Ozone Toxicity & Ozone Gas Exposure Hazards InspectAPedia® -
The toxicity of ozone gas in buildings and ozone gas exposure limits
The effects of using ozone in buildings to "purify air" or to "kill mold"
The hazards of ozone generators in buildings
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This article discusses Ozone Toxicity in Buildings - A Summary of Hazards of Indoor Ozone, Ozone Generators, and Use of Ozone for Mold Remediation.
While there are some important uses of ozone (such as for medical disinfection under controlled conditions),
in general this is an idea which ranges from bad to dangerous in the home.
"Ozone
is a kind (called an "allotrope") of oxygen . It is formed in the
ionosphere by the action of ultraviolet radiation from sunlight on oxygen.
Lightning strokes are another natural source of ozone and the characteristic
odor of that material can often be noted during and after a thunderstorm.
When
pollutants are emitted into the air either by man or nature, almost all are
eventually removed by one or more of several processes including reaction under
the influence of ultraviolet radiation. One series of such reactions results in
the formation of ozone as a "secondary" (formed by reaction in the
air) air pollutant, often in rather high concentrations (several tenths of a
part per million).
"As
ozone can be formed by nature's sparks (lightning), it can also be formed by
man's. Whenever an electrical spark or corona occurs in air, some ozone is
formed. This accounts for the characteristic odor noted near an operating
electric motor such as an electric shaver.
"Because
ozone is found in so many places, its toxicity (ability to injure a living
organism by other than mechanical means) has been investigated extensively
since the early 1900s. Experimentation has shown that the odor of ozone can be
detected and identified by most people at a concentration of from 0.02 to 0.05
ppm (parts ozone per million parts air + ozone). As the concentration increases
to a few tenths of a part per million, the first effect noted is likely to be a
feeling of dryness in the back of the throat. If a concentration on the order
of 0.2 or 0.3 ppm is inhaled more or less continuously for several hours to a
few days some lung irritation may result.
"Higher
concentrations can produce several kinds of toxic effects if exposures are
sufficiently prolonged. Eye irritation (despite newspaper and TV accounts
seemingly indicating otherwise) occurs only at concentrations high enough to
result in other, more severe, toxic effects.
"Ozone
is a very reactive substance. It will readily react with just about any material
capable of being oxidized, and with many that are not. The material with which
it reacts may be a gas or vapor, a particle floating in the air (a mold spore,
for example), or a solid (or liquid) surface. For this reason, when ozone is
present in most enclosed spaces its concentration declines quite rapidly with
time. Of course, if ozone is being generated more rapidly than it is destroyed
by reaction, its concentration can build up. This is the main reason why
devices that produce relatively large amounts of ozone are safe only in
relatively large enclosures and why the ozone generation rate should be reduced
in small enclosures.
"Ozone
is well known for its ability to eliminate certain odors. How this is
accomplished is controversial. At concentrations just above the odor threshold,
some odors do seem to vanish. The main reason for this may be ozone's ability
to desensitize the olfactory apparatus so that the odors can no longer be
perceived. Some evidence indicates that this may be the case at least occasionally.
Other evidence indicates that ozone may react with the odor-causing substances,
eliminating them from the air (this is probably the only mechanism that
operates when concentrations are below the odor threshold).
"Finally,
some people have insisted that even if ozone does not paralyze the olfactory
sense, its odor is such that it "masks" other odors. Perhaps all
three mechanisms operate, each in its own area of effectiveness.
"As
with all other materials, ozone has a dose-effect relationship with a
threshold. That is, once the threshold dose has been exceeded, toxic effects
are proportional to dose. For inhaled gases, dose is proportional to both time
and concentration. If the duration of exposures cannot be controlled (as is
usually the case), then the concentration must be kept low enough so that no
injury will occur even from prolonged and repeated exposures.
For ozone, that
"threshold" concentration is 0.1 ppm. So long as concentrations are
kept at or below that level, injury is not expected even in the most sensitive
workers so long as their exposure durations coincide reasonably well with or
are less than the 8 hr/day, 40 hr/wk regimen. This "threshold" level
is accepted by the American Conference of Governmental Industrial Hygienists
(and is called the Threshold Limit Value by that organization) and by the
Occupational Safety and Health Administration, OSHA.
The TLV or OSHA's
Permissible Exposure Level (PEL) is not a fine line between safe and non-safe.
Instead, it represents the best judgment of a group of experts of the highest
concentration that can be inhaled repeatedly by a population of workers with no
resulting injury. Higher concentrations may or may not have any particular
effect on a specific individual.
"Ozone is a highly toxic gas
but even highly toxic substances can be encountered safely. The main concern
with this material is that concentrations to which people are exposed do not average more than 0.1 ppm over an 8-hr day, and do not exceed that value by more
than a factor of 2 or 3 during the exposure."
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Additional technical contributors & reference sources for this article are listed below.
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[6]Ozone
is not a substitute for mold removal and its reaction with building materials,
but applied by an expert may help deodorize, a cleaning article by Jim Holland -
http://www.icsmag.com/CDA/ArticleInformation/features/BNP__Features__Item/0,3035,118663,00.html
[7] Ozone as an oxidant, a few references from the Canadian Government
Bogaty,
H., Campbell K. S., and Appel, W. D. (1952). The oxidation of cellulose by ozone in small
concentrations. Text. Res. J. 22: 81-83.
Bradley,
C. E., and Haagen-Smit, A. J. (1951). The application of rubber in the
quantitative determination of ozone. Rubber Chem. Technol. 24: 750-755.
Cass, G. R., Nazaroff, W. W., Tiller, C., and Whitmore, P. M. (1991). Protection of
works of art from damage due to atmospheric ozone. Atmospheric Environment,
25A( 2): 441-451.
Druzik, J. R. (1985). Ozone: The Intractable Problem. We stern Association for Art
Conservation newsletter. Http://sul-server-2.stanford.edu/waac/wn/wn07/wn07-3/wn07-302.html
(vol.7, no. 3)
[8] "Health Hazards of some Gases" Jack E. Peterson, P.E., CIH, Ph.D., May, 1987
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