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EC number: 242-582-0 | CAS number: 18794-84-8
- 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 in vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study is conducted according to well established method, but not a GLP guideline study.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
Materials and methods
- Objective of study:
- absorption
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- In vitro absorption across everted gut sac measured as estimation of absorption from the small intestine via the oral route.
- GLP compliance:
- no
Test material
- Reference substance name:
- (E)-7,11-dimethyl-3-methylenedodeca-1,6,10-triene
- EC Number:
- 242-582-0
- EC Name:
- (E)-7,11-dimethyl-3-methylenedodeca-1,6,10-triene
- Cas Number:
- 18794-84-8
- Molecular formula:
- C15H24
- IUPAC Name:
- (E)-7,11-dimethyl-3-methylenedodeca-1,6,10-triene
- Reference substance name:
- Farnesene
- IUPAC Name:
- Farnesene
- Test material form:
- other: liquid
Constituent 1
Constituent 2
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Intestinal gut sacs were harvested from rats.
Animal: Male Han Wistar rats. Age: approx. 8-12 weeks old obtained from: Charles River, Research Models and Services, Margate, UK.
Administration / exposure
- Route of administration:
- other: in vitro test
- Vehicle:
- other: Fed State Simulated Intestinal Fluid
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- There was detectable trans-β-Farnesene present in the serosal media from the everted rat intestinal sac incubations with trans-β-Farnesene. The calculated mean concentrations of trans-β-Farnesene in the serosal fluid were 0.12mM from Rat 1 intestinal sacs and 0.13mM from Rat 2 intestinal sacs . These concentrations are deemed to be very low (approximately 1% of the original incubation conditions of 10mM) and are considered to show minimal absorption.
The concentration of trans-β-Farnesene (approximately 3.4mM) measured in the external media after the 1 hour incubation may reflect the poor solubility of these compounds at 10mM, which was deemed to be a saturated concentration. It was noted that there was a film/layer present on the glass flasks after the incubation.
The results from the everted rat intestinal sacs incubations with the control mix of alkanes show good absorption of decane with concentrations in the serosal fluid calculated at 0.79mM from Rat 1 intestinal sacs and 0.47mM from Rat 2 intestinal sacs. These concentrations are approximately 20% and 12% respectively of the original incubation conditions of 3.85mM.
Decreased absorption was detected with the increased carbon chain length of the alkanes in the control mix with concentrations of dodecane in the serosal fluid calculated at 0.24mM and 0.14mM (8% and 5% respectively of the original incubation concentration of 3.01mM). Tetradecane concentrations in the serosal fluid were minimal at 0.06mM and 0.03mM (2% and 1% respectively of the original incubation concentration of 2.67mM).
No absorption of the hexadecane and octadecane into the serosal fluid could be detected.
These results are consistent with previous studies performed in this laboratory which have shown an inverse correlation between carbon chain length and the rat small intestinal absorption potential of a series of alkenes, using everted rat intestinal sacs.
Any other information on results incl. tables
Calculated concentration of trans-β-Farnesene in serosal fluid and external media.
Sample |
Calculated concentration of trans-β-Farnesene in serosal fluid and external media (mM) |
Mean (mM) |
±SD |
|
|
|
|
Serosal fluid 1 Rat 1 |
0.12 (1.2%) |
|
|
Serosal fluid 2 Rat 1 |
0.13 (1.3%) |
|
|
Serosal fluid 3 Rat 1 |
0.12 (1.2%) |
0.12 |
0.00 |
|
|
|
|
Serosal fluid 1 Rat 2 |
0.10 (1.0%) |
|
|
Serosal fluid 2 Rat 2 |
0.17 (1.7%) |
|
|
Serosal fluid 3 Rat 2 |
0.12 (1.2%) |
0.13 |
0.04 |
|
|
|
|
External fluid 1 Rat 1 |
3.31 |
|
|
External fluid 2 Rat 1 |
3.33 |
|
|
External fluid 3 Rat 1 |
3.37 |
3.34 |
0.03 |
|
|
|
|
External fluid 1 Rat 2 |
3.53 |
|
|
External fluid 2 Rat 2 |
3.42 |
|
|
External fluid 3 Rat 2 |
3.39 |
3.45 |
0.08 |
Calculated amount of trans-β-Farnesene absorbed into serosal fluid
Sample |
Calculated amount of trans-β-Farnesene absorbed into serosal fluid (nmoles/400µL) |
Mean (nmoles/400µL) |
±SD |
|
|
|
|
Serosal fluid 1 Rat 1 |
47.3 |
|
|
Serosal fluid 2 Rat 1 |
50.8 |
|
|
Serosal fluid 3 Rat 1 |
47.9 |
48.7 |
1.9 |
|
|
|
|
Serosal fluid 1 Rat 2 |
40.2 |
|
|
Serosal fluid 2 Rat 2 |
69.0 |
|
|
Serosal fluid 3 Rat 2 |
48.4 |
52.5 |
14.8 |
Calculated amount of trans-β-Farnesene absorbed into serosal fluid (corrected by volume factor)
Sample |
Calculated amount of trans-β-Farnesene absorbed into serosal fluid (nmoles/sac) |
Mean (nmoles/sac) |
±SD |
|
|
|
|
Serosal fluid 1 Rat 1 |
58.4 |
|
|
Serosal fluid 2 Rat 1 |
61.8 |
|
|
Serosal fluid 3 Rat 1 |
68.6 |
62.9 |
5.2 |
|
|
|
|
Serosal fluid 1 Rat 2 |
61.2 |
|
|
Serosal fluid 2 Rat 2 |
113.6 |
|
|
Serosal fluid 3 Rat 2 |
73.5 |
82.8 |
27.4 |
Original incubation amount of 4µmoles/400µL (Total incubation volume of 10mL)
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): low bioaccumulation potential based on study results
Negligible gut sac absorption (<1%) - Executive summary:
The aim of this study was to determine the rat, small intestinal absorption potential of two Test Items, Farnesane and trans-β-Farnesene using everted rat intestinal sacs.
There was detectable trans-β-Farnesene present in the serosal media from the everted rat intestinal sac incubations with trans-β-Farnesene. The calculated concentrations of trans-β-Farnesene in the serosal fluid were 0.12mM from Rat 1 intestinal sacs and 0.13mM from Rat 2 intestinal sacs. These concentrations are deemed to be very low (approximately 1% of the original incubation conditions of 10mM) and are considered to show minimal absorption.
The results from the everted rat intestinal sacs incubations with the control mix of alkanes show good absorption of decane with concentrations in the serosal fluid calculated at 0.79mM from Rat 1 intestinal sacs and 0.47mM from Rat 2 intestinal sacs. These concentrations are approximately 20% and 12% respectively of the original incubation conditions of 3.85mM.
There was diminishing absorption detected with increased carbon chain length of the alkanes in the control mix with concentrations of dodecane in the serosal fluid calculated at 0.24mM and 0.14mM (8% and 5% respectively of the original incubation concentration of 3.01mM). Tetradecane concentrations in the serosal fluid were minimal at 0.06mM and 0.03mM (2% and 1% respectively of the original incubation concentration of 2.67mM). No absorption of the hexadecane and octadecane into the serosal fluid could be detected.
These results are consistent with previous studies performed in this laboratory which have shown an inverse correlation between carbon chain length and the rat small intestinal absorption potential of a series of alpha olefins using everted rat intestinal sacs.
Reference - “The use of everted rat small intestinal sacsin-vitroto estimate relative absorption potential of a series of alpha olefins” M. Penman, R. H. Powrie and C. R. Elcombe, Society of Toxicology 2014 Meeting, poster presentation #1593
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