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THE CATALYTIC OZONE OXIDATION OF AQUEOUS SOLUTIONS OF HYDRAZINE, MONOMETHYL HYDRAZINE AND UNSYMMETRICAL DIMETHYLHYDRAZINE Raymond A. Sierka, Professor Civil Engineering Department University of Arizona Tucson, Arizona 85721 William F. Cowen, Senior Analytical Chemist Catalytic, Inc. Philadelphia, Pennsylvania 19102 INTRODUCTION The hydrazine family of fuels includes hydrazine (H), monomethylhydrazine (MMH) and unsymmetrical dimethylhydrazine (UDMH) as well as mixtures of the above. The United States Air Force is responsible for the procurement, storage and transport of hydrazine fuels not only for its own systems, such as Minuteman III and the F-l 6, but also for NASA and the space shuttle program. During the course of these operations there is a potential for environmental degradation. For example, accidental spdls could occur directly from tank traders and tank cars or when transfer lines are connected or disconnected during loading and unloading. Since the transport container must be sampled at the site of production as well as the destination point, the problem of proper disposal of these materials and residual purged liquids must be carefuUy considered. This research centered on the treatment of aqueous solutions of H, MMH and UDMH by ozone. A parametric study was conducted to evaluate the effect of ultraviolet (UV) light as a catalyst, pH, solution concentration, reactor inlet ozone gas phase concentration and superficial gas velocity. Additionally, the effect of gas sparging (air or oxygen) in the presence and absence of UV light was evaluated. Finally, the partial oxidation products of ozone treated hydrazine fuels were characterized and aquatic toxicity testing accomphsh- ed. EXPERIMENTAL APPARATUS The basic apparatus used for all experiments is presented in a process flow diagram shown in Figure 1. All experiments were conducted in a semi-batch mode, that is, a constant liquid volume and a continuous supply of gas. Two reactors were employed in this work. The primary reactor was the Life Systems Modified Torricelli Ozone Contactor (LMTOC) and the second one was an ozone-ultrasonic reactor. The information generated with the latter reactor is not reported in this paper. The reader is referred to Reference 1 for results obtained with the ozone-ultrasound catalyzed system. The basic design characteristics and construction materials of the LMTOC are listed in Table I. More complete design and development information can be found elsewhere [2,3]. A grace ozonator Model LG-2-L2 was used to produce ozone. The unit contained two corona cells and was designed to operate at gas pressures to 15 psig, with gas flows from 10 to 100 SCFH and an electrical power input from 0 to 200 watts per corona ceU. Ozone was produced from both air and oxygen. For runs when an ozone concentration of 13 mg/l gas or less (approximately 1% ozone in air) was desired, air was the ozonator feed gas. Air was compressed in a Puregas Compressor Model 4 HCJ-12-M 400 X and passed through 0.25-in. stainless steel tubing to the ozonator at 15 psig. Tank oxygen, (extra-dry grade) was supplied to the ozonator in the same manner as the air. Oxygen feed gas permitted the production of higher concentrations of ozone (i.e., approximately 2% ozone in oxygen) than with air for the same electrical power input to the generator. 406
Object Description
Purdue Identification Number | ETRIWC198039 |
Title | Catalytic ozone oxidation of aqueous solutions of hydrazine, monomethyl hydrazine and unsymmetrical dimethylhydrazine |
Author |
Sierka, Raymond A. Cowen, William F. |
Date of Original | 1980 |
Conference Title | Proceedings of the 35th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,31542 |
Extent of Original | p. 406-415 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Date Digitized | 2009-10-22 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 406 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | THE CATALYTIC OZONE OXIDATION OF AQUEOUS SOLUTIONS OF HYDRAZINE, MONOMETHYL HYDRAZINE AND UNSYMMETRICAL DIMETHYLHYDRAZINE Raymond A. Sierka, Professor Civil Engineering Department University of Arizona Tucson, Arizona 85721 William F. Cowen, Senior Analytical Chemist Catalytic, Inc. Philadelphia, Pennsylvania 19102 INTRODUCTION The hydrazine family of fuels includes hydrazine (H), monomethylhydrazine (MMH) and unsymmetrical dimethylhydrazine (UDMH) as well as mixtures of the above. The United States Air Force is responsible for the procurement, storage and transport of hydrazine fuels not only for its own systems, such as Minuteman III and the F-l 6, but also for NASA and the space shuttle program. During the course of these operations there is a potential for environmental degradation. For example, accidental spdls could occur directly from tank traders and tank cars or when transfer lines are connected or disconnected during loading and unloading. Since the transport container must be sampled at the site of production as well as the destination point, the problem of proper disposal of these materials and residual purged liquids must be carefuUy considered. This research centered on the treatment of aqueous solutions of H, MMH and UDMH by ozone. A parametric study was conducted to evaluate the effect of ultraviolet (UV) light as a catalyst, pH, solution concentration, reactor inlet ozone gas phase concentration and superficial gas velocity. Additionally, the effect of gas sparging (air or oxygen) in the presence and absence of UV light was evaluated. Finally, the partial oxidation products of ozone treated hydrazine fuels were characterized and aquatic toxicity testing accomphsh- ed. EXPERIMENTAL APPARATUS The basic apparatus used for all experiments is presented in a process flow diagram shown in Figure 1. All experiments were conducted in a semi-batch mode, that is, a constant liquid volume and a continuous supply of gas. Two reactors were employed in this work. The primary reactor was the Life Systems Modified Torricelli Ozone Contactor (LMTOC) and the second one was an ozone-ultrasonic reactor. The information generated with the latter reactor is not reported in this paper. The reader is referred to Reference 1 for results obtained with the ozone-ultrasound catalyzed system. The basic design characteristics and construction materials of the LMTOC are listed in Table I. More complete design and development information can be found elsewhere [2,3]. A grace ozonator Model LG-2-L2 was used to produce ozone. The unit contained two corona cells and was designed to operate at gas pressures to 15 psig, with gas flows from 10 to 100 SCFH and an electrical power input from 0 to 200 watts per corona ceU. Ozone was produced from both air and oxygen. For runs when an ozone concentration of 13 mg/l gas or less (approximately 1% ozone in air) was desired, air was the ozonator feed gas. Air was compressed in a Puregas Compressor Model 4 HCJ-12-M 400 X and passed through 0.25-in. stainless steel tubing to the ozonator at 15 psig. Tank oxygen, (extra-dry grade) was supplied to the ozonator in the same manner as the air. Oxygen feed gas permitted the production of higher concentrations of ozone (i.e., approximately 2% ozone in oxygen) than with air for the same electrical power input to the generator. 406 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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