1,1,1-Trichloroethane

Not to be confused with 1,1,1-Trifluoroethane.

1,1,1-Trichloroethane

Skeletal formula of 1,1,1-trichloroethane Space-filling model of 1,1,1-trichloroethane
Names
IUPAC name 1,1,1-trichloroethane
Other names methyl chloroform, chlorothene, Solvent 111, Genklene, R-140a
Identifiers
CAS Number	71-55-6 Y
3D model (JSmol)	Interactive image
ChEBI	CHEBI:36015 Y
ChEMBL	ChEMBL16080 Y
ChemSpider	6042 Y
ECHA InfoCard	100.000.688
IUPHAR/BPS	5482
KEGG	C18246 Y
PubChem CID	6278
UNII	113C650IR1 Y
CompTox Dashboard (EPA)	DTXSID0021381
InChI InChI=1S/C2H3Cl3/c1-2(3,4)5/h1H3 Y Key: UOCLXMDMGBRAIB-UHFFFAOYSA-N Y InChI=1/C2H3Cl3/c1-2(3,4)5/h1H3 Key: UOCLXMDMGBRAIB-UHFFFAOYAP
SMILES ClC(Cl)(Cl)C
Properties
Chemical formula	C2H3Cl3 or CH3CCl3
Molar mass	133.40 g/mol
Appearance	Colorless liquid
Odor	mild, chloroform-like
Density	1.32 g/cm3
Melting point	−33 °C (−27 °F; 240 K)
Boiling point	74 °C (165 °F; 347 K)
Solubility in water	0.4% (20°C) 0.480 g/litre at 20 °C
Vapor pressure	100 mmHg (20°C)
Hazards
Occupational safety and health (OHS/OSH):
Main hazards	Ozone layer impact. Irritant to the upper respiratory tract. Causes severe irritation and swelling to eyes.
NFPA 704 (fire diamond)	3 1 1
Explosive limits	7.5%-12.5%
Lethal dose or concentration (LD, LC):
LD50 (median dose)	9600 mg/kg (oral, rat) 6000 mg/kg (oral, mouse) 5660 mg/kg (oral, rabbit)
LC50 (median concentration)	3911 ppm (mouse, 2 hr) 18000 ppm (rat, 4 hr)
NIOSH (US health exposure limits):
PEL (Permissible)	TWA 350 ppm (1900 mg/m3)
REL (Recommended)	C 350 ppm (1900 mg/m3) [15-minute]
IDLH (Immediate danger)	700 ppm
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa). Y verify (what is YN ?) Infobox references

The organic compound 1,1,1-trichloroethane, also known as methyl chloroform, is a chloroalkane. This colourless, sweet-smelling liquid was once produced industrially in large quantities for use as a solvent. It is regulated by the Montreal Protocol as an ozone-depleting substance and its use is being rapidly phased out.

Production

1,1,1-Trichloroethane was first reported by Henri Victor Regnault in 1840. Industrially, it is usually produced in a two-step process from vinyl chloride. In the first step, vinyl chloride reacts with hydrogen chloride at 20-50 °C to produce 1,1-dichloroethane:

CH₂=CHCl + HCl → CH₃CHCl₂

This reaction is catalyzed by a variety of Lewis acids, mainly aluminium chloride, iron(III) chloride, or zinc chloride. The 1,1-dichloroethane is then converted to 1,1,1-trichloroethane by reaction with chlorine under ultraviolet irradiation:

CH₃CHCl₂ + Cl₂ → CH₃CCl₃ + HCl

This reaction proceeds at 80-90% yield, and the hydrogen chloride byproduct can be recycled to the first step in the process. The major side-product is the related compound 1,1,2-trichloroethane, from which the 1,1,1-trichloroethane can be separated by distillation.

A somewhat smaller amount of 1,1,1-trichloroethane is produced from the reaction of vinylidene chloride and hydrogen chloride in the presence of an iron(III) chloride catalyst:

CH₂=CCl₂ + HCl → CH₃CCl₃

1,1,1-Trichloroethane is marketed with stabilizers since it is unstable with respect to dehydrochlorination and attacks some metals. Stabilizers comprise up to 8% of the formulation, including acid scavengers (epoxides, amines) and complexants. The Montreal Protocol targeted 1,1,1-trichloroethane as one of those compounds responsible for ozone depletion and banned its use beginning in 1996. Since then, its manufacture and use has been phased out throughout most of the world.

Uses

1,1,1-trichloroethane is generally considered a non-polar solvent. Owing to the good polarizability of the chlorine atoms, it is a superior solvent for organic compounds that do not dissolve well in hydrocarbons such as hexane. It is an excellent solvent for many organic materials and also one of the least toxic of the chlorinated hydrocarbons. Prior to the Montreal Protocol, it was widely used for cleaning metal parts and circuit boards, as a photoresist solvent in the electronics industry, as an aerosol propellant, as a cutting fluid additive, and as a solvent for inks, paints, adhesives and other coatings. 1,1,1-trichloroethane is also used as an insecticidal fumigant.

It was also the standard cleaner for photographic film (movie/slide/negatives, etc.). Other commonly available solvents damage emulsion, and thus are not suitable for this application. The standard replacement, Forane 141 is much less effective, and tends to leave a residue. 1,1,1-trichloroethane was used as a thinner in correction fluid products such as liquid paper. Many of its applications previously used carbon tetrachloride (which was banned in US consumer products in 1970). In turn, 1,1,1-trichloroethane itself is now being replaced by other solvents in the laboratory.

Safety

Although not as toxic as many similar compounds, inhaled or ingested 1,1,1-trichloroethane does act as a central nervous system depressant and can cause effects similar to those of ethanol intoxication, including dizziness, confusion, and in sufficiently high concentrations, unconsciousness and death. Fatal poisonings and illnesses linked to intentional inhalation of trichloroethane have been reported. The removal of the chemical from correction fluid commenced due to Proposition 65 declaring it hazardous and toxic

Prolonged skin contact with the liquid can result in the removal of fats from the skin, resulting in chronic skin irritation. Studies on laboratory animals have shown that 1,1,1-trichloroethane is not retained in the body for long periods of time. However, chronic exposure has been linked to abnormalities in the liver, kidneys, and heart. Pregnant women should avoid exposure, as the compound has been linked to birth defects in laboratory animals (see teratogenesis).

Further reading

• Doherty, R.E. (2000). "A History of the Production and Use of Carbon Tetrachloride, Tetrachloroethylene, Trichloroethylene and 1,1,1-Trichloroethane in the United States: Part 2 - Trichloroethylene and 1,1,1-Trichloroethane". Journal of Environmental Forensics. 1: 83–93. doi:10.1006/enfo.2000.0011.