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EC number: 266-928-5 | CAS number: 67701-03-5 This substance is identified by SDA Substance Name: C16-C18 alkyl carboxylic acid and SDA Reporting Number: 19-005-00.
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
Fatty acids are typically unbranched, long chain organic acids with different chain length. They are found in all living organism fulfilling three fundamental roles. Besides their function as part of molecules like phospholipids and glycolipids important for the cell-structure, they are often precursors of signalling molecules such as prostanoids in animals or phytohormones in plants. The third and best understood role of fatty acid is their role as an energy source, particularly in higher animals and plants. Thus, the absorption, distribution, metabolism and elimination of fatty acids have been well investigated for years (Lehninger 1970, Nelson and Cox, 2008).
Absorption
Due to the role as nutritional energy source, fatty acids are absorbed from the lumen of the intestine by different uptake mechanisms depending on the chain length. Short- and medium chain fatty acids (C1 - C12) are rapidly absorbed via intestine capillaries into the blood stream. For butyrate (C4) for example, an absorption rate of 1.9 µmol/cm²/h (= 167 µg/cm²/h) was found in the human intestine (McNeil et al., 1978). In contrast, long chain fatty acids (>C12) are absorbed into the walls of the intestine villi and assembled into triglycerides, which then are transported in the blood stream via lipoprotein particles (chylomicrons). This difference in the uptake mechanism of fatty acids is reflected by the percentage of absorption found when human infants were fed a diet containing different fat sources (Jensen et al., 1986). While an absorption of 99.9 % was found for C8 fatty acid, the long chain C18 fatty acid showed only 64.4 % absorption.
The dermal penetration of fatty acid is very variable based on the heterogeneous physico-chemical properties such as melting temperature, solubility and polarity. The polarity, for example, decreases with increasing chain lengths and/or the abolition of ionisable charged groups, so that they are less-water soluble but more permeable through lipophilic membranes like the skin. As an example, unsaturated long chain fatty acids like oleic acid (C18) have been shown to increase the transepithelial water loss significantly compared to shorter unsaturated fatty acids (Tanojo et al., 1998). Unsaturated long chain fatty acids are therefore used in pharmaceutical transdermal drugs as a flux enhancer for drugs that do not readily cross the skin-barrier on their own. However, the fatty acid itself remains within the lipophilic dermal layer due its polarity.
In contrast to the rapid uptake of fatty acidsviathe oral exposure route, fatty acids are in general poorly absorbed through skin, with a measured rate of less than 1 % after 24-hours exposure (Schaefer and Redelmeier, 1996). The dermal absorption of fatty acids ranged from moderate to very low according to QSAR calculations which are based on molecular weight, logPow and water solubility. The resulting calculated absorption rates are 0.021 mg/cm² for C8 octanoic acid, 0.005 mg/cm² for lauric acid (C12), and 0.26 µg/cm² for stearic acid (C18), respectively (Danish EPA Database, 2004). Thus, the dermal absorption is definitely lower than the absorption after oral uptake.
This was demonstrated in a study where excretion of azelaic acid was analyzed in urine after dermal application of six healthy male volunteers with a single treatment with 5 g of an anti-acne cream containing 20% azelaic acid and after oral application (Taeuber et al., 1992). While 61% of orally administered azelaic acid was detected in the urine, only 2.2% azelaic acid was found in the urine after dermal application.
The dermal uptake of fatty acid is further influenced by the fact that significant skin irritation/corrosion is observed for fatty acids with a chain length less than C10. In these cases local irritation/corrosion is considered as the primary effect.
Taken together the experimental and calculated data show that fatty acids are almost completely absorbed after oral intake, whereas only limited dermal uptake has to be expected.
Distribution and Metabolism
Fatty acids are absorbed through the intestine and transported throughout the body. Short chain fatty acids are taken up and transported complexed to albumin via the portal vain into the blood vessels supplying the liver. Medium and long chain fatty acids are esterified with glycerol to triacylglycerides (TAGs) and packaged in chylomicrons (Spector, 1984). These are transported via the lymphatic system and the blood stream to hepatocytes in the liver as well as to adipocytes and muscle fibers, where they are either stored (i.e. adipose tissue storage depots) or oxidized to yield energy. In addition, some cell types are known to synthesize medium and long chain fatty acids via elongation of shorter fatty acids (Hellerstein, 1999).
The quantitatively most significant oxidation pathway (β-oxidation pathway) is predominantly located in the cardiac and skeletal muscle. In a first step, the fatty acids are converted to acyl-CoA derivatives (aliphatic acyl-CoA) and transported into cells and mitochondria by specific transport systems. Then, the acyl-CoA derivatives are completely metabolized to acetyl-CoA or other key metabolites by the efficient enzymatic removal of the 2-carbon units from the aliphatic acyl-CoA molecule (Coppack et al., 1994). The complete oxidation of fatty acids via the citric acid cycle leads to H2O and CO2 (Coppack, 1994; MacFarlane, 2008). Other pathways for fatty acid catabolism also exist and include α- and ω-oxidation. The resulting main metabolites are acyl-carnitine, acetyl CoA, fatty acyl-CoA, propionyl-CoA and succinyl-CoA (Wanders et al., 2010).
Excretion
Fatty acids are metabolised by various routes in the body to provide energy. Besides this, fatty acids are stored as lipids in adipose tissue, used as part of cellular membranes, as well as precursors for signalling molecules and even long chain fatty acids. Thus, fatty acids are not expected to be excreted to any significant amount in the urine or faeces.
References
Coppack, S.W. et al., 1994. In vivo regulation of lipolysis in humans. Journal of Lipid Research 35 177–193.
Dermwin v 1.43, US EPA, 2009. Estimation Programs Interface Suite™ for Microsoft® Windows, v 4.1.43],, DC,.
Hellerstein, M.K., 1999. De novo lipogenesis in humans: metabolic and regulatory aspects. European Journal of Clinical Nutrition 53 S53–S65.
Lehninger, A.L. 1970. Biochemistry. Worth Publishers, Inc.,.
Jensen, C. et al., 1996. Absorption of individual fatty acids from long chain or medium chain triglycerides in very small infants. The American Journal of Clinical Nutrition 43: May 1986, pp 745-751.
MacFarlane, D.P., 2008. Glucocorticoids and fatty acid metabolism in humans: fuelling fat redistribution in the metabolic syndrome. Journal of Endocrinology (2008) 197, 189–204
McNeil, N.I. et al., 1976.Short chain fatty acid absorption by the human large intestine. Gut, 1978, 19, 819-822
Nelson, D.L. and Cox, M.M. 2008. Lehninger Principles of Biochemistry, Fifth Edition. W. H. Freeman,.
Schaefer, H. and Redelmeier, T.E. 1996.Skin barrier: principles of percutaneous absorption. S. Karger Publishers, New York.
Spector A.A., 1984. Plasma lipid transport.Clin Physiol Biochem. 1984;2(2-3):123-34. Review.
Tanojo, H. et al., 1998. In vivo human skin barrier modulation by topical application of fatty acids. Skin Pharmacol Appl Skin Physiol. 1998 Mar-Apr;11(2):87-97.
Wanders, R.J. et al., 2010. Peroxisoms, lipid metabolism and lipotoxicity. Biochim Biophys Acta. 2010 Mar;1801(3):272-80.
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