Smoke
Smoke
Smoke is a
collection of airborne solid and liquid particulates and gases emitted when a material undergoes combustion or pyrolysis, together with the quantity of air
that is entrained or otherwise mixed into the mass. It is
commonly an unwanted by-product of fires (including stoves, candles, oil lamps, and fireplaces), but may also be used for pest control (fumigation), communication (smoke signals), defensive and offensive
capabilities in the military (smoke-screen), cooking, or smoking (tobacco, cannabis, etc.). Smoke is used in rituals
where incense, sage, or resin is burned to produce a smell for spiritual
purposes. Smoke is sometimes used as a flavoring agent, and preservative for
various foodstuffs. Smoke is also a component of internal
combustion engine exhaust gas, particularly diesel exhaust.
Smoke inhalation is the primary cause of death in victims of
indoor fires.
The smoke kills by a combination of thermal damage, poisoningand pulmonary irritation caused by carbon monoxide, hydrogen cyanide and other combustion products.
Smoke is an aerosol (or mist) of solid particles and
liquid droplets that are close to the ideal range of sizes for Mie scattering of visible light. This effect has been likened to
three-dimensional textured privacy glass[citation
needed] — a
smoke cloud does not obstruct an image, but thoroughly scrambles it.
Chemical
composition
The composition of smoke depends on the nature of the burning
fuel and the conditions of combustion.
Fires with high availability of oxygen burn at a high
temperature and with small amount of smoke produced; the particles are mostly
composed of ash, or with large temperature differences, of condensed aerosol of
water. High temperature also leads to production of nitrogen oxides. Sulfur content yields sulfur dioxide, or in case of incomplete
combustion, hydrogen sulfide. Carbon and hydrogen are almost
completely oxidized to carbon dioxide and water. Fires burning with lack of oxygen
produce a significantly wider palette of compounds, many of them toxic. Partial oxidation of carbon produces carbon monoxide, nitrogen-containing materials
can yield hydrogen cyanide, ammonia, and nitrogen oxides. Hydrogen gas
can be produced instead of water. Content
of halogens such
as chlorine (e.g.
in polyvinyl chloride or brominated flame
retardants) may lead to production of e.g. hydrogen chloride, phosgene, dioxin,
and chloromethane, bromomethane and
other halocarbons. Hydrogen fluoride can be formed from fluorocarbons, whether fluoropolymers subjected to fire or halocarbon fire suppression
agents. Phosphorus and antimony oxides
and their reaction products can be formed from some fire retardant additives, increasing smoke toxicity
and corrosivity. Pyrolysis of polychlorinated
biphenyls (PCB), e.g. from
burning older transformer oil, and to lower degree also of
other chlorine-containing materials, can produce 2,3,7,8-tetrachlorodibenzodioxin,
a potent carcinogen, and other polychlorinated
dibenzodioxins. Pyrolysis
of fluoropolymers, e.g. teflon, in presence of oxygen yields carbonyl fluoride (which hydrolyzes readily to HF and CO2);
other compounds may be formed as well, e.g. carbon tetrafluoride, hexafluoropropylene,
and highly toxic perfluoroisobutene (PFIB).
Emission
of soot in the fumes of a large diesel truck,
without particle filters.
Pyrolysis of burning material, especially incomplete combustion or smoldering without
adequate oxygen supply, also results in production of a large amount of hydrocarbons, both aliphatic (methane, ethane, ethylene, acetylene) and aromatic (benzene and
its derivates, polycyclic
aromatic hydrocarbons; e.g. benzo[a]pyrene, studied as a carcinogen, or retene), terpenes. Heterocyclic
compounds may be also
present. Heavier hydrocarbons may
condense as tar;
smoke with significant tar content is yellow to brown. Presence of such smoke, soot, and/or
brown oily deposits during a fire indicates a possible hazardous situation, as
the atmosphere may be saturated with combustible pyrolysis products with
concentration above the upper flammability limit,
and sudden inrush of air can cause flashover or backdraft.
Presence of sulfur can lead to formation of e.g. hydrogen sulfide, carbonyl sulfide, sulfur dioxide, carbon disulfide, and thiols;
especially thiols tend to get adsorbed on surfaces and produce a lingering odor
even long after the fire. Partial oxidation of the released hydrocarbons yields
in a wide palette of other compounds: aldehydes (e.g. formaldehyde, acrolein, and furfural), ketones, alcohols (often aromatic,
e.g. phenol, guaiacol, syringol, catechol, and cresols), carboxylic acids (formic acid, acetic acid, etc.).
The visible particulate
matter in such smokes
is most commonly composed of carbon (soot).
Other particulates may be composed of drops of condensed tar,
or solid particles of ash. The presence of metals in the fuel yields particles
of metal oxides.
Particles of inorganic saltsmay also be formed, e.g. ammonium sulfate, ammonium nitrate, or sodium chloride. Inorganic salts present on
the surface of the soot particles may make them hydrophilic. Many organic compounds, typically
the aromatic hydrocarbons,
may be also adsorbed on
the surface of the solid particles. Metal oxides can be present when
metal-containing fuels are burned, e.g. solid rocket fuels
containing aluminium. Depleted uranium projectiles after impacting the target
ignite, producing particles of uranium oxides. Magnetic particles,
spherules of magnetite-like ferrous ferric oxide,
are present in coal smoke; their increase in deposits after 1860 marks the
beginning of the Industrial Revolution. (Magnetic
iron oxide nanoparticles can be also produced in the smoke from meteorites burning
in the atmosphere.) Magnetic remanence, recorded in
the iron oxide particles, indicates the strength of Earth's magnetic field when
they were cooled beyond their Curie temperature; this can be used to
distinguish magnetic particles of terrestrial and meteoric origin. Fly ash is
composed mainly of silica and calcium oxide. Cenospheres are
present in smoke from liquid hydrocarbon fuels. Minute metal particles produced
by abrasion can be present in engine smokes. Amorphous silica particles are present in smokes from
burning silicones; small proportion of silicon nitride particles can be formed in fires with
insufficient oxygen. The silica particles have about 10 nm size, clumped
to 70-100 nm aggregates and further agglomerated to chains. Radioactive particles may be present
due to traces of uranium, thorium, or other radionuclides in the fuel; hot particles can be present in case of fires during nuclear accidents (e.g. Chernobyl disaster)
or nuclear war.
Smoke particulates, like other aerosols, are categorized into
three modes based on particle size:
· nuclei
mode, with geometric mean radius between 2.5–20 nm, likely
forming by condensation of carbon moieties.
· accumulation mode,
ranging between 75–250 nm and formed by coagulation of nuclei mode
particles
·
coarse mode, with particles in
micrometer range
Most of the smoke material is primarily in coarse particles.
Those undergo rapid dry precipitation, and the smoke damage in
more distant areas outside of the room where the fire occurs is therefore
primarily mediated by the smaller particles.
Aerosol of particles beyond visible size is an early indicator
of materials in a preignition stage of a fire.
Burning of hydrogen-rich fuel produces water; this results in
smoke containing droplets of water vapor. In absence of other color sources
(nitrogen oxides, particulates...), such smoke is white and cloud-like.
Smoke emissions may contain characteristic trace elements. Vanadium is
present in emissions from oil fired power plants and refineries; oil plants also emit some nickel. Coal combustion produces emissions containing aluminium, arsenic, chromium, cobalt, copper, iron, mercury, selenium, and uranium.
Traces of vanadium in high-temperature combustion products form
droplets of molten vanadates. These attack the passivation layers on metals and cause high temperature
corrosion, which is a concern especially for internal
combustion engines. Molten sulfate and lead particulates also have such effect.
Some components of smoke are characteristic of the combustion
source. Guaiacol and
its derivatives are products of pyrolysis of lignin and
are characteristic of wood smoke; other markers are syringol and
derivates, and other methoxy phenols. Retene, a product of pyrolysis of conifer trees,
is an indicator of forest fires. Levoglucosan is
a pyrolysis product of cellulose. Hardwood vs softwood smokes
differ in the ratio of guaiacols/syringols. Markers for vehicle exhaust include polycyclic
aromatic hydrocarbons, hopanes, steranes, and specific nitroarenes (e.g. 1-nitropyrene). The ratio of hopanes and
steranes to elemental carbon can be used to distinguish between emissions of
gasoline and diesel engines.
Many compounds can be associated with particulates; whether by
being adsorbed on
their surfaces, or by being dissolved in liquid droplets. Hydrogen chloride is
well absorbed in the soot particles.
Inert particulate matter can be disturbed and entrained into the
smoke. Of particular concern are particles of asbestos.
Deposited hot particles of radioactive fallout and bioaccumulated radioisotopes can
be reintroduced into the atmosphere by wildfires and forest fires; this is a concern in e.g. the Zone of alienation containing contaminants from the Chernobyl disaster.
Polymers are a significant source of smoke. Aromatic side groups, e.g. in polystyrene, enhance generation of smoke.
Aromatic groups integrated in the polymer backbone produce less smoke, likely
due to significant charring. Aliphatic polymers tend to generate
the least smoke, and are non-self-extinguishing. However presence of additives
can significantly increase smoke formation. Phosphorus-based and halogen-based flame retardants decrease production of smoke. Higher
degree of cross-linking between the polymer chains has such
effect too.
Visible and
invisible particles of combustion
Smoke
from a wildfire
Smoke
rising up from the smoldering remains of a recently extingished mountain fire
in South Africa.
The naked eye detects
particle sizes greater than 7 µm (micrometres). Visible particles
emitted from a fire are referred to as smoke. Invisible particles
are generally referred to as gas or fumes. This is best illustrated when toasting bread in a toaster. As the bread heats
up, the products of combustion increase in size. The fumes initially produced
are invisible but become visible if the toast is burnt.
An ionization chamber type smoke detector is technically a product of combustion
detector, not a smoke detector. Ionization chamber type smoke detectors detect particles of combustion that
are invisible to the naked eye. This explains why they may
frequently false alarm from
the fumes emitted from the red-hot heating elements of a toaster, before the
presence of visible smoke, yet they may fail to activate in the early, low-heat smoldering stage
of a fire.
Smoke from a typical house fire contains hundreds of different
chemicals and fumes. As a result, the damage caused by the smoke can often
exceed that caused by the actual heat of the fire. In addition to the physical
damage caused by the smoke of a fire – which manifests itself in the form
of stains – is the often even harder to eliminate problem of a smoky odor. Just
as there are contractors that specialize in rebuilding/repairing homes that
have been damaged by fire and smoke, fabric restoration companies specialize in restoring
fabrics that have been damaged in a fire.
Dangers of smoke
Smoke from oxygen-deprived fires contains a significant
concentration of compounds that are flammable. A cloud of smoke, in contact
with atmospheric oxygen, therefore has the potential of being ignited – either
by another open flame in the area, or by its own temperature. This leads to
effects like backdraft and flashover. Smoke inhalation is also a danger of smoke that can
cause serious injury and death.
Many compounds of smoke from fires are highly toxic and/or
irritating. The most dangerous is carbon monoxide leading to carbon monoxide
poisoning, sometimes with the additive effects of hydrogen cyanide and phosgene. Smoke inhalation can therefore
quickly lead to incapacitation and loss of consciousness. Sulfur oxides,
hydrogen chloride and hydrogen fluoride in contact with moisture form sulfuric, hydrochloric and hydrofluoric acid, which are corrosive to both
lungs and materials. When asleep the nose does not sense smoke nor does the
brain, but the body will wake up if the lungs become enveloped in smoke and the
brain will be stimulated and the person will be awoken. This does not work if
the person is incapacitated or under the influence of drugs and/or alcohol.
Cigarette smoke is a major modifiable risk factor for lung disease, heart disease, and many cancers. Smoke can also be a component of
ambient air pollution due to the burning of coal in power plants, forest fires
or other sources, although the concentration of pollutants in ambient air is
typically much less than that in cigarette smoke. One day of exposure to PM2.5
at a concentration of 880 μg/m3, such as occurs in Beijing, China, is the
equivalent of smoking one or two cigarettes in terms of particulate inhalation
by weight.The analysis is complicated, however, by the fact that the organic
compounds present in various ambient particulates may have a higher
carcinogenicity than the compounds in cigarette smoke particulates.
Reduced
visibility due to wildfire smoke in Sheremetyevo
airport(Moscow, Russia) 7 August 2010.
Smoke can obscure visibility, impeding occupant exiting from
fire areas. In fact, the poor visibility due to the smoke that was in the Worcester
Cold Storage Warehouse fire in Worcester,
Massachusetts was the
exact reason why the trapped rescue firefighters couldn't evacuate the building
in time. Because of the striking similarity that each floor shared, the dense
smoke caused the firefighters to become disoriented.
The effect of smoke burning off the end of a tobacco product or
the smoke exhaled by a smoker is known as secondhand smoke. This smoke is
contained with harmful substances that can harm the body of the smoker. A
person could have serious health problems from the result of breathing in
secondhand smoke such as diseases or cancers. A child’s undeveloped body can
face respiratory problems that could affect their lives forever. Secondhand
smoke also harms the environment by being an indoor air pollutant that people
breathe in.
Smoke corrosion
Smoke contains a wide variety of chemicals, many of them aggressive
in nature. Examples are hydrochloric acid and hydrobromic acid, produced from halogen-containing plastics and fire retardants, hydrofluoric acid released by pyrolysis of fluorocarbon fire suppression
agents, sulfuric acid from burning of sulfur-containing materials, nitric acid from
high-temperature fires where nitrous oxide gets formed, phosphoric acid and antimony compounds
from P and Sb based fire retardants, and many others. Such corrosion is
not significant for structural materials, but delicate structures, especially microelectronics, are strongly affected.
Corrosion of circuit board traces, penetration of aggressive
chemicals through the casings of parts, and other effects can cause an
immediate or gradual deterioration of parameters or even premature (and often
delayed, as the corrosion can progress over long time) failure of equipment
subjected to smoke. Many smoke components are also electrically
conductive; deposition of a conductive layer on the circuits can
cause crosstalks and
other deteriorations of the operating parameters or even cause short circuits
and total failures. Electrical contacts can be affected by corrosion of
surfaces, and by deposition of soot and other conductive particles or
nonconductive layers on or across the contacts. Deposited particles may
adversely affect the performance of optoelectronics by absorbing or scattering the light
beams.
Corrosivity of smoke produced by materials is characterized by
the corrosion index (CI), defined as material loss
rate (angstrom/minute) per amount of material gasified products (grams) per
volume of air (m3). It is measured by exposing strips of metal to flow of
combustion products in a test tunnel. Polymers containing halogen and hydrogen (polyvinyl chloride, polyolefins with
halogenated additives, etc.) have the highest CI as the corrosive acids are
formed directly with water produced by the combustion, polymers containing
halogen only (e.g. polytetrafluoroethylene)
have lower CI as the formation of acid is limited to reactions with airborne
humidity, and halogen-free materials (polyolefins, wood)
have the lowest CI.[15] However, some halogen-free materials can
also release significant amount of corrosive products.
Smoke damage to electronic equipment can be significantly more
extensive than the fire itself. Cable fires are of special concern; low smoke zero
halogen materials are
preferable for cable insulation.
When smoke comes into contact with the surface of any substance
or structure, the chemicals contained in it are transferred to it. The
corrosive properties of the chemicals cause the substance or structure to
decompose at a rapid rate. Certain materials or structures absorb these
chemicals, which is why clothing, unsealed surfaces, potable water, piping,
wood, etc., are replaced in most cases of structural fires.
Secondhand tobacco smoke inhalation
Secondhand tobacco smoke is the combination of both sidestream
and mainstream smoke emissions. These emissions contain more than 50
carcinogenic chemicals. According to the Surgeon General's latest report on the
subject, "Short exposures to secondhand [tobacco] smoke can cause blood
platelets to become stickier, damage the lining of blood vessels, decrease
coronary flow velocity reserves, and reduce heart variability, potentially
increasing the risk of a heart attack". The
American Cancer Society lists "heart disease, lung infections, increased
asthma attacks, middle ear infections, and low birth weight" as
ramifications of smoker's emission.
Measurement
As early as the 15th century Leonardo da Vinci commented at length on the difficulty
of assessing smoke, and distinguished between black smoke (carbonized
particles) and white 'smoke' which is not a smoke at all but merely a
suspension of harmless water particulates. Smoke
from heating appliances is commonly measured in one of the following ways:
In-line capture. A smoke
sample is simply sucked through a filter which is weighed before and after the
test and the mass of smoke found. This is the simplest and probably the most
accurate method, but can only be used where the smoke concentration is slight,
as the filter can quickly become blocked.
The ASTM smoke pump is a simple and widely used method of
in-line capture where a measured volume of smoke is pulled through a filter
paper and the dark spot so formed is compared with a standard.
Filter/dilution tunnel. A smoke sample is drawn through a tube
where it is diluted with air, the resulting smoke/air mixture is then pulled
through a filter and weighed. This is the internationally recognized method of
measuring smoke from combustion.
Electrostatic precipitation. The smoke is passed through an array of
metal tubes which contain suspended wires. A (huge) electrical potential is
applied across the tubes and wires so that the smoke particles become charged
and are attracted to the sides of the tubes. This method can over-read by
capturing harmless condensates, or under-read due to the insulating effect of
the smoke. However, it is the necessary method for assessing volumes of smoke
too great to be forced through a filter, i.e., from bituminous coal.
Ringelmann scale. A measure of smoke color. Invented by
Professor Maximilian
Ringelmann in Paris in
1888, it is essentially a card with squares of black, white and shades of gray
which is held up and the comparative grayness of the smoke judged. Highly
dependent on light conditions and the skill of the observer it allocates a
grayness number from 0 (white) to 5 (black) which has only a passing
relationship to the actual quantity of smoke. Nonetheless, the simplicity of
the Ringelmann scale means that it has been adopted as a standard in many
countries.
Cossar
scale. The
change of atmospheric smoke particulate concentration resulting from the
presence of Barry Cossar. The ratio of smoke to air exiting Barry Cossar is
measured and compared against that in the surrounding atmosphere. This dynamic
scale ranges from zero to seven; reported measurements typically average very
near seven.
Optical scattering. A light
beam is passed through the smoke. A light detector is situated at an angle to
the light source, typically at 90°, so that it receives only light reflected
from passing particles. A measurement is made of the light received which will
be higher as the concentration of smoke particles becomes higher.
Optical obscuration. A light beam is passed through the smoke
and a detector opposite measures the light. The more smoke particles are
present between the two, the less light will be measured.
Combined optical methods. There are various proprietary optical smoke
measurement devices such as the 'nephelometer' or the 'aethalometer' which use several different
optical methods, including more than one wavelength of light, inside a single
instrument and apply an algorithm to give a good estimate of smoke. It has been
claimed that these devices can differentiate types of smoke and so their
probable source can be inferred, though this is disputed.
Inference from carbon monoxide. Smoke is incompletely burned fuel,
carbon monoxide is incompletely burned carbon, therefore it has long been
assumed that measurement of CO in flue gas (a
cheap, simple and very accurate procedure) will provide a good indication of
the levels of smoke. Indeed, several jurisdictions use CO measurement as the
basis of smoke control. However it is far from clear how accurate the
correspondence is.
Medicinal smoke
Throughout recorded history, humans have used the smoke of medicinal plants to cure illness. A sculpture from Persepolis shows Darius the Great (522–486 BC), the king of Persia, with two censers in
front of him for burning Peganum harmala and/or sandalwood Santalum album, which was believed to protect
the king from evil and disease. More than 300 plant species in 5 continents are
used in smoke form for different diseases. As a method of drug administration,
smoking is important as it is a simple, inexpensive, but very effective method
of extracting particles containing active agents. More importantly, generating
smoke reduces the particle size to a microscopic scale thereby increasing the
absorption of its active chemical principles.
Source : https://en.wikipedia.org/wiki/Smoke
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