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EC number: 629-780-6 | CAS number: 1234694-02-0
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well documented publication.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- The safety of the use of ethyl oleate in food is supported by metabolism data in rats and clinical safety data in humans.
- Author:
- Bookstaff, R.C. et al.
- Year:
- 2 003
- Bibliographic source:
- Regul Toxicol Pharmacol.; 37(1):133-48.
Materials and methods
- Objective of study:
- other: ADME
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Principles of method if other than guideline:
- The absorption, distribution, and excretion of radiolabelled ethyl oleate (EO) was studied in Sprague-Dawley rats after a single, peroral dose of 1.7 or 3.4 g/kg body weight and was compared with a radiolabelled triacylglycerol (TG) containing only oleic acid as the fatty acid (triolein).
- GLP compliance:
- yes
Test material
- Reference substance name:
- Ethyl oleate
- EC Number:
- 203-889-5
- EC Name:
- Ethyl oleate
- Cas Number:
- 111-62-6
- Molecular formula:
- C20H38O2
- IUPAC Name:
- ethyl (Z)-octadec-9-enoate
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- (14C) Ethyl oleate
Test animals
- Species:
- rat
- Strain:
- other: Sprague-Dawley [Crl:CD (SD) IGS BR]
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratory
- Age at study initiation: At dosing, the animals were approximately 8-10 weeks of age.
- Weight at study initiation: At dosing, the animals weighed 194-253 g.
- Housing: Housed individually in glass metabolism cages designed for the separation and collection of urine, feces, and expaired air.
- Individual metabolism cages: yes
- Diet :A certified standard rodent diet (Harlan Teklad) were available, ad libitum, at all times throughout the study period.
- Water :Water was available, ad libitum, at all times throughout the study period.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): Temperature was controlled throughout the study.
- Humidity (%): Humidity was controlled throughout the study.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Duration and frequency of treatment / exposure:
- Single dose
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1.7 or 3.4 g/kg. Each animal received approximately 120 µCi/mg of radioactivity.
- No. of animals per sex per dose / concentration:
- Twenty male and twenty female rats were divided into four groups, each group consisting of five rats per gender.
- Control animals:
- no
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled :Adrenal glands, Bone (both femurs), Bone marrow (both), Brain, Carcass (residual), Cecum, Colon, Duodenum, Eyes (both), Fat (mesenteric), Heart, Ileum, Jejunum, Kidneys, Liver, Lungs, Lymph nodes (mes), Muscles (thigh), Ovaries, Pancreas, Pituitary gland, Prostate, Rectum, Salivary glands, Spleen, Stomach, Testes, Thymus, Thyroid/parathyroids, Urine, feces and expired air.
- Time and frequency of sampling: Urine and feces were collected every 24 h until 72 h post-dose. Expired air was measured at 6, 12, 18, and 24 h post-dose. Animals were sacrificed at 72 h post-dose by exsanguination (cardiac puncture) under halothane anesthesia and tissues, including blood, were collected for anlaysis of radioactivity in ech matrix (See table 3 for details).
- Other: All samples were homogenised or mixed prior to radioanalysis, which was performed by either direct liquid scintillation counting (LSC) or by combustion followed by LSC, as appropriate. All samples were analysed in duplicate, if sample size allowed. Analysis was repeaed, sample size allowing, if the variability between the replicates was more than 10%. - Statistics:
- Statistical analyses were limited to simple expressions of variation, such as mean and standard deviations.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Ethyl oleate was well absorbed with approximately 75-88 % of the dose absorbed (see table 2 for details).
- Details on distribution in tissues:
- Radioactivity (presumably in the form of oleic acid) recovered from all the tissues (including residual carcass) collected at sacrifice accounted for approximately 14-23% of the dose of (14C)EO. The males in all groups had a higher percentage of radioactivity in the tissues than did the corresponding females. In the treatment groups, the vast majority of radioactivity was found in the residual carcass (84-89% of the total tissue radioactivity). Aside from the residual carcass, the tissue with the highest percentage of radioactivity for all the groups was mesentric fat with levels ranging from 0.4-0.7% in the EO group ( See table 3 for detail).
Tissue concentration were roughly dose-proportional with no remarkable-related differences. The overall mean blood to plasma concentration ratios for total radioactivity was very close to 1, thus indicating that radioactivity partitioned into both the cellular and plasma components of blood.
With the exception of the brain and eyes, which had a tissue: plasma ratios of approximately 1 or less, the tissue to plasma ratio for all other tissues at sacrifice was higher than 1, indicating that (14C) EO- derived radioactivity had a tendency to accumulate in the tissue.
- Details on excretion:
- The cumulative excretion of radioactivity in each matrix per group is presented in table 2a and 2b for the lower (1.7 g/kg) and higher (3.4 g/kg) dose levels.
The main route of excretion of radioactivity in the groups was via expired air as CO2. Excretion of (14C) CO2 was rapid in the groups such that by 12 h after dosing 40-70% of the administered dose was excreted in expired air. The females in the groups had a higher percentage of radioactivity expired as CO2 than did the corresponding males. A second route of elimination of radioactivity was via the feces in the groups. The mean percent dose recovered in the feces over the first 24 h post-dose was approximately 8 and 20% for the low and high doses of (14C) EO, respectively.
Renal elimination was minimal, with approximately 2% of the radioactivity recovered in urine over 72 h post-dose for the groups (See table 2a and 2b for detail).
Metabolite characterisation studies
- Details on metabolites:
- Ethyl oleate (EO) is rapidly and extensively hydrolysed to free oleic acid, absorbed, and delivered to tissue where it undergoes β- oxidation. The basis for this conclusion is the rapid excretion of a significant percentage of the administered dose (30-40%) as CO2 within the first 6 h and 40-70% of the dose within 12 h. For this to happen, the free oleic acid moiety has to be available.
At the 1.7 g/kg dose, the tissue distribution of EO-derived radioactivity was similar to that of triacylglycerol (TG)-derived radioactivity. Again, this supports the conclusion that EO is rapidly hydrolysed to oleic acid, absorbed, and distributed within the body in the same way as dietary sources of oleic acid. The similar tissue distribution between EO-derived radioactivity and TG-derived radioactivity suggests that the radiolabel in tissue represents the same chemical form (i.e., the oleic acid moiety).
Any other information on results incl. tables
It is likely that the vast majority of the actual chemical form of the ethyl oleate molecule absorbed is the oleic acid moiety. This is based on published in vivo studies which have demonstrated that EO and other fatty acid esters are rapidly hydrolysed to ethanol and free fatty acid within the GI tract(Froyland et al., 1996; Saghir et al.,199). Other supporting evidence for absorption of the free fatty acid (or very rapid in situ formation of the free acid) is the rapid excretion of radioactivity as CO2. This is because the radiolabel was located on the carboxyl carbon. Oxidation of fatty acids requires a free carboxyl end (i.e., not esterified). The rate and extent of 14CO2 extretion was similar between the EO and the TG groups indicating that both lipids deliver free fatty acid to tissue for oxidation at approximately the same rate and extent.
Table 2. The overall mean total recovery of radioactive dose by 72 h post-dose.
|
Males (%) |
Females (%) |
Group 1 (Ethyl oleate 3.4 g/kg) |
74.9 |
70.5 |
Group 2 (Ethyl oleate 1.7 g/kg) |
87.5 |
87.3 |
Table 2A. Cumulative percent recovery of radioactivity following administration of a single oral dose of (14C) Ethyl oleate (1.7 g/kg) to males and females rats.
Collection intervals (h) |
Percent of dose |
|||
(14C) Ethyl oleate (1.7 g/kg) |
||||
Males |
Females |
|||
Mean (n=5) SD |
Mean (n=5) SD |
|||
Urine |
|
|||
0-24 |
1.62 |
0.10 |
1.84 |
0.13 |
0-48 |
1.88 |
0.11 |
2.09 |
0.14 |
0-72 |
1.98 |
0.12 |
2.21 |
0.13 |
Feces |
|
|
|
|
0-24 |
6.81 |
1.83 |
7.57 |
1.25 |
0-48 |
7.50 |
1.80 |
8.24 |
1.10 |
0-72 |
7.68 |
1.80 |
8.42 |
1.10 |
Expired air (carbon dioxide) |
|
|
|
|
0-6 |
35.7 |
8.3 |
42.7 |
6.1 |
0-12 |
49.8 |
7.8 |
59.5 |
7.1 |
0-18 |
53.1 |
7.5 |
63.2 |
7.3 |
0-24 |
55.1 |
7.1 |
65.2 |
6.9 |
0-48 |
60.0 |
7.5 |
69.0 |
6.7 |
0-72 |
62.3 |
7.4 |
70.7 |
6.3 |
Tissues |
|
|
|
|
72h |
23.2 |
4.3 |
14.4 |
5.1 |
Mass balancea |
95.3 |
2.0 |
95.9 |
0.7 |
2B. Cumulative percent recovery of radioactivity following administration of single dose of (14C) Ethyl oleate (3.4 g/kg) to male and female rats.
Collection intervals (h) |
Percent of dose |
|||
(14C) Ethyl oleate (3.4 g/kg) |
||||
Males |
Females |
|||
Mean (n=5) SD |
Mean (n=5) SD |
|||
Urine |
|
|||
0-24 |
1.10 |
0.13 |
1.11 |
0.17 |
0-48 |
1.29 |
0.14 |
1.33 |
0.21 |
0-72 |
1.37 |
0.15 |
1.44 |
0.21 |
Feces |
|
|
|
|
0-24 |
16.7 |
8.2 |
20.3 |
10.0 |
0-48 |
17.6 |
8.0 |
21.5 |
10.3 |
0-72 |
17.7 |
8.0 |
21.7 |
10.3 |
Expired air (carbon dioxide) |
|
|
|
|
0-6 |
25.4 |
1.4 |
22.8 |
6.2 |
0-12 |
41.5 |
2.5 |
43.4 |
9.8 |
0-18 |
44.7 |
3.8 |
47.2 |
9.4 |
0-24 |
45.9 |
3.9 |
49.0 |
9.2 |
0-48 |
49.6 |
4.0 |
53.3 |
9.4 |
0-72 |
51.4 |
4.1 |
54.8 |
10.0 |
Tissues |
|
|
|
|
72h |
22.1 |
6.0 |
14.3 |
2.6 |
Mass balancea |
92.8 |
0.6 |
92.8 |
4.0 |
aIncludes radioactivity recovered in cage, cage wipe and from analysis of activated charcoal trap to determine of volatile organic compounds in expired air.
Table 3. Percent recovery of radioactive dose in tissue.
|
Ethyl oleate (1.7 g/kg) |
Ethyl oleate (1.7 g/kg) |
Ethyl oleate (3.4 g/kg) |
Ethyl oleate (3.4 g/kg) |
||||
|
Mean |
SD |
Mean |
SD |
Mean |
SD |
Mean |
SD |
Adrenal glands |
0.01 |
0 |
0.02 |
0.01 |
0.01 |
0 |
0.01 |
0 |
Bone (both femurs) |
0.05 |
0.03 |
0.03 |
0.01 |
0.03 |
0.02 |
0.02 |
0.01 |
Bone marrow (both) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Brain |
0.01 |
0 |
0.01 |
0 |
0.02 |
0.01 |
0.01 |
0.01 |
Carcass (residual) |
20.7 |
3.77 |
12.1 |
4.31 |
19.1 |
5.14 |
12.1 |
2.15 |
Cecum |
0.1 |
0.03 |
0.08 |
0.03 |
0.11 |
0.02 |
0.08 |
0.05 |
Cecum (content/wash) |
0.03 |
0.01 |
0.02 |
0 |
0.03 |
0.02 |
0.03 |
0.01 |
Colon |
0.16 |
0.04 |
0.09 |
0.04 |
0.14 |
0.07 |
0.09 |
0.22 |
Colon(content/wash) |
0.02 |
0.01 |
0.01 |
0 |
0.02 |
0.01 |
0.01 |
0 |
Duodenum |
0.03 |
0.01 |
0.03 |
0.01 |
0.03 |
0.01 |
0.02 |
0.01 |
Duodenum(content/wash) |
0.01 |
0.01 |
0.01 |
0 |
0 |
0.01 |
0.01 |
0 |
Eyes (both) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Fat (mesenteric) |
0.68 |
0.36 |
0.38 |
0.19 |
0.74 |
0.37 |
0.55 |
0.28 |
Heart |
0.03 |
0 |
0.03 |
0.01 |
0.02 |
0.01 |
0.02 |
0.01 |
Ileum |
0.2 |
0.06 |
0.16 |
0.04 |
0.22 |
0.01 |
0.02 |
0.01 |
Ileum(content/wash) |
0.05 |
0.01 |
0.05 |
0.02 |
0.06 |
0.01 |
0.07 |
0.01 |
Jejunum |
0.11 |
0.03 |
0.09 |
0.02 |
0.12 |
0.06 |
0.02 |
0.07 |
Jejunum(content/wash) |
0.02 |
0.01 |
0.02 |
0.01 |
0.01 |
0.02 |
0.03 |
0.01 |
Kidneys |
0.12 |
0.02 |
0.1 |
0.02 |
0.12 |
0.03 |
0.1 |
0.01 |
Liver |
0.51 |
0.06 |
0.52 |
0.15 |
0.45 |
0.09 |
0.4 |
0.12 |
Lungs |
0.11 |
0.04 |
0.11 |
0.06 |
0.14 |
0.28 |
0.09 |
0.02 |
Lymph nodes (mes) |
0.02 |
0 |
0.02 |
0.01 |
0.02 |
0.02 |
0.03 |
0.01 |
Muscles (thigh) |
0.1 |
0.04 |
0.06 |
0.02 |
0.11 |
0.06 |
0.05 |
0.02 |
Ovaries |
- |
- |
- |
- |
- |
- |
0.01 |
0 |
Pancreas |
0.14 |
0.04 |
0.16 |
0.11 |
0.16 |
0.07 |
0.12 |
0.05 |
Pituitary gland |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Prostate |
0.02 |
0.01 |
- |
- |
0.02 |
0.01 |
- |
- |
Rectum |
0.06 |
0.05 |
0.03 |
0.01 |
0.07 |
0.06 |
0.03 |
0.02 |
Salivary glands |
0.04 |
0.01 |
0.03 |
0 |
0.04 |
0.02 |
0.03 |
0.01 |
Spleen |
0.02 |
0 |
0.01 |
0.01 |
0.02 |
0.01 |
0.02 |
0.01 |
Stomach |
0.13 |
0.04 |
0.09 |
0.02 |
0.11 |
0.03 |
0.09 |
0.02 |
Stomach(content/wash) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Testes |
0.03 |
0.01 |
- |
- |
0.03 |
0.02 |
- |
- |
Thymus |
0.06 |
0.04 |
0.08 |
0.07 |
0.06 |
0.02 |
0.06 |
0.01 |
Thyroid/parathyroids |
0 |
0 |
0 |
0.01 |
0 |
0 |
0 |
0 |
Uterus |
- |
- |
0.01 |
0 |
- |
- |
0.01 |
0 |
Total |
23.2 |
4.34 |
14.4 |
5.06 |
22.1 |
6.03 |
14.3 |
2.56 |
Applicant's summary and conclusion
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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