and interfacial mass transfer. Validation of the model was conducted for each phase separately and the combined model was applied to a few reactor accident scenarios. The aqueous model successfùlly reflected various experimental data over a wide range in pH, iodide concentration, temperature, and dose rate. The incorporation of gas phase chemistry served to determine the dominant chemical forms of gaseous iodine. In addition, it was observed that hydrogen, likely to be present in the containment atmosphere, would hinder the elimination of molecular iodine. Finally, the interaction of iodine with nitrogen oxides was signincant when compared to reactions with ozone. Hence, the deposition of ozone onto surfaces did not impact iodine behaviour. The development of this model will serve as a usefbl tool for reactor safety assessments. The people acknowledged in this section assisted by either providing technical assistance or emotional support while completing this thesis. 1 am very grateful to them. Professor G.J. Evans for his supervision, patience and guidance throughout the course of my research. I tmly appreciated your critical review of my thesis document. You enabled me to learn a great deal. NSERC for fbnding my research. Professon M.J. Philiips and C.A. Mims for their participation in my defence cornittee and reviewing my thesis document. The entire nuclear and aerosol research group for their friendship; in particuiar Tutun for his constant assistance throughout, Fariborz for helping me get started and Lis for critiquing my presentation. Paul, Samar and Vani for the coffees, lunches and chats: a much needed break. My mother, father, Desi, Anin and Rudy for their unconditional love and support. Finally God, without whom I would not be. 1.0 INTRODUCTION.... ..w...w..m.I*000.8*a... ...............8...e...........................................8....... f 2.0 LITERATURE REVIEW .......................... ... ......................................................4 2 .L Severe Reactor Accidents .................................................................................. 4 2.2 Aqueous Phase Radiolysis ........................................................................................ 6 2.2.1 Statw cf Iodine Models ...................................................................................... 6 2.2.2 Aquesous Phase Chemistry .............................................................................. 11 2.2.2.1 Effect of pH ............................................................................................. 11 2.2.2.2 Effect of Temperature ............................................................................. 12 2.2.2.3 Effect of Total Iodide Concentration .......................... ...... ....................... 12 2.2.2.4 Effect of Dose Rate ................................................................................... 13 2.2.2.5 Effect of Dissolved Gases ........................................................................ 13 2.3 Gas Phase Radiolysis ............................................................................................. 15 2.3.1 Status of Models ............................................................................................... 15 2.3.2 Gus Phase Chernistry ....................................................................................... 17 3.1 Introduction to Radiation Chernisûy ...................................................................... 22 3.2 Aqueous Phase Radiolysis .................................................................................. 22 3.2.1 Water Radiolysis ............................................................................................. 23 3.2.2 Aqueous Iodine Chemistry ............................................................................... 24 3.3 Gas Phase Radiolysis .............................................................................................. 26 3.3.1 Primav Yields ................................................................................................. 27 3.3.2 Radiation Chemistry of Moist and Dry Air ...................................................... 29 3.3.3 Gas Phase lodine Chemistry............................................................................ 31 3.3.4 Ozone Deposition ............................................................................................. 32 3.4 interfacial Mass Transfer ........................................................................................ 36 4.0 MOOEL DEVELOPMENT .......e...............~~oe.~...................................................... 38 4.1 Facsimile Code ........................................................................................................ 38 4.2 Basis for Aqueous Mode1...................... .. .......................................................... 38 4.3 Basis for Gas Mode1............................................................................................ 39 4.4 Combined Mode1 .................................................................................................... 40 5.0 RESULTS AND DISCUSSION ...................................m. ............ 41 5.1 Aqueous Mode1 Analysis .................................................................................... 4 1 5.1. I Water Radiolysis .............................................................................................. 41 5.1.2 ludine Volatility ............................................................................................. 48 5.1.2.1 Impact of pH and Iodide Concentration............................................... 48 5.1.2.1.1 Flow Experiment................................................................................ 49 5.1 .2. L .2 Sparging Apparatus Experiment ........................................................ 50 5.1.2.1.3 Effect of pH for High Iodine Concentration ...................................... 53 5.1.2.1.4 Effect of pH for Low Ioduie Concentration ....................................... 54 5.1.2.2 impact of Dose Rate .................................................................................. 55 5.1.2.3 Impact of Temperature............................................................................. 58 5. 1.2.4 Impact of Organics.................................................................................. 61 5.1.3 Summary of Mode l.. ......................................................................................... 64 5.2 Gas Model .b slysis ................................................................................................ 67 5.2.1 Air Radiolysis ................................................................................................. 67 5.2.1.1 Ozone Yield: Theoreticai Estimation in Dry Air ...................................... 67 5.2.1.2 Ozone Yield: Theoretical Estimation in Moist Air ................................... 69 5.2.1.3 Ozone. Formation: Experimental Cornparison .......................................... 71 5.2.1.4 Nitnc Acid Formation ............................................................................... 75 5.2.2 Iodine Elimination ......................................................................................... 75 5.2.2.1 Mechanisin for Iodine Elirnination ........................................................... 76 5.2.2.2 Effect of Steam ......................................................................................... 79 5.2.2.3 Effect of Dose Rate ................................................................................... 80 5.2.2.4 Effect of Temperature .............................................................................. 80 5.2.2.5 Effect of Ozone ........................................................................................
Recommended publications
  • Iodine Oxoacids in Atmospheric Aerosol Formation – from Chamber Simulations to Field Observations
    REPORT SERIES IN AEROSOL SCIENCE No. 239 (2021) IODINE OXOACIDS IN ATMOSPHERIC AEROSOL FORMATION – FROM CHAMBER SIMULATIONS TO FIELD OBSERVATIONS XU-CHENG HE (何旭成) Institute for Atmospheric and Earth System Research / Physics Faculty of Science, University of Helsinki, Helsinki, Finland Academic dissertation To be presented, with the permission of the Faculty of Science of the University of Helsinki, for public criticism in Exactum auditorium CK112, Pietari Kalmin Katu 5, on August 23rd, 2021, at 14 o'clock. Helsinki 2021 Author’s Address Institute for Atmospheric and Earth System Research / Physics P.O. box 64 FI-00140 University of Helsinki [email protected] Supervisors Academician, Professor Markku Kulmala, Ph.D. Institute for Atmospheric and Earth System Research / Physics University of Helsinki Associate Professor Mikko Sipilä, Ph.D. Institute for Atmospheric and Earth System Research / Physics University of Helsinki Assistant Professor Matti Petteri Rissanen, Ph.D. Aerosol Physics Laboratory Tampere University Lecturer Theo Kurtén, Ph.D. Department of Chemistry University of Helsinki Reviewers Research Professor Hannele Hakola, Ph.D. Air Quality Group Finnish Meteorological Institute Assistant Professor Julia Schmale, Ph.D. Extreme Environments Research Laboratory École polytechnique fédérale de Lausanne Opponent Professor Gordon McFiggans, Ph.D. Department of Earth and Environmental Sciences University of Manchester ISBN 978-952-7276-59-4 (printed version) ISSN 0784-3496 Helsinki 2021 Unigrafia Oy ISBN 978-952-7276-60-0 (pdf version) http://www.atm.helsinki.fi FAAR Helsinki 2021 Acknowledgements The work for this thesis was carried out at the Division of Atmospheric Sciences at the Department of Physics and later at the Institute for Atmospheric and Earth System Research (INAR), University of Helsinki.
    [Show full text]
  • Atmospheric Chemistry of Iodine ,† ,‡ § || § Alfonso Saiz-Lopez,* John† M
    REVIEW pubs.acs.org/CR Atmospheric Chemistry of Iodine ,† ,‡ § || § Alfonso Saiz-Lopez,* John† M. C. Plane,* Alex^ R. Baker, Lucy J. Carpenter,‡ Roland von Glasow, Juan C. Gomez Martín, Gordon McFiggans, and Russell W. Saunders † Laboratory for Atmospheric and Climate Science (CIAC), CSIC, Toledo, Spain ‡ School of Chemistry, University of Leeds, Leeds, LS2 9JT, United Kingdom §School of Environmental Sciences, University of East Anglia, Norwich NR4 7TJ, United Kingdom Department) of Chemistry, University of York, Heslington, York YO10 5DD, United Kingdom ^ School of Earth, Atmospheric & Environmental Sciences, University of Manchester, Manchester, M13 9PL, United Kingdom CONTENTS 5.2.2. Particle Formation in Macroalgal 1. Introduction A Incubation Experiments R 2. Sources of Iodine to the Atmosphere C 5.2.3. Iodine Oxide Particle Growth to 2.1. Atmospheric Mixing Ratios, Seasonality, and Potential Cloud Condensation Nuclei S Trends in Distributions C 5.3. Unresolved Aspects of Iodine-Mediated Particle 2.2. Emission Rates and Mechanisms E formation S 2.3. Molecular Iodine H 6. Accumulation of Iodine in Aerosol U 2.4. Summary H 6.1. Iodine Concentrations in Aerosol U 3. Measurements of Gas-Phase Reactive Iodine Species I 6.2. Iodine Speciation U 3.1. Coastal Marine Boundary Layer I 6.3. Key Uncertainties V 7. Impacts and Modeling of Reactive Iodine Species V 3.2. Remote, Open Ocean, and Tropical Marine 7.1. Impacts of Iodine Chemistry V Boundary Layer I 7.1.1. Ozone Depletion V 3.3. Polar Boundary Layer J 7.1.2. Influence on the NO and HO Balance W 3.4. Salt Lakes and Volcanoes K x x 7.1.3.
    [Show full text]
  • Phenol Disgrace Via Periodate in Integrating by Using Supersonic Radiation
    Journal of Medicine and Life Vol. 8, Special Issue 3, 2015, pp.233-237 Phenol disgrace via Periodate in integrating by using Supersonic Radiation Seid-Mohamadi A*, Asgari G**, Shokoohi R**, Adabi S** *Social Determinants of Health Research Center, Department of Environmental Health Engineering, School of Public Health, Hamadan University of Medical Sciences, Hamedan, Iran, **Department of Environmental Health Engineering, School of Public Health, Hamadan University of Medical Sciences, Hamadan, Iran Correspondence to: Shervin Adabi, MSc, Department of Environmental Health Engineering, School of Public Health, Hamadan University of Medical Sciences, Shahid Fahmideh Street, Hamadan, Iran Mobile phone: +989374196112, E-mail: [email protected] Received: March 14th, 2015 – Accepted: June 18th, 2015 Abstract In this study, a successful degradation of phenol was achieved by a combination of processes, ultrasonic irradiation and periodate. The effect of pH, dosage of IO4-, dosage of initial phenol and ultrasonic irradiation time on the phenol degradation were examined. Furthermore, the impacts of ion intensity on phenol degradation were examined. The findings indicated that the disgrace ratio advanced in acidic conditions and an upper degradation was achieved in combination processes. The current new investigation examined the effect of ion intensity and the findings determined that the principal intensity of solution is an inactive variable on phenol disgrace with these systems. A comparison research among IO4-/ US system and IO4- and US separately determined the COD removal and indicated that an combined method of IO4-/ US system had the best execution. Introduction degrade phenol residuals before the discharge to water sources. Advanced Oxidation Processes (AOPs) have Industries generate a considerable amount of been studied as efficient methods in last decades [5,6].
    [Show full text]
  • Passivated Iodine Pentoxide Oxidizer for Potential Biocidal Nanoenergetic Applications Jingyu Feng, Guoqiang Jian, Qing Liu, and Michael R
    Research Article www.acsami.org Passivated Iodine Pentoxide Oxidizer for Potential Biocidal Nanoenergetic Applications Jingyu Feng, Guoqiang Jian, Qing Liu, and Michael R. Zachariah* Department of Chemistry and Biochemistry, and Department of Chemical and Biomolecular Engineering, University of Maryland, College Park, Maryland 20742, United States *S Supporting Information ABSTRACT: Iodine pentoxide (I2O5), also known as diiodine pentoxide, is a strong oxidizer which has been recently proposed as an iodine-rich oxidizer in nanoenergetic formulations, whose combustion products lead to molecular iodine as a biocidal agent. However, its highly hygroscopic nature hinders its performance as a strong oxidizer and an iodine releasing agent and prevents its implementation. In this work, we developed a gas phase assisted aerosol spray pyrolysis which enables creation of iron oxide passivated I2O5. Transmission electron microscopy elemental imaging as well as temperature-jump mass spectrometry confirmed the core shell fi nature of the material and the fact that I2O5 could be encapsulated in pure unhydrated form. Combustion performance nds an optimal coating thickness that enables combustion performance similar to a high performing CuO based thermite. KEYWORDS: passivated, aerosol spray pyrolysis, nanothermite, energetic materials, nanocomposite, biocide 1. INTRODUCTION spores, presumably because of the release of elemental iodine as a combustion product when reacted with aluminum:16 10Al + Nanoenergetic materials, including metal based fuels and metal → 3I2O5 5Al2O3 +3I2. However, I2O5 is sensitive to humid oxide oxidizers with typically nanosized dimensions, have been 20,21 shown to have reactive properties superior to traditional environments and reacts with water in the ambient air. This 1−4 not only increases the particle size which degrades combustion energetic materials.
    [Show full text]
  • The Effect of Low Solubility Organic Acids on the Hygroscopicity of Sodium Halide Aerosols
    Atmos. Chem. Phys., 14, 11409–11425, 2014 www.atmos-chem-phys.net/14/11409/2014/ doi:10.5194/acp-14-11409-2014 © Author(s) 2014. CC Attribution 3.0 License. The effect of low solubility organic acids on the hygroscopicity of sodium halide aerosols L. Miñambres, E. Méndez, M. N. Sánchez, F. Castaño, and F. J. Basterretxea Departamento de Química Física, Facultad de Ciencia y Tecnología, University of the Basque Country, UPV/EHU, Campus de Leioa, B. Sarriena, s/n, Leioa 48940, Spain Correspondence to: L. Miñambres ([email protected]) Received: 28 November 2013 – Published in Atmos. Chem. Phys. Discuss.: 18 February 2014 Revised: 13 August 2014 – Accepted: 31 August 2014 – Published: 29 October 2014 Abstract. In order to accurately assess the influence of fatty 1 Introduction acids on the hygroscopic and other physicochemical prop- erties of sea salt aerosols, hexanoic, octanoic or lauric acid Marine aerosol is one of the most abundant types of nat- together with sodium halide salts (NaCl, NaBr and NaI) ural particulate matter in the Earth’s troposphere. Sea salt have been chosen to be investigated in this study. The hy- particles play an active role in the Earth’s radiative bal- groscopic properties of sodium halide sub-micrometre par- ance, influence mass transfer of gaseous compounds and ticles covered with organic acids have been examined by cloud-precipitation mechanisms, contribute to the formation Fourier-transform infrared spectroscopy in an aerosol flow of cloud condensation nuclei and have highly reactive sur- cell. Covered particles were generated by flowing atomized faces that take part in heterogeneous and multiphase chemi- sodium halide particles (either dry or aqueous) through a cal reactions (Andreae and Rosenfeld, 2008; Carslaw et al., heated oven containing the gaseous acid.
    [Show full text]
  • On the Mechanism of Iodine Oxide Particle Formation
    This is a repository copy of On the mechanism of iodine oxide particle formation. White Rose Research Online URL for this paper: http://eprints.whiterose.ac.uk/87171/ Version: Accepted Version Article: Gomez Martin, JC, Gálvez, O, Baeza-Romero, MT et al. (3 more authors) (2013) On the mechanism of iodine oxide particle formation. Physical Chemistry Chemical Physics, 15 (37). 15612 - 15622. ISSN 1463-9076 https://doi.org/10.1039/c3cp51217g Reuse Unless indicated otherwise, fulltext items are protected by copyright with all rights reserved. The copyright exception in section 29 of the Copyright, Designs and Patents Act 1988 allows the making of a single copy solely for the purpose of non-commercial research or private study within the limits of fair dealing. The publisher or other rights-holder may allow further reproduction and re-use of this version - refer to the White Rose Research Online record for this item. Where records identify the publisher as the copyright holder, users can verify any specific terms of use on the publisher’s website. Takedown If you consider content in White Rose Research Online to be in breach of UK law, please notify us by emailing [email protected] including the URL of the record and the reason for the withdrawal request. [email protected] https://eprints.whiterose.ac.uk/ ⊇•≈♥ ⇓→←•×≈ ∇″ו″≈ ⊇•≈♥ √±↔→″↵× This article can be cited before page numbers have been issued, to do this please use: J. C. Gomez Martin, Ó. Gálvez, M. T. B. Romero, T. Ingham, J. M. C. Plane and M. A. Blitz, Phys. Chem. Chem. Phys., 2013, DOI: 10.1039/C3CP51217G.
    [Show full text]
  • The Water–Iodine Oxide System: a Revised Mechanism for Hydration and Dehydration† Cite This: RSC Adv.,2017,7,10183 Dylan K
    RSC Advances PAPER The water–iodine oxide system: a revised mechanism for hydration and dehydration† Cite this: RSC Adv.,2017,7,10183 Dylan K. Smith,a Michelle L. Pantoya,*a Jeffrey S. Parkeyb and Mehmet Kesmezb Iodic acids are widely studied in atmospheric and biological applications but their inherent hydrophilic properties introduce complexities that affect their functionality and reactivity. We have shown that iodic acid (HIO3) dehydrates directly into iodine pentoxide (I2O5) in contradiction to the generally accepted multi-step dehydration mechanism where HIO3 dehydrates into HI3O8 first, then dehydrates into I2O5. The generally accepted mechanism is used to determine the concentration of iodic acid by TGA and is only valid for special conditions. The revised mechanism allows for the determination of concentrations of iodic acids under all conditions, and the more specific conditions where the accepted mechanism is Received 6th December 2016 valid are shown. The determination of concentration of iodic acid with the revised dehydration Accepted 1st February 2017 mechanism is dependent on assumptions of residual water and initial concentration of HI3O8. The DOI: 10.1039/c6ra27854j validity of these assumptions is established by studying the absorption and hydration behavior of I2O5 rsc.li/rsc-advances from atmospheric water. These results will have an impact on the handling and use of iodine. Introduction absorption begins; variations in concentration of iodic acids (HIO3,HI3O8); crystal structure; onset temperature for dehy- Iodine(V) oxides have biocidal potential in neutralizing bacterial dration and decomposition; and, absorption rates. All of the agents released in certain weapon systems. Handling iodine(V) inconsistencies discussed below are affected by the hydration oxides is one of the biggest challenges toward their effective and dehydration mechanism.
    [Show full text]
  • Chemical Substances Exempt from Notification of Manufacturing/Import Amount
    Chemical Substances Exempt from Notification of Manufacturing/Import Amount A list under Chemical Substance Control Law (Japan) 2014-3-24 Official issuance: Joint Notice No.1 of MHLW, METI and MOE English source: Chemical Risk Information Platform (CHRIP) Edited by: https://ChemLinked.com ChemLinked Team, REACH24H Consulting Group| http://chemlinked.com 6 Floor, Building 2, Hesheng Trade Centre, No.327 Tianmu Mountain Road, Hangzhou, China. PC: 310023 Tel: +86 571 8700 7545 Fax: +86 571 8700 7566 Email: [email protected] 1 / 1 Specification: In Japan, all existing chemical substances and notified substances are given register numbers by Ministry of International Trade and Industry (MITI Number) as a chemical identifier. The Japanese Chemical Management Center continuously works on confirming the mapping relationships between MITI Numbers and CAS Registry Numbers. Please enter CHRIP to find if there are corresponding CAS Numbers by searching the substances’ names or MITI Numbers. The first digit of a MITI number is a category code. Those adopted in this List are as follows: 1: Inorganic compounds 2: Chained organic low-molecular-weight compounds 3: Mono-carbocyclic organic low-molecular-weight compounds 5: Heterocyclic organic low-molecular-weight compounds 6: Organic compounds of addition polymerization 7: Organic compounds of condensation polymerization 8: Organic compounds of modified starch, and processed fats and oils 9: Compounds of pharmaceutical active ingredients, etc. This document is provided by ChemLinked, a division of REACH24H Consulting Group. ChemLinked is a unique portal to must-know EHS issues in China, and essential regulatory database to keep all EHS & Regulatory Affairs managers well-equipped. You may subscribe and download this document from ChemLinked.com.
    [Show full text]
  • Removal of Radioactive Iodine Using Silver/Iron Oxide Composite Nanoadsorbents
    nanomaterials Communication Removal of Radioactive Iodine Using Silver/Iron Oxide Composite Nanoadsorbents Mah Rukh Zia 1,†, Muhammad Asim Raza 2,3,† , Sang Hyun Park 2,3 , Naseem Irfan 1, Rizwan Ahmed 1, Jung Eun Park 4, Jongho Jeon 4,* and Sajid Mushtaq 1,2,3,* 1 Department of Nuclear Engineering, Pakistan Institute of Engineering and Applied Sciences, P. O. Nilore, Islamabad 45650, Pakistan; [email protected] (M.R.Z.); [email protected] (N.I.); [email protected] (R.A.) 2 Advanced Radiation Technology Institute, Korea Atomic Energy Research Institute, Jeongeup 56212, Korea; [email protected] (M.A.R.); [email protected] (S.H.P.) 3 Radiation Science and Technology, University of Science and Technology, Daejeon 34113, Korea 4 Department of Applied Chemistry, College of Engineering, Kyungpook National University, Daegu 41566, Korea; [email protected] * Correspondence: [email protected] (J.J.); [email protected] (S.M.); Tel.: +82-53-950-5584 (J.J.); +92-51-9248611-3716 (S.M.) † These Authors contributed equally to this study. Abstract: Efficient and cost-effective removal of radioactive iodine (radioiodine) from radioactive contaminated water has become a crucial task, following nuclear power plant disasters. Several materials for removing radioiodine have been reported in the literature. However, most of these materials exhibit some limitations, such as high production cost, slow adsorption kinetics, and poor adsorption capacity. Herein, we present silver/iron oxide nanocomposites (Ag/Fe3O4) for the efficient and specific removal of iodine anions from contaminated water. The Ag/Fe3O4 were Citation: Zia, M.R.; Raza, M.A.; Park, synthesized using a modified method and characterized via scanning electron microscopy, transmis- S.H.; Irfan, N.; Ahmed, R.; Park, J.E.; Jeon, J.; Mushtaq, S.
    [Show full text]
  • Absolute Absorption Cross-Section and Photolysis Rate of I2 A
    Absolute absorption cross-section and photolysis rate of I2 A. Saiz-Lopez, R. W. Saunders, D. M. Joseph, S. H. Ashworth, J. M. C. Plane To cite this version: A. Saiz-Lopez, R. W. Saunders, D. M. Joseph, S. H. Ashworth, J. M. C. Plane. Absolute absorption cross-section and photolysis rate of I2. Atmospheric Chemistry and Physics, European Geosciences Union, 2004, 4 (5), pp.1443-1450. hal-00295493 HAL Id: hal-00295493 https://hal.archives-ouvertes.fr/hal-00295493 Submitted on 1 Sep 2004 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Atmos. Chem. Phys., 4, 1443–1450, 2004 www.atmos-chem-phys.org/acp/4/1443/ Atmospheric SRef-ID: 1680-7324/acp/2004-4-1443 Chemistry and Physics Absolute absorption cross-section and photolysis rate of I2 A. Saiz-Lopez1, R. W. Saunders1, D. M. Joseph1, S. H. Ashworth2, and J. M. C. Plane1 1School of Environmental Sciences, University of East Anglia, Norwich, UK 2School of Chemical Sciences and Pharmacy, University of East Anglia, Norwich, UK Received: 23 February 2004 – Published in Atmos. Chem. Phys. Discuss.: 5 May 2004 Revised: 27 July 2004 – Accepted: 20 August 2004 – Published: 1 September 2004 Abstract.
    [Show full text]
  • United States Patent As Fice Patiented Sept
    s 2,904,403 United States Patent As fice Patiented Sept. 15, 1959 1 2 are agitated during this period by any suitable means. The vessel is then cooled, opened and iodine penta 2,904,403 fluoride collected and purified by conventional procedures such as distillation. When alkali or alkaline earth metal PREPARATION OF BF iodates are used in the process, the iodine pentafluoride William Channing Smith, Wilmington, Del, assignor to may be isolated in the form of a solid complex compound E. H. du Pont de Nemours and Company, Wilmington, with alkali or alkaline earth metal fluorides. Dei, a corporation of Delaware in a continuous process gaseous sulfur tetrafluoride is No Drawing. Application June 7, 1957 passed through a tube containing the iodine compound, Serial No. 664,162 0 preferably heated to a temperature high enough to vola tilize the iodine pentafluoride as it is formed. The 5 Claims. (C. 23-205) iodine pentafluoride is separated from the gas effluent by cooling in traps and the unreacted sulfur tetrafluoride is recycled through the reaction tube. This invention relates to iodine fluorides and has as 5 The following examples illustrate the process of the its primary object provision of a novel method of prepar invention. ing such fluorides, iodine pentafluoride in particular. Iodine pentafluoride is a versatile and well-known Example 1 fluorinating agent which can be used to prepare fluorine (A) A bomb, lined with stainless steel and of 145 mi. bearing compounds that are not readily accessible by 20 capacity, was charged with 33.4 g. (0.10 mode) of iodine other routes.
    [Show full text]
  • Reaction Kinetics and Combustion Dynamics of I4O9 and Aluminum Mixtures
    Journal of Visualized Experiments www.jove.com Video Article Reaction Kinetics and Combustion Dynamics of I4O9 and Aluminum Mixtures Dylan K. Smith1, Michelle L. Pantoya1, Jeffrey S. Parkey2, Mehmet Kesmez2 1 Department of Mechanical Engineering, Texas Tech University 2 Lynntech Inc. Correspondence to: Michelle L. Pantoya at [email protected] URL: https://www.jove.com/video/54661 DOI: doi:10.3791/54661 Keywords: Engineering, Issue 117, iodine compounds, tetraiodine nonoxide, I4O9, reactivity, aluminum combustion, biocidal agent, iodine gas, flame speed, DSC, TGA Date Published: 11/7/2016 Citation: Smith, D.K., Pantoya, M.L., Parkey, J.S., Kesmez, M. Reaction Kinetics and Combustion Dynamics of I4O9 and Aluminum Mixtures. J. Vis. Exp. (117), e54661, doi:10.3791/54661 (2016). Abstract Tetraiodine nonoxide (I4O9) has been synthesized using a dry approach that combines elemental oxygen and iodine without the introduction of hydrated species. The synthesis approach inhibits the topochemical effect promoting rapid hydration when exposed to the relative humidity of ambient air. This stable, amorphous, nano-particle material was analyzed using differential scanning calorimetry (DSC) and thermal gravimetric analysis (TGA) and showed an exothermic energy release at low temperature (i.e., 180 °C) for the transformation of I4O9 into I2O5. This additional exothermic energy release contributes to an increase in overall reactivity of I4O9 when dry mixed with nano-aluminum (Al) powder, resulting in a minimum of 150% increase in flame speed compared to Al + I2O5. This study shows that as an oxidizer, I4O9 has more reactive potential than other forms of iodine(V) oxide when combined with Al, especially if I4O9 can be passivated to inhibit absorption of water from its surrounding environment.
    [Show full text]