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Passivated Iodine Pentoxide Oxidizer for Potential Biocidal Nanoenergetic Applications Jingyu Feng, Guoqiang Jian, Qing Liu, and Michael R

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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. Essentially, our current understanding is 20,21 that the importance of the nanoscale is to more intimately mix performance but also hydrolyzes I2O5 to iodic acid HIO3 fuel and oxidizer, thus reducing the heat and mass transport which is corrosive to metal. HIO3 will undergo reaction with fi elemental aluminum to give aluminum oxide under ambient limitations, leading to a signi cant enhancement in its reactivity 22 5−11 conditions. This not only severely limits the combustion and burn rate. ’ The growing threat of biological weapons has prompted performance of I2O5 containing thermite but also inhibits I2O5 s research efforts into new energetic materials with biocidal application as an iodine-releasing oxidizer for agent defeat in − capabilities.12 18 Such materials possess an energetic compo- thermite formulations. To address this limitation, one approach nent to deliver thermal energy but also release biocidal agents, is to create the passivated structure for I2O5 particles. Several methods that are currently available to fabricate e.g., silver or halogen that can function over a longer period of fi time. For many applications, energetic components involve the passivated nanoparticles can be generally classi ed into two categories: “wet treatment”23 and “gas phase”.24 The use of aluminum as a fuel component with a strong oxidizer, “ ” which releases the biocide. Clark et al. showed from the group approaches involving liquid phase , such as the co-precip- itation, sol-gel, and microemulsion, dispersing core particles in a of energetic oxidizers, I2O5,Ag2O, Fe2O3, that the iodine containing thermite was extremely effective at neutralizing solvent containing reactive precursors, are not applicable to 20 “ ” spores postcombustion.16 Other oxidizers including AgIO and passivate I2O5. The alternative gas phase methods, which 3 have the possibility to scale up,24 are easier and more suitable to Ag2O were investigated experimentally for potential biocidal 17,18 make passivated I2O5 nanoparticles. applications. AgIO3, which thermally decomposed to releaseiodineandoxygen,wasshowntohavebetter Prakash et al. reported a single step, two-temperature aerosol − performance than the traditional oxidizers copper oxide and spray pyrolysis process to create a pure core shell nanostruc- 17 ture for nanothermite formulations, whereby a thin layer of iron oxide in nano-Al based combustion tests. Ag2O, a relatively weak oxidizer (Fe2O3) was coated on a strong relatively poor oxidizer, if combined with CuO and AgIO3, can 25 generate a high amount of biocidal silver in nanoaluminum oxidizer (KMnO4) nanoparticle. In this process, precursors of · based thermite reactions.18 Fe(NO3)3 9H2O and KMnO4 are dissolved in an aqueous Due to the biocidal property of iodine, other oxidizers are being considered, most notably I2O5 which is a very strong Received: January 14, 2013 oxidizer with a high mass fraction of iodine (∼76%).19 “Al + Accepted: August 29, 2013 ” ff I2O5 reaction has been shown to be e ective at neutralizing Published: August 29, 2013 © 2013 American Chemical Society 8875 dx.doi.org/10.1021/am4028263 | ACS Appl. Mater. Interfaces 2013, 5, 8875−8880 ACS Applied Materials & Interfaces Research Article Figure 1. Experimental system for synthesis of I2O5 and its passivation with iron oxide. solution and sprayed into droplets that are typically one Fe2O3 nanopowder (<50 nm), and CuO nanopowder (< 50 nm) were micrometer in diameter. The droplets pass through the from Sigma-Aldrich and used as received. The nano-sized aluminum ∼ diffusion dryer and to two tube furnaces maintained at different ( 50 nm ALEX) for the thermite reaction was purchased from the temperatures. The first furnace was maintained above the iron Argonide Corporation. The aluminum nanopowders were measured to ∼ ° contain 70 wt % active Al by thermogravimetric analysis (TGA). nitrate decomposition temperature ( 120 C), and the second 2.2. Aerosol Spray Pyrolysis and Materials Characterization. furnace was operated at the temperature near the melting point Aerosol spray pyrolysis includes two steps: atomization and thermal of potassium permanganate (∼240 °C). At 120 °C, the iron decomposition (Figure 1). In the atomization step, the dissolved nitrate decomposes into Fe2O3, in the permanganate solid precursor solution was atomized to produce the aerosol droplets by a matrix. When the temperature is raised to 240 °C, where the home-made Collison-type atomizer. The droplet diameter was permanganate melts, Fe O phase separates and aggregates as a measured to be around 1 μm by a laser aerosol spectrometer. Aerosol 2 3 fi ff fi shell around the KMnO core. The reactivity of the resulting droplets were rstly passed through a di usion dryer lled with silica 4 gel to remove most of the precursor solvent (water) and then through materials can be tuned by coating the KMnO4 core with Fe2O3 ff 25 tube furnaces for the thermal decomposition. In the atomizer, the shell of di erent thicknesses. This approach can also be precursor iodic acid solution concentration was 5.0 wt %. The generalized and applied to other systems. For example, Wu et residence time of the reaction was estimated to be ∼8 seconds at a al. employed this strategy to successfully incorporate high fl fi ow rate of 3.5 L/min. The nal iron oxide coated I2O5 products were oxygen content perchlorate salts (KClO4 and NH4ClO4) into collected on a HTTP membrane filter (0.4 μm pore, Millipore). TEM 26 the common metal oxide (Fe2O3 and CuO) shell. The key to (JEOL JEM 2100 FEG) and EDS (Oxford INCA 250) line scans this strategy is to take advantage of the aerosol spray pyrolysis provided information of particle size, morphology, and elemental method, where all the physical and chemical processes occur in core−shell structure. the confined aerosol droplet as a micro-reactor. 2.3. Iron Oxide Passivation Coating. Iron oxide was chosen as a Although the above-mentioned single step, two-temperature passivating coating because of its prior success in passivating potassium permanganate.25 The iron oxide coating was fabricated via a thermal aerosol spray pyrolysis strategy is simple, it failed to passivate decomposition method, in which iron pentacarbonyl is vaporized and I O particles because the shell precursors, Fe(NO ) and 2 5 3 3 decomposed followed by deposition onto the surface of the I2O5. Iron Cu(NO3)2, reacted immediately with iodic acid to form metal pentacarbonyl vapor was generated by introducing a metered flow of iodate precipitates in the starting solution. Thus, an alternative argon into the liquid in an ice bath. The vapor was then mixed with the approach was required. aerosol stream and decomposed at ∼200 °C. In this work, we developed a modified gas phase assisted Assuming all the iron pentacarbonyl decomposed and ended up as iron oxide on the surface of I2O5 core particles, the coating thickness, aerosol synthesis approach to successfully passivate I2O5 within fl an iron oxide shell to create an air-stable passivated oxidizer. for volumetric ow rates of argon at 26, 75, 210, and 300 sccm, is calculated to be 4.3, 12, 34, and 49 nm. The related Fe/I molar ratios The size, morphology, and composition characterizations of the were determined gravimetrically (detailed in 2.4.1.) to be 0.25, 1.8, 4.3, as prepared Fe2O3/I2O5 passivated oxidizer were done by a and 6.2, respectively. transmission electron microscope (TEM) with an energy 2.4. Combustion Tests. 2.4.1. Thermite Sample Preparation. In dispersive X-ray spectrometer (EDS). A time resolved high order to create a stoichiometric thermite mixture with nanoaluminum, heating rate mass spectrometer was employed to characterize knowledge
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