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Tetrachloroethylene
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Names | |||
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Preferred IUPAC name
Tetrachloroethene | |||
Other names
Perchloroethene; perchloroethylene; perc; PCE; carbon dichloride; carboneum dichloratum
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Identifiers | |||
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3D model (JSmol)
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1304635 | |||
ChEBI | |||
ChEMBL | |||
ChemSpider |
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ECHA InfoCard | 100.004.388 | ||
EC Number |
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101142 | |||
KEGG |
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PubChem CID
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RTECS number |
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UNII | |||
UN number | 1897 | ||
CompTox Dashboard (EPA)
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Properties | |||
C2Cl4 | |||
Molar mass | 165.82 g/mol | ||
Appearance | Clear, colorless liquid | ||
Odor | Strong and sweetish, chloroform-like | ||
Density | 1.622 g/cm3 | ||
Melting point | −19 °C (−2 °F; 254 K) | ||
Boiling point | 121.1 °C (250.0 °F; 394.2 K) | ||
0.15 g/L (25 °C) | |||
Vapor pressure | 14 mmHg (20 °C) | ||
−81.6·10−6 cm3/mol | |||
Viscosity | 0.89 cP at 25 °C | ||
Hazards | |||
GHS labelling: | |||
Warning | |||
H351, H411 | |||
P201, P202, P273, P281, P308+P313, P391, P405, P501 | |||
NFPA 704 (fire diamond) | |||
Flash point | Not flammable | ||
Lethal dose or concentration (LD, LC): | |||
LC50 (median concentration)
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4000 ppm (rat, 4 hr) 5200 ppm (mouse, 4 hr) 4964 ppm (rat, 8 hr) |
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NIOSH (US health exposure limits): | |||
PEL (Permissible)
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TWA 100 ppm C 200 ppm (for 5 minutes in any 3-hour period), with a maximum peak of 300 ppm |
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REL (Recommended)
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Ca Minimize workplace exposure concentrations. | ||
IDLH (Immediate danger)
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Ca [150 ppm] | ||
Safety data sheet (SDS) | External MSDS | ||
Related compounds | |||
Related organohalides
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Tetrafluoroethylene Tetrabromoethylene Tetraiodoethylene |
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Related compounds
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Trichloroethylene Dichloroethene Tetrachloroethane |
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Supplementary data page | |||
Tetrachloroethylene (data page) | |||
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
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Tetrachloroethylene, also known under the systematic name tetrachloroethene, or perchloroethylene, and abbreviations such as "perc" (or "PERC"), and "PCE", is a chlorocarbon with the formula Cl2C=CCl2. It is a colorless liquid widely used for dry cleaning of fabrics, hence it is sometimes called "dry-cleaning fluid". It also has its uses as an effective automotive brake cleaner. It has a sweet odor, similar to the smell of chloroform, detectable by most people at a concentration of 1 part per million (1 ppm). Worldwide production was about 1 million metric tons (980,000 long tons; 1,100,000 short tons) in 1985.
History and production
French chemist Henri Victor Regnault first synthesized tetrachloroethylene in 1839 by thermal decomposition of hexachloroethane following Michael Faraday's 1820 synthesis of protochloride of carbon (carbon tetrachloride).
- C2Cl6 → C2Cl4 + Cl2
Faraday was previously falsely credited for the synthesis of tetrachloroethylene, which in reality, was carbon tetrachloride. While trying to make Faraday's "protochloride of carbon", Regnault found that his compound was different from Faraday's. Victor Regnault stated "according to Faraday, the chloride of carbon boiled around 70 °C (158 °F) to 77 °C (171 °F) degrees Celsius but mine did not begin to boil until 120 °C (248 °F) ".
Tetrachloroethylene can be made by passing chloroform vapour through a red-hot tube, the side products include hexachlorobenzene and hexachloroethane, as reported in 1886.
Most tetrachloroethylene is produced by high temperature chlorinolysis of light hydrocarbons. The method is related to Faraday's discovery since hexachloroethane is generated and thermally decomposes. Side products include carbon tetrachloride, hydrogen chloride, and hexachlorobutadiene.
Several other methods have been developed. When 1,2-dichloroethane is heated to 400 °C with chlorine, tetrachloroethylene is produced by the chemical reaction:
- ClCH2CH2Cl + 3 Cl2 → Cl2C=CCl2 + 4 HCl
This reaction can be catalyzed by a mixture of potassium chloride and aluminium chloride or by activated carbon. Trichloroethylene is a major byproduct, which is separated by distillation.
Uses
Tetrachloroethylene is an excellent solvent for organic materials. Otherwise it is volatile, highly stable and nonflammable, and has low toxicity. For these reasons, it is widely used in dry cleaning. It is also used to degrease metal parts in the automotive and other metalworking industries, usually as a mixture with other chlorocarbons. It appears in a few consumer products including paint strippers, aerosol preparations and spot removers.
Historical applications
Tetrachloroethylene was once extensively used as an intermediate in the manufacture of HFC-134a and related refrigerants. In the early 20th century, tetrachloroethene was used for the treatment of hookworm infestation.
Health and safety
The acute toxicity of tetrachloroethylene is moderate to low. Reports of human injury are uncommon despite its wide usage in dry cleaning and degreasing.
Despite the advantages of tetrachloroethylene, many have called for its replacement from widespread commercial use. It has been described as a possible "neurotoxicant, liver and kidney toxicant, and reproductive and developmental toxicant ... a 'potential occupational carcinogen'"..
Testing for exposure
Tetrachloroethylene exposure can be evaluated by a breath test, analogous to breath-alcohol measurements. Also, for acute exposures, tetrachloroethylene in expired air can be measured. Tetrachloroethylene can be detected in the breath for weeks following a heavy exposure. Tetrachloroethylene and trichloroacetic acid (TCA), a breakdown product of tetrachloroethylene, can be detected in the blood.
In Europe, the Scientific Committee on Occupational Exposure Limits (SCOEL) recommends for tetrachloroethylene an occupational exposure limit (8 hour time-weighted average) of 20 ppm and a short-term exposure limit (15 min) of 40 ppm.
Remediation and degradation
In principle, tetrachloroethylene contamination can be remediated by chemical treatment. Chemical treatment involves reducing metals such as iron powder.
In addition to bioremediation, tetrachloroethylene hydrolyzes on contact with soil.
Bioremediation usually entails reductive dechlorination usually under anaerobic conditions.Dehalococcoides sp. under aerobic conditions by cometabolism by Pseudomonas sp. Products of biodegradation products include trichloroethylene, cis-1,2-dichloroethene and vinyl chloride; full degradation converts tetrachloroethylene into ethylene and chloride.
Further reading
- "Toxicological Profile for Tetrachloroethene". Agency for Toxic Substances and Disease Registry. 1997.
- 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 1 - Historical Background; Carbon Tetrachloride and Tetrachloroethylene". Environmental Forensics. 1 (2): 69–81. doi:10.1006/enfo.2000.0010. S2CID 97680726.
External links
- ATSDR Case Studies in Environmental Medicine: Tetrachloroethylene Toxicity U.S. Department of Health and Human Services
- Tetrachloroethylene (Perchloroethylene) U.S. Department of Health and Human Services
- Australian National Pollutant Inventory (NPI) page
- Sustainable uses and Industry recommendations
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