Ozone

Base Information

• Chemical Name: Ozone
• CAS No.: 10028-15-6
• Deprecated CAS: 74087-86-8,412908-40-8,728855-47-8,855426-80-1,412908-40-8,855426-80-1
• Molecular Formula: O3
• Molecular Weight: 47.9982
• European Community (EC) Number: 233-069-2,629-936-3
• ICSC Number: 0068
• UN Number: 1955,1956
• UNII: 66H7ZZK23N
• DSSTox Substance ID: DTXSID0021098
• Nikkaji Number: J2.505.688D
• Wikipedia: Ozone
• Wikidata: Q36933
• Pharos Ligand ID: 6297
• ChEMBL ID: CHEMBL2447938
• Mol file: 10028-15-6.mol

Synonyms:Ground Level Ozone;Level Ozone, Ground;Level Ozone, Low;Low Level Ozone;Ozone;Ozone, Ground Level;Ozone, Low Level;Ozone, Tropospheric;Tropospheric Ozone

Chemical Property of Ozone

Chemical Property:

• Appearance/Colour: colourless gas or dark blue liquid.
• Vapor Pressure: 55kPa at -12℃
• Melting Point: -192.7℃
• Refractive Index: 1.278
• Boiling Point: -111.9℃
• Flash Point: °C
• Density: 1.48g/cm³
• Water Solubility.: 570mg/L at 20℃
• XLogP3: -1.7
• Hydrogen Bond Donor Count: 0
• Hydrogen Bond Acceptor Count: 2
• Rotatable Bond Count: 0
• Exact Mass: 47.984743858
• Heavy Atom Count: 3
• Complexity: 4.8
• Transport DOT Label: Poison Gas

Purity/Quality:

99.9% ^*data from raw suppliers

OZONE 95.00% ^*data from reagent suppliers

Safty Information:

• Pictogram(s): Dangerous fire and explosion risk in contact with organic materials. Toxic by inhalation, strong irritant. TLV: ceiling of 0.1 ppm; STEL 0.3 ppm. EPA standard for ambient air is 0.12 ppm.
• Hazard Codes: Dangerous fire and explosion risk in contact with organic materials. Toxic by inhalation, strong irritant. TLV: ceiling of 0.1 ppm; STEL 0.3 ppm. EPA standard for ambient air is 0.12 ppm.

MSDS Files:

SDS file from LookChem

Total 1 MSDS from other Authors

Useful:

• Chemical Classes: Toxic Gases & Vapors -> Oxidizers
• Canonical SMILES: [O-][O+]=O
• Recent ClinicalTrials: Macrophage Regulation of Ozone-Induced Lung Inflammation
• Recent EU Clinical Trials: Effect of rectal ozone therapy on the clinical progress of hospitalized patients with mild-moderate covid19 infection: A triple- blind, randomized controlled trial.
• Recent NIPH Clinical Trials: The effect of functiona water rinsing for aged persons
• Inhalation Risk: A harmful concentration of this gas in the air will be reached very quickly on loss of containment.
• Effects of Short Term Exposure: The substance is irritating to the eyes and respiratory tract. The substance may cause effects on the central nervous system. This may result in impaired vigilance and performance. Inhalation of the gas may cause lung oedema. The effects may be delayed. The liquid may cause frostbite.
• Effects of Long Term Exposure: Repeated or prolonged inhalation of the gas may cause effects on the lungs.
• Description: Ozone in the upper layers of the atmosphere (stratosphere) is formed by the reaction of O2 with the elemental oxygen formed from the splitting of O2 by UV radiation. The ozone layer in the stratosphere, though containing a relatively low amount of O3 relative to O2, absorbs UV radiation and serves to protect Earth fromthe destructive andmutagenic properties of solarUV.Ozone is more unstable than O2 and thus more reactive. Ground-level ozone (troposphere) is formed largely fromthe reactionof the byproducts of the incomplete combustion of fossil fuels with elemental oxygen present. Common industrial pollutants and car exhaust by-products such asnitrogen oxides, sulfur oxides, carbon oxides, and hydrocarbons are photochemically cleaved and then react with the O2 present. Natural sources of tropospheric ozone come from ozone migration from the stratosphere with average concentration of about 10–20 ppb in nonurban areas. Tropospheric ozone can be very harmful to human health, and people with conditions such as emphysema, asthma, bronchitis, and heart conditions are especially susceptible. Health effects from ozone are due to its high reactivity resulting in reactions with biological macromolecules and subsequent cellular damage. In addition, ozone conversion to diatomic oxygen results in the production of free oxygen radicals, which can also cause damage. Due to the harmful health effects of ozone, theUS Environmental Protection Agency (EPA) among other government entities has established exposure limits. The National Ambient Air Quality Standards limit for ozone is 0.075 ppm, taken as the annual fourth-highest dailymaximum8 h concentration, averaged over 3 years. Ozone exceeds its limit more often than all other regulated air chemicals, and is in excess most frequently in California.
• Physical properties: Ozone is an allotropic molecular form of oxygen containing three atoms of oxygen (O3).It is a much more powerful oxidizing agent than diatomic oxygen (O2) or monatomic oxygen(O). It is the second most powerful oxidizer of all the elements. Only fluorine is a strongeroxidizer. It is not colorless as is oxygen gas. Rather, ozone is bluish in the gaseous state, butblackish-blue in the liquid and solid states (similar to the color of ink).Ozone’s boiling point is –112°C, and its freezing point is –192°C.
• Uses: Ozone is much more reactive than O2, which makes it a very powerful oxidizing agent.Only fluorine is more reactive. It has many commercial uses. It is a strong oxidizer, particularlyof organic compounds, it is a strong bleaching agent for textiles, oils, and waxes, and it is apowerful germicide. It is also used in the manufacture of paper, steroid hormones, waxes, andcyanide and in the processing of acids.Ozone produced by electrical discharge is used to purify drinking water and to treatindustrial wastes and sewage. It is also use to deodorize air and kill bacteria by passing dry airthrough special ozone-producing electronic devices. Ozone is used as an oxidizing compound, as a disinfectant for air and water, for bleaching waxes and oil, and in organic synthesis. It occurs in the atmosphere at sea level to about 0.05 ppm. It is produced by the action of ultraviolet (UV) radiation on oxygen in air. As disinfectant for air and water by virtue of its oxidizing power. For bleaching waxes, textiles, oils. In organic syntheses. Forms ozonides which are sometimes useful oxidizing Compounds.

Technology Process of Ozone

There total 331 articles about Ozone which guide to synthetic route it. The literature collected by LookChem mainly comes from the sharing of users and the free literature resources found by Internet computing technology. We keep the original model of the professional version of literature to make it easier and faster for users to retrieve and use. At the same time, we analyze and calculate the most feasible synthesis route with the highest yield for your reference as below:

synthetic route:

Reference yield:

caro's acid (7722-86-3) → ozone (10028-15-6)

Guidance literature:

In not given; reaction by let standing of 92% concd. H2SO5 soln. shortly above 0 °C;; not isolated, detection by odor;;

Reference yield:

water (7732-18-5) + dichromic acid (13530-68-2) → ozone (10028-15-6)

Guidance literature:

In water; Electrolysis; reaction by use of different types and dimensions of anodes in aq. H2Cr2O7 solns. with concentrations up to 3.0 M/l;; highest O3 concentrations by use of a Pt needle, traces only by use of a Pt plate;;

Reference yield:

oxygen (80937-33-3) + hypobromite → ozone (10028-15-6) + ozonide

Guidance literature:

In water; Irradiation (UV/VIS); pH>12;

DOI:10.1039/f19848002969

upstream raw materials:

carbon disulfide

ethene

n-Butyl nitrite

methyl hydroperoxide

Downstream raw materials:

L-erythrose

phenylglyoxal hydrate

6-formyl-7-hydroxy-5-methoxycoumarin

2-bromo-4,6-dihydroxy-5-methoxy-isophthalaldehyde

Refernces

• 1、 Shinoda, Takako,Shima, Nobuyuki,Tsukada, Masaru. "". . p. 311 - 335. Retrieved 1988.
• 2、 Horowitz,Von Helden,Simon,Crutzen,Moortgat. "OZONE GENERATION IN THE 214-nm PHOTOLYSIS OF OXYGEN AT 25 degree C.". . p. 4956 - 4960. Retrieved 1988.
• 3、 Dunlea, Edward J.,Talukdar, Ranajit K.,Ravishankara. "Kinetics and products of the reaction O2(1σ g+) with N2O". . p. 989 - 1007. Retrieved 2010.
• 4、 Vigasin,Schriver-Mazzuoli,Schriver. "Systematic trends in the vibrational frequency shifts of some molecules trapped in amorphous water ice". . p. 101 - 113. Retrieved 2003.
• 5、 Ehrlich, V.,Russ, F.. "-". . . Retrieved 1911.
• 6、 Griffith, R. H.,Hill, S. G.. "". . . Retrieved 1938.
• 7、 Green, Martina,Lee, Edward K. C.. "Conversion of SO2 to SO3 Facilitated by in Situ UV Photolysis of H2CO and SO2 in an O2 Matrix at 12 K". . p. 6470 - 6475. Retrieved 1986.
• 8、 Poirier, Gregory E.,Herne, Tonya M.,Miller, C. Cameron,Tarlov, Michael J.. "Molecular-scale characterization of the reaction of ozone with decanethiol monolayers on Au(111)". . p. 9703 - 9711. Retrieved 1999.
• 9、 Larichev, Michael,Maguin, Francoise,Bras, Georges Le,Poulet, Gilles. "Kinetics and Mechanism of the BrO+HO2 Reaction". . p. 15911 - 15918. Retrieved 1995.
• 10、 Crowley, John N.,Sodeau, John R.. "Reaction between the Amidogen Radical, .NH2, and Molecular Oxygen in Low-Temperature Matrices". . p. 4785 - 4790. Retrieved 1989.