“Ethoxylation”的意思、由来-开放百科全书

Ethoxylation is a chemical reaction in which ethylene oxide adds to a substrate. It is the most widely practiced alkoxylation, which involves the addition of epoxides to substrates.

In the usual application, alcohols and phenols are converted into R(OC₂H₄)_nOH where n ranges from 1 to 10. Such compounds are called alcohol ethoxylates. Alcohol ethoxlates are often converted to related species called ethoxysulfates. Alcohol ethoxylates and ethoxysulfates are surfactants, used widely in cosmetic and other commercial products.^[1] The process is of great industrial significance with more than 2,000,000 metric tons of various ethoxylates produced worldwide in 1994.^[2]

Production

The process was developed at the Ludwigshafen laboratories of I.G. Farben by Conrad Schöller and Max Wittwer during the 1930s.^[3]^[4]

Alcohol ethoxylates

Industrial ethoxylation is primarily performed upon fatty alcohols in order to generate fatty alcohol ethoxylates (FAE's), which are a common form of nonionic surfactant (e.g. octaethylene glycol monododecyl ether. Such alcohols may be obtained by the hydrogenation of fatty acids from seed oils,^[5] or via hydroformylation in the Shell higher olefin process.^[6] The reaction proceeds by blowing ethylene oxide through the alcohol at 180 °C and under 1-2 bar of pressure, with potassium hydroxide (KOH) serving as a catalyst.^[6] The process is highly exothermic (ΔH -92000 J/mol of ethylene oxide reacted) and requires careful control to avoid a potentially disastrous thermal runaway.^[6]

The starting materials are usually primary alcohols as they react ~10-30x faster than do secondary alcohols.^[7]

Typically 5-10 units of ethylene oxide are added to each alcohol,^[8] however ethoxylated alcohols can be more prone to ethoxylation than the starting alcohol, making the reaction difficult to control and leading to the formation of a product with varying repeat unit length (the value of n in the equation above). Better control can be afforded by the use of more sophisticated catalysts,^[9] which can be used to generate narrow-range ethoxylates. Ethoxylated alcohols are considered to be a high production volume (HPV) chemical by the US EPA.^[10]

Ethoxylation/propoxylation

Ethoxylation is sometimes combined with propoxylation, the analogous reaction using propylene oxide as the monomer. Both reactions are normally performed in the same reactor and may be run simultaneously to give a random polymer, or in alternation to obtain block copolymers such as poloxamers.^[6] Propylene oxide is more hydrophobic than ethylene oxide and its inclusion at low levels can significantly affect the properties of the surfactant. In particular ethoxylated fatty alcohols which have been 'capped' with ~1 propylene oxide unit are extensively marketed as low-foaming surfactants.

Ethoxysulfates

Ethoxylated fatty alcohols are often converted to the corresponding organosulfates, which can be easily deprotonated to give anionic surfactants such as sodium laureth sulfate. Being salts, ethoxysulfates exhibit good water solubility (high HLB value). The conversion is achieved by treating ethoxylated alcohols with sulfur trioxide.^[11] Laboratory scale synthesis may be performed using chlorosulfuric acid:

Small volumes are neutralized with alkanolamines such as triethanolamine (TEA).^[12]{{page needed|date=March 2016}} In 2006, 382,500 metric tons of alcohol ethoxysulfates (AES) were consumed in North America.^[13]^{{{subscription}}}{{page needed|date=March 2016}}{{better source|date=March 2016}}

Other materials

Although alcohols are by far the major substrate for ethoxylation, many nucleophiles are reactive toward ethylene oxide. Primary amines will react to give di-chain materials such as polyethoxylated tallow amine. The reaction of ammonia produces important bulk chemicals such as ethanolamine, diethanolamine, and triethanolamine.

Applications of ethoxylated products

Alcohol ethoxylates (AE) and alcohol ethoxysulfates (AES) are surfactants found in products such as laundry detergents, surface cleaners, cosmetics, agricultural products, textiles, and paint.^[14]{{primary source inline|date=March 2016}}

Alcohol ethoxylates

As alcohol ethoxylate based surfactants are non-ionic they typically require longer ethoxylate chains than their sulfonated analogues in order to be water-soluble.^[15] Examples synthesized on an industrial scale include octyl phenol ethoxylate, polysorbate 80 and poloxamers.

Ethoxylation is commonly practiced, albeit on a much smaller scale, in the biotechnology and pharmaceutical industries to increase water solubility and, in the case of pharmaceuticals, circulatory half-life of non-polar organic compounds. In this application, ethoxylation is known as "PEGylation" (polyethylene oxide is synonymous with polyethylene glycol, abbreviated as PEG). Carbon chain length is 8-18 while the ethoxylated chain is usually 3 to 12 ethylene oxides long in home products.^[16]{{page needed|date=March 2016}} They feature both lipophilic tails, indicated by the alkyl group abbreviation, R, and relatively polar headgroups, represented by the formula (OC₂H₄)_nOH.

Alcohol ethoxysulfates

AES found in consumer products generally are linear alcohols, which could be mixtures of entirely linear alkyl chains or of both linear and mono-branched alkyl chains.^[17]{{page needed|date=March 2016}} A high-volume example of these is sodium laureth sulfate a foaming agent in shampoos and toothpastes, as well as industrial detergents.{{citation needed|date=March 2016}}

Environmental and safety

Alcohol ethoxylates (AEs)

Human health

Alcohol ethoxylates are not observed to be mutagenic, carcinogenic, or skin sensitizers, nor cause reproductive or developmental effects.^[18] One byproduct of ethoxylation is 1,4-dioxane, a possible human carcinogen.^[19] Undiluted AEs can cause dermal or eye irritation. In aqueous solution, the level of irritation is dependent on the concentration. AEs are considered to have low to moderate toxicity for acute oral exposure, low acute dermal toxicity, and have mild irritation potential for skin and eyes at concentrations found in consumer products.^[16]

Aquatic and environmental aspects

AEs are usually released down the drain, where they may be adsorbed into solids and biodegrade through anaerobic processes, with ~28–58% degraded in the sewer.^[20]{{primary source inline|date=March 2016}} The remaining AEs are treated at waste water treatment plants and biodegraded via aerobic processes with less than 0.8% of AEs released in effluent.^[20] If released into surface waters, sediment or soil, AEs will degrade through aerobic and anaerobic processes or be taken up by plants and animals.

Toxicity to certain invertebrates has a range of EC50 values for linear AE from 0.1 mg/l to greater than 100 mg/l. For branched alcohol exthoxylates, toxicity ranges from 0.5 mg/l to 50 mg/l.^[16] The EC50 toxicity for algae from linear and branched AEs was 0.05 mg/l to 50 mg/l. Acute toxicity to fish ranges from LC50 values for linear AE of 0.4 mg/l to 100 mg/l, and branched is 0.25 mg/l to 40 mg/l. For invertebrates, algae and fish the essentially linear and branched AEs are considered to not have greater toxicity than Linear AE.^[16]

Alcohol ethoxysulfates (AESs)

Biodegradation

The degradation of AES proceeds by ω- or β-oxidation of the alkyl chain, enzymatic hydrolysis of the sulfate ester, and by cleavage of an ether bond in the AES producing alcohol or alcohol ethoxylate and an ethylene glycol sulfate. Studies of aerobic processes also found AES to be readily biodegradable.^[12] The half-life of both AE and AES in surface water is estimated to be less than 12 hours.^[21]{{primary source inline|date=March 2016}} The removal of AES due to degradation via anaerobic processes is estimated to be between 75 and 87%.

Aquatic

Flow-through laboratory tests in a terminal pool of AES with mollusks found the NOEC of a snail, Goniobasis and the Asian clam, Corbicula to be greater than 730 ug/L. Corbicula growth was measured to be affected at a concentration of 75 ug/L.^[22]{{primary source inline|date=March 2016}} The mayfly, genus Tricorythodes has a normalized density NOEC value of 190 ug/L.^[23]{{primary source inline|date=March 2016}}

Human Safety

References

1. ^{{cite book |author1=Smulders, E. |author2=von Rybinski, W. |author3=Sung, E. |author4=Rähse, W. |author5=Steber, J. |author6=Wiebel, F. |author7=Nordskog, A. | year = 2011 | title = Ullmann's Encyclopedia of Industrial Chemistry | chapter = Laundry Detergents, 1. Introduction| editors = Elvers, Barbara, et al. | doi = 10.1002/14356007.a08_315.pub3| location = Weinheim, GER | publisher = Wiley-VCH | ref = published online, 15 July 2007 |isbn=978-3527306732 }}
2. ^{{cite book|author=Arno Cahn|title=Proceedings of the 3rd World Conference on Detergents: Global Perspectives|url=https://books.google.com/books?id=Pbr2HJ1X_DkC&pg=PA141|date=30 January 1994|publisher=The American Oil Chemists Society|isbn=978-0-935315-52-3|page=141}}
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4. ^{{cite patent |country=US | title = Assistants for the textile and related industries | number=1970578 A | status = patent | gdate=1934-08-21 | fdate = 1931-11-24 | pridate = 1930-11-29 | inventor = Schoeller, Conrad & Wittwer, Max | assign1 = IG Farbenindustrie AG. }}
5. ^{{cite journal|last1=Kreutzer|first1=Udo R.|title=Manufacture of fatty alcohols based on natural fats and oils|journal=Journal of the American Oil Chemists' Society|date=February 1984|volume=61|issue=2|pages=343–348|doi=10.1007/BF02678792}}
6. ^¹²{{cite journal|last1=Di Serio|first1=Martino|last2=Tesser|first2=Riccardo|last3=Santacesaria|first3=Elio|title=Comparison of Different Reactor Types Used in the Manufacture of Ethoxylated, Propoxylated Products|journal=Industrial & Engineering Chemistry Research|date=December 2005|volume=44|issue=25|pages=9482–9489|doi=10.1021/ie0502234}}
7. ^{{cite journal|last1=Di Serio|first1=M.|last2=Vairo|first2=G.|last3=Iengo|first3=P.|last4=Felippone|first4=F.|last5=Santacesaria|first5=E.|title=Kinetics of Ethoxylation and Propoxylation of 1- and 2-Octanol Catalyzed by KOH|journal=Industrial & Engineering Chemistry Research|date=January 1996|volume=35|issue=11|pages=3848–3853|doi=10.1021/ie960200c}}
8. ^¹{{cite book | author = Kosswig, Kurt | year = 2002 | title = Ullmann's Encyclopedia of Industrial Chemistry | chapter = Surfactants | editors = Elvers, Barbara, et al. | doi = 10.1002/14356007.a25_747 | location = Weinheim, GER | publisher = Wiley-VCH | ref = published online, 15 June 2000 | isbn = 978-3527306732 }}
9. ^{{cite journal|last1=Cox|first1=Michael F.|title=The effect of "peaking" the ethylene oxide distribution on the performance of alcohol ethoxylates and ether sulfates|journal=Journal of the American Oil Chemists' Society|date=September 1990|volume=67|issue=9|pages=599–604|doi=10.1007/BF02540775}}
10. ^{{cite web|last=US EPA |title=High production volume (HPV) challenge program |url=http://www.epa.gov/chemrtk/index.htm |date=July 2006 |deadurl=yes |archiveurl=https://web.archive.org/web/20111117112747/http://www.epa.gov/chemrtk/index.htm |archivedate=2011-11-17 |df= }}
11. ^{{cite journal|last1=Roberts|first1=David W.|title=Sulfonation Technology for Anionic Surfactant Manufacture|journal=Organic Process Research & Development|date=May 1998|volume=2|issue=3|pages=194–202|doi=10.1021/op9700439}}
12. ^¹{{cite book | authors = Anon. [HERA Substance Team] |title = Alcohol Ethoxysulphates (AES) Environmental Risk Assessment | date = 2004-06-15 | url=http://www.heraproject.com/files/1-E-04-HERA%20AES%20ENV%20%20web%20wd.pdf | location = Brussels, BEL | publisher = Human and Environmental Risk Assessment (HERA) Project | quote = The HERA (Human and Environmental Risk Assessment) project is a European voluntary initiative launched in 1999 by the following organizations: A.I.S.E. representing the formulators and manufacturers of household and maintenance cleaning products. Cefic representing the suppliers and manufacturers of the raw materials. }}{{page needed|date=March 2016}} This 36 page report is an HERA document on this ingredient in European household cleaning products.
13. ^{{cite book | authors = Modler R., Gubler R, & Inoguchi, Y. | chapter = Detergent Alcohols | title=Chemical Economics Handbook |year=2007 | publisher=SRI Consulting | location=Menlo Park, CA | chapter-url=http://www.sriconsulting.com/CEH/Public/Reports/583.8000/ | pages = | chapter-format=narrow distribution consultant trade report}}^{{{subscription}}}{{page needed|date=March 2016}}{{better source|date=March 2016}}
14. ^{{cite journal|last=Federle|first=Thomas W|author2=Nina R. Itrich|title=Effect of Ethoxylate Number and Alkyl Chain Length on the Pathway and Kinetics of Linear Alcohol Ethoxylate Biodegradation in Activated Sludge|journal=Environmental Toxicology and Chemistry|year=2004|pages=2790–2798|doi=10.1897/04-053.1|volume=23|issue=12}}{{primary source inline|date=March 2016}}
15. ^{{cite journal|last1=Varadaraj|first1=Ramesh|last2=Bock|first2=Jan|last3=Brons|first3=Neil|last4=Zushma|first4=Steve|title=Influence of Surfactant Structure on Wettability Modification of Hydrophobic Granular Surfaces|journal=Journal of Colloid and Interface Science|volume=167|issue=1|year=1994|pages=207–210|issn=0021-9797|doi=10.1006/jcis.1994.1350|bibcode=1994JCIS..167..207V}}
16. ^¹²³{{cite book | authors = Anon. [HERA Substance Team] |title = Alcohol Ethoxylates, Version 2.0 | date = 2009-09-01 | url=http://www.heraproject.com/files/34-F-09%20HERA%20AE%20Report%20Version%202%20-%203%20Sept%2009.pdf | location = Brussels, BEL | publisher = Human and Environmental Risk Assessment (HERA) Project | quote = }}{{page needed|date=March 2016}} See preceding HERA reference for explanation of the publishing organisation. This 244 page book is the latest HERA document on ingredients of European household cleaning products.
17. ^¹{{cite book | authors = Anon. [HERA Substance Team] |title = Alcohol Ethoxysulphates Human Health Risk Assessment, Draft | date = 2003-12-02 | url=http://www.heraproject.com/files/1-HH-04-HERA%20AES%20HH%20web%20wd.pdf | location = Brussels, BEL | publisher = Human and Environmental Risk Assessment (HERA) Project | access-date = 14 March 2016 | quote = }}{{page needed|date=March 2016}} See preceding HERA reference for explanation of the publishing organisation. This 57 page report is the latest HERA document on this ingredient of European household cleaning products. Note, the HERA web site, , access date as above, bears the December date; the document bears a date of January 2003.
18. ^{{cite journal|last1=Fruijtier-Pölloth|first1=Claudia|title=Safety assessment on polyethylene glycols (PEGs) and their derivatives as used in cosmetic products|journal=Toxicology|volume=214|issue=1–2|year=2005|pages=1–38|issn=0300-483X|doi=10.1016/j.tox.2005.06.001|pmid=16011869}}
19. ^{{cite journal|last1=Stickney|first1=Julie A|last2=Sager|first2=Shawn L|last3=Clarkson|first3=Jacquelyn R|last4=Smith|first4=Lee Ann|last5=Locey|first5=Betty J|last6=Bock|first6=Michael J|last7=Hartung|first7=Rolf|last8=Olp|first8=Steven F|title=An updated evaluation of the carcinogenic potential of 1,4-dioxane|journal=Regulatory Toxicology and Pharmacology|volume=38|issue=2|year=2003|pages=183–195|issn=0273-2300|doi=10.1016/S0273-2300(03)00090-4}}
20. ^¹{{cite journal|last=Prats|first=Daniel|author2=Carmen Lopez |author3=Diana Vallejo |author4=Pedro Varo |author5=Victor M. Leon |title=Effect of Temperature on the Biodegradation of Linear Alkylbenzene Sulfonate and Alcohol Ethoxylate|journal=Journal of Surfactants and Detergents|year=2006|volume=9|issue=1|pages=69–75|doi=10.1007/s11743-006-0377-8}}{{primary source inline|date=March 2016}}
21. ^{{cite journal|last=Guckert|first=J.B.|author2=Walker, D.D. |author3=Belanger, S.E |title=Environmental chemistry for a surfactant exotoxicology study supports rapid degradation of C12 alkyl sulfate in a continuous-flow stream mesocosm|journal=Environ. Chem. Toxicol.|year=1996|volume=15|issue=3|pages=262–269|doi=10.1002/etc.5620150306}}{{primary source inline|date=March 2016}}
22. ^{{cite journal|last=Belanger|first=SE|author2=KL Rupe |author3=RG Bausch |title=Responses of Invertebrates and Fish to Alkyl Sulfate and Alkyl Ethoxylate Sulfate Anionic Surfactants During Chronic Exposure|journal=Environmental Contamination and Toxicology|year=1995|volume=55|issue=5|pages=751–758|doi=10.1007/BF00203763}}{{primary source inline|date=March 2016}}
23. ^{{cite journal|last1=van de Plassche|first1=Erik J.|last2=de Bruijn|first2=Jack H. M.|last3=Stephenson|first3=Richard R.|last4=Marshall|first4=Stuart J.|last5=Feijtel|first5=Tom C. J.|last6=Belanger|first6=Scott E.|title=Predicted no-effect concentrations and risk characterization of four surfactants: Linear alkyl benzene sulfonate, alcohol ethoxylates, alcohol ethoxylated sulfates, and soap|journal=Environmental Toxicology and Chemistry|volume=18|issue=11|year=1999|pages=2653–2663|issn=0730-7268|doi=10.1002/etc.5620181135}}{{primary source inline|date=March 2016}}