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{{short description|Chemical compound in very wide use}}
{{use dmy dates |date=September 2022}}
{{chembox
{{chembox
| Verifiedfields = changed
| verifiedrevid = 418144966
| Watchedfields = changed
| Name = Tetrachloroethylene
| verifiedrevid = 433348706
| ImageFileL1 = Tetrachloroethylene.svg
| Name = Tetrachloroethylene
| ImageSizeL1 = 100px
| ImageNameL1 = Tetrachloroethylene
| ImageFileL1 = Tetrachloroethylene.svg
| ImageFileR1 = Tetrachloroethylene-3D-vdW.png
| ImageNameL1 = Tetrachloroethylene
| ImageFileR1 = Tetrachloroethylene-3D-vdW.png
| ImageSizeR1 = 120px
| ImageNameR1 = Tetrachloroethylene
| ImageNameR1 = Tetrachloroethylene
| ImageCaptionR1 = {{legend|black|[[Carbon]], C}}{{legend|lime|[[Chlorine]], Cl}}
| IUPACName = Tetrachloroethene
| ImageFile2 = Tetrakloroetilen2.jpg
| OtherNames = Perchloroethene; Perchloroethylene; Perc; PCE
| ImageSize2 = 150
| Section1 = {{Chembox Identifiers
| PIN = Tetrachloroethene
| SMILES = Cl/C(Cl)=C(/Cl)Cl
| OtherNames = Carbon bichloride; Carbon dichloride (''Carboneum Dichloratum''); Dicarbon tetrachloride;<ref>C. Chabrie "General Method for the Preparation of Carbon Fluorides" in Journal - Chemical Society, London. (1890). UK: Chemical Society.</ref> Ethylene tetrachloride; Perchlor; Perchloroethene; Perchloroethylene; Chlorethose<ref>Justus Liebigs Annalen der Chemie. (1845). Germany: Verlag Chemie. Page 277 </ref>
| ChemSpiderID_Ref = {{chemspidercite|correct|chemspider}}
|Section1={{Chembox Identifiers
| Abbreviations= PCE; Perc; Per
| CASNo_Ref = {{cascite|correct|CAS}}
| CASNo = 127-18-4
| Beilstein = 1304635
| ChEBI_Ref = {{ebicite|changed|EBI}}
| ChEBI = 17300
| ChEMBL_Ref = {{ebicite|correct|EBI}}
| ChEMBL = 114062
| ChemSpiderID_Ref = {{chemspidercite|correct|chemspider}}
| ChemSpiderID = 13837281
| ChemSpiderID = 13837281
| EINECS = 204-825-9
| Gmelin = 101142
| KEGG_Ref = {{keggcite|correct|kegg}}
| KEGG = C06789
| PubChem = 31373
| RTECS = KX3850000
| UNII_Ref = {{fdacite|correct|FDA}}
| UNII_Ref = {{fdacite|correct|FDA}}
| UNII = TJ904HH8SN
| UNII = TJ904HH8SN
| UNNumber = 1897
| InChI = 1/C2Cl4/c3-1(4)2(5)6
| InChI = 1/C2Cl4/c3-1(4)2(5)6
| InChIKey = CYTYCFOTNPOANT-UHFFFAOYAO
| InChIKey = CYTYCFOTNPOANT-UHFFFAOYAO
| ChEMBL_Ref = {{ebicite|correct|EBI}}
| ChEMBL = 114062
| StdInChI_Ref = {{stdinchicite|correct|chemspider}}
| StdInChI_Ref = {{stdinchicite|correct|chemspider}}
| StdInChI = 1S/C2Cl4/c3-1(4)2(5)6
| StdInChI = 1S/C2Cl4/c3-1(4)2(5)6
| StdInChIKey_Ref = {{stdinchicite|correct|chemspider}}
| StdInChIKey_Ref = {{stdinchicite|correct|chemspider}}
| StdInChIKey = CYTYCFOTNPOANT-UHFFFAOYSA-N
| StdInChIKey = CYTYCFOTNPOANT-UHFFFAOYSA-N
| SMILES = ClC(Cl)=C(Cl)Cl
| CASNo_Ref = {{cascite|correct|CAS}}
| CASNo = 127-18-4
| EINECS = 204-825-9
| RTECS = KX3850000
| UNNumber = 1897
| KEGG_Ref = {{keggcite|correct|kegg}}
| KEGG = C06789
}}
}}
| Section2 = {{Chembox Properties
|Section2={{Chembox Properties
| C=2|Cl=4
| C=2 | Cl=4
| MolarMassUnit = g/mol
| Appearance = Clear, colorless liquid
| Appearance = Clear, very refractive, colorless liquid
| Density = 1.622 g/cm<sup>3</sup>
| Odor = Mild, sharp and sweetish<ref name=PGCH/>
| Solubility = 0.015 g/100 mL (20 °C)
| Density = 1.622{{nbsp}}g/cm<sup>3</sup>
| MeltingPtC = -19
| Solubility = 0.15{{nbsp}}g/L (25{{nbsp}}°C)
| BoilingPtC = 121.1
| MeltingPtC = -22.0 to -22.7
| Viscosity = 0.89 [[Poise|cP]] at 25 °C
| BoilingPtC = 121.1
| Viscosity = 0.89{{nbsp}}[[Poise (unit)|cP]] at 25{{nbsp}}°C
| VaporPressure = 14{{nbsp}}mmHg (20{{nbsp}}°C)<ref name=PGCH/>
| MagSus = −81.6·10<sup>−6</sup>{{nbsp}}cm<sup>3</sup>/mol
| RefractIndex = 1.505
}}
}}
| Section7 = {{Chembox Hazards
|Section7={{Chembox Hazards
| NFPA-F = 0 | NFPA-H = 2 | NFPA-R = 0 | NFPA-O =
| NFPA-F = 0 | NFPA-H = 2 | NFPA-R = 0 | NFPA-S =
| NFPA_ref = <ref>{{cite web |url= https://pubchem.ncbi.nlm.nih.gov/compound/31373#section=NFPA-Hazard-Classification |title= Compound Summary: Tetrachloroethylene |work= [[PubChem]] |access-date= 9 September 2020}}</ref>
| ExternalMSDS = [http://www.jtbaker.com/msds/englishhtml/t0767.htm External MSDS]
| MainHazards = Harmful (Xn),<br />Dangerous for<br /> the environment (N)
| MainHazards = Mild skin and respiratory irritant
| ExternalSDS = [https://pubchem.ncbi.nlm.nih.gov/compound/31373 External MSDS]
| FlashPt = Not flammable
| FlashPt = Not flammable
| RPhrases = {{R40}} {{R51/53}}
| SPhrases = {{S23}} {{S36/37}} {{S61}}
| GHSPictograms = {{GHS08}}{{GHS09}}
| GHSSignalWord = Warning
| HPhrases = {{H-phrases|351|411}}
| PPhrases = {{P-phrases|201|202|273|281|308+313|391|405|501}}
| IDLH = Ca [150 ppm]<ref name=PGCH>{{PGCH|0599}}</ref>
| REL = Ca Minimize workplace exposure concentrations.<ref name=PGCH/>
| PEL = TWA 100{{nbsp}}ppm<br/>C 200{{nbsp}}ppm (for 5 minutes in any 3-hour period), with a maximum peak of 300{{nbsp}}ppm<ref name=PGCH/>
| LD50 = 3420 mg/kg (oral, rat)<ref>[https://www.sigmaaldrich.com/BR/pt/sds/sial/371696 Sigma Aldrich Tetrachloroethylene MSDS]</ref><br>2629 mg/kg (oral, rat), >10000 mg/kg (dermal, rat)<ref>[https://www.fishersci.ca/shop/msdsproxy?productName=C18220&productDescription=tetrachloroethylene-technical-fisher-chemical-2 Fischer Scientific Tetrachloroethylene MSDS]</ref>
| LC50 = 4000{{nbsp}}ppm (rat, 4{{nbsp}}hr)<br/>5200{{nbsp}}ppm (mouse, 4{{nbsp}}hr)<br/>4964{{nbsp}}ppm (rat, 8{{nbsp}}hr)<ref>{{IDLH|127184|Tetrachloroethylene}}</ref>
}}
}}
| Section8 = {{Chembox Related
|Section8={{Chembox Related
| Function = Related [[organohalide]]s
| OtherFunction_label = analogous [[organohalide]]s
| OtherFunctn = [[Tetrabromoethylene]]<br />[[Tetraiodoethylene]]
| OtherFunction = [[Tetrafluoroethylene]] <br /> [[Tetrabromoethylene]]<br />[[Tetraiodoethylene]]
| OtherCpds = [[Trichloroethylene]]<br />[[Dichloroethene]]<br />[[Tetrachloroethane]]
| OtherCompounds = [[Trichloroethylene]]<br />[[Dichloroethylene]]<br />[[1,1,2,2-Tetrachloroethane]]<br />[[Carbon tetrachloride]]

}}
}}
}}
}}


'''Tetrachloroethylene''', also known under its systematic name '''tetrachloroethene''' and many other names, is a [[chlorocarbon]] with the formula Cl<sub>2</sub>C=CCl<sub>2</sub>. It is a colourless liquid widely used for [[dry cleaning]] of fabrics, hence it is sometimes called "dry-cleaning fluid." It has a sweet odor detectable by most people at a concentration of 1 part per million (1 ppm). Worldwide production was about 1 megatonne in 1985.<ref name=Ullmann>M. Rossberg et al. “Chlorinated Hydrocarbons” in ''Ullmann’s Encyclopedia of Industrial Chemistry'', 2006, Wiley-VCH, Weinheim. {{DOI|10.1002/14356007.a06 233.pub2}}</ref>
'''Tetrachloroethylene''', also known under the systematic name '''tetrachloroethene''', or '''perchloroethylene''',{{efn|Also spelt as '''perchlorethylene''', especially in older texts.}} and abbreviations such as "'''perc'''" (or "'''PERC'''"), and "'''PCE'''", is a [[chlorocarbon]] with the formula {{chem2|Cl2C\dCCl2}}. 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 mild sweet, sharp odor, detectable by most people at a concentration of 50 ppm.<ref name=browning>Ethel Browning, ''Toxicity of Industrial Organic Solvents'' (1953, [ https://archive.org/details/cftri.3112toxicityofindust0000ethe/page/182/mode/1up pages 182-185]</ref>


==History and production==
==Production==
[[Michael Faraday]] first synthesized tetrachloroethene in 1821 by thermal decomposition of [[hexachloroethane]].
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).
:{{chem2|C2Cl6 → C2Cl4 + Cl2}}
:C<sub>2</sub>Cl<sub>6</sub> &rarr; C<sub>2</sub>Cl<sub>4</sub> + Cl<sub>2</sub>
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 {{convert|70|C|F}} to {{convert|77|C|F}} degrees Celsius but mine did not begin to boil until {{convert|120|C|F}}
".<ref>V. Regnault (1839) [https://books.google.com/books?id=px0AAAAAMAAJ&pg=PA104 "Sur les chlorures de carbone CCl et CCl<sup>2</sup>"] (On the chlorides of carbon CCl and CCl<sup>2</sup> ), ''Annales de Chimie et de Physique'', vol. 70, pages 104-107. Reprinted in German as: {{cite journal
|journal =Annalen der Pharmacie
|volume = 30
|issue = 3
|year = 1839
|title = Ueber die Chlorverbindungen des Kohlenstoffs, C2Cl2 und CCl2
|author = V. Regnault
|doi = 10.1002/jlac.18390300310
|pages =350–352
|url = https://zenodo.org/record/1426937
}}</ref>


A few years after its discovery, in the 1840s, Tetrachloroethylene was named '''Chlorethose''' by [[Auguste Laurent]]. The ''-ose'' ending was explained as the fourfold replacement of the hydrogens in ethylene. If only one atom of hydrogen was replaced, the word would end with ''-ase''. By Laurent's logic, [[vinyl chloride]] would be named ''Chlorethase''.<ref>Transactions of the Pharmaceutical Meetings. (1847). UK: J. Churchill. [https://books.google.com/books?id=wugKAAAAYAAJ&pg=PA548&dq=%22chlorethose%22&hl=tr&newbks=1&newbks_redir=0&source=gb_mobile_search&sa=X&ved=2ahUKEwiw-fDlsYmCAxUeSvEDHe4rAGk4FBDoAXoECAoQAw#v=onepage&q&f=false page 548]</ref>
Most tetrachloroethene is produced by high temperature chlorinolysis of light hydrocarbons. The method is related to Faraday's discovery since hexachloroethane is generated and thermally decomposes.<ref name=Ullmann/> Side products include [[carbon tetrachloride]], [[hydrogen chloride]], and [[hexachlorobutadiene]].


Tetrachloroethylene can be made by passing chloroform vapour through a red-hot tube, the side products include [[hexachlorobenzene]] and [[hexachloroethane]], as reported in 1886.<ref>W. Ramsay and S. Young, Jahresberichte, 1886, p. 628</ref>
Several other methods have been developed. When [[1,2-dichloroethane]] is heated to 400 °C with [[chlorine]], tetrachloroethene is produced by the [[chemical reaction]]:

:ClCH<sub>2</sub>CH<sub>2</sub>Cl + 3 Cl<sub>2</sub> → Cl<sub>2</sub>C=CCl<sub>2</sub> + 4 [[hydrogen chloride|HCl]]
Most tetrachloroethylene is produced by high-temperature chlorinolysis of light hydrocarbons. The method is related to Faraday's method since hexachloroethane is generated and thermally decomposes.<ref name=Ullmann/> Side products include [[carbon tetrachloride]], [[hydrogen chloride]], and [[hexachlorobutadiene]].

Several other methods have been developed. When [[1,2-dichloroethane]] is heated to 400&nbsp;°C with [[chlorine]], tetrachloroethylene is produced by the [[chemical reaction]]:
:{{chem2|ClCH2CH2Cl + 3 Cl2 → Cl2C\dCCl2 + 4 HCl}}
This reaction can be [[catalyst|catalyzed]] by a mixture of [[potassium chloride]] and [[aluminium chloride]] or by activated [[carbon]]. [[Trichloroethylene]] is a major byproduct, which is separated by [[distillation]].
This reaction can be [[catalyst|catalyzed]] by a mixture of [[potassium chloride]] and [[aluminium chloride]] or by activated [[carbon]]. [[Trichloroethylene]] is a major byproduct, which is separated by [[distillation]].


Worldwide production was about {{convert|1|e6MT}} in 1985.<ref name=Ullmann>M. Rossberg et al. "Chlorinated Hydrocarbons" in ''Ullmann's Encyclopedia of Industrial Chemistry'', 2006, Wiley-VCH, Weinheim. {{doi|10.1002/14356007.a06_233.pub2}}</ref>
According to an EPA report of 1976, the quantity of Tetrachloroethylene (also known as perchloroethylene or PCE) produced in the United States in just one year 1973, totaled 706 million pounds (320,000 metric tons). Daimond Shamrock, Dow Chemical Compnay, E.I DuPont and Vulcan Materials Company (Chemical Division) were among the top eight producers nationwide. <ref>"Assessment of Hazardous Waste Practices: Organic Chemicals, Pesticides and Explosives Industries" prebpublication issue for EPA Libraries and Solid Waste Management Agencies under contract # 68-01-2919, USEPA 1976 </ref>

Although in very small amounts, tetrachloroethylene occurs naturally in volcanoes along with [[trichloroethylene]].<ref>{{cite journal | doi = 10.1021/np50088a001 | author = Gribble, G. W. | title = Naturally occurring organohalogen compounds – A comprehensive survey | journal = Progress in the Chemistry of Organic Natural Products | year = 1996 | volume = 68 | pages = 1–423 | pmid = 8795309 | issue = 10}}</ref>


==Uses==
==Uses==
[[File:You Can Cut Operating Costs with Dow-PER - DPLA - ee749e230034a7ce59dde05b9dfc5fcc.jpg|thumb|left|Advertisement for [[Dow Chemical]]'s Tetrachloroethylene, 1952]]
Tetrachloroethylene is an excellent [[solvent]] for [[organic chemistry|organic]] materials. Otherwise it is volatile, highly stable, and [[flammable|nonflammable]]. For these reasons, it is widely used in [[dry cleaning]]. Usually as a mixture with other chlorocarbons, it is also used to degrease metal parts in the [[automobile|automotive]] and other metalworking industries. It appears in a few consumer products including [[paint stripper]]s and spot removers.
Tetrachloroethylene is an excellent nonpolar [[solvent]] for [[organic chemistry|organic]] materials. Otherwise, it is volatile, highly stable and [[flammable|nonflammable]], and has low toxicity. For these reasons, it has been widely used in [[dry cleaning]] worldwide since the 1930s. The chemist [[Sylvia Stoesser]] (1901–1991) suggested Tetrachloroethylene to be used in dry cleaning as an alternative to highly flammable dry cleaning solvents such as [[naphtha]].<ref name="Amos">{{Cite book |last=Amos |first=J. Lawrence |title=A History of the Dow Chemical Physics Lab : the freedom to be creative |date=1990 |publisher=Marcel Dekker, Inc. |editor-last=Boundy |editor-first=Ray H. |location=New York and Basel |pages=71–79 |chapter=Chlorinated solvents |editor-last2=Amos |editor-first2=J. Lawrence}}</ref>

It is also used to degrease metal parts in the [[automobile|automotive]] and other metalworking industries, usually as a mixture with other chlorocarbons. It appears in a few consumer products including [[paint stripper]]s, aerosol preparations and spot removers.


===Historical applications===
===Historical applications===
Tetrachloroethene was once extensively used as an intermediate in the manufacture of [[1,1,1,2-Tetrafluoroethane|HFC-134a]] and related [[refrigerant]]s. In the early 20th century, tetrachloroethene was used for the treatment for [[hookworm]] infestation.<ref>{{cite journal |last=Young |first=M.D. |authorlink= |coauthors=''et al.'' |year=1960 |month= |title=The Comparative Efficacy of Bephenium Hydroxynaphthoate and Tetrachloroethylene against Hookworm and other Parasites of Man |journal=American Journal of Tropical Medicine and Hygiene |volume=9 |issue=5 |pages=488–491 |pmid=13787477 |url= |accessdate= |quote= }}</ref>
Tetrachloroethylene was once extensively used as an intermediate in the manufacture of [[1,1,1,2-Tetrafluoroethane|HFC-134a]] and related [[refrigerant]]s. In the early 20th century, tetrachloroethene was used for the treatment of [[hookworm]] infestation.<ref>{{cite journal |last=Young |first=M.D. |year=1960 |title=The Comparative Efficacy of Bephenium Hydroxynaphthoate and Tetrachloroethylene against Hookworm and other Parasites of Man |journal=American Journal of Tropical Medicine and Hygiene |volume=9 |issue=5 |pages=488–491 |doi=10.4269/ajtmh.1960.9.488 |pmid=13787477 |display-authors=etal}}</ref><ref>{{cite journal |author=<!--Staff writer(s); no by-line.--> | title=Clinical Aspects and Treatment of the More Common Intestinal Parasites of Man (TB-33) | journal=Veterans Administration Technical Bulletin 1946 & 1947 | year=1948 | volume=10 | pages=1–14 | url=https://books.google.com/books?id=uJWxEzwqRiMC }}</ref>


==Health and safety==
==Health and safety==
Tetrachloroethylene is much less toxic than other chlorinated solvents.<ref name=browning/> The acute and chronic toxicity of tetrachloroethylene is moderate to low. Reports of human injury are uncommon despite its wide usage in dry cleaning and degreasing.<ref>{{cite book | author = E.-L. Dreher | author2 = T. R. Torkelson | author3 = K. K. Beutel | chapter = Chlorethanes and Chloroethylenes | title = Ullmann's Encyclopedia of Industrial Chemistry | year = 2011 | publisher = Wiley-VCH | location = Weinheim | doi = 10.1002/14356007.o06_o01| isbn = 978-3527306732 }}</ref>
The [[International Agency for Research on Cancer]] has classified tetrachloroethene as a Group 2A [[carcinogen]], which means that it is probably carcinogenic to humans.<ref>IARC monograph. [http://www.inchem.org/documents/iarc/vol63/tetrachloroethylene.html Tetrachloroethylene], Vol. 63, p. 159. Last Updated May 20, 1997. Last retrieved June 22, 2007.</ref> Like many [[Organochlorine compound|chlorinated hydrocarbons]], tetrachloroethene is a [[central nervous system]] depressant and can enter the body through respiratory or dermal exposure.<ref>[http://www.cdc.gov/niosh/hc19.html Control of Exposure to Perchloroethylene in Commercial Drycleaning]. Hazard Controls: Publication 97-157. National Institute for Occupational Safety and Health.</ref> Tetrachloroethene dissolves fats from the skin, potentially resulting in skin irritation.


Despite the advantages of tetrachloroethylene, many{{who|date=July 2023}} have called for its replacement from widespread commercial use. It has been described as a possible "neurotoxicant, [[hepatotoxin|liver]] and
Animal studies and a study of 99 twins by Dr. Samuel Goldman and researchers at the Parkinson's Institute in Sunnyvale, California determined there is a "lot of circumstantial evidence" that exposure to Tetrachloroethlene increases the risk of developing Parkinson's disease ninefold. Larger population studies are planned.<ref>[http://www.michaeljfox.org/newsEvents_parkinsonsInTheNews_article.cfm?ID=605 Industrial Solvent Linked to Increased Risk of Parkinson's Disease]</ref>
[[nephrotoxin|kidney toxicant]] and reproductive and developmental toxicant (...) a 'potential occupational carcinogen'".<ref>{{cite journal |doi=10.3389/fpubh.2021.638082|doi-access=free |title=Perchloroethylene and Dry Cleaning: It's Time to Move the Industry to Safer Alternatives |year=2021 |last1=Ceballos |first1=Diana M. |last2=Fellows |first2=Katie M. |last3=Evans |first3=Ashley E. |last4=Janulewicz |first4=Patricia A. |last5=Lee |first5=Eun Gyung |last6=Whittaker |first6=Stephen G. |journal=Frontiers in Public Health |volume=9 |page=638082 |pmid=33748070 |pmc=7973082 }}</ref>{{Better source needed|date=August 2023}}


As an anthelmintic, tetrachloroethylene was given orally to approximately fifty thousand people between 1925 and 1943. The most severe side effects were nausea and vomiting due to the irritation of gastric tract. Most reported poisonings were manifestations of its narcotic effects.<ref>Ellen B. Foot, Virginia Apgar and Kingsley Bishop, [https://archive.org/details/sim_anesthesiology_1943-05_4_3/page/283/mode/1up
===Testing for exposure===
''Tetrachlorethylene as an Anesthetic Agent''], in Anesthesiology, 1943-05: Vol 4 Iss 3 </ref>
Tetrachloroethene exposure can be evaluated by a breath test, analogous to breath-alcohol measurements. Because it is stored in the body's fat and slowly released into the bloodstream, tetrachloroethene can be detected in the breath for weeks following a heavy exposure. Tetrachloroethylene and [[trichloroacetic acid]] (TCA), a breakdown product of tetrachloroethene, can be detected in the [[blood]].


=== Metabolism ===
In Europe, the Scientific Committee on Occupational Exposure Limits ([[SCOEL]]) recommends for tetrachloroethylene an [[occupational exposure limit]] (8h time-weighted average) of 20 ppm and a short-term exposure limit (15 min) of 40 ppm.<ref>{{cite web|url= http://ec.europa.eu/social/keyDocuments.jsp?type=0&policyArea=82&subCategory=153&country=0&year=0&advSearchKey=recommendation&mode=advancedSubmit&langId=en|title=SCOEL recommendations|date=2011-04-22|accessdate=2011-04-22}}</ref>
Tetrachloroethylene's biological half-life is approximately 3 days.<ref name=bio/> About 98% of the inhaled Tetrachloroethylene is exhaled unchanged and only about 1–3% is metabolised to [[tetrachloroethylene oxide]] which rapidly isomerises into [[trichloroacetyl chloride]]. Trichloroacetyl chloride hydrolyses to [[trichloroacetic acid]].<ref>Toxicological Profile for Tetrachloroethylene: Draft. (1995). U.S. Department of Health and Human Services, Public Health Service, Agency for Toxic Substances and Disease Registry.</ref><ref name=bio>Biological Monitoring: An Introduction. (1993). page 470</ref>


=== Carcinogenicity ===
== Environmental contamination ==
Tetrachloroethylene has been classified as "probably carcinogenic to humans" (Group 2A) by the [[International Agency for Research on Cancer]] (IARC). There is a possibility that it is carcinogenic to humans in long-term exposure, but the evidence is limited since most of the evaluated dry-cleaners had heavy smoking and drinking habits which are known to cause multiple types of cancer.<ref name=iarc>{{Cite web|url=https://www.inchem.org/documents/iarc/vol63/tetrachloroethylene.html|title=Tetrachloroethylene (IARC Summary & Evaluation, Volume 63, 1995)|website=www.inchem.org}}</ref>
Epidemiological research has been conducted in the dry-cleaning industry because of the widespread use of tetrachloroethylene in the industry since 1960. The evidence demonstrates a positive association between tetrachloroethylene exposure, bladder cancer, non-Hodgkin lymphoma, and multiple myeloma in adults. A review of 109 occupational studies estimated a mean exposure of 59 ppm in dry-cleaning employees. Epidemiological evidence shows that exposure via ingestion or inhalation can increase tumor incidence.<ref>{{Cite journal |last1=Guyton |first1=KZ |last2=Hogan |first2=KA |last3=Scott |first3=CS |last4=Cooper |first4=GS |last5=Bale |first5=AS |last6=Kopylev |first6=L |last7=Barone, Jr. |first7=S |last8=Makris |first8=SL |last9=Glenn |first9=B |last10=Subramaniam |first10=RP |last11=Gwinn |first11=MR |last12=Dzubow |first12=RC |last13=Chiu |first13=WA |display-authors=3 |date=14 February 2014 |title=Human health effects of tetrachloroethylene: key findings and scientific issues |journal=Environ Health Perspect. |volume=122 |issue=4 |pages=325–334 |doi=10.1289/ehp.1307359 |pmid=24531164 |pmc=3984230 }}</ref> Exposure to tetrachloroethylene in a typical dry cleaning shop is considered far below the levels required to cause any risk.<ref>{{cite journal |pmid=19367044 |year=2009 |last1=Azimi Pirsaraei |first1=S. R. |title=Occupational exposure to perchloroethylene in dry-cleaning shops in Tehran, Iran |journal=Industrial Health |volume=47 |issue=2 |pages=155–9 |last2=Khavanin |first2=A |last3=Asilian |first3=H |last4=Soleimanian |first4=A |doi=10.2486/indhealth.47.155 |doi-access=free }}</ref>


===Testing for exposure===
Tetrachloroethene is a common [[soil contaminant]]. With a specific gravity greater than 1, tetrachloroethylene will be present as a [[dense nonaqueous phase liquid]] if sufficient quantities of liquid are spilled in the environment. Because of its mobility in groundwater, its [[toxicity]] at low levels, and its density (which causes it to sink below the [[water table]]), cleanup activities are more difficult than for oil spills. Recent research has focused on the in place [[environmental remediation|remediation]] of soil and ground water pollution by tetrachloroethylene. Instead of excavation or extraction for above-ground treatment or disposal, tetrachloroethylene contamination has been successfully remediated by chemical treatment or bioremediation. Bioremediation has been successful under anaerobic conditions by reductive dechlorination by ''Dehalococcoides'' sp. and under aerobic conditions by cometabolism by ''Pseudomonas'' sp.<ref>{{cite journal | doi = 10.1007/s002530100675 | author = Ryoo, D., Shim, H., Arenghi, F. L. G., Barbieri, P., Wood T. K. | year = 2001 | title = Tetrachloroethylene, Trichloroethylene, and Chlorinated Phenols Induce Toluene-o-xylene Monooxoygenase Activity in Pseudomonas Stutzeri OX1 | journal = Applied Microbiol Biotechnol | volume = 56 | pages = 545–549}}</ref><ref>{{cite journal | doi = 10.1007/BF01020855 | author = Deckard, L. A., Wills, J. C., Rivers, D. B. | year = 1994 | title = Evidence for aerobic degradation of tetrachloroethylene by bacterial isolate | journal = Biotechnol. Lett. | volume = 16 | pages = 1221–1224}}</ref> Partial degradation daughter products include [[trichloroethylene]], cis-[[1,2-dichloroethene]] and [[vinyl chloride]]; full degradation converts tetrachloroethylene to ethene and chloride dissolved in water.
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.<ref>{{Cite web |date=2021-02-09 |title=Tetrachloroethylene Toxicity: Section 3.1. Evaluation and Diagnosis {{!}} Environmental Medicine {{!}} ATSDR |url=https://www.atsdr.cdc.gov/csem/tetrachloroethylene/section_3_1.html |access-date=2023-03-02 |website=www.atsdr.cdc.gov |language=en-us}}</ref> Tetrachloroethylene can be detected in the breath for weeks following a heavy exposure. Tetrachloroethylene and its metabolite [[trichloroacetic acid]], can be detected in the blood.


In Europe, the [[Scientific Committee on Occupational Exposure Limit Values|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.<ref>{{cite web|url= http://ec.europa.eu/social/keyDocuments.jsp?type=0&policyArea=82&subCategory=153&country=0&year=0&advSearchKey=recommendation&mode=advancedSubmit&langId=en|title=SCOEL recommendations|date=2011-04-22|access-date=2011-04-22}}</ref>
It has been estimated that about 85% of tetrachloroethylene is released into the [[atmosphere]]; [[OECD]] models assumed 90% release into the air and 10% to water. Based on these models, its distribution in the environment is estimated to be in the air (76.39% - 99.69%), water (0.23% - 23.2%), soil (0.06-7%), with the remainder in the sediment and biota. Estimates of lifetime in the atmosphere vary, but a 1987 survey estimated the lifetime in the air has been estimated at about 2 months in the Southern Hemisphere and 5–6 months in the Northern Hemisphere. Degradation products observed in a laboratory include phosgene, trichloroacetyl chloride, hydrogen chloride, carbon dioxide, and carbon monoxide. In water, tetrachloroethylene is degraded very slowly by [[hydrolysis]], and it is persistent under [[aerobic]] conditions. It is degraded through reductive dechlorination under anaerobic conditions, with the degradation products including trichloroethene, dichloroethene, vinyl chloride, ethene, and ethane.<ref>Watts P. (2006). [http://www.who.int/ipcs/publications/cicad/cicad68.pdf Concise International Chemical Assessment Document 68: TETRACHLOROETHENE], [[World Health Organization]]</ref>

==Remediation and degradation==
In principle, tetrachloroethylene contamination can be remediated by chemical treatment. Chemical treatment involves reducing metals such as iron powder.

[[Bioremediation]] usually entails reductive dechlorination under anaerobic conditions by ''Dehalococcoides'' spp.<ref>{{cite journal |doi=10.1016/j.watres.2017.02.001|title=Anaerobic biodegradation of (Emerging) organic contaminants in the aquatic environment |year=2017 |last1=Ghattas |first1=Ann-Kathrin |last2=Fischer |first2=Ferdinand |last3=Wick |first3=Arne |last4=Ternes |first4=Thomas A. |journal=Water Research |volume=116 |pages=268–295 |pmid=28347952 |doi-access=free |bibcode=2017WatRe.116..268G }}</ref> Under aerobic conditions, degradation may occur via cometabolism by ''Pseudomonas'' sp.<ref>{{cite journal |doi=10.1007/s002530100675 |last1=Ryoo |first1=D. |last2=Shim |first2=H. |last3=Arenghi |first3=F. L. G. |last4=Barbieri |first4=P. |last5=Wood |first5=T. K. |year=2001 |title=Tetrachloroethylene, Trichloroethylene, and Chlorinated Phenols Induce Toluene-o-xylene Monooxoygenase Activity in Pseudomonas stutzeri OX1 |journal = Appl Microbiol Biotechnol |volume=56 |pages=545–549 | issue = 3–4| pmid = 11549035 | s2cid = 23770815 }}</ref> Products of biological reductive dechlorination include [[trichloroethene]], ''cis''-[[1,2-dichloroethene]], [[vinyl chloride]], ethene and chloride.
== Explanatory notes ==
{{Notelist}}


==References==
==References==
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==Further reading==
==Further reading==
* {{cite web | publisher = [[Agency for Toxic Substances and Disease Registry]] | year = 1997 | title = Toxicological Profile for Tetrachloroethene | url = http://www.atsdr.cdc.gov/toxprofiles/tp18.html}}
*{{cite web | publisher = [[Agency for Toxic Substances and Disease Registry]] | year = 1997 | title = Toxicological Profile for Tetrachloroethene | url = https://www.atsdr.cdc.gov/toxprofiledocs/index.html?id=265&tid=48}}
*{{cite journal | author = Doherty, R.E. | year = 2000 | title = 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 | journal = Environmental Forensics | volume = 1 | pages = 69–81 | doi = 10.1006/enfo.2000.0010 | issue = 2 | bibcode = 2000EnvFo...1...69D | s2cid = 97680726 }}

* {{cite journal | author = Doherty, R.E. | year = 2000 | title = 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 | journal = [[Journal of Environmental Forensics]] | volume = 1 | pages = 69–81 | doi = 10.1006/enfo.2000.0010 }}


==External links==
==External links==
* [http://www.atsdr.cdc.gov/csem/pce/ ATSDR Case Studies in Environmental Medicine: Tetrachloroethylene Toxicity] U.S. [[Department of Health and Human Services]]
*[https://www.atsdr.cdc.gov/csem/csem.html ATSDR Case Studies in Environmental Medicine: Tetrachloroethylene Toxicity] U.S. [[Department of Health and Human Services]]
*[https://www.cdc.gov/niosh/topics/tetrachloro/ Tetrachloroethylene (Perchloroethylene)] U.S. [[Department of Health and Human Services]]
* Australian [http://www.npi.gov.au/database/substance-info/profiles/80.html National Pollutant Inventory (NPI)] page
*Australian [http://www.npi.gov.au/substances/tetrachloroethylene/index.html National Pollutant Inventory (NPI)] page
* [http://www.nydailynews.com/news/crime_file/2007/04/20/2007-04-20_toxic_fumes_may_have_made_gunman_snap-1.html "Toxic Fumes May Have Made Gunman Snap"], by Julian Kesner, New York ''Daily News'', April 20, 2007.
*[http://www.chlorinated-solvents.eu Sustainable uses and Industry recommendations]


{{Authority control}}
[[Category:Organochlorides]]
{{Chlorides}}
[[Category:Commodity chemicals]]
[[Category:Dry cleaning]]
[[Category:Halogenated solvents]]
[[Category:Halogenated solvents]]
[[Category:Hazardous air pollutants]]
[[Category:Hazardous air pollutants]]
[[Category:IARC Group 2A carcinogens]]
[[Category:IARC Group 2A carcinogens]]
[[Category:Chloroalkenes]]

[[Category:Perchlorocarbons]]
[[bg:Тетрахлороетен]]
[[Category:Anthelmintics]]
[[ca:Tetracloroetilè]]
[[cs:Tetrachlorethylen]]
[[de:Tetrachlorethen]]
[[es:Tetracloroetileno]]
[[fr:Perchloroéthylène]]
[[id:Tetrakloroetilena]]
[[it:Tetracloroetene]]
[[nl:Tetrachlooretheen]]
[[ja:テトラクロロエチレン]]
[[pl:Tetrachloroeten]]
[[pt:Percloroetileno]]
[[ru:Перхлорэтилен]]
[[sv:Perkloretylen]]
[[zh:四氯乙烯]]