Hydrocarbon - Mansfield Gas Well Awareness

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Hydrocarbon
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Ball-and-stick model of the methane molecule, CH4. Methane is part of a homologous series known as
the alkanes, which contain single bonds only.
In organic chemistry, a hydrocarbon is an organic compound consisting entirely of hydrogen
and carbon.[1] Hydrocarbons from which one hydrogen atom has been removed are functional
groups, called hydrocarbyls.[2] Aromatic hydrocarbons (arenes), alkanes, alkenes, cycloalkanes
and alkyne-based compounds are different types of hydrocarbons.
The majority of hydrocarbons found on Earth naturally occur in crude oil, where decomposed
organic matter provides an abundance of carbon and hydrogen which, when bonded, can catenate
to form seemingly limitless chains.[3][4]
Contents
[hide]


1 Types of hydrocarbons
o 1.1 General properties
o 1.2 Simple hydrocarbons and their variations
2 Usage






3 Poisoning
4 Reactions
o 4.1 Substitution Reaction
o 4.2 Addition Reaction
o 4.3 Combustion
 4.3.1 Petroleum
 4.3.2 Bioremediation
5 See also
6 References
7 Bibliography
8 External links
Types of hydrocarbons[edit]
The classifications for hydrocarbons, defined by IUPAC nomenclature of organic chemistry are
as follows:
1. Saturated hydrocarbons (alkanes) are the simplest of the hydrocarbon species. They are
composed entirely of single bonds and are saturated with hydrogen. The general formula for
saturated hydrocarbons is CnH2n+2 (assuming non-cyclic structures).[5] Saturated hydrocarbons are
the basis of petroleum fuels and are found as either linear or branched species. Substitution
reaction is their characteristics property (like chlorination reaction to form chloroform).
Hydrocarbons with the same molecular formula but different structural formulae are called
structural isomers.[6] As given in the example of 3-methylhexane and its higher homologues,
branched hydrocarbons can be chiral.[7] Chiral saturated hydrocarbons constitute the side chains
of biomolecules such as chlorophyll and tocopherol.[8]
2. Unsaturated hydrocarbons have one or more double or triple bonds between carbon atoms.
Those with double bond are called alkenes. Those with one double bond have the formula CnH2n
(assuming non-cyclic structures).[9] Those containing triple bonds are called alkynes, with general
formula CnH2n-2.[10]
3. Cycloalkanes are hydrocarbons containing one or more carbon rings to which hydrogen atoms
are attached. The general formula for a saturated hydrocarbon containing one ring is CnH2n.[6]
4. Aromatic hydrocarbons, also known as arenes, are hydrocarbons that have at least one aromatic
ring.
Hydrocarbons can be gases (e.g. methane and propane), liquids (e.g. hexane and benzene), waxes
or low melting solids (e.g. paraffin wax and naphthalene) or polymers (e.g. polyethylene,
polypropylene and polystyrene).
General properties[edit]
Because of differences in molecular structure, the empirical formula remains different between
hydrocarbons; in linear, or "straight-run" alkanes, alkenes and alkynes, the amount of bonded
hydrogen lessens in alkenes and alkynes due to the "self-bonding" or catenation of carbon
preventing entire saturation of the hydrocarbon by the formation of double or triple bonds.
This inherent ability of hydrocarbons to bond to themselves is known as catenation, and allows
hydrocarbon to form more complex molecules, such as cyclohexane, and in rarer cases, arenes
such as benzene. This ability comes from the fact that the bond character between carbon atoms
is entirely non-polar, in that the distribution of electrons between the two elements is somewhat
even due to the same electronegativity values of the elements (~0.30), and does not result in the
formation of an electrophile.
Generally, with catenation comes the loss of the total amount of bonded hydrocarbons and an
increase in the amount of energy required for bond cleavage due to strain exerted upon the
molecule;in molecules such as cyclohexane, this is referred to as ring strain, and occurs due to
the "destabilized" spatial electron configuration of the atom.
In simple chemistry, as per valence bond theory, the carbon atom must follow the "4-hydrogen
rule", which states that the maximum number of atoms available to bond with carbon is equal to
the number of electrons that are attracted into the outer shell of carbon. In terms of shells, carbon
consists of an incomplete outer shell, which comprises 4 electrons, and thus has 4 electrons
available for covalent or dative bonding.
Hydrocarbons are hydrophobic like lipids.
Some hydrocarbons also are abundant in the solar system. Lakes of liquid methane and ethane
have been found on Titan, Saturn's largest moon, confirmed by the Cassini-Huygens Mission.[11]
Hydrocarbons are also abundant in nebulae forming polycyclic aromatic hydrocarbon (PAH)
compounds.[12]
Simple hydrocarbons and their variations[edit]
Number of
Alkane (single
carbon
bond)
atoms
Alkene (double
bond)
Alkyne (triple bond)
Cycloalkane
Alkadiene
1
Methane
-
-
-
-
2
Ethane
Ethene
(ethylene)
Ethyne (acetylene)
–
–
3
Propane
Propene
(propylene)
Propyne
(methylacetylene)
Cyclopropane
Propadiene
(allene)
4
Butane
Butene
(butylene)
Butyne
Cyclobutane
Butadiene
5
Pentane
Pentene
Pentyne
Cyclopentane
Pentadiene
(piperylene)
6
Hexane
Hexene
Hexyne
Cyclohexane
Hexadiene
7
Heptane
Heptene
Heptyne
Cycloheptane
Heptadiene
8
Octane
Octene
Octyne
Cyclooctane
Octadiene
9
Nonane
Nonene
Nonyne
Cyclononane
Nonadiene
10
Decane
Decene
Decyne
Cyclodecane
Decadiene
Usage[edit]
Oil refineries are one way hydrocarbons are processed for use. Crude oil is processed in several stages to
form desired hydrocarbons, used as fuel and in other products.
Hydrocarbons are a primary energy source for current civilizations. The predominant use of
hydrocarbons is as a combustible fuel source. In their solid form, hydrocarbons take the form of
asphalt (bitumen).[13]
Mixtures of volatile hydrocarbons are now used in preference to the chlorofluorocarbons as a
propellant for aerosol sprays, due to chlorofluorocarbon's impact on the ozone layer.
Methane [1C] and ethane [2C] are gaseous at ambient temperatures and cannot be readily
liquefied by pressure alone. Propane [3C] is however easily liquefied, and exists in 'propane
bottles' mostly as a liquid. Butane [4C] is so easily liquefied that it provides a safe, volatile fuel
for small pocket lighters. Pentane [5C] is a clear liquid at room temperature, commonly used in
chemistry and industry as a powerful nearly odorless solvent of waxes and high molecular
weight organic compounds, including greases. Hexane [6C] is also a widely used non-polar, nonaromatic solvent, as well as a significant fraction of common gasoline. The [6C] through [10C]
alkanes, alkenes and isomeric cycloalkanes are the top components of gasoline, naphtha, jet fuel
and specialized industrial solvent mixtures. With the progressive addition of carbon units, the
simple non-ring structured hydrocarbons have higher viscosities, lubricating indices, boiling
points, solidification temperatures, and deeper color. At the opposite extreme from [1C] methane
lie the heavy tars that remain as the lowest fraction in a crude oil refining retort. They are
collected and widely utilized as roofing compounds, pavement composition, wood preservatives
(the creosote series) and as extremely high viscosity shear-resisting liquids.
Poisoning[edit]
Hydrocarbon poisoning such as that of benzene and petroleum usually occurs accidentally by
inhalation or ingestion of these cytotoxic chemical compounds. Intravenous or subcutaneous
injection of petroleum compounds with intent of suicide or abuse is an extraordinary event that
can result in local damage or systemic toxicity such as tissue necrosis, abscess formation,
respiratory system failure and partial damage to the kidneys, the brain and the nervous system.
Moaddab and Eskandarlou report a case of chest wall necrosis and empyema resulting from
attempting suicide by injection of petroleum into the pleural cavity.[14]
Reactions[edit]
There are three main types of reactions :



Substitution Reaction
Addition Reaction
Combustion
Substitution Reaction[edit]
Substitution reaction only occur in saturated hydrocarbons (single carbon-carbon bonds). In this
reaction, an alkane reacts with a chlorine molecule. One of the chlorine atoms displace an
hydrogen atom. This forms hydrochloride acid as well as the hydrocarbon with one chlorine.
e.g. CH4 + Cl2 →CH3Cl + HCl
e.g. CH3Cl3 + Cl2 →CH2Cl2 + HCl
All the way until CCl4 (Carbon tetrachloride)
e.g. C2H6 + Cl2 →C2H5Cl1 + HCl
e.g. C2H4Cl2 + Cl2 →C2H4Cl3 + HCl
All the way until C2Cl4 (DiCarbon tetrachloride)
Addition Reaction[edit]
Addition reactions involve alkenes and alkynes. In this reaction a halogen molecule breaks the
double or triple bond in the hydrocarbon and forms a bond.
Combustion[edit]
Container of ethanol vapour mixed with air, undergoing rapid combustion
Main article: Combustion
Hydrocarbons are currently the main source of the world’s electric energy and heat sources (such
as home heating) because of the energy produced when burnt.[15] Often this energy is used
directly as heat such as in home heaters, which use either petroleum or natural gas. The
hydrocarbon is burnt and the heat is used to heat water, which is then circulated. A similar
principle is used to create electric energy in power plants.
Common properties of hydrocarbons are the facts that they produce steam, carbon dioxide and
heat during combustion and that oxygen is required for combustion to take place. The simplest
hydrocarbon, methane, burns as follows:
CH4 + 2 O2 → 2 H2O + CO2 + Energy
In inadequate supply of air, CO gas and water vapour are formed:
2 CH4 + 3 O2 → 2CO + 4H2O
Another example of this reaction is propane:
C3H8 + 5 O2 → 4 H2O + 3 CO2 + Energy
CnH2n+2 + (3n+1)/2 O2 → (n+1) H2O + n CO2 + Energy
Burning of hydrocarbons is an example of an exothermic chemical reaction.
Hydrocarbons can also be burned with elemental fluorine, resulting in carbon tetrafluoride and
hydrogen fluoride products
Petroleum[edit]
Main article: Petroleum
Natural oil spring in Korňa, Slovakia.
Extracted hydrocarbons in a liquid form are referred to as petroleum (literally "rock oil") or
mineral oil, whereas hydrocarbons in a gaseous form are referred to as natural gas. Petroleum
and natural gas are found in the Earth's subsurface with the tools of petroleum geology and are a
significant source of fuel and raw materials for the production of organic chemicals.
The extraction of liquid hydrocarbon fuel from sedimentary basins is integral to modern energy
development. Hydrocarbons are mined from oil sands and oil shale, and potentially extracted
from sedimentary methane hydrates. These reserves require distillation and upgrading to produce
synthetic crude and petroleum.
Oil reserves in sedimentary rocks are the source of hydrocarbons for the energy, transport and
petrochemical industry.
Economically important hydrocarbons include fossil fuels such as coal, petroleum and natural
gas, and its derivatives such as plastics, paraffin, waxes, solvents and oils. Hydrocarbons – along
with NOx and sunlight – contribute to the formation of tropospheric ozone and greenhouse
gases.
Bioremediation[edit]
Bacteria in the gabbroic layer of the ocean's crust can degrade hydrocarbons; but the extreme
environment makes research difficult.[16] Other bacteria such as Lutibacterium anuloederans can
also degrade hydrocarbons.[17] Mycoremediation or breaking down of hydrocarbon by mycellium
and mushroom is possible.[18]
See also[edit]
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







Abiogenic petroleum origin
Biohydrocarbon
Carbohydrates
Energy storage
Fractional distillation
Functional group
Hydrocarbon mixtures
Hydrocarbons on other planets
Organically moderated and cooled reactor
References[edit]
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
12.
13.
14.
15.
16.
17.
18.
Jump up ^ Silberberg, 620
Jump up ^ IUPAC Goldbook hydrocarbyl groups
Jump up ^ Clayden, J., Greeves, N., et al. (2001) Organic Chemistry Oxford ISBN 0-19-850346-6 p. 21
Jump up ^ McMurry, J. (2000). Organic Chemistry 5th ed. Brooks/Cole: Thomson Learning. ISBN 0-49511837-0 pp. 75–81
Jump up ^ Silderberg, 623
^ Jump up to: a b Silderberg, 625
Jump up ^ Silderberg, 627
Jump up ^ Meierhenrich, Uwe. Amino Acids and the Asymmetry of Life. Springer, 2008. ISBN 978-3-54076885-2
Jump up ^ Silderberg, 628
Jump up ^ Silderberg, 631
Jump up ^ http://www.jpl.nasa.gov/news/news.php?release=2013-364
Jump up ^ http://arxiv.org/abs/1403.1856
Jump up ^ Dan Morgan, Lecture ENVIRO 100, University of Washington, 11/5/08
Jump up ^ Eskandarlou M, Moaddab AH. Chest wall necrosis and empyema resulting from attempting
suicide by injection of petroleum into the pleural cavity. Emerg Med J. 2010 Aug;27(8):616-8. doi:
10.1136/emj.2009.073486. Epub 2010 Jun 17.
Jump up ^ World Coal, Coal and Electricity, http://www.worldcoal.org/coal/uses-of-coal/coal-electricity/,
retrieved 07/03/2012
Jump up ^ Mason OU, Nakagawa T, Rosner M, Van Nostrand JD, Zhou J, Maruyama A, Fisk MR,
Giovannoni SJ. (2010). "First investigation of the microbiology of the deepest layer of ocean crust.". PLoS
ONE 5 (11): e15399. doi:10.1371/journal.pone.0015399. PMC 2974637. PMID 21079766.
Jump up ^ M.M. Yakimov, K.N. Timmis & P.N. Golyshin (2007). "Obligate oil-degrading marine bacteria".
Curr. Opin. Biotech. 18 (3): 257–266. doi:10.1016/j.copbio.2007.04.006. PMID 17493798.
Jump up ^ Paul Stamets in Mycellium Running, Chapter 7, page 86, Mycoremediation, ISBN
9781580085793, or his TEDx video
http://www.ted.com/talks/paul_stamets_on_6_ways_mushrooms_can_save_the_world?language=en
Bibliography[edit]

Silberberg, Martin. Chemistry: The Molecular Nature Of Matter and Change. New York:
McGraw-Hill Companies, 2004. ISBN 0-07-310169-9
External links[edit]
Aromatic hydrocarbon
From Wikipedia, the free encyclopedia
Jump to: navigation, search
"Arene" redirects here. For other uses, see Arene (disambiguation).
An aromatic hydrocarbon or arene[1] (or sometimes aryl hydrocarbon)[2] is a hydrocarbon with
alternating double and single bonds between carbon atoms forming rings. The term 'aromatic'
was assigned before the physical mechanism determining aromaticity was discovered; the term
was coined as such simply because many of the compounds have a sweet or pleasant odor. The
configuration of six carbon atoms in aromatic compounds is known as a benzene ring, after the
simplest possible such hydrocarbon, benzene. Aromatic hydrocarbons can be monocyclic (MAH)
or polycyclic (PAH).
Some non-benzene-based compounds called heteroarenes, which follow Hückel's rule (for
monocyclic rings: when the number of its π-electrons equals 4n+2), are also called as aromatic
compounds. In these compounds, at least one carbon atom is replaced by one of the heteroatoms
oxygen, nitrogen, or sulfur. Examples of non-benzene compounds with aromatic properties are
furan, a heterocyclic compound with a five-membered ring that includes an oxygen atom, and
pyridine, a heterocyclic compound with a six-membered ring containing one nitrogen atom.[3]
Contents
[hide]








1 Benzene ring model
2 Arene synthesis
3 Arene reactions
o 3.1 Aromatic substitution
o 3.2 Coupling reactions
o 3.3 Hydrogenation
o 3.4 Cycloadditions
4 Benzene and derivatives of benzene
5 Polycyclic aromatic hydrocarbons
6 See also
7 References
8 External links
Benzene ring model[edit]
Benzene
Main article: aromaticity
Benzene, C6H6, is the simplest aromatic hydrocarbon, and it was the first one recognized. The
nature of its bonding was first recognized by August Kekulé in the 19th century. Each carbon
atom in the hexagonal cycle has four electrons to share. One goes to the hydrogen atom, and one
each to the two neighboring carbons. This leaves one to share with one of its two neighboring
carbon atoms, which is why the benzene molecule is drawn with alternating single and double
bonds around the hexagon.
The structure is also illustrated as a circle around the inside of the ring to show six electrons
floating around in delocalized molecular orbitals the size of the ring itself. This also represents
the equivalent nature of the six carbon-carbon bonds all of bond order ~1.5. This equivalency is
well explained by resonance forms. The electrons are visualized as floating above and below the
ring with the electromagnetic fields they generate acting to keep the ring flat.
General properties:
1.
2.
3.
4.
Display aromaticity.
The carbon-hydrogen ratio is high.
They burn with a sooty yellow flame because of the high carbon-hydrogen ratio.
They undergo electrophilic substitution reactions and nucleophilic aromatic substitutions.
The circle symbol for aromaticity was introduced by Sir Robert Robinson and his student James
Armit in 1925[4] and popularized starting in 1959 by the Morrison & Boyd textbook on organic
chemistry. The proper use of the symbol is debated; it is used to describe any cyclic pi system in
some publications, or only those pi systems that obey Hückel's rule on others. Jensen[5] argues
that in line with Robinson's original proposal, the use of the circle symbol should be limited to
monocyclic 6 pi-electron systems. In this way the circle symbol for a 6c–6e bond can be
compared to the Y symbol for a 3c–2e bond.
Arene synthesis[edit]
A reaction that forms an arene compound from an unsaturated or partially unsaturated cyclic
precursor is simply called an aromatization. Many laboratory methods exist for the organic
synthesis of arenes from non-arene precursors. Many methods rely on cycloaddition reactions.
Alkyne trimerization describes the [2+2+2] cyclization of three alkynes, in the Dötz reaction an
alkyne, carbon monoxide and a chromium carbene complex are the reactants.Diels-Alder
reactions of alkynes with pyrone or cyclopentadienone with expulsion of carbon dioxide or
carbon monoxide also form arene compounds. In Bergman cyclization the reactants are an enyne
plus a hydrogen donor.
Another set of methods is the aromatization of cyclohexanes and other aliphatic rings: reagents
are catalysts used in hydrogenation such as platinum, palladium and nickel (reverse
hydrogenation), quinones and the elements sulfur and selenium.[6]
Arene reactions[edit]
Arenes are reactants in many organic reactions.
Aromatic substitution[edit]
In aromatic substitution one substituent on the arene ring, usually hydrogen, is replaced by
another substituent. The two main types are electrophilic aromatic substitution when the active
reagent is an electrophile and nucleophilic aromatic substitution when the reagent is a
nucleophile. In radical-nucleophilic aromatic substitution the active reagent is a radical. An
example of electrophilic aromatic substitution is the nitration of salicylic acid:[7]
Coupling reactions[edit]
In coupling reactions a metal catalyses a coupling between two formal radical fragments.
Common coupling reactions with arenes result in the formation of new carbon–carbon bonds
e.g., alkylarenes, vinyl arenes, biraryls, new carbon–nitrogen bonds (anilines) or new carbon–
oxygen bonds (aryloxy compounds). An example is the direct arylation of perfluorobenzenes [8]
Hydrogenation[edit]
Hydrogenation of arenes create saturated rings. The compound 1-naphthol is completely reduced
to a mixture of decalin-ol isomers.[9]
The compound resorcinol, hydrogenated with Raney nickel in presence of aqueous sodium
hydroxide forms an enolate which is alkylated with methyl iodide to 2-methyl-1,3cyclohexandione:[10]
Cycloadditions[edit]
Cycloaddition reaction are not common. Unusual thermal Diels-Alder reactivity of arenes can be
found in the Wagner-Jauregg reaction. Other photochemical cycloaddition reactions with alkenes
occur through excimers.
Benzene and derivatives of benzene[edit]
Benzene derivatives have from one to six substituents attached to the central benzene core.
Examples of benzene compounds with just one substituent are phenol, which carries a hydroxyl
group, and toluene with a methyl group. When there is more than one substituent present on the
ring, their spatial relationship becomes important for which the arene substitution patterns ortho,
meta, and para are devised. For example, three isomers exist for cresol because the methyl group
and the hydroxyl group can be placed next to each other (ortho), one position removed from each
other (meta), or two positions removed from each other (para). Xylenol has two methyl groups in
addition to the hydroxyl group, and, for this structure, 6 isomers exist.

Representative arene compounds

Toluene

Ethylbenzene

p-Xylene

m-Xylene

Mesitylene

Durene

2-Phenylhexane

Biphenyl

Phenol

Aniline

Nitrobenzene

Benzoic acid

Aspirin

Paracetamol

Picric acid
The arene ring has an ability to stabilize charges. This is seen in, for example, phenol (C6H5-OH),
which is acidic at the hydroxyl (OH), since a charge on this oxygen (alkoxide -O–) is partially
delocalized into the benzene ring.
Polycyclic aromatic hydrocarbons[edit]
An illustration of typical polycyclic aromatic hydrocarbons. Clockwise from top left:
benz(e)acephenanthrylene, pyrene and dibenz(ah)anthracene.
Main article: Polycyclic aromatic hydrocarbon
Polycyclic aromatic hydrocarbons (PAHs) are aromatic hydrocarbons that consist of fused
aromatic rings and do not contain heteroatoms or carry substituents.[11] Naphthalene is the
simplest example of a PAH. PAHs occur in oil, coal, and tar deposits, and are produced as
byproducts of fuel burning (whether fossil fuel or biomass). As pollutants, they are of concern
because some compounds have been identified as carcinogenic, mutagenic, and teratogenic.
PAHs are also found in cooked foods. Studies have shown that high levels of PAHs are found,
for example, in meat cooked at high temperatures such as grilling or barbecuing, and in smoked
fish.[12][13][14]
They are also found in the interstellar medium, in comets, and in meteorites and are a candidate
molecule to act as a basis for the earliest forms of life. In graphene the PAH motif is extended to
large 2D sheets.
See also[edit]




Aromatic substituents: Aryl, Aryloxy and Arenediyl
Asphaltene
Hydrodealkylation
Simple aromatic rings
References[edit]
1.
2.
Jump up ^ Definition IUPAC Gold Book Link
Jump up ^ Mechanisms of Activation of the Aryl Hydrocarbon Receptor by Maria Backlund, Institute of
Environmental Medicine, Karolinska Institutet
3. Jump up ^ HighBeam Encyclopedia: aromatic compound
4. Jump up ^ James Wilkins Armit and Robert Robinson (1925) "Polynuclear heterocyclic aromatic types.
Part II. Some anhydronium bases," Journal of the Chemical Society, Transactions, 127: 1604-1618.
5. Jump up ^ William B. Jensen (April 2009) "The circle symbol for aromaticity," Journal of Chemical
Education, 86(4): 423-424.
6. Jump up ^ Jerry March Advanced Organic Chemistry 3Ed., ISBN 0-471-85472-7
7. Jump up ^ Webb, K.; Seneviratne, V. (1995). "A mild oxidation of aromatic amines". Tetrahedron Letters
36 (14): 2377–2378. doi:10.1016/0040-4039(95)00281-G.edit
8. Jump up ^ Lafrance, M.; Rowley, C.; Woo, T.; Fagnou, K. (2006). "Catalytic intermolecular direct arylation
of perfluorobenzenes.". Journal of the American Chemical Society 128 (27): 8754–8756.
doi:10.1021/ja062509l. PMID 16819868.edit
9. Jump up ^ Organic Syntheses, Coll. Vol. 6, p.371 (1988); Vol. 51, p.103 (1971).
http://orgsynth.org/orgsyn/pdfs/CV6P0371.pdf
10. Jump up ^ Organic Syntheses, Coll. Vol. 5, p.743 (1973); Vol. 41, p.56 (1961).
http://orgsynth.org/orgsyn/pdfs/CV5P0567.pdf
11. Jump up ^ Fetzer, J. C. (2000). "The Chemistry and Analysis of the Large Polycyclic Aromatic
Hydrocarbons". Polycyclic Aromatic Compounds (New York: Wiley) 27 (2): 143.
doi:10.1080/10406630701268255. ISBN 0-471-36354-5.
12. Jump up ^ "Polycyclic Aromatic Hydrocarbons – Occurrence in foods, dietary exposure and health
effects". European Commission, Scientific Committee on Food. December 4, 2002.
13. Jump up ^ Larsson, B. K.; Sahlberg, GP; Eriksson, AT; Busk, LA (1983). "Polycyclic aromatic hydrocarbons in
grilled food". J Agric Food Chem. 31 (4): 867–873. doi:10.1021/jf00118a049. PMID 6352775.
14. Jump up ^ "Polycyclic Aromatic Hydrocarbons (PAHs)". Agency for Toxic Substances and Disease Registry.
1996.
External links[edit]
Media related to Aromatic hydrocarbons at Wikimedia Commons
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Categories:

Aromatic hydrocarbons
BTEX
From Wikipedia, the free encyclopedia
Jump to: navigation, search
BTEX is an acronym that stands for benzene, toluene, ethylbenzene, and xylenes.[1] These
compounds are some of the volatile organic compounds (VOCs) found in petroleum derivatives
such as petrol (gasoline). Toluene, ethylbenzene, and xylenes have harmful effects on the central
nervous system.
BTEX compounds are notorious due to the contamination of soil and groundwater with these
compounds. Contamination typically occurs near petroleum and natural gas production sites,
petrol stations, and other areas with underground storage tanks (USTs) or above-ground storage
tanks (ASTs), containing gasoline or other petroleum-related products.
The amount of 'Total BTEX', the sum of the concentrations of each of the constituents of BTEX,
is sometimes used to aid in assessing the relative risk or seriousness at contaminated locations
and the need of remediation of such sites. Naphthalene may also be included in Total BTEX
analysis yielding results referred to as BTEXN. In the same way, styrene is sometimes added,
making it BTEXS.
See also[edit]
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Alkylation
BTX (chemistry)
Friedel–Crafts reaction
Hydrodealkylation
References[edit]
1. Jump up ^ "BTEX Definition Page". USGS. December 14, 2006.
<img src="//en.wikipedia.org/wiki/Special:CentralAutoLogin/start?type=1x1" alt="" title=""
width="1" height="1" style="border: none; position: absolute;" />
Retrieved from "http://en.wikipedia.org/w/index.php?title=BTEX&oldid=643330670"
Categories:

Aromatic compounds
Volatile organic compound
From Wikipedia, the free encyclopedia
Jump to: navigation, search
Volatile organic compounds (VOCs) are organic chemicals that have a high vapor pressure at
ordinary room temperature. Their high vapor pressure results from a low boiling point, which
causes large numbers of molecules to evaporate or sublimate from the liquid or solid form of the
compound and enter the surrounding air. For example, formaldehyde, which evaporates from
paint, has a boiling point of only –19 °C (–2 °F).
VOCs are numerous, varied, and ubiquitous. They include both human-made and naturally
occurring chemical compounds. Most scents or odours are of VOCs. VOCs play an important
role in communication between plants, [1] and messages from plants to animals. Some VOCs are
dangerous to human health or cause harm to the environment. Anthropogenic VOCs are
regulated by law, especially indoors, where concentrations are the highest. Harmful VOCs
typically are not acutely toxic, but have compounding long-term health effects. Because the
concentrations are usually low and the symptoms slow to develop, research into VOCs and their
effects is difficult.
Contents
[hide]



1 Definitions
o 1.1 Canada
o 1.2 European Union
o 1.3 US
2 Biologically generated VOCs
3 Anthropogenic sources
o






3.1 Specific components
 3.1.1 Paints and coatings
 3.1.2 Chlorofluorocarbons and chlorocarbons
 3.1.3 Benzene
 3.1.4 Methylene chloride
 3.1.5 Perchloroethylene
 3.1.6 MTBE
o 3.2 Indoor air
o 3.3 Regulation of indoor VOC emissions
o 3.4 Formaldehyde
4 Health risks
o 4.1 Reducing exposure
o 4.2 Limit values for VOC emissions
5 Chemical fingerprinting
6 VOC sensors
7 See also
8 References
9 External links
Definitions[edit]
Diverse definitions of the term VOC[2] are in use.
The definitions of VOCs used for control of precursors of photochemical smog used by the EPA,
and states in the US with independent outdoor air pollution regulations include exemptions for
VOCs that are determined to be non-reactive, or of low-reactivity in the smog formation process.
EPA formerly defined these compounds as reactive organic gases (ROG) but changed the
terminology to VOC.[citation needed]
In the USA, different regulations vary between states - most prominent is the VOC regulation by
SCAQMD and by the California Air Resources Board.[3] However, this specific use of the term
VOCs can be misleading, especially when applied to indoor air quality because many chemicals
that are not regulated as outdoor air pollution can still be important for indoor air pollution.
Canada[edit]
Health Canada classes VOCs as organic compounds that have boiling points roughly in the range
of 50 to 250 °C (122 to 482 °F). The emphasis is placed on commonly encountered VOCs that
would have an effect on air quality.[4]
European Union[edit]
A VOC is any organic compound having an initial boiling point less than or equal to 250 °C (482
°F) measured at a standard atmospheric pressure of 101.3 kPa[5] and can do damage to visual or
audible senses.[citation needed]
US[edit]
VOCs (or specific subsets of the VOCs) are legally defined in the various laws and codes under
which they are regulated. Other definitions may be found from government agencies
investigating or advising about VOCs.[6] The United States Environmental Protection Agency
(EPA) regulates VOCs in the air, water, and land. The Safe Drinking Water Act implementation
includes a list labeled "VOCs in connection with contaminants that are organic and volatile."[7]
The EPA also publishes testing methods for chemical compounds, some of which refer to
VOCs.[8]
In addition to drinking water, VOCs are regulated in discharges to waters (sewage treatment and
stormwater disposal), as hazardous waste,[9] but not in non industrial indoor air.[10] The United
States Department of Labor and its Occupational Safety and Health Administration (OSHA)
regulate VOC exposure in the workplace. Volatile organic compounds that are hazardous
material would be regulated by the Pipeline and Hazardous Materials Safety Administration
while being transported.
Biologically generated VOCs[edit]
Not counting methane, biological sources emit an estimated 1150 teragrams of carbon per year in
the form of VOCs.[11] The majority of VOCs are produced by plants, the main compound being
isoprene. The remainder are produced by animals, microbes, and fungi, such as molds.
The strong odor emitted by many plants consists of green leaf volatiles, a subset of VOCs.
Emissions are affected by a variety of factors, such as temperature, which determines rates of
volatilization and growth, and sunlight, which determines rates of biosynthesis. Emission occurs
almost exclusively from the leaves, the stomata in particular. A major class of VOCs is terpenes,
such as myrcene.[12] Providing a sense of scale, a forest 62,000 km2 in area (the U.S. state of
Pennsylvania) is estimated to emit 3,400,000 kilograms of terpenes on a typical August day
during the growing season.[13] VOCs should be a factor in choosing which trees to plant in urban
areas.[14] Induction of genes producing volatile organic compounds, and subsequent increase in
volatile terpenes has been achieved in maize using (Z)-3-Hexen-1-ol and other plant hormones.[15]
Anthropogenic sources[edit]
Anthropogenic sources emit about 142 teragrams of carbon per year in the form of VOCs.[11]
Specific components[edit]
Paints and coatings[edit]
A major source of man-made VOCs are coatings, especially paints and protective coatings.
Solvents are required to spread a protective or decorative film. Approximately 12 billion litres of
paints are produced annually. Typical solvents are aliphatic hydrocarbons, ethyl acetate, glycol
ethers, and acetone. Motivated by cost, environmental concerns, and regulation, the paint and
coating industries are increasingly shifting toward aqueous solvents.[16]
Chlorofluorocarbons and chlorocarbons[edit]
Chlorofluorocarbons, which are banned or highly regulated, were widely used cleaning products
and refrigerants. Tetrachloroethene is used widely in dry cleaning and by industry. Industrial use
of fossil fuels produces VOCs either directly as products (e.g., gasoline) or indirectly as
byproducts (e.g., automobile exhaust).[citation needed]
Benzene[edit]
Main article: Benzene
One VOC that is a known human carcinogen is benzene, which is a chemical found in
environmental tobacco smoke, stored fuels, and exhaust from cars. Benzene also has natural
sources such as volcanoes and forest fires. It is frequently used to make other chemicals in the
production of plastics, resins, and synthetic fibers. Benzene evaporates into the air quickly and
the vapor of benzene is heavier than air allowing the compound to sink into low-lying areas.
Benzene has also been known to contaminate food and water and if digested can lead to
vomiting, dizziness, sleepiness, rapid heartbeat, and at high levels, even death may occur.[citation
needed]
Methylene chloride[edit]
Methylene chloride is another VOC that is highly dangerous to human health. It can be found in
adhesive removers and aerosol spray paints and the chemical has been proven to cause cancer in
animals. In the human body, methylene chloride is converted to carbon monoxide and a person
will suffer the same symptoms as exposure to carbon monoxide. If a product that contains
methylene chloride needs to be used the best way to protect human health is to use the product
outdoors. If it must be used indoors, proper ventilation is essential to keeping exposure levels
down.[citation needed]
Perchloroethylene[edit]
Perchloroethylene is a volatile organic compound that has been linked to causing cancer in
animals. It is also suspected to cause many of the breathing related symptoms of exposure to
VOCs.[citation needed] Perchloroethylene is used mostly in dry cleaning. While dry cleaners recapture
perchloroethylene in the dry cleaning process to reuse it, some environmental release is
unavoidable. Studies show that people breathe in low levels of this VOC in homes where drycleaned clothes are stored and while wearing dry-cleaned clothing.[citation needed]
MTBE[edit]
MTBE was banned in the US around 2004 in order to limit further contamination of drinking
water aquifers primarily from leaking underground gasoline storage tanks where MTBE was
used as an octane booster and oxygenated-additive.[citation needed]
Indoor air[edit]
Main article: Indoor air quality
Since many people spend much of their time indoors, long-term exposure to VOCs in the indoor
environment can contribute to sick building syndrome.[17] In offices, VOC results from new
furnishings, wall coverings, and office equipment such as photocopy machines, which can offgas VOCs into the air.[18][19] Good ventilation and air-conditioning systems are helpful at reducing
VOCs in the indoor environment.[18] Studies also show that relative leukemia and lymphoma can
increase through prolonged exposure of VOCs in the indoor environment.[20]
There are two standardized methods for measuring VOCs, one by the National Institute for
Occupational Safety and Health (NIOSH) and another by Occupational Safety and Health
Administration (OSHA). Each method uses a single component solvent; butanol and hexane
cannot be sampled, however, on the same sample matrix using the NIOSH or OSHA method.[21]
The aromatic VOC compound benzene, emitted from exhaled cigarette smoke is labeled as
carcinogenic, and is ten times higher in smokers than in nonsmokers.[18]
The United States Environmental Protection Agency (EPA) has found concentrations of VOCs in
indoor air to be 2 to 5 times greater than in outdoor air and sometimes far greater. During certain
activities indoor levels of VOCs may reach 1,000 times that of the outside air.[22] Studies have
shown that individual VOC emissions by themselves are not that high in an indoor environment,
but the indoor total VOC (TVOC) concentrations can be up to five times higher than the VOC
outdoor levels.[23] New buildings especially, contribute to the highest level of VOC off-gassing in
an indoor environment because of the abundant new materials generating VOC particles at the
same time in such a short time period.[17] In addition to new buildings, we also use many
consumer products that emit VOC compounds, therefore the total concentration of VOC levels is
much greater within the indoor environment.[17]
VOC concentration in an indoor environment during winter is three to four times higher than the
VOC concentrations during the summer.[24] High indoor VOC levels are attributed to the low
rates of air exchange between the indoor and outdoor environment as a result of tight-shut
windows and the increasing use of humidifiers.[25]
Regulation of indoor VOC emissions[edit]
In most countries, a separate definition of VOCs is used with regard to indoor air quality that
comprises each organic chemical compound that can be measured as follows: Adsorption from
air on Tenax TA, thermal desorption, gas chromatographic separation over a 100% nonpolar
column (dimethylpolysiloxane). VOC (volatile organic compounds) are all compounds that
appear in the gas chromatogram between and including n-hexane and n-hexadecane. Compounds
appearing earlier are called VVOC (very volatile organic compounds) compounds appearing
later are called SVOC (semi-volatile organic compounds). See also these standards: ISO 160006, ISO 13999-2, VDI 4300-6, German AgBB evaluating scheme, German DIBt approval scheme,
GEV testing method for the EMICODE. Some overviews over VOC emissions rating schemes [26]
have been collected and compared.
France and Germany have enacted regulations to limit VOC emissions from commercial
products, and industry has developed numerous voluntary ecolabels and rating systems, such as
EMICODE,[27] M1,[28] Blue Angel[29] and Indoor Air Comfort[30] In the United States, several
standards exist; California Standard CDPH Section 01350[31] is the most popular one. Over the
last few decades, these regulations and standards changed the marketplace, leading to an
increasing number of low-emitting products: The leading voluntary labels report that licenses to
several hundreds of low-emitting products have been issued (see the respective webpages such as
MAS Certified Green.- Certified Products[32]).
Formaldehyde[edit]
Many building materials such as paints, adhesives, wall boards, and ceiling tiles slowly emit
formaldehyde, which irritates the mucous membranes and can make a person irritated and
uncomfortable.[18] Formaldehyde emissions from wood are in the range of 0.02 – 0.04 ppm.
Relative humidity within an indoor environment can also affect the emissions of formaldehyde.
High relative humidity and high temperatures allow more vaporization of formaldehyde from
wood-materials.[33]
Health risks[edit]
Respiratory, allergic, or immune effects in infants or children are associated with man-made
VOCs and other indoor or outdoor air pollutants.[34]
Some VOCs, such as styrene and limonene, can react with nitrogen oxides or with ozone to
produce new oxidation products and secondary aerosols, which can cause sensory irritation
symptoms.[18][35] Unspecified VOCs are important in the creation of smog.[36]
Health effects include eye, nose, and throat irritation; headaches, loss of coordination, nausea;
damage to liver, kidney, and central nervous system. Some organics can cause cancer in animals;
some are suspected or known to cause cancer in humans. Key signs or symptoms associated with
exposure to VOCs include conjunctival irritation, nose and throat discomfort, headache, allergic
skin reaction, dyspnea, declines in serum cholinesterase levels, nausea, vomiting, nose bleeding,
fatigue, dizziness.[citation needed]
The ability of organic chemicals to cause health effects varies greatly from those that are highly
toxic, to those with no known health effects. As with other pollutants, the extent and nature of
the health effect will depend on many factors including level of exposure and length of time
exposed. Eye and respiratory tract irritation, headaches, dizziness, visual disorders, and memory
impairment are among the immediate symptoms that some people have experienced soon after
exposure to some organics. At present, not much is known about what health effects occur from
the levels of organics usually found in homes. Many organic compounds are known to cause
cancer in animals; some are suspected of causing, or are known to cause, cancer in humans.[37]
Reducing exposure[edit]
To reduce exposure to these toxins, one should buy products that contain Low-VOCs or No
VOCs. Only the quantity which will soon be needed should be purchased, eliminating
stockpiling of these chemicals. Use products with VOCs in well ventilated areas. When
designing homes and buildings, design teams can implement the best possible ventilation plans,
call for the best mechanical systems available, and design assemblies to reduce the amount of
infiltration into the building. These methods will help improve indoor air quality, but by
themselves they cannot keep a building from becoming an unhealthy place to breathe.[citation needed]
Limit values for VOC emissions[edit]
Limit values for VOC emissions into indoor air are published by e.g. AgBB, AFSSET, California
Department of Public Health, and others. These regulations have prompted several companies to
adapt with VOC level reductions in products that have VOCs in their formula, such Benjamin
Moore & Co. in the paint industry and Weld-On in the adhesive industry.[citation needed]
Chemical fingerprinting[edit]
The exhaled human breath contains a few hundred volatile organic compounds and is used in
breath analysis to serve as a VOC biomarker to test for diseases such as lung cancer.[38] One study
has shown that "volatile organic compounds ... are mainly blood borne and therefore enable
monitoring of different processes in the body."[39] And it appears that VOC compounds in the
body "may be either produced by metabolic processes or inhaled/absorbed from exogenous
sources" such as environmental tobacco smoke.[38][40] Research is still in the process to determine
whether VOCs in the body are contributed by cellular processes or by the cancerous tumors in
the lung or other organs.
VOC sensors[edit]
Main article: VOC sensors
VOCs in the environment or certain atmospheres can be detected based on different principles
and interactions between the organic compounds and the sensor components. There are
electronic devices that can detect ppm concentrations despite the non-selectivity. Others can
predict with reasonable accuracy the molecular structure of the volatile organic compounds in
the environment or enclosed atmospheres[41] and could be used as accurate monitors of the
Chemical Fingerprint and further as health monitoring devices.
Solid-phase microextraction (SPME) techniques are used to collect VOCs at low concentrations
for analysis.[42]
See also[edit]
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Aroma compound
Criteria air contaminants
Dutch standards
Fugitive emissions
NMVOC (non-methane volatile organic compounds)
NoVOC (classification)
Organic compound
Photochemical smog
Volatility (chemistry)
NTA Inc VOC Testing Laboratory
Volatile Organic Compounds Protocol
Ozone
References[edit]
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
12.
13.
14.
15.
16.
17.
Jump up ^ "Plants: A Different Perspective". Content.yudu.com. Retrieved 2012-07-03.
Jump up ^ "What does VOC mean?". Eurofins.com. Retrieved 2012-07-03.
Jump up ^ California ARB
Jump up ^ Health Canada
Jump up ^ Directive 2004/42/CE of the European Parliament and of the Council of 21 April 2004 on the
limitation of emissions of volatile organic compounds due to the use of organic solvents in certain paints
and varnishes and vehicle refinishing products EUR-Lex, European Union Publications Office. Retrieved on
2010-09-28.
Jump up ^ USGS definition
Jump up ^ 40CFR141
Jump up ^ "Clean Water Act Analytical Methods | CWA Methods | US EPA". Epa.gov. Retrieved 2012-0703.
Jump up ^ CERCLA and RCRA
Jump up ^ "Volatile Organic Compounds | Indoor Air | US Environmental Protection Agency". Epa.gov.
2010-11-17. Retrieved 2012-07-03.
^ Jump up to: a b Goldstein, Allen H.; Galbally, Ian E. (2007). "Known and Unexplored Organic Constituents
in the Earth's Atmosphere". Environmental Science & Technology 41 (5): 1514–21.
doi:10.1021/es072476p. PMID 17396635.
Jump up ^ Niinemets, Ülo; Loreto, Francesco; Reichstein, Markus (2004). "Physiological and
physicochemical controls on foliar volatile organic compound emissions". Trends in Plant Science 9 (4):
180–6. doi:10.1016/j.tplants.2004.02.006. PMID 15063868.
Jump up ^ Behr, Arno; Johnen, Leif (2009). "Myrcene as a Natural Base Chemical in Sustainable Chemistry:
A Critical Review". ChemSusChem 2 (12): 1072–95. doi:10.1002/cssc.200900186. PMID 20013989.
Jump up ^ Xie, Jenny. "Not All Tree Planting Programs Are Great for the Environment". City Lab. Atlantic
Media. Retrieved 20 June 2014.
Jump up ^ Farag, Mohamed A.; Fokar, Mohamed; Abd, Haggag; Zhang, Huiming; Allen, Randy D.; Paré,
Paul W. (2004). "(Z)-3-Hexenol induces defense genes and downstream metabolites in maize". Planta 220
(6): 900–9. doi:10.1007/s00425-004-1404-5. PMID 15599762.
Jump up ^ Stoye, D.; Funke, W.; Hoppe, L. et al. (2006). "Paints and Coatings". Ullmann's Encyclopedia of
Industrial Chemistry. doi:10.1002/14356007.a18_359.pub2. ISBN 3527306730.edit
^ Jump up to: a b c Wang, Shaobin; Ang, H.M.; Tade, Moses O. (2007). "Volatile organic compounds in
indoor environment and photocatalytic oxidation: State of the art". Environment International 33 (5):
694–705. doi:10.1016/j.envint.2007.02.011. PMID 17376530.
18. ^ Jump up to: a b c d e Dales, R.; Liu, L.; Wheeler, A. J.; Gilbert, N. L. (2008). "Quality of indoor residential air
and health". Canadian Medical Association Journal 179 (2): 147–52. doi:10.1503/cmaj.070359. PMC
2443227. PMID 18625986.
19. Jump up ^ Yu, Chuck; Crump, Derrick (1998). "A review of the emission of VOCs from polymeric materials
used in buildings". Building and Environment 33 (6): 357–74. doi:10.1016/S0360-1323(97)00055-3.
20. Jump up ^ Irigaray, P.; Newby, J.A.; Clapp, R.; Hardell, L.; Howard, V.; Montagnier, L.; Epstein, S.;
Belpomme, D. (2007). "Lifestyle-related factors and environmental agents causing cancer: An overview".
Biomedicine & Pharmacotherapy 61 (10): 640–58. doi:10.1016/j.biopha.2007.10.006. PMID 18055160.
21. Jump up ^ Who Says Alcohol and Benzene Don't Mix?[dead link]
22. Jump up ^ An Introduction to Indoor Air Quality
23. Jump up ^ Jones, A.P. (1999). "Indoor air quality and health". Atmospheric Environment 33 (28): 4535–64.
doi:10.1016/S1352-2310(99)00272-1.
24. Jump up ^ Barro, R.; Regueiro, J.; Llompart, M. A.; Garcia-Jares, C. (2009). "Analysis of industrial
contaminants in indoor air: Part 1. Volatile organic compounds, carbonyl compounds, polycyclic aromatic
hydrocarbons and polychlorinated biphenyls". Journal of Chromatography A 1216 (3): 540–566.
doi:10.1016/j.chroma.2008.10.117. PMID 19019381.edit
25. Jump up ^ Schlink, U; Rehwagen, M; Damm, M; Richter, M; Borte, M; Herbarth, O (2004). "Seasonal cycle
of indoor-VOCs: Comparison of apartments and cities". Atmospheric Environment 38 (8): 1181–90.
doi:10.1016/j.atmosenv.2003.11.003.
26. Jump up ^ "Ecolabels, Quality Labels, and VOC emissions". Eurofins.com. Retrieved 2012-07-03.
27. Jump up ^ EMICODE
28. Jump up ^ M1 Finnish label
29. Jump up ^ Blue Angel German ecolabel
30. Jump up ^ Indoor Air Comfort
31. Jump up ^ CDPH Section 01350
32. Jump up ^ IAQ Certified Products
33. Jump up ^ Wolkoff, Peder; Kjaergaard, Søren K. (2007). "The dichotomy of relative humidity on indoor air
quality". Environment International 33 (6): 850–7. doi:10.1016/j.envint.2007.04.004. PMID 17499853.
34. Jump up ^ Mendell, M. J. (2007). "Indoor residential chemical emissions as risk factors for respiratory and
allergic effects in children: A review". Indoor Air 17 (4): 259–77. doi:10.1111/j.1600-0668.2007.00478.x.
PMID 17661923.
35. Jump up ^ Wolkoff, P.; Wilkins, C. K.; Clausen, P. A.; Nielsen, G. D. (2006). "Organic compounds in office
environments - sensory irritation, odor, measurements and the role of reactive chemistry". Indoor Air 16
(1): 7–19. doi:10.1111/j.1600-0668.2005.00393.x. PMID 16420493.
36. Jump up ^ "What is Smog?", Canadian Council of Ministers of the Environment, CCME.ca
37. Jump up ^ EPA -- An Introduction to Indoor Air Quality Pollutants and Sources of Indoor Air Pollution
Volatile Organic Compounds (VOCs)
38. ^ Jump up to: a b Buszewski, B. A.; Kesy, M.; Ligor, T.; Amann, A. (2007). "Human exhaled air analytics:
Biomarkers of diseases". Biomedical Chromatography 21 (6): 553–566. doi:10.1002/bmc.835. PMID
17431933.edit
39. Jump up ^ Miekisch, W.; Schubert, J. K.; Noeldge-Schomburg, G. F. E. (2004). "Diagnostic potential of
breath analysis—focus on volatile organic compounds". Clinica Chimica Acta 347: 25.
doi:10.1016/j.cccn.2004.04.023.edit
40. Jump up ^ Mazzone, P. J. (2008). "Analysis of Volatile Organic Compounds in the Exhaled Breath for the
Diagnosis of Lung Cancer". Journal of Thoracic Oncology 3 (7): 774–780.
doi:10.1097/JTO.0b013e31817c7439. PMID 18594325.
41. Jump up ^ MartíNez-Hurtado, J. L.; Davidson, C. A. B.; Blyth, J.; Lowe, C. R. (2010). "Holographic Detection
of Hydrocarbon Gases and Other Volatile Organic Compounds". Langmuir 26 (19): 15694–9.
doi:10.1021/la102693m. PMID 20836549.
42. Jump up ^ Lattuati-Derieux, Agnès; Bonnassies-Termes, Sylvette; Lavédrine, Bertrand (2004).
"Identification of volatile organic compounds emitted by a naturally aged book using solid-phase
microextraction/gas chromatography/mass spectrometry". Journal of Chromatography A 1026 (1–2): 9–
18. doi:10.1016/j.chroma.2003.11.069. PMID 14870711.
External links[edit]
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Volatile Organic Compounds (VOCs) web site of the Chemicals Control Branch of Environment
Canada[dead link]
An Introduction to Indoor Air Quality, US EPA website
VOC in paints, finishes and adhesives
VOC emissions testing
EPA NE: Ground-level Ozone (Smog) Information
emission from crude oil tankers
VOC emissions and calculations
VOCs, ozone and air pollution information from the American Lung Association of New England
VOC Tests
Post doc in Volatile organic compound in Food
VOC emissions from printing processes, European legislation and biological treatment
Examples of product labels with low VOC emission criteria
Information about VOCs in Drinking Water
Formaldehyde and VOCs in Indoor Air Quality Determinations by GC/MS
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