Ethoxylation

This article is about the industrial scale process. For the attachment of polyethylene glycol to pharmaceuticals, see PEGylation.

Ethoxylation is a chemical reaction in which ethylene oxide adds to alcohols and phenols. The process converts the group ROH into R(OC2H4)nOH where n ranges from 1 to as high as 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 various ethoxylates produced world wide 1994.[2]

Production

The process was developed at the Ludwigshafen laboratories of I.G. Farben by Conrad Schöller and Max Wittwer during the 1930's.[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. 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.[7] The process is highly exothermic (ΔH) -92000 J/mol of ethylene oxide reacted) and requires careful control to avoid a potentially disastrous thermal runaway.[7]

ROH + n C2H4O → R(OC2H4)nOH

The starting materials are usually primary alcohols as their rate constant is ~10-30 times that of secondary alcohols.[8] Typically 5-10 units of ethylene oxide are added to each alcohol,[6] 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] Ethoxylated alcohols are considered to be a high production volume (HPV) chemical by the US EPA,[10]

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. The negative charge increases the water solubility of the compounds, giving them a higher HLB value. The conversion is achieved industrially by blowing a sulfur trioxide/air mixture through a solution of ethoxylated starting material.[11] Laboratory scale synthesis may be performed using chlorosulfuric acid:

R(OC2H4)nOH + SO3 → R(OC2H4)nOSO3H
R(OC2H4)nOH + HSO3Cl → R(OC2H4)nOSO3H + HCl

The resulting sulfate esters are neutralized to give the salt:

R(OC2H4)nOSO3H + NaOH → R(OC2H4)nOSO3Na + H2O

Small volumes are neutralized with alkanolamines such as triethanolamine (TEA).[12] In 2006, 382,500 metric tons of alcohol ethoxysulfates (AES) were consumed in North America.[13](subscription required)

Applications of ethoxylated products

Alcohol ethoxylates (AE) and alcohol ethoxysulfates (AES) are surfactants found in products such as laundry detergents, surface cleaners, cosmetics and for use in agriculture, textiles and paint.[14]

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] 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] A high-volume example of these is sodium laureth sulfate a foaming agent in shampoos and toothpastes, as well as industrial detergents.

Environmental and safety

Alcohol ethoxylates (AE's)

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 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

Some ethoxylated materials have been controversial because of their widespread use and the toxicity posed to aquatic life due to degradation products, such as nonylphenol.[1]

Alcohols containing ethylene oxides of C
6–C
18 length are considered to be rapidly biodegraded.[20] 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.[21] 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.[21] 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 larger 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 (AES's)

Biodegradation

The degradation of AES proceeds by ω- or β-oxidation of the alkyl chain, enzyme cleavage of the sulfate substituent leaving the alcohol ethoxylate, and by cleavage of an ether bond in the AES molecule 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.[22] The removal of AES due to degradation via anaerobic processes is estimated to be between 75 to 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.[23] The mayfly, genus Tricorythodes has a normalized density NOEC value of 190 ug/L.[24]

Human Safety

AES has not been found to be genotoxic, mutagenic, or carcinogenic.[17]

References

  1. 1 2 Smulders, E.; von Rybinski, W.; Sung, E.; Rähse, W.; Steber, J.; Wiebel, F. & Nordskog, A. (2011). "Laundry Detergents, 1. Introduction". In Elvers, Barbara, et al. Ullmann's Encyclopedia of Industrial Chemistry. Weinheim, GER: Wiley-VCH. doi:10.1002/14356007.a08_315.pub3/abstract.
  2. ↑ Arno Cahn (30 January 1994). Proceedings of the 3rd World Conference on Detergents: Global Perspectives. The American Oil Chemists Society. p. 141. ISBN 978-0-935315-52-3.
  3. ↑ Jelinek, Charles F.; Mayhew, Raymond L. (September 1954). "Nonionic Detergents". Industrial & Engineering Chemistry 46 (9): 1930–1934. doi:10.1021/ie50537a045.
  4. ↑ A US patent 1970578 A, Schoeller, Conrad & Wittwer, Max, "Assistants for the textile and related industries", issued 1934-08-21, assigned to IG Farbenindustrie AG.
  5. ↑ Kreutzer, Udo R. (February 1984). "Manufacture of fatty alcohols based on natural fats and oils". Journal of the American Oil Chemists’ Society 61 (2): 343–348. doi:10.1007/BF02678792.
  6. 1 2 Kosswig, Kurt (2002). "Surfactants". In Elvers, Barbara, et al. Ullmann's Encyclopedia of Industrial Chemistry. Weinheim, GER: Wiley-VCH. doi:10.1002/14356007.a25_747.
  7. 1 2 Di Serio, Martino; Tesser, Riccardo; Santacesaria, Elio (December 2005). "Comparison of Different Reactor Types Used in the Manufacture of Ethoxylated, Propoxylated Products". Industrial & Engineering Chemistry Research 44 (25): 9482–9489. doi:10.1021/ie0502234.
  8. ↑ Di Serio, M.; Vairo, G.; Iengo, P.; Felippone, F.; Santacesaria, E. (January 1996). "Kinetics of Ethoxylation and Propoxylation of 1- and 2-Octanol Catalyzed by KOH". Industrial & Engineering Chemistry Research 35 (11): 3848–3853. doi:10.1021/ie960200c.
  9. ↑ Cox, Michael F. (September 1990). "The effect of “peaking” the ethylene oxide distribution on the performance of alcohol ethoxylates and ether sulfates". Journal of the American Oil Chemists’ Society 67 (9): 599–604. doi:10.1007/BF02540775.
  10. ↑ US EPA (July 2006). "High production volume (HPV) challenge program".
  11. ↑ Roberts, David W. (May 1998). "Sulfonation Technology for Anionic Surfactant Manufacture". Organic Process Research & Development 2 (3): 194–202. doi:10.1021/op9700439.
  12. 1 2 Anon. [HERA Substance Team] (2004-06-15). Alcohol Ethoxysulphates (AES) Environmental Risk Assessment (PDF). Brussels, BEL: Human and Environmental Risk Assessment (HERA) Project. 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. This 36 page report is an HERA document on this ingredient in European household cleaning products.
  13. ↑ Modler R., Gubler R, & Inoguchi, Y. (2007). "Detergent Alcohols". Chemical Economics Handbook (narrow distribution consultant trade report). Menlo Park, CA: SRI Consulting.(subscription required)
  14. ↑ Federle, Thomas W; Nina R. Itrich (2004). "Effect of Ethoxylate Number and Alkyl Chain Length on the Pathway and Kinetics of Linear Alcohol Ethoxylate Biodegradation in Activated Sludge". Environmental Toxicology and Chemistry: 2790–2798. doi:10.1897/04-053.1.
  15. ↑ Varadaraj, Ramesh; Bock, Jan; Brons, Neil; Zushma, Steve (1994). "Influence of Surfactant Structure on Wettability Modification of Hydrophobic Granular Surfaces". Journal of Colloid and Interface Science 167 (1): 207–210. doi:10.1006/jcis.1994.1350. ISSN 0021-9797.
  16. 1 2 3 4 Anon. [HERA Substance Team] (2009-09-01). Alcohol Ethoxylates, Version 2.0 (PDF). Brussels, BEL: Human and Environmental Risk Assessment (HERA) Project. 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 2 Anon. [HERA Substance Team] (2003-12-02). Alcohol Ethoxysulphates Human Health Risk Assessment, Draft (PDF). Brussels, BEL: Human and Environmental Risk Assessment (HERA) Project. Retrieved 14 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. ↑ Fruijtier-Pölloth, Claudia (2005). "Safety assessment on polyethylene glycols (PEGs) and their derivatives as used in cosmetic products". Toxicology 214 (1-2): 1–38. doi:10.1016/j.tox.2005.06.001. ISSN 0300-483X.
  19. ↑ Stickney, Julie A; Sager, Shawn L; Clarkson, Jacquelyn R; Smith, Lee Ann; Locey, Betty J; Bock, Michael J; Hartung, Rolf; Olp, Steven F (2003). "An updated evaluation of the carcinogenic potential of 1,4-dioxane". Regulatory Toxicology and Pharmacology 38 (2): 183–195. doi:10.1016/S0273-2300(03)00090-4. ISSN 0273-2300.
  20. ↑ SIAR (2006). "SIDS Initial Assessment Report for Long Chain Alcohols" (PDF).
  21. 1 2 Prats, Daniel; Carmen Lopez; Diana Vallejo; Pedro Varo; Victor M. Leon (2006). "Effect of Temperature on the Biodegradation of Linear Alkylbenzene Sulfonate and Alcohol Ethoxylate". Journal of Surfactants and Detergents 9 (1): 69–75. doi:10.1007/s11743-006-0377-8.
  22. ↑ Guckert, J.B.; Walker, D.D.; Belanger, S.E (1996). "Environmental chemistry for a surfactant exotoxicology study supports rapid degradation of C12 alkyl sulfate in a continuous-flow stream mesocosm". Environ. Chem. Toxicol. 15: 262–269. doi:10.1002/etc.5620150306.
  23. ↑ Belanger, SE; KL Rupe; RG Bausch (1995). "Responses of Invertebrates and Fish to Alkyl Sulfate and Alkyl Ethoxylate Sulfate Anionic Surfactants During Chronic Exposure". Environmental Contamination and Toxicology 55: 751–758. doi:10.1007/BF00203763.
  24. ↑ van de Plassche, Erik J.; de Bruijn, Jack H. M.; Stephenson, Richard R.; Marshall, Stuart J.; Feijtel, Tom C. J.; Belanger, Scott E. (1999). "Predicted no-effect concentrations and risk characterization of four surfactants: Linear alkyl benzene sulfonate, alcohol ethoxylates, alcohol ethoxylated sulfates, and soap". Environmental Toxicology and Chemistry 18 (11): 2653–2663. doi:10.1002/etc.5620181135. ISSN 0730-7268.
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