| Ozone |

 |
| General |
| Systematic name |
Trioxygen |
| Molecular formula |
O3 |
| Molar mass |
47.998 g·mol−1 |
| Appearance |
bluish colored gas |
| CAS number |
[10028-15-6] |
| Properties |
| Density and phase |
2.144 g·L−1 (0 °C), gas |
| Solubility in water |
0.105 g·100mL−1 (0 °C) |
| Melting point |
80.7 K, −192.5 °C |
| Boiling point |
161.3 K, −111.9 °C |
| Thermodynamic data |
Standard enthalpy of
formation ΔfH°solid |
+142.3 kJ·mol−1 |
Standard molar entropy
S°solid |
237.7 J·K−1.mol−1 |
| Hazards |
| EU classification |
not listed |
| NFPA 704 |
|
| Supplementary data page |
Structure and
properties |
n, εr, etc. |
Thermodynamic
data |
Phase behaviour
Solid, liquid, gas |
| Spectral data |
UV, IR,
NMR, MS |
| Regulatory data |
Flash point,
RTECS number, etc. |
Except where noted otherwise, data are given for
materials in their standard state (at 25 °C, 100 kPa)
Infobox disclaimer and references |
Ozone (O3) is a triatomic molecule, consisting of three oxygen atoms. It is
an allotrope of oxygen that is much less stable than the
diatomic O2. Ground-level ozone is an air pollutant with harmful effects on
the respiratory systems of animals. Ozone in the upper atmosphere filters potentially damaging ultraviolet light from reaching
the Earth's surface. It is present in low concentrations throughout the Earth's
atmosphere. It has many industrial and consumer applications. Ozone therapy is a
controversial alternative medicine practice; mainstream scientific medicine has
found ozone to be harmful to humans,[1] and equipment
intended to be used for ozone therapy is banned in the United States.[2]
Ozone, the first allotrope of a chemical element to be described by science, was discovered
by Christian Friedrich Schönbein in 1840,
who named it after the Greek word for smell (ozein), from the peculiar odor in
lightning storms.[3] The odor from a lightning strike is
from ions produced during the rapid chemical changes, not from the ozone itself.[4]
Physical properties
Undiluted ozone is a pale blue gas at standard temperature and pressure; it forms a dark blue
liquid below −112 °C and a violet-black solid below
−193 °C.[5] At concentrations found in the atmosphere
it is colorless.[6] The concentration above which it can be
smelled (odor threshold) is between 0.0076 and 0.036 ppm.[7]
Structure
The structure of ozone, according to experimental evidence from microwave
spectroscopy, is bent, with C2v symmetry (similar to the
water molecule), O – O distance of 127.2 pm and O – O – O angle of
116.78°.[8] The central atom forms an sp²
hybridization with one lone pair. Ozone is a polar molecule with a dipole moment of 0.5337
D.[9] The bonding is
single bond on one side and double bond on the
other side, and these bonds are blended to become known as resonance structures.
The bond order is 1.5 for each side.
Chemistry
Ozone is a powerful oxidizing agent. It is also unstable at high concentrations, decaying to
ordinary diatomic oxygen (in about half an hour in atmospheric conditions[10]):
- 2 O3 → 3 O2.
This reaction proceeds more rapidly with increasing temperature and decreasing pressure. Ozone will oxidize metals (except
gold, platinum, and iridium) to
oxides of the metals in their highest oxidation
state:
- 2 Cu2+(aq) + 2 H3O+(aq) + O3(g) → 2
Cu3+(aq) + 3 H2O(l) + O2(g)
Ozone also increases the oxidation number of oxides:
- NO + O3 → NO2 +
O2
The above reaction is accompanied by chemiluminescence. The NO2 can be
further oxidized:
- NO2 + O3 → NO3 + O2
The NO3 formed can react with NO2 to form N2O5:
- NO2 + NO3 → N2O5
Ozone reacts with carbon to form carbon dioxide, even
at room temperature:
- C + 2 O3 → CO2 + 2 O2
Ozone does not react with ammonium salts but it reacts with ammonia to form ammonium nitrate:
- 2 NH3 + 4 O3 → NH4NO3 + 4 O2 +
H2O
Ozone reacts with sulfides to make sulfates:
- PbS + 4 O3 → PbSO4
+ 4 O2
Sulfuric acid can be produced from ozone, either starting from elemental
sulfur or from sulfur dioxide:
- S + H2O + O3 → H2SO4
- 3 SO2 + 3 H2O + O3 → 3 H2SO4
All three atoms of ozone may also react, as in the reaction with tin(II) chloride and hydrochloric acid:
- 3 SnCl2 + 6 HCl + O3 → 3 SnCl4 + 3 H2O
In the gas phase, ozone reacts with hydrogen
sulfide to form sulfur dioxide:
- H2S + O3 → SO2 + H2O
In an aqueous solution, however, two competing simultaneous reactions occur, one to
produce elemental sulfur, and one to produce sulfuric acid:
- H2S + O3 → S + O2 + H2O
- 3 H2S + 4 O3 → 3 H2SO4
Iodine perchlorate can be made by treating iodine
dissolved in cold anhydrous perchloric acid with
ozone:
- I2 + 6 HClO4 + O3 → 2 I(ClO4)3 + 3 H2O
Solid nitryl perchlorate can be made from NO2, ClO2, and O3
gases:
- 2 NO2 + 2 ClO2 + 2 O3 → 2 NO2ClO4 + O2
Ozone can be used for combustion reactions and combusting gases in ozone provides higher
temperatures than combusting in dioxygen (O2). Following is a reaction for the
combustion of carbon subnitride:
- 3 C4N2 + 4 O3 → 12 CO + 3 N2
Ozone can react at cryogenic temperatures. At 77 K (-196 °C), atomic hydrogen reacts with
liquid ozone to form a hydrogen superoxide radical, which dimerizes:[11]
- H + O3 → HO2 + O
- 2 HO2 → H2O4
Ozonides can be formed, which contain the ozonide anion, O3-. These
compounds are explosive and must be stored at cryogenic temperatures. Ozonides for all the alkali
metals are known. KO3, RbO3, and CsO3 can be prepared from their respective
superoxides:
- KO2 + O3 → KO3 + O2
Although KO3 can be formed as above, it can also be formed from potassium
hydroxide and ozone:[12]
- 2 KOH + 5 O3 → 2 KO3 + 5 O2 + H2O
NaO3 and LiO3 must be prepared by action of CsO3 in liquid NH3 on an
ion exchange resin containing Na+ or Li+ ions:[13]
- CsO3 + Na+ → Cs+ + NaO3
Treatment with ozone of calcium dissolved in ammonia leads to ammonium ozonide and not
calcium ozonide:[14]
- 3 Ca + 10 NH3 + 6 O3 → Ca•6NH3 + Ca(OH)2 + Ca(NO3)2 + 2
NH4O3 + 2 O2 + H2
Ozone can be used to remove manganese from the water, forming a precipitate which
can be filtered:
- 2 Mn2+ + 2 O3 + 4 H2O → 2 MnO(OH)2 (s) + 2 O2 + 4 H+
Ozone will also turn cyanides to the one thousand times less toxic cyanates:
- CN- + O3 → CNO- + O2
Finally, ozone will also completely decompose urea:[15]
- (NH2)2CO + O3 → N2 + CO2 + 2 H2O
Ozone in Earth's atmosphere
The distribution of atmospheric ozone in partial pressure as a function of altitude.
Concentration of ozone as measured by the
Nimbus-7 satellite.
Total ozone concentration in June 2000 as measured by EP-TOMS satellite instrument.
The standard way to express total ozone levels (the volume of ozone in a vertical column) in the atmosphere is by using
Dobson units. Concentrations at a point are measured in parts per billion (ppb) or in μg/m³.
Ozone layer
-
The highest levels of ozone in the atmosphere are in the stratosphere, in a region also
known as the ozone layer between about 10 km and 50 km above the surface (or between 6.21
and 31.1 miles). Here it filters out the shorter wavelengths (less than 320 nm) of ultraviolet light (270 to 400 nm) from the Sun that would be harmful to most
forms of life in large doses. These same wavelengths are also among those
responsible for the production of vitamin D, which is essential for human health. Ozone in the stratosphere is mostly produced from ultraviolet rays reacting with oxygen:
- O2 + (radiation < 240 nm) → 2 O
- O + O2 → O3
It is destroyed by the reaction with atomic oxygen:
- O3 + O → 2 O2
(See Ozone-oxygen cycle for more detail.)
The latter reaction is catalysed by the presence of certain free radicals, of which the
most important are hydroxyl (OH), nitric oxide (NO) and atomic chlorine (Cl) and bromine (Br). In recent decades the amount of
ozone in the stratosphere has been declining mostly due to emissions of CFCs and similar
chlorinated and brominated organic molecules, which have increased the concentration of ozone-depleting catalysts above the
natural background. See ozone depletion for more information.
Low level ozone
-
Low level ozone (or tropospheric ozone) is regarded as a pollutant by the World
Health Organization.[16] It is
not emitted directly by car engines or by industrial operations. It is formed
by the reaction of sunlight on air containing hydrocarbons and
nitrogen oxides that react to form ozone directly at the source of the pollution or many
kilometers down wind. For more details of the complex chemical reactions that produce low level ozone see tropospheric ozone.
Ozone reacts directly with some hydrocarbons such as aldehydes and thus begins their removal
from the air, but the products are themselves key components of smog. Ozone photolysis by UV light leads to production of the hydroxyl
radical and this plays a part in the removal of hydrocarbons from the air, but is also the first step in the creation of
components of smog such as peroxyacyl nitrates which can be powerful eye irritants.
The atmospheric lifetime of tropospheric ozone is about 22 days and its main removal mechanisms are being deposited to the
ground, the above mentioned reaction giving OH, and by reactions with OH and the peroxy radical
HO2· (Stevenson et al, 2006).[17]
As well as having an impact on human health (see below) there is also evidence of significant reduction in agricultural yields
due to increased ground-level ozone and pollution which interferes with photosynthesis
and stunts overall growth of some plant species.[18][19]
Ozone as a greenhouse gas
Although ozone was present at ground level before the industrial revolution,
peak concentrations are far higher than the pre-industrial levels and even background concentrations well away from sources of
pollution are substantially higher.[20][21] This increase in ozone is of further concern as ozone
present in the upper troposphere acts as a greenhouse
gas, absorbing some of the infrared energy emitted by the earth. Quantifying the
greenhouse gas potency of ozone is difficult as it is not present in uniform concentrations across the globe. However, the most
recent scientific review on the climate change (the IPCC Third Assessment
Report[22]) suggests that the radiative forcing of tropospheric ozone is about 25% that of carbon
dioxide.
Ozone and health
Ozone in air pollution
There is a great deal of evidence to show that high concentrations (ppm) of ozone, created by high concentrations of pollution
and daylight UV rays at the earth's surface, can harm lung function and irritate the respiratory system.[16][23] A connection
has also been shown to exist between increased ozone caused by thunderstorms and hospital admissions of asthma sufferers.[24] Air quality
guidelines such as those from the World Health Organization are based on
detailed studies of what levels can cause measurable health effects.
A common British folk myth dating back to the Victorian era holds that the smell of the sea is caused by ozone, and that this
smell has "bracing" health benefits.[25] Neither of these
is true. The characteristic "smell of the sea" is not caused by ozone, but by the presence of dimethyl sulfide generated by phytoplankton, and dimethyl
sulfide, like ozone, is toxic in high concentrations.[26]
The United States Environmental Protection Agency has
developed an Air Quality index to help explain air pollution levels to the general public. 8-hour average ozone concentrations of
85 to 104 ppbv are described as "Unhealthy for Sensitive Groups", 105 ppbv to 124
ppbv as "unhealthy" and 125 ppb to 404 ppb as "very unhealthy".[27] The EPA has designated over 300 counties of the United States, clustered around the most heavily
populated areas (especially in California and the Northeast), as failing to comply with the National Ambient Air Quality Standards.
Physiology of ozone
Ozone, along with reactive forms of oxygen such as superoxide, singlet oxygen (see oxygen), hydrogen
peroxide, and hypochlorite ions, is naturally produced by white blood cells and other biological systems (such as the roots of marigolds) as a means of destroying foreign bodies. Ozone reacts directly with organic double bonds. Also, when
ozone breaks down to dioxygen it gives rise to oxygen free radicals, which are
highly reactive and capable of damaging many organic molecules. Ozone has been found to
convert cholesterol in the blood stream to plaque (which
causes hardening and narrowing of arteries). Moreover, it is believed that the powerful oxidizing properties of ozone may be a
contributing factor of inflammation. The cause-and-effect relationship of how the ozone is
created in the body and what it does is still under consideration and still subject to various interpretations, since other body
chemical processes can trigger some of the same reactions. A team headed by Dr. Paul Wentworth
Jr. of the Department of Chemistry at the Scripps Research
Institute has shown evidence linking the antibody-catalyzed water-oxidation pathway of the human immune response to the production of ozone. In this system, ozone is produced by antibody-catalyzed
production of trioxidane from water and neutrophil-produced singlet oxygen.[28] See also
trioxidane for more on this biological ozone-producing reaction.
Ozone has also been proven to form specific, cholesterol-derived metabolites that are
thought to facilitate the build-up and pathogenesis of atherosclerotic plaques (a form
of heart disease). These metabolites have been confirmed as naturally occurring in human
atherosclerotic arteries and are categorized into a class of secosterols termed “Atheronals”, generated by ozonolysis of cholesterol's double bond to form a 5,6 secosterol as well as a
secondary condensation product via aldolization.[29]
Production techniques
Ozone used in industry is measured in g/Nm³ or weight percent. The regime of applied concentrations ranges from 1 to 5 weight
percent in air and from 6 to 13 weight percent in oxygen.
Ozone generators currently on the market generate ozone molecules by employing one of the methods below.
Corona discharge method
This is the most popular type of ozone generator for most industrial and personal uses. While variations of the "hot spark"
coronal discharge method of ozone production exist, including medical grade and industrial grade ozone generators, these units
usually work by means of a corona discharge tube.[30] They are typically very cost-effective, and do not require an oxygen source
other than the ambient air. However, they also produce nitrogen oxides as a by-product.
Use of an air dryer can reduce or eliminate nitric acid formation by removing water vapor and
increase ozone production. Use of an oxygen concentrator can further increase the
ozone production and further reduce the risk of nitric acid formation due to removing not only the water vapor, but also the bulk
of the nitrogen.
Ultraviolet light
UV ozone generators employ a light source that generates the same narrow-band ultraviolet
light that is responsible for the sustenance of the ozone layer in the stratosphere of the Earth [31].
While standard UV ozone generators tend to be less expensive, they usually produce ozone with a concentration of about 2% or
lower. Another disadvantage of this method is that it requires the air to be exposed to the UV source for a longer amount of
time, and any air that is not exposed to the UV source will not be treated. This makes UV generators impractical for use in
situations that deal with rapidly moving air or water streams (in-duct air sterilization, for example).
Cold plasma
In the cold plasma method, pure oxygen gas is exposed to a plasma created by dielectric barrier discharge.
The diatomic oxygen is split into single atoms, which then recombine in triplets to form ozone.
Cold plasma machines utilize pure oxygen as the input source, and produce a maximum
concentration of about 5% ozone. They produce far greater quantities of ozone in a given space of time compared to ultraviolet
production. However, because cold plasma ozone generators are very expensive, and still require occasional maintenance, they are
found less frequently than the previous two types.
The discharges manifest as filamentary transfer of electrons (micro discharges) in a gap between two electrodes. In order to
evenly distribute the micro discharges, a dielectric insulator must be used to
separate the metallic electrodes and to prevent arcing.
Some cold plasma units also have the capability of producing short-lived allotropes of oxygen which include O4,
O5, O6, O7, etc. These anions are even more reactive than ordinary O3.
Special considerations
Ozone cannot be stored and transported like other industrial gases (because it quickly decays into diatomic oxygen) and must
therefore be produced on site. Available ozone generators vary in the arrangement and design of the high-voltage electrodes. At
production capacities higher than 20kg per hour, a gas/water tube heat-exchanger is utilized as ground electrode and assembled
with tubular high-voltage electrodes on the gas-side. The regime of typical gas pressures is around 2 bar absolute in oxygen and 3 bar absolute in air. Several megawatts of electrical power may be installed
in large facilities, applied as one phase AC current at 600 to 2000 Hz and peak
voltages between 3000 and 20000 volts.
The dominating parameter influencing ozone generation efficiency is the gas temperature, which is controlled by the cooling
water temperature. The cooler the water, the better the ozone synthesis. At typical industrial conditions, almost 90 percent of
the effective power is dissipated as heat and needs to be removed by a sufficient cooling water flow.
Due to the high reactivity of ozone, only few materials may be used like stainless steel (quality 316L), glass,
polytetrafluorethylene, or polyvinylidene fluoride. Viton may be used with the restriction
of constant mechanical forces and absence of humidity.
Incidental production
Ozone may be formed from O2 by electrical discharges and by action of high energy electromagnetic radiation. Certain electrical
equipment generate significant levels of ozone. This is especially true of devices using high voltages, such as ionic air purifiers, laser printers, photocopiers, and arc
welders. Electric motors using brushes
can generate ozone from repeated sparking inside the unit. Large motors that use brushes, such
as those used by elevators or hydraulic pumps, will generate more ozone than smaller motors.
Laboratory production
In the laboratory ozone can be produced by electrolysis using a 9 volt battery, a pencil graphite rod cathode, a platinum wire anode and a 3M sulfuric
acid electrolyte.[32] The half cell reactions taking place are
- 3 H2O → O3 + 6 H+ + 6 e−; ΔEo = −1.53 V;
- 6 H+ + 6 e− → 3 H2; ΔEo = 0 V;
- 2 H2O → O2 + 4 H+ + 4 e−; ΔEo = −1.23 V;
so that in the net reaction three equivalents of water are converted into one equivalent of ozone and three equivalents of
hydrogen. Oxygen formation is a competing reaction.
Applications
Industrial applications
Ozone can be used for bleaching substances and for killing microorganisms in air and water
sources. Many municipal drinking water systems kill bacteria with ozone instead of the more common chlorine.[33] Ozone has a very high
oxidation
potential. Ozone does not form organochlorine compounds, nor does it remain in the
water after treatment, so some systems introduce a small amount of chlorine to prevent bacterial growth in the pipes, or may use chlorine intermittently, based on results of periodic
testing. Where electrical power is abundant, ozone is a cost-effective method of treating
water, as it is produced on demand and does not require transportation and storage of hazardous chemicals. Once it has decayed,
it leaves no taste or odor in drinking water. Low levels of ozone have been advertised to be of some disinfectant use in
residential homes, however, the concentration of ozone required to have a substantial effect on airborne pathogens greatly
exceeds safe levels recommended by the U.S. Occupational Safety
and Health Administration and Environmental Protection
Agency.[citation needed]
Industrially, ozone or ozonated water is used to:
- Disinfect laundry in hospitals, food factories, care homes etc;[34]
- Disinfect water before it is bottled;
- Deodorize air and objects, such as after a fire. This process is extensively used in Fabric Restoration;
- Kill bacteria on food or on contact surfaces;
- Ozone swimming pool and spa sanitation
- Scrub yeast and mold spores from the air in food processing plants;
- Wash fresh fruits and vegetables to kill yeast, mold and bacteria;
- Chemically attack contaminants in water (iron, arsenic, hydrogen sulfide, nitrites,
and complex organics lumped together as "colour");
- Provide an aid to flocculation (agglomeration of molecules, which aids in filtration,
where the iron and arsenic are removed);
- Manufacture chemical compounds via chemical synthesis [1]
- Clean and bleach fabrics (the former use is utilized in Fabric Restoration)(the
latter use is patented);
- Assist in processing plastics to allow adhesion of inks;
- Age rubber samples to determine the useful life of a batch of rubber;
- Hospital operating rooms where air needs to be sterile;
- Eradicate water borne parasites such as Giardia and Cryptosporidium in surface water treatment plants. This
process is known as ozonation.
Ozone is a reagent in many organic reactions in the laboratory and in industry.
Ozonolysis is the cleavage of an alkene to carbonyl compounds.
Many hospitals in the U.S. and around the world use large ozone generators to decontaminate operating rooms between surgeries.
The rooms are cleaned and then sealed airtight before being filled with ozone which effectively kills or neutralizes all
remaining bacteria. [citation needed]
Ozone is used as an alternative to chlorine or chlorine
dioxide in the bleaching of wood pulp [35] . It is often used in conjunction with oxygen
and hydrogen peroxide to completely eliminate the need for chlorine-containing
compounds in the manufacture of high-quality, white paper[36]
Ozone can be used to detoxify cyanide wastes (for example from gold and silver mining) by oxidizing cyanide to
cyanate and eventually to carbon dioxide.[37]
Consumer applications
Ozone machines, with or without ionisation, are currently used to sanitise (high ozone output) and deodorize non-inhabited
rooms, ductwork, vehicles, boats, woodsheds, and buildings.
Some models of air purifiers that also emit low levels of ozone have been sold in the
US. These type of air purifiers claim to imitate nature's "filterless" air purifying mechanisms[38] and claim to "sanitise" the air and/or household surfaces. The government
successfully sued one company in 1995, ordering them to stop repeating health claims without supporting scientific studies.
Ozonated water is used to launder clothes, sanitise food, drinking water, and surfaces in the home. According to the
FDA, it is "amending the food
additive regulations to provide for the safe use of ozone in gaseous and aqueous phases as an antimicrobial agent on food, including meat and poultry." Studies at California Polytechnic University,
have proven that low levels of ozone dissolved in filtered tapwater can produce more than a four-log (99.99%) reduction in such
food-borne microorganisms as salmonella, e. Coli 0157:H7, campylobacter and others.[39] Ironically, while ozone is considered an atmospheric pollutant, pollution and
smog by the US government, it can actually decrease the levels of pollutants like pesticides
in fruits and vegetables.[40]
New patented technology utilizes ozone to disinfect and deodorize protective sports gear, as is used in football, hockey and
lacrosse, by blowing it into the gear. Thereby, destroying bacteria that may be lurking deep in the padding of the sports gear.
This has proven particularly useful in battling the spread of MRSA.[41]
Ozone is used in spas or hot tubs with reduced levels of chlorine or bromine for keeping the
water free of bacteria. As it does not remain in the water after treatment, it is ineffective at preventing bather
cross-contamination, and must be used in conjunction with another sanitizer. Ozone gas is created by an ultraviolet light bulb or
corona discharge chip and injected into the plumbing system[citation needed].
Ozone is also widely used in treatment of water in aquaria and fish ponds. Its use can minimize bacterial growth control
parasites and removes or reduces "yellowing" of the water. As the ozone rapidly decomposes, at correctly controlled levels the
application has no effect on the fish[citation needed].
Most countries restrict the amount of ozone that can be generated by popular "ionizing" devices because ozone contributes to
the development of smog. Smaller ozone machines may be employed by personal users for home use, and
typically produce far less ozone than their larger counterparts. Due to their lower costs, almost all ozone generators designed
for personal use employ the corona discharge method. In many countries, the production or operation of ozone generating devices
is illegal.[citation needed]
Ozone therapy
-
Ozone therapy has been used in alternative
medicine as a medical treatment in a number of different countries.[42] Its use, however, is controversial.[43]
The United States Food and Drug Administration (FDA) has banned ozone
generators or ozone gas from being marketed for treatment of any medical conditions, based on the toxicity of ozone and the lack
of scientific evidence for any beneficial effects at non-toxic levels.[2]
One couple, Kenneth R. Thiefault and Mardel Barber, were convicted of and sent to prison in 1999 for violating this ban, which
involved marketing ozone generators to cure AIDS, cancer, herpes, hepatitis, gangrene, or "almost any disease", without
presenting any evidence to the FDA of effectiveness or safety.[44]
However, it is worth noting that the FDA cannot allow any device to claim to treat any medical condition unless the device
and/or treatment have gone through rigorous trials. It is not illegal to sell medical-grade ozone machines in the US, nor is it
illegal to own one or use one. What is illegal is to sell them while claiming it treats disease. Many people use ozone therapy in
the US, despite its unrecognized status with the FDA and allopathic medicine. It is legal to sell or own a medical-grade ozone
machine in the US. It is also legal to self-administer ozone. Whether practitioners can administer or recommend the use of ozone
presents a more complex issue.
See also
Notes and references
- ^ Lewis, Jr, R. J. (1993). Sax’s Dangerous Properties of Industrial Materials. New York: Van
Nostrand Rienhold, Co., Inc.,. ISBN 9780442016753.
- ^ a b "TITLE
21--FOOD AND DRUGS; CHAPTER I--FOOD AND DRUG ADMINISTRATION DEPARTMENT OF HEALTH AND HUMAN SERVICES; SUBCHAPTER H--MEDICAL
DEVICES", U.S. Food & Drug Administration (FDA) website, August 30, 2006.
- ^ Today in Science History. Retrieved on 2006-05-10.
- ^ Ozone FAQ. Global Change Master Directory. Retrieved on 2006-05-10.
- ^ Oxygen.
WebElements. Retrieved on 2006-09-23.
- ^ Ozone: Helpful or
Harmful?. Aerias AQS IAQ Resource Center. Retrieved on 2006-09-23.
- ^ Ozone.
Haz-MAP (occupational health database}. Retrieved on 2006-09-23.
- ^ Takehiko Tanaka; Yonezo Morino. Coriolis interaction and anharmonic
potential function of ozone from the microwave spectra in the excited vibrational states Journal of Molecular Spectroscopy
1970, 33, 538–551.
- ^ Kenneth M. Mack; J. S. Muenter. Stark and Zeeman properties of ozone from
molecular beam spectroscopy. Journal of Chemical Physics 1977, 66, 5278–5283. doi:10.1063/1.433909
- ^ http://gcmd.gsfc.nasa.gov/Resources/FAQs/ozone.html
- ^ Horvath M., Bilitzky L., & Huttner J., 1985. "Ozone." pg 44–49
- ^ Housecroft & Sharpe, 2005. "Inorganic Chemistry." pg 439
- ^ Housecroft & Sharpe, 2005. "Inorganic Chemistry." pg 265
- ^ Horvath M., Bilitzky L., & Huttner J., 1985. "Ozone." pg 44–49
- ^ Horvath M., Bilitzky L., & Huttner J., 1985. "Ozone." pg 259,
269–270
- ^ a b WHO-Europe reports: Health Aspects of Air Pollution (2003) (PDF)
- ^ Stevenson et al (2006). Multimodel ensemble simulations
of present-day and near-future tropospheric ozone. American Geophysical
Union. Retrieved on 2006-09-16.
- ^ Rising Ozone
Levels Pose Challenge to U.S. Soybean Production, Scientists Say. NASA Earth Observatory (2003-07-31). Retrieved on 2006-05-10.
- ^ Mutters, Randall (March 1999). Statewide Potential Crop Yield Losses
From Ozone Exposure. California Air Resources Board. Retrieved on 2006-05-10.
- ^ Tropospheric Ozone in EU - The consolidated report. European Environmental Agency (1998).
Retrieved on 2006-05-10.
- ^ Atmospheric Chemistry and Greenhouse Gases. Intergovernmental Panel on Climate Change.
Retrieved on 2006-05-10.
- ^ Climate Change 2001. Intergovernmental Panel on Climate Change (2001). Retrieved on 2006-09-12.
- ^ Answer to follow-up questions from CAFE (2004) (PDF)
- ^ Anderson, W.; G.J. Prescott, S. Packham,
J. Mullins, M. Brookes, and A. Seaton (August 2001). "Asthma admissions and thunderstorms: a study of pollen, fungal spores, rainfall, and ozone".
QJM: An International Journal of Medicine 94 (8): 429–433. Oxford Journals. Retrieved on 2006-09-23.
- ^ Ashfield District Council: Monitored Air Pollutants, downloaded February 2, 2007
- ^ University of East Anglia press release, Cloning the smell of the seaside,
February 2, 2007
- ^ Smog - Who does it hurt? What You Need to Know About Ozone and Your Health. AIRNow.gov.
Retrieved on 2007-07-10.
- ^ Hoffmann, Roald (January 2004). "The
Story of O". American Scientist 92 (1): 23. DOI:10.1511/2004.1.23. Retrieved on 2006-10-11.
- ^ Paul Wentworth (November 2003). Evidence for Ozone Formation in
Human Atherosclerotic Arteries. Retrieved on 2006-08-03.
- ^ Organic Syntheses, Coll. Vol. 3, p.673 (1955); Vol. 26, p.63 (1946).
(Article)
- ^ Dohan, J. M.; W. J. Masschelein (1987).
"Photochemical Generation of Ozone: Present State-of-the-Art". Ozone Sci. Eng. 9: 315–334. Retrieved on
2007-08-31.
- ^ Ibanez, Jorge G.; Rodrigo Mayen-Mondragon
and M. T. Moran-Moran (October 2005). "Laboratory Experiments on the Electrochemical Remediation of the Environment. Part 7: Microscale
Production of Ozone". Journal of Chemical Education 82: 1546. Retrieved on 2006-05-10.
- ^ Hoigné, J. (1998). Handbook of Environmental Chemistry, Vol. 5 part C, p83-141. Berlin:
Springer-Verlag.
- ^ Decontamination: Ozone scores on spores. Hospital Development. Wilmington Media Ltd.
(2007-04-01). Retrieved on 2007-05-30.
- ^ Sjöström, Eero (1993). Wood Chemistry: Fundamentals and Applications. San Diego, CA:
Academic Press, Inc.. ISBN 0-12-64748.
- ^
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