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EC number: 205-572-7 | CAS number: 142-92-7
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- No data
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Abstract only available; suitable only as part of a WoE assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- A teratology screening study in rats with n-hexanol
- Author:
- Rodwell DE, Mercieca MD, Rusch CM & Tasker EJ
- Year:
- 1 988
- Bibliographic source:
- Toxicologist 8(1):213 (1988)
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- n-Hexanol
- IUPAC Name:
- n-Hexanol
- Test material form:
- not specified
- Details on test material:
- - Name of test material (as cited in study report): n-hexanol
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: COBS CD
- Details on test animals or test system and environmental conditions:
- 25 mated female COBS CD rats per group..
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- N-hexanol was mixed with corn oil and administered by oral gavage at doses of 200 or 1000 mg/kg bw/day. Each group consisted of 25 mated female COBS CD rats. Ten consecutive daily doses were administered over gestation days 6-15, in a dose volume of 5 ml/kg bw.
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No information
- Details on mating procedure:
- No data
- Duration of treatment / exposure:
- ten days GD 6-15
- Frequency of treatment:
- daily
- Duration of test:
- dams terminated on gestation day 20
Doses / concentrations
- Remarks:
- Doses / Concentrations:
200 or 1000 mg/kg bw/day
Basis:
nominal conc.
- No. of animals per sex per dose:
- 25 mated females per group
- Control animals:
- no
- Details on study design:
- No further details available
Examinations
- Maternal examinations:
- Throughout gestation the rats were observed for appearance and behaviour, and bodyweights were recorded. On gestation day 20 intrauterine survival was evaluated following Caesarean section and foetal development indices – bodyweight, external, skeletal and visceral morphology – were assessed.
- Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: No data
- Number of corpora lutea: No data
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: intrauterine survival and foetal development indices - Fetal examinations:
- On gestation day 20 intrauterine survival was evaluated following Caesarean section and foetal development indices – bodyweight, external, skeletal and visceral morphology – were assessed.
- Statistics:
- No data
- Indices:
- No information presented on how foetal development indices were determined
- Historical control data:
- No data
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes. Remark: 1000 mg/kg bw/day
Details on maternal toxic effects:
Maternal toxicity was only evident at 1000 mg/kg bw/day – indicated by clinical signs and decreased maternal bodyweights during the treatment period.
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- 200 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects. Remark: No embryotoxicity or teratologic effects were observed at either dose level.
Details on embryotoxic / teratogenic effects:
No embryotoxicity or teratologic effects were observed at either dose level.
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- 200 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: developmental toxicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Mean foetal bodyweight was slightly decreased at 1000 mg/kg bw/day, but weights were within the laboratory historical range. An increase in the number of litters with the foetal variant ‘malaligned sternebrae’ occurred at the low dose level, 200 mg/kg bw/day. The incidence of this variation in the high dose group was similar to incidence in the controls.
Applicant's summary and conclusion
- Conclusions:
- Maternal toxicity and developmental toxicity were evident at the highest dose level of 1000 mg/kg bw/d; there is no evidence for specific developmental toxicity.
- Executive summary:
The potential maternal, embryotoxic and teratologic effects of N-hexanol were evaluated. N-hexanol was mixed with corn oil and administered by oral gavage at doses of 200 or 1000 mg/kg bw/day. Each group consisted of 25 mated female COBS CD rats. Ten consecutive daily doses were administered over gestation days 6-15, in a dose volume of 5 ml/kg bw. Throughout gestation the rats were observed for appearance and behaviour, and bodyweights were recorded. On gestation day 20 intrauterine survival was evaluated following Caesarean section and foetal development indices – bodyweight, external, skeletal and visceral morphology – were assessed. No embryotoxicity or teratologic effects were observed at either dose level. Maternal toxicity was only evident at 1000 mg/kg bw/day – indicated by clinical signs and decreased maternal bodyweights during the treatment period. Mean foetal bodyweight was slightly decreased at 1000 mg/kg bw/day, but weights were within the laboratory historical range. An increase in the number of litters with the foetal variant ‘malaligned sternebrae’ occurred at the low dose level, 200 mg/kg bw/day. The incidence of this variation in the high dose group was similar to incidence in the controls. The 200 mg/kg bw/day dose level was considered a no-effect level. Maternal toxicity and developmental toxicity were evident at the highest dose level of 1000 mg/kg bw/d; there is no evidence for specific developmental toxicity.
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