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Oxygenation with ozone

The calculated half-life of 1 mol % (1.5 wt %) of pure gaseous ozone diluted with oxygen at 25, 100, and 250°C (based on rate constants from Ref. 19) is 19.3 yr, 5.2 h, and 0.1 s, respectively. Although pure ozone—oxygen mixtures are stable at ordinary temperatures ia the absence of catalysts and light, ozone produced on an iadustrial scale by silent discharge is less stable due to the presence of impurities however, ozone produced from oxygen is more stable than that from air. At 20°C, 1 mol % ozone produced from air is - 30% decomposed ia 12 h. [Pg.491]

Ozone can be destroyed thermally, by electron impact, by reaction with oxygen atoms, and by reaction with electronically and vibrationaHy excited oxygen molecules (90). Rate constants for these reactions are given ia References 11 and 93. Processes involving ions such as 0/, 0/, 0 , 0 , and 0/ are of minor importance. The reaction O3 + 0( P) — 2 O2, is exothermic and can contribute significantly to heat evolution. Efftcientiy cooled ozone generators with typical short residence times (seconds) can operate near ambient temperature where thermal decomposition is small. [Pg.498]

Bismuth pentafluoride is an active fluorinating agent. It reacts explosively with water to form ozone, oxygen difluoride, and a voluminous chocolate-brown precipitate, possibly a hydrated bismuth(V) oxyfluoride. A similar brown precipitate is observed when the white soHd compound bismuth oxytrifluoride [66172-91 -6] BiOF, is hydrolyzed. Upon standing, the chocolate-brown precipitate slowly undergoes reduction to yield a white bismuth(Ill) compound. At room temperature BiF reacts vigorously with iodine or sulfur above 50°C it converts paraffin oil to fluorocarbons at 150°C it fluorinates uranium tetrafluoride to uranium pentafluoride and at 180°C it converts Br2 to bromine trifluoride, BrF, and bromine pentafluoride, BrF, and chlorine to chlorine fluoride, GIF. It apparently does not react with dry oxygen. [Pg.129]

Variation in Percentage (by Volume) or Ozone (from Oxygen) with Rate or Flow and Secondary Voltage... [Pg.70]

Pure ozone is made by fraetional distillation of the blue liquid resulting from the eooling of ozonized oxygen in liquid air. Commereially it is often supplied dissolved in ehlorofluoroearbons in stainless steel eyiinders at ea 475 psig eyiinder pressure at 20°C often transported ehilled with dry iee. These solutions ean be handled safely at vapour eoneentrations of ea 20% by volume of ozone. [Pg.303]

The acid (3 g) is refluxed with excess acetic anhydride for 45 min, and the excess anhydride evaporated in vacuo. The residue is dissolved in 100 ml. of chloroform and cooled in a bath of ice and hydrochloric acid. With stirring, a solution of 1.45 g of bromine (1 mole) in 50 ml of chloroform is added during 1 hr. Ozonized oxygen is passed through the cold solution until no more ozone is absorbed. The solvent is evaporated in vacuo below 30° and... [Pg.161]

We see that chiorine atoms provide an aitemative mechanism for the reaction of ozone with oxygen atoms. The iower-energy pathway breaks down ozone in the stratosphere at a significantiy faster rate than in the absence of the cataiyst. This disturbs the deiicate baiance among ozone, oxygen atoms, and oxygen molecules in a way that poses a serious threat to the iife-protecting ozone iayer. [Pg.1106]

With isoprene, 2,3-dimethylbuta-1,3-diene and cyclopentadiene, if the ozone concentration in the ozone/oxygen mixture exceeds a certain limit (not stated), the medium immediately combusts when incorporating this mixture at -78°C. [Pg.243]

Finally, acetylene detonates violently when it comes into contact with an ozone/oxygen mixture in which the quantity of ozone exceeds 50 mg/l. [Pg.243]

A PP sample after ozonization in the presence of UV-irradiation becomes brittle after 8 hrs of exposure, whereas the same effect in ozone is noticeable after 50-60 hours.Degradation of polymer chain occurs as a result of decomposition of peroxy radicals. The oxidation rapidly reaches saturation, suggesting the surface nature of ozone and atomic oxygen against of PP as a consequence of limited diffusion of both oxygen species into the polymer. Ozone reacts with PP mainly on the surface since the reaction rate and the concentration of intermediate peroxy radicals are proportional to the surface area and not the weight of the polymer. It has been found that polyethylene is attacked only to a depth of 5-7 microns (45). [Pg.197]

In order to calculate the steady-state concentration of ozone in the stratosphere, we need to balance the rate of production of odd oxygen with its rate of destruction. Chapman originally thought that the destruction was due to the reaction O + 03 —> 2O2, but we now know that this pathway is a minor sink compared to the catalytic destruction of 03 by the trace species OH, NO, and Cl. The former two of these are natural constituents of the atmosphere, formed primarily in the photodissociation of water or nitric oxide, respectively. The Cl atoms are produced as the result of manmade chlorofluorocarbons, which are photodissociated by sunlight in the stratosphere to produce free chlorine atoms. It was Rowland and Molina who proposed in 1974 that the reactions Cl + 03 —> CIO + O2 followed by CIO + O —> Cl + O2 could act to reduce the concentration of stratospheric ozone.10 The net result of ah of these catalytic reactions is 2O3 — 3O2. [Pg.283]

Treatment of isoprene, 2,3-dimethylbutadiene or cyclopentadiene in pentane at —78°C with a high ratio ozone/oxygen stream led to immediate ignition and flames in both liquid and gas phases. [Pg.1869]

For laboratory use, ozone is normally produced at the time and location of use by means of an ozonizer. This device bombards oxygen with low frequency electrical oscillation (so-called silent... [Pg.436]

Both processes are switched on by the absorption of short-wavelength radiation X < 240 nm for H20 and X < 230 nm for C02. On the assumption that H atoms escape from the atmosphere, there is a net gain in oxygen to the atmosphere. Reactions of O atoms and 02 chemistry would then lead to the formation of a small ozone layer with a low ozone concentration. [Pg.216]

Schubert, C.C., Pease, R.N. (1956) The oxidation of lower paraffin hydrocarbons. I. Room temperature reaction of methane, propane, n-butane and isobutane with ozonized oxygen. J. Am. Chem. Soc. 78, 2044—2048. [Pg.403]

Hibernia A process for making formaldehyde by the partial oxidation of methane by ozonized oxygen. The catalyst is barium peroxide activated with silver oxide. Developed in Germany during World War II but not commercialized. [Pg.127]

Even if few systems are proposed for inorganic compounds (with regard to the number of potential pollutants), instruments or sensors for parameters used for treatment process control are available UV systems for residual chlorine in deodorization, electrochemical sensors for dissolved oxygen (with nowadays a luminescent dissolved-oxygen probe utilizing a sensor coated with a luminescent material) and a colorimetric technique for residual ozone. [Pg.259]

The price of the oxidation equivalent varies with the reagent [288]. Oxygen in air is the cheapest, followed by chlorine, electricity, hydrogen peroxide and finally ozone. Oxydation with oxygen at low temperature is only feasible biologically. Chlorine often forms very stable, highly toxic chlorinated compounds, which often limits its use. [Pg.212]

The student is strongly recommended to determine iodometrically the amount of ozone delivered in a fixed time and to regulate the strength of the current of oxygen with a gas meter. The determination should be made before the experiment is begun about ten minutes after the current in the ozoniser has been switched on. [Pg.385]

Chemical radicals—such as hydroxyl, peroxyhydroxyl, and various alkyl and aryl species—have either been observed in laboratory studies or have been postulated as photochemical reaction intermediates. Atmospheric photochemical reactions also result in the formation of finely divided suspended particles (secondary aerosols), which create atmospheric haze. Their chemical content is enriched with sulfates (from sulfur dioxide), nitrates (from nitrogen dioxide, nitric oxide, and peroxyacylnitrates), ammonium (from ammonia), chloride (from sea salt), water, and oxygenated, sulfiirated, and nitrated organic compounds (from chemical combination of ozone and oxygen with hydrocarbon, sulfur oxide, and nitrogen oxide fragments). ... [Pg.239]


See other pages where Oxygenation with ozone is mentioned: [Pg.115]    [Pg.115]    [Pg.498]    [Pg.104]    [Pg.71]    [Pg.485]    [Pg.492]    [Pg.103]    [Pg.37]    [Pg.468]    [Pg.827]    [Pg.54]    [Pg.224]    [Pg.243]    [Pg.439]    [Pg.198]    [Pg.84]    [Pg.386]    [Pg.242]    [Pg.273]    [Pg.61]    [Pg.76]    [Pg.78]    [Pg.108]    [Pg.468]    [Pg.77]   
See also in sourсe #XX -- [ Pg.667 ]




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