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EC number: 247-655-0 | CAS number: 26399-02-0
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
LC50 = 2978 mg/kg for Corophium volutator (OSPARCOM, 1995)
Key value for chemical safety assessment
- EC50 or LC50 for marine water sediment:
- 2 978 mg/kg sediment dw
Additional information
The Short Chain Alcohol Esters (SCAE C2-C8) category covers esters from
a fatty acid (C8-C29) and a C2-C8 alcohol (ethanol, isopropanol,
butanol, isobutanol, pentanol, iso-pentanol, hexanol, 2-ethylhexanol or
octanol). This category includes both well-defined mono-constituent
substances as well as related UVCB substances with varying fatty acid
chain lengths.
Fatty acid esters are generally produced by chemical reaction of an
alcohol (e.g. isopropanol) with an organic acid (e.g. stearic acid) in
the presence of an acid catalyst (Radzi et al., 2005). The
esterification reaction is started by a transfer of a proton from the
acid catalyst to the alcohol to form an alkyloxonium ion. Acid is
protonated on its carbonyl oxygen followed by a nucleophilic addition of
a molecule of the alcohol to a carbonyl carbon of acid. An intermediate
product is formed. This intermediate product loses a water molecule and
proton to give an ester (Liu et al, 2006; Lilja et al., 2005; Gubicza et
al., 2000; Zhao, 2000). Esters are the final product of esterification.
In accordance with Article 13 (1) of Regulation (EC) No 1907/2006,
"information on intrinsic properties of substances may be generated by
means other than tests, provided that the conditions set out in Annex XI
are met”. In particular, information shall be generated whenever
possible by means other than vertebrate animal tests, which includes the
use of information from structurally related substances (grouping or
read-across).
The rationale for grouping the substances in the SCAE C2-C8 category is
based on similarities in physicochemical, ecotoxicological and
toxicological properties.
In this particular case, the similarity of the SCAE C2-C8 category
members is justified, in accordance with the specifications listed in
Regulation (EC) No. 1907/2006 Annex XI, 1.5
Grouping of substances and read across, based on representative
molecular structure, physico-chemical properties, tox-, ecotoxicological
profiles, supported by a robust set of experimental data and QSAR
calculations. There is no convincing evidence that any one of these
chemicals might lie out of the overall profile of this category,
respectively.
Grouping of substances into this category is based on:
• Similar/overlapping structural features or functional groups: All category members are monoesters of alcohols (C2-C8) and fatty acids (C8-C29), with 13 to 32 carbons in total.
• Common precursors and the likelihood of common breakdown products via biological
processes: All category members are subject to enzymatic hydrolysis by pancreatic lipases (Mattson and Volpenhein, 1972; and references therein). The resulting free fatty acids and alcohols are absorbed from the intestine into the blood stream. Fatty acids are either metabolised via the beta-oxidation pathway in order to generate energy for the cell or reconstituted into glyceride esters and stored in the fat depots in the body. The alcohols are metabolised primarily in the liver through a series of oxidative steps, finally yielding carbon dioxide (Berg et al., 2002).
• Similar physico-chemical properties: The log Kow and log Koc values of all category members are high (log Kow > 4, log Koc > 3), increasing with the size of the molecule. The substances are poorly soluble in water and have low vapour pressure.
• Common properties for environmental fate & eco-toxicology: Based on experimental data, all substances are readily biodegradable, with the exception of Fatty acids, C16-18 and C18 unsatd. branched and linear, butyl esters (CAS No. 163961-32 -8), which is inherently biodegradable, and do not show toxic effects up to the limit of water solubility.
• Common levels and mode of human health related effects: All available
experimental data indicate that the members of the SCAE C2-C18 category
are not acutely toxic, are not irritating to the skin or to the eyes and
do not have sensitizing properties. Repeated dose toxicity was shown to
be low for all substances. None of the substances showed mutagenic
effects, and toxicity to reproduction was low throughout the category.
Having regard to the general rules for grouping of substances and read-across approach laid down in Annex XI, Item 1.5, of Regulation (EC) No 1907/2006, whereby substances may be considered as a category provided that their physicochemical, toxicological and ecotoxicological properties are likely to be similar or follow a regular pattern as a result of structural similarity, the substances listed below are allocated to the category of SCAE C2-C8.
Members of the SCAE C2-C8 Category:
EC No. |
CAS No. |
Chemical name |
Alcohol Carbon No. |
Fatty acid Carbon No. |
Total Carbon |
MW |
208 -868-4 |
544-35-4 (b) |
Ethyl linoleate |
2 |
18 |
20 |
308.50 |
203-889-5 |
111-62-6 |
Ethyl oleate |
2 |
18 |
20 |
310.52 |
293-054-1 |
91051-05-7 |
Fatty acids, essential, ethyl esters |
2 |
14 - 22 |
16 - 24 |
252.39-368.64 |
233-560-1 |
10233-13-3 |
Isopropyl laurate |
3 |
12 |
15 |
242.41 |
203-751-4 |
110-27-0 |
Isopropyl myristate |
3 |
14 |
17 |
270.46 |
205-571-1 |
142-91-6 |
Isopropyl palmitate |
3 |
16 |
19 |
298.51 |
203-934-9 |
112-10-7 |
Isopropyl stearate |
3 |
18 |
21 |
326.56 |
269-023-3 |
68171-33-5 (a) |
Isopropyl isostearate |
3 |
18 |
21 |
326.56 |
203-935-4 |
112-11-8 |
Isopropyl oleate |
3 |
18 |
21 |
324.55 |
292-962-5 |
91031-58-2 |
Fatty acids, C16-18, isopropyl esters |
3 |
16 - 18 |
19 - 21 |
312.54-326.57 |
264-119-1 |
63393-93-1 |
Fatty acids, lanolin, isopropyl esters |
3 |
10 - 29 |
13 - 32 |
214.34-480.85 |
204-666-5 |
123-95-5 |
butyl stearate |
4 |
18 |
22 |
340.59 |
267-028-5 |
67762-63-4 |
Fatty acids, tall-oil, butyl esters |
4 |
18 |
22 |
423.72 |
287-039-9 |
85408-76-0 |
Fatty acids, C16-18, Bu esters |
4 |
16 - 18 |
20 - 22 |
312.53-340.58 |
284-863-0 |
84988-74-9 |
Fatty acids, C16-18 and C18-unsatd., Bu esters |
4 |
16 - 18 |
20 - 22 |
312.53- 340.58 |
|
163961-32-8 |
Fatty acids, C16-18 and C18 unsatd. branched and linear, butyl esters |
4 |
16 - 18 |
20 - 22 |
312.54- 340.58 |
211-466-1 |
646-13-9 |
Isobutyl stearate |
4 |
18 |
22 |
340.59 |
288-668-1 |
85865-69-6 |
Fatty acids, C16-18, iso-Bu esters |
4 |
16 - 18 |
20 - 22 |
312.54- 340.60 |
84988-79-4 |
84988-79-4 |
Fatty acids, C16-18 and C18-unsatd., iso-Bu esters |
4 |
16 - 18 |
20 - 22 |
312.54- 340.60 |
228-626-1 |
6309-51-9 |
Isopenthyl laurate Dodecanoic acid, 2-methyl butyl ester |
5 |
12 |
17 |
270.46 |
694-886-1 |
1365095-43-7 |
Isopentyl decanoate and octanoate |
5 |
8 - 10 |
13 - 15 |
214.344- 242.40 |
251-932-1 |
34316-64-8 |
Dodecanoic acid, hexyl ester |
6 |
12 |
18 |
284.49 |
218-980-5 |
2306-88-9 |
octyl octanoate |
8 |
8 |
16 |
256.42 |
|
84713-06-4 |
Dodecanoic acid, isooctyl ester |
8 |
12 |
20 |
312.53 |
243-697-9 |
20292-08-4 |
2-Ethylhexyl laurate |
8 |
12 |
20 |
312.53 |
692-946-1 |
649747-80-8 |
Fatty acids, C8-10, 2-ethylhexyl esters |
8 |
8 - 10 |
16 - 18 |
256.42-284.48 |
603-931-6 |
135800-37-2 |
Fatty acids, C8-16, 2-ethylhexyl esters |
8 |
12 - 14 |
20 - 22 |
256.42-368.65 |
249-862-1 |
29806-73-3 |
2-ethylhexyl ester palmitate |
8 |
16 |
24 |
368.64 |
|
22047-49-0 |
2-Ethyl hexyl Stearate |
8 |
18 |
26 |
396.69 |
295-366-3 |
92044-87-6 |
Fatty acids, coco, 2-ethylhexyl esters |
8 |
12 - 18 |
20 - 26 |
312.53-340.60 |
292-951-5 |
91031-48-0 |
Fatty acids, C16-18, 2-ethylhexyl esters |
8 |
16 - 18 |
24 - 26 |
368.65-396.70 |
285-207-6 |
85049-37-2 |
Fatty acids, C16-18 and C18-unsatd., 2-ethylhexyl esters |
8 |
16 - 18 |
24 - 26 |
368.65-396.70 |
247-655-0 |
26399-02-0 |
2-Ethylhexyl oleate |
8 |
18 |
26 |
394.67 |
261-819-9 |
59587-44-9 |
2-ethylhexyl nonanoate |
8 |
9 |
17 |
270.45 |
297-443-7 |
93572-14-6 |
Fatty acids, soya, 2-ethylhexyl esters |
8 |
16 - 18 |
24 - 26 |
368.65-396.70 |
(a) Category members subject to the REACh Phase-in registration deadline
of 31 May 2013 are indicated in bold font.
(b) Substances that are either already registered under REACh, or not
subject to the REACh Phase-in registration deadline of 31 May 2013, are
indicated in normal font.
For all category members registered under REACh a full data set for each
endpoint is provided. For substances not subject to the current REACh
Phase-in registration, lack of data for a given endpoint is indicated by
"--".
The available data allow for an accurate hazard and risk assessment of
the category and the category concept is applied for the assessment of
environmental fate and environmental and human health hazards. Thus,
where applicable, environmental and human health effects are predicted
from adequate and reliable data for source substance(s) within the group
by interpolation to the target substances in the group (read-across
approach) applying the group concept in accordance with Annex XI, Item
1.5, of Regulation (EC) No 1907/2006. In particular, for each specific
endpoint the source substance(s) structurally closest to the target
substance is/are chosen for read-across, with due regard to the
requirements of adequacy and reliability of the available data.
Structural similarities and similarities in properties and/or activities
of the source and target substance are the basis of read-across. For a
detailed review of the data matrix please refer to the category
justification attached in section 13 in IUCLID.
Sediment toxicity
Three reliable marine sediment studies are available for the SCAE C2-C8 category members Fatty acids, C16-18 and C18-unsaturated, isobutyl esters (CAS No. 84988-74-9), Fatty acids, C8-16, 2-ethylhexyl esters (CAS No. 135800-37-2) and Fatty acids, C16-18 and C18-unsaturated, 2-ethylhexyl esters (CAS No. 85049-37-2). All studies were conducted according to the OSPARCOM guideline (Paris Commission Guidelines for conducting sediment toxicity tests with the amphipod Corophium volutator, 1995) and GLP (Gibson, 1999; White, 1999; Hudson, 2000). In these studies, the test organism, Corophium volutator, was exposed to the test substance in a static system with natural sediment for 10 days. The LC50 values were determined to be 2978.47 mg/kg for Fatty acids, C16-18 and C18-unsatd., iso-Bu esters, > 1439.41 mg/kg for Fatty acids, C16-18 and C18-unsatd., 2-ethylhexyl esters and > 10000 mg/kg for Fatty acids, C8-16, 2-ethylhexyl esters, respectively.
The experimental results indicate a very low toxicity to sediment organism for the substances tested. The test substances represent C16-C24, C20-22 and C24-26 fatty acid esters. Since all category members are poorly soluble in water (< 0.05 mg/L to < 0.15 mg/L), have high adsorption potential (Koc > 3) and a high log Kow (> 4), their behaviour in the sediment compartment is expected to be highly similar to the tested substances. They are all esters of fatty acids and alcohols, with 13 to 32 carbons, and are therefore expected to follow similar metabolic pathways if taken up by organisms. The available studies can therefore be used as read-across to cover all other substances within the category.
The three short-term sediment tests available within the SCAE C2-C8
category all show a very low toxicity. The substances are also readily
biodegradable and acute and chronic data available indicate no hazard to
aquatic or terrestrial organisms. Long-term testing of sediment
organisms is therefore not considered necessary.
References:
Berg, J.M., Tymoczko, J.L. and Stryer, L., 2002, Biochemistry, 5thedition, W.H. Freeman and Company
Gubicza, L., Kabiri-Badr, A., Keoves, E., Belafi-Bako, K. (2000): Large-scale enzymatic production of natural flavour esters in organic solvent with continuous water removal. Journal of Biotechnology 84(2): 193-196
Lilja, J. et al. (2005). Esterification of propanoic acid with ethanol, 1-propanol and butanol over a heterogeneous fiber catalyst. Chemical Engineering Journal, 115(1-2): 1-12.
Liu, Y. et al. (2006). A comparison of the esterification of acetic acid with methanol using heterogeneous versus homogeneous acid catalysis. Journal of Catalysis 242: 278-286.
Mattson, F.H. and Volpenheim, R.A. (1972): Relative rates of hydrolysis by rat pancreatic lipase of esters of C2-C18 fatty acids with C1-C18 primary n-alcohols, Journal of Lipid Research, 10, 1969
Radzi, S.M. et al.(2005). High performance enzymatic synthesis of oleyl oleate using immobilised lipase from Candida antartica. Electronic Journal of Biotechnology 8: 292-298.
Tocher, D.R. (2003):Metabolism and function of lipids and fatty acids in teleost fish,Reviews of Fisheries Science, 11 (2), 197
Zhao, Z. (2000). Synthesis of butyl propionate using novel aluminophosphate molecular sieve as catalyst. Journal of Molecular Catalysis 154(1-2): 131-135
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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