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EC number: 208-008-8 | CAS number: 505-32-8
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Peer-reviewed data, available as short summary from secondary source, reliability according to HPV/ICCA SIDS.
Data source
Reference
- Reference Type:
- secondary source
- Title:
- Unnamed
- Year:
- 2 002
- Report date:
- 2002
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- Limit test
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 3,7,11,15-tetramethylhexadec-1-en-3-ol
- EC Number:
- 208-008-8
- EC Name:
- 3,7,11,15-tetramethylhexadec-1-en-3-ol
- Cas Number:
- 505-32-8
- Molecular formula:
- C20H40O
- IUPAC Name:
- 3,7,11,15-tetramethylhexadec-1-en-3-ol
- Details on test material:
- - Name of test material (as cited in study report): Isophytol
- Physical state: not reported
- Analytical purity: 97.5 % (weight, GC) respective 98.0 % (area, GC)
- Impurities (identity and concentrations): no data
- Purity test date: 23 Jan 2002
- Lot/batch No.: UU02013601
- Other: Source: Teranol AG, Lalden, Switzerland
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Sulzfeld, Germany
- Age at study initiation: 6-8 weeks
- Weight at study initiation: not reported
- Assigned to test groups randomly: yes, under following basis: no data
- Fasting period before study: 3-4 hours prior to dosing
- Housing: 5/cage
- Diet: pelleted diet (Altromin, code VRF 1, Lage, Germany); ad libitum
- Water: tap water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21±3
- Humidity (%): 30 to over 70; despite the relative humidity partly exceeding 70 %, no abnormalities were noted in the animals. The deviation was concluded not to affect the integrity of the study.
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Concentration of test material in vehicle: 200mg/ml
- Amount of vehicle (if gavage or dermal): 10 ml/kg bw - Duration of treatment / exposure:
- not applicable
- Frequency of treatment:
- once
- Post exposure period:
- 24 and 48 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
2000 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 males (3 males and 3 females in range-finding study)
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Route of administration: not reported
- Doses / concentrations: 50 mg/kg bw
Examinations
- Tissues and cell types examined:
- bone marrow erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Range-finder study: 3 males and 3 females dosed with 2000 mg/kg bw showed no abnormalities during an observation period of 3 days.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): Application by oral gavage, animals of the 2 treated groups were sacrificed 24 and 48 hours, respectively, after dosing. The control groups were sacrificed 24 hours after treatment.
DETAILS OF SLIDE PREPARATION: Both femurs of each animal were removed, freed of blood and muscles, and both ends of the bone were cut open. The bone marrow was flushed out with fetal calf serum (FCS). The suspension was centrifuged and the cells resuspended in FCS. A drop of the suspension was placed on the end of a previously cleaned and marked microscopic slide, spread using a clean slide and air-dried, fixed with 100 % methanol, automatically stained in HEMA-tek Slide Stainer (Miles, Bayer Nederland, The Netherlands) and covered with a glass coverslip.
METHOD OF ANALYSIS: Before analysis, the slides were randomised by labelling with codes. They were first screened at a magnification of x100 for suitable regions, then scored at x1000. The number of micronucleated polychromatic erythrocytes was counted in a total of 2000 polychromatic erythrocytes per slide. The ratio of polychromatic to normochromatic erythrocytes was determined in the first 1000 erythrocytes scanned. Micronuclei were only counted in polychromatic erythrocytes. - Evaluation criteria:
- The test was considered acceptable if the positive control substance induced a significant increase in micronucleated polychromatic erythrocytes and the incidence of micronucleated polychromatic erythrocytes was reasonably within the laboratory historical controls range (mean ± 3 SD).
- Statistics:
- Averages and standard deviations for the four groups were calculated. Positive: induction of a statistically significant (Wilcoxon Rank sum test, two-sided test at p<0.05) increase in the frequency of micronucleated polychromatic erythrocytes, at any dose or sampling time. Negative: no such statistically significant increase.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 2000 mg/kg bw
- Clinical signs of toxicity in test animals: none
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): none
- Ratio of PCE/NCE (for Micronucleus assay): yes: see table
- Appropriateness of dose levels and route: yes
- Statistical evaluation: yes
Any other information on results incl. tables
As there were no obvoius differences between the sexes, it was decided to use only males in the main test. The mean body weights of all 4 groups, recorded just before dosing, were not statistically different. All animals treated with 2000 mg/kg bw showed no abnormalities; this was also true for both the negative and the positive controls.
Average numbers of micronucleated polychromatic erythrocytes and ratios of polychromatic to normochromatic erythrocytes:
Group | Dose (mg/kg bw) | Sampling time (h) | Number (mean±SD) | Ratio (mean±SD) |
Vehicle | 0 | 24 | 0.6 ± 0.9 | 1.15 ± 0.20 |
Isophytol | 2000 | 24 | 0.2 ± 0.4 | 1.09 ± 0.11 |
Isophytol | 2000 | 48 | 0.4 ± 0.9 | 1.17 ± 0.10 |
Cyclophosphamide | 50 | 24 | 25.8 ± 5.5 ** | 0.39 ± 0.06 |
** Significantly different from vehicle control group, p <= 0.01
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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