Surfactants are compounds that lower the surface tension (or interfacial tension) between two liquids or between a liquid and a solid. Surfactants may act as detergents, wetting agents, emulsifiers, foaming agents, and dispersants.
- 1 Etymology and definition
- 2 Composition and structure
- 3 Characterization of interfaces and surfactant layers
- 4 Classification of surfactants
- 5 Current market and forecast
- 6 Health and environmental controversy
- 7 Biosurfactants
- 8 Safety and environmental risks
- 9 Applications
- 10 See also
- 11 References
- 12 External links
Etymology and definition
In Index Medicus and the United States National Library of Medicine, surfactant/surfactants is reserved for the meaning pulmonary surfactant. For the more general meaning, surface active agent/s is the heading.
Composition and structure
Surfactants are usually organic compounds that are amphiphilic, meaning they contain both hydrophobic groups (their tails) and hydrophilic groups (their heads). Therefore, a surfactant contains both a water insoluble (or oil soluble) component and a water soluble component. Surfactants will diffuse in water and adsorb at interfaces between air and water or at the interface between oil and water, in the case where water is mixed with oil. The water-insoluble hydrophobic group may extend out of the bulk water phase, into the air or into the oil phase, while the water-soluble head group remains in the water phase. This alignment of surfactants at the surface modifies the surface properties of water at the water/air or water/oil interface.
World production of surfactants is estimated at 15 Mton/y, of which about half are soaps. Other surfactants produced on a particularly large scale are linear alkylbenzenesulfonates (1700 kton/y), lignin sulfonates (600 kton/y), fatty alcohol ethoxylates (700 ktons/y), and alkylphenol ethoxylates (500 kton/y).
Structure of surfactant phases in water
In the bulk aqueous phase, surfactants form aggregates, such as micelles, where the hydrophobic tails form the core of the aggregate and the hydrophilic heads are in contact with the surrounding liquid. Other types of aggregates such as spherical or cylindrical micelles or bilayers can be formed. The shape of the aggregates depends on the chemical structure of the surfactants, depending on the balance of the sizes of the hydrophobic tail and hydrophilic head. This is known as the HLB, Hydrophilic-lipophilic balance. Surfactants reduce the surface tension of water by adsorbing at the liquid-gas interface. The relation that links the surface tension and the surface excess is known as the Gibbs isotherm.
Dynamics of surfactants at interfaces
The dynamics of adsorption of surfactants is of great importance for practical applications such as foaming, emulsifying or coating processes, where bubbles or drops are rapidly generated and need to be stabilized. The dynamics of adsorption depends on the diffusion coefficient of the surfactants. Indeed, as the interface is created, the adsorption is limited by the diffusion of the surfactants to the interface. In some cases, there exists a barrier of energy for the adsorption or the desorption of the surfactants, then the adsorption dynamics is known as ‘kinetically limited'. Such energy barrier can be due to steric or electrostatic repulsions. The surface rheology of surfactant layers, including the elasticity and viscosity of the surfactant layers plays a very important role in foam or emulsion stability.
Characterization of interfaces and surfactant layers
Interfacial and surface tension can be characterized by classical methods such as the -pendant or spinning drop method. Dynamic surface tensions, i.e. surface tension as a function of time, can be obtained by the Maximum Bubble Pressure apparatus
The structure of surfactant layers can be studied by ellipsometry or X-Ray reflectivity.
Surface rheology can be characterized by the oscillating drop method or shear surface rheometers such as double-cone, double-ring or magnetic rod shear surface rheometer.
Detergents in biochemistry and biotechnology
In solution, detergents help solubilize a variety of chemical species by dissociating aggregates and unfolding proteins. Popular surfactants in the biochemistry laboratory are SDS and CTAB. Detergents are key reagents to extract protein by lysis of the cells and tissues: They disorganize the membrane's lipidic bilayer (SDS, Triton X-100, X-114, CHAPS, DOC, and NP-40), and solubilize proteins. Milder detergents such as octyl thioglucoside, octyl glucoside or dodecyl maltoside are used to solubilize membrane proteins such as enzymes and receptors without denaturing them. Non-solubilized material is harvested by centrifugation or other means. For electrophoresis, for example, proteins are classically treated with SDS to denature the native tertiary and quaternary structures, allowing the separation of proteins according to their molecular weight.
Detergents have also been used to decellularise organs. This process maintains a matrix of proteins that preserves the structure of the organ and often the microvascular network. The process has been successfully used to prepare organs such as the liver and heart for transplant in rats. Pulmonary surfactants are also naturally secreted by type II cells of the lung alveoli in mammals.
Classification of surfactants
The "tail" of most surfactants are fairly similar, consisting of a hydrocarbon chain, which can be branch, linear, or aromatic. Fluorosurfactants have fluorocarbon chains. Siloxane surfactants have siloxane chains.
Many important surfactants include a polyether chain terminating in a highly polar anionic group. The polyether groups often comprise ethoxylated (polyethylene oxide-like) sequences inserted to increase the hydrophilic character of a surfactant. Polypropylene oxides conversely, may be inserted to increase the lipophilic character of a surfactant.
Surfactant molecules have either one tail or two; those with two tails are said to be double-chained.
Most commonly, surfactants are classified according to polar head group. A non-ionic surfactant has no charge groups in its head. The head of an ionic surfactant carries a net charge. If the charge is negative, the surfactant is more specifically called anionic; if the charge is positive, it is called cationic. If a surfactant contains a head with two oppositely charged groups, it is termed zwitterionic. Commonly encountered surfactants of each type include:
Sulfate, sulfonate, and phosphate esters
Anionic surfactants contain anionic functional groups at their head, such as sulfate, sulfonate, phosphate, and carboxylates. Prominent alkyl sulfates include ammonium lauryl sulfate, sodium lauryl sulfate (SDS, sodium dodecyl sulfate, another name for the compound) and the related alkyl-ether sulfates sodium laureth sulfate, also known as sodium lauryl ether sulfate (SLES), and sodium myreth sulfate.
These include alkyl-aryl ether phosphates and the alkyl ether phosphate
These are the most common surfactants and comprise the alkyl carboxylates (soaps), such as sodium stearate. More specialized species include sodium lauroyl sarcosinate and carboxylate-based fluorosurfactants such as perfluorononanoate, perfluorooctanoate (PFOA or PFO).
Cationic head groups
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- pH-dependent primary, secondary, or tertiary amines: Primary and secondary amines become positively charged at pH < 10:
- Permanently charged quaternary ammonium cation:
- Alkyltrimethylammonium salts: cetyl trimethylammonium bromide (CTAB) a.k.a. hexadecyl trimethyl ammonium bromide, cetyl trimethylammonium chloride (CTAC)
- Cetylpyridinium chloride (CPC)
- Benzalkonium chloride (BAC)
- Benzethonium chloride (BZT)
- Dimethyldioctadecylammonium chloride
- Cetrimonium bromide
- Dioctadecyldimethylammonium bromide (DODAB)
Zwitterionic (amphoteric) surfactants have both cationic and anionic centers attached to the same molecule. The cationic part is based on primary, secondary, or tertiary amines or quaternary ammonium cations. The anionic part can be more variable and include sulfonates, as in CHAPS (3-[(3-Cholamidopropyl)dimethylammonio]-1-propanesulfonate). Other anionic groups are sultaines illustrated by cocamidopropyl hydroxysultaine. Betaines, e.g., cocamidopropyl betaine. Phosphates: lecithin
Many long chain alcohols exhibit some surfactant properties. Prominent among these are the fatty alcohols, cetyl alcohol, stearyl alcohol, and cetostearyl alcohol (consisting predominantly of cetyl and stearyl alcohols), and oleyl alcohol.
- Polyoxyethylene glycol alkyl ethers (Brij): CH3–(CH2)10–16–(O-C2H4)1–25–OH:
- Polyoxypropylene glycol alkyl ethers: CH3–(CH2)10–16–(O-C3H6)1–25–OH
- Glucoside alkyl ethers: CH3–(CH2)10–16–(O-Glucoside)1–3–OH:
- Polyoxyethylene glycol octylphenol ethers: C8H17–(C6H4)–(O-C2H4)1–25–OH:
- Polyoxyethylene glycol alkylphenol ethers: C9H19–(C6H4)–(O-C2H4)1–25–OH:
- Glycerol alkyl esters:
- Polyoxyethylene glycol sorbitan alkyl esters: Polysorbate
- Sorbitan alkyl esters: Spans
- Cocamide MEA, cocamide DEA
- Dodecyldimethylamine oxide
- Block copolymers of polyethylene glycol and polypropylene glycol: Poloxamers
- Polyethoxylated tallow amine (POEA).
According to the composition of their counter-ion
In the case of ionic surfactants, the counter-ion can be:
- Monatomic / Inorganic:
- Polyatomic / Organic:
Current market and forecast
The annual global production of surfactants was 13 million metric tons in 2008, and the annual turnover reached US$24.33 billion in 2009, nearly 2% up from the previous year. The market is expected to experience quite healthy growth by 2.8% annually to 2012 and by 3.5–4% thereafter. Specialists expect the global surfactant market to generate revenues of more than US$41 billion in 2018 – translating to an average annual growth of 4.5%
Health and environmental controversy
Surfactants are routinely deposited in numerous ways on land and into water systems, whether as part of an intended process or as industrial and household waste. Some of them are known to be toxic to animals, ecosystems, and humans, and can increase the diffusion of other environmental contaminants. As a result, there are proposed or voluntary restrictions on the use of some surfactants. For example, PFOS is a persistent organic pollutant as judged by the Stockholm Convention. Additionally, PFOA has been subject to a voluntary agreement by the U.S. Environmental Protection Agency and eight chemical companies to reduce and eliminate emissions of the chemical and its precursors.
The two major surfactants used in the year 2000 were linear alkylbenzene sulfonates (LAS) and the alkyl phenol ethoxylates (APE). They break down in the aerobic conditions found in sewage treatment plants and in soil.
Ordinary dishwashing detergent, for example, will promote water penetration in soil, but the effect would last only a few days (many standard laundry detergent powders contain levels of chemicals such as alkali and chelating agents that can be damaging to plants and should not be applied to soils). Commercial soil wetting agents will continue to work for a considerable period, but they will eventually be degraded by soil micro-organisms. Some can, however, interfere with the life-cycles of some aquatic organisms, so care should be taken to prevent run-off of these products into streams, and excess product should not be washed down.
Anionic surfactants can be found in soils as the result of sludge application, wastewater irrigation, and remediation processes. Relatively high concentrations of surfactants together with multimetals can represent an environmental risk. At low concentrations, surfactant application is unlikely to have a significant effect on trace metal mobility.
Biosurfactants are surface-active substances synthesised by living cells. Interest in microbial surfactants has been steadily increasing in recent years due to their diversity, environmentally friendly nature, possibility of large-scale production, selectivity, performance under extreme conditions, and potential applications in environmental protection. Few of the popular examples of microbial biosurfactants includes Emulsan produced by Acinetobacter calcoaceticus, Sophorolipids produced by several yeasts belonging to candida and starmerella clade, and Rhamnolipid produced by Pseudomonas aeruginosa  etc.
Biosurfactants enhance the emulsification of hydrocarbons, have the potential to solubilise hydrocarbon contaminants and increase their availability for microbial degradation. The use of chemicals for the treatment of a hydrocarbon polluted site may contaminate the environment with their by-products, whereas biological treatment may efficiently destroy pollutants, while being biodegradable themselves. Hence, biosurfactant-producing microorganisms may play an important role in the accelerated bioremediation of hydrocarbon-contaminated sites. These compounds can also be used in enhanced oil recovery and may be considered for other potential applications in environmental protection. Other applications include herbicides and pesticides formulations, detergents, healthcare and cosmetics, pulp and paper, coal, textiles, ceramic processing and food industries, uranium ore-processing, and mechanical dewatering of peat.
Several microorganisms are known to synthesise surface-active agents; most of them are bacteria and yeasts. When grown on hydrocarbon substrate as the carbon source, these microorganisms synthesise a wide range of chemicals with surface activity, such as glycolipid, phospholipid, and others. These chemicals are synthesised to emulsify the hydrocarbon substrate and facilitate its transport into the cells. In some bacterial species such as Pseudomonas aeruginosa, biosurfactants are also involved in a group motility behavior called swarming motility.
Safety and environmental risks
Most anionic and nonionic surfactants are nontoxic, having LD50 comparable to sodium chloride. The situation for cationic surfactants is more diverse. Dialkyldimethylammonium chlorides have very low LD50's (5 g/kg) but alkylbenzyldimethylammonium chloride has an LD50 of 0.35 g/kg. Prolonged exposure of skin to surfactants can cause chaffing because surfactants (e.g., soap) disrupts the lipid coating that protects skin (and other) cells.
Biosurfactants and Deepwater Horizon
The use of biosurfactants as a way to remove petroleum from contaminated sites has been studied and found to be safe and effective in the removal petroleum products from soil. Biosurfactants were not used by BP after the Deepwater Horizon oil spill. However, unprecedented amounts of Corexit (active ingredient: Tween-80), were sprayed directly into the ocean at the leak and on the sea-water's surface, the theory being that the surfactants isolate droplets of oil, making it easier for petroleum-consuming microbes to digest the oil.
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- Fabric softeners
- Ski waxes, snowboard wax
- Deinking of recycled papers, in flotation, washing and enzymatic processes
- Agrochemical formulations
- Quantum dot coatings
- Biocides (sanitizers)
- Spermicides (nonoxynol-9)
- Pipelines, liquid drag reducing agent
- Alkali Surfactant Polymers (used to mobilize oil in oil wells)
- Leak Detectors
- Cleavable detergent
- MBAS assay, an assay that indicates anionic surfactants in water with a bluing reaction.
- Oil dispersants
- Pulmonary surfactant
- Surfactants in paint
- Rosen MJ and Kunjappu JT (2012). Surfactants and Interfacial Phenomena (4th ed.). Hoboken, New Jersey: John Wiley & Sons. p. 1. ISBN 1-118-22902-9.
- "Bubbles, Bubbles, Everywhere, But Not a Drop to Drink". The Lipid Chronicles. Retrieved 08/01/2012.
- Kurt Kosswig "Surfactants" in Ullmann's Encyclopedia of Industrial Chemistry, Wiley-VCH, 2005, Weinheim. doi:10.1002/14356007.a25_747
- Wein, Harrison (28 June 2010). "Progress Toward an Artificial Liver Transplant – NIH Research Matters". National Institutes of Health (NIH).
- http://www.chem.wisc.edu/areas/reich/pkatable/index.htm. Missing or empty
- "Market Report: World Surfactant Market". Acmite Market Intelligence.
- Reznik, Gabriel O.; Vishwanath, Prashanth; Pynn, Michelle A.; Sitnik, Joy M.; Todd, Jeffrey J.; Wu, Jun; Jiang, Yan; Keenan, Brendan G. et al. (2010). "Use of sustainable chemistry to produce an acyl amino acid surfactant". Applied Microbiology and Biotechnology 86 (5): 1387–97. doi:10.1007/s00253-009-2431-8. PMID 20094712.
- Market Study on Surfactants by Ceresana Research
- Metcalfe, Tracy L.; Dillon, Peter J.; Metcalfe, Chris D. (2008). "DETECTING THE TRANSPORT OF TOXIC PESTICIDES FROM GOLF COURSES INTO WATERSHEDS IN THE PRECAMBRIAN SHIELD REGION OF ONTARIO, CANADA". Environmental Toxicology and Chemistry 27 (4): 811–8. doi:10.1897/07-216.1. PMID 18333674.
- Emmanuel, E; Hanna, K; Bazin, C; Keck, G; Clement, B; Perrodin, Y (2005). "Fate of glutaraldehyde in hospital wastewater and combined effects of glutaraldehyde and surfactants on aquatic organisms". Environment International 31 (3): 399–406. doi:10.1016/j.envint.2004.08.011. PMID 15734192.
- Murphy, M; Alkhalidi, M; Crocker, J; Lee, S; Oregan, P; Acott, P (2005). "Two formulations of the industrial surfactant, Toximul, differentially reduce mouse weight gain and hepatic glycogen in vivo during early development: effects of exposure to Influenza B Virus". Chemosphere 59 (2): 235–46. doi:10.1016/j.chemosphere.2004.11.084. PMID 15722095.
- USEPA: "2010/15 PFOA Stewardship Program" Accessed October 26, 2008.
- Scott, M; Jones, Malcolm N (2000). "The biodegradation of surfactants in the environment". Biochimica et Biophysica Acta (BBA) – Biomembranes 1508: 235–251. doi:10.1016/S0304-4157(00)00013-7.
- Hernández-Soriano Mdel, C; Degryse, F; Smolders, E (2011). "Mechanisms of enhanced mobilisation of trace metals by anionic surfactants in soil". Environmental pollution (Barking, Essex : 1987) 159 (3): 809–16. doi:10.1016/j.envpol.2010.11.009. PMID 21163562.
- Hernández-Soriano Mdel, C; Peña, A; Dolores Mingorance, M (2010). "Release of metals from metal-amended soil treated with a sulfosuccinamate surfactant: effects of surfactant concentration, soil/solution ratio, and pH". Journal of environmental quality 39 (4): 1298–305. doi:10.2134/jeq2009.0242. PMID 20830918.
- Banat, I. M., Makkar, R. S., Cameotra, S. S. (2000). "Potential commercial applications of microbial surfactants". Appl. Microbiol. Biotechnol. 53 (5): 495–508. doi:10.1007/s002530051648. PMID 10855707.
- Rahman, K. S. M., Thahira-Rahman, J., McClean, S., Marchant, R., Banat, I.M (2002). "Rhamnolipid biosurfactants production by strains of Pseudomonas aeruginosa using low cost raw materials". Biotechnol Prog. 18 (6): 1277–1281. doi:10.1021/bp020071x. PMID 12467462.
- Appl. Environ. Microbiol. September 1983 vol. 46 no. 3 573–579
- Kurtzman, C. P.; Price, N. P.; Ray, K. J.; Kuo, T. M., Production of sophorolipid biosurfactants by multiple strains of the Starmerella (Candida) bombicola yeast clade. FEMS Microbiol Lett 2010, 311 (2), 140–146.
- Parekh, V. J.; Pandit, A. B., Optimization of fermentative production of sophorolipid biosurfactant by starmerella bombicola NRRL Y-17069 using response surface methodology. International Journal of Pharmacy and Biological Sciences 2011, 1 (3), 103–116
- Ito S, Honda H, Tomita F, Suzuki T. Rhamnolipids produced by Pseudomonas aeruginosa grown on n-paraffin (mixture of C 12 , C 13 and C 14 fractions). J Antibiot (Tokyo) 1971 Dec;24(12):855–859
- Rosenberg, E., Ron, E. Z (1999). "High and low molecular mass microbial surfactants". Appl. Microbiol. Biotechnol. 52 (2): 154–162. doi:10.1007/s002530051502. PMID 10499255.
- Del ‘Arco, J. P., De Franca, F. P (2001). "Influence of oil contamination levels on hydrocarbon biodegradation in sandy sediments". Environ. Pollut. 110: 515–519.
- Rahman, K. S. M., Banat, I.M., Thahira-Rahman, J., Thayumanavan, T., Lakshmanaperumalsamy, P (2002). "Bioremediation of gasoline contaminated soil by a bacterial consortium amended with poultry litter, coir pith and rhamnolipid biosurfactant". Bioresource Technol. 81: 25–32. doi:10.1016/S0960-8524(01)00105-5.
- Shulga, A., Karpenko, E., Vildanova-Martsishin, R., Turovsky, A., Soltys, M (1999). "Biosurfactant enhanced remediation of oil-contaminated environments". Adsorpt. Sci. Technol. 18: 171–176.
- Ron, E. Z., Rosenberg, E (2001). "Natural roles of biosurfactants". Environ. Microbiol. 3 (4): 229–236. doi:10.1046/j.1462-2920.2001.00190.x. PMID 11359508.
- Banat, I. M (1995). "Biosurfactants production and possible uses in microbial enhanced oil recovery and oil pollution remediation: a review". Bioresource Technol. 51: 1–12. doi:10.1016/0960-8524(94)00101-6.
- Kim, S.E., Lim, E. J., Lee, S.O., Lee , J. D., Lee, T.H (2000). "Purification and characterisation of biosurfactants from Nocardia sp. L-417". Biotechnol. Appl. Biochem. 31 (3): 249–253. doi:10.1042/BA19990111.
- Muriel, J.M., Bruque, J.M., Olias, J.M., Sanchez, A. J (1996). "Production of biosurfactants by Cladosporium resinae". Biotechnol. Lett. 18 (3): 235–240. doi:10.1007/BF00142937.
- Desai, J.D., Banat, I.M (1997). "Microbial production of surfactants and their commercial potential". Microbiol. Mol. Biol. Rev. 61 (1): 47–64. PMC 232600. PMID 9106364.
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