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EC number: 310-080-1 | CAS number: 102242-49-9 The complex residue resulting from the vacuum distillation of C6-24 fatty alcohols which is derived from hydrogenation of C6-24 fatty acids methyl esters. It consists predominantly of satd. fatty alcohols having carbon numbers greater than C18, dimerization products, and long chain esters having carbon numbers greater than C32 and boils at > 250°C (482°F) at 10 torr.
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Remarks:
- based on test type (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study according to OECD test guideline 422 under GLP.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 992
- Report date:
- 1992
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 112-95-5
- IUPAC Name:
- 112-95-5
- Details on test material:
- - Name of test material (as cited in study report): 1-Octadecanol
- Molecular formula (if other than submission substance): C18H38O
- Analytical purity: 99% (Sigma L 5751)
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Mollegard breeding center, Denmark
- Age at study initiation: females: 7 weeks; males: 8 weeks
- Housing: The rats were kept in steel wire cages type 3 until day 20 in
pregnancy where the pregnant female were placed in macroIon cages type 3.
- Diet (e.g. ad libitum):
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 8 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2°C.
- Humidity (%): 55 ± 10%.
- Photoperiod (hrs dark / hrs light): Fluorescent light was on from 20 pm. to 8 am.
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: IT CHOW 101
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
DIET PREPARATION
- Rate of preparation of diet (frequency): once
- Mixing appropriate amounts with (Type of food):
BARLEY 6,060 KG
MINERALMIXTURE 0,660 KG
VITAMINS B-K 0,240 KG
1-0CTADECANOL 0,600 KG
SKIM MILK POWDER 6,540 KG
OATS 5,400 KG
SOIA BEAN OIL,cc A.D.E. VIT. 0,500 KG
VEHICLE
- Justification for use and choice of vehicle (if other than water): feed, as the substance is well digestable
- Concentration in vehicle: 3% - Details on mating procedure:
- After a 14 days dosing period the females were placed together with the males, 1 to 1. Check for mating included inspection for plugs during the morning, at lunch time and during the afternoon. The day on which a plug was recorded at lunch time or during the afternoon was defined day O. The day on which a plug was recorded during the morning was defined day 1 in pregnancy. Females, in which no mating was recorded, were kept together with the same male for a 14 days period. If no plug and no indication on pregnancy was found after a 14 days period, the female rat was placed together with an other male for an 8 day period.
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 14 days
- Frequency of treatment:
- daily by diet
- Details on study schedule:
- females: 14 treatment before mating; mating for up to 22 days; termination 5 days after birth
males: 45 day
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
100 mg/kg bw
Basis:
actual ingested
calculated from food consumption
- Remarks:
- Doses / Concentrations:
500 mg/kg bw
Basis:
actual ingested
calculated from food consumption
- Remarks:
- Doses / Concentrations:
2000 mg/kg bw
Basis:
actual ingested
calculated from food consumption
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, plain diet
- Details on study design:
- 1-0ctadecanol was mixed in the diet. In a preliminary test, 1-octadecanol was placed on the skin and mixed in the diet. The skin application was without success as the compound remained on the skin or failed off in cakes so the mixing in the diet procedure was chosen. Doses too were chosen from results of the preliminary test.
The intake as calculated from the food consumption and the concentrations in the diet.
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: No
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes - Litter observations:
- number of pups per litter, weight, sex distribution and dead foetuses from day 1-5
- Postmortem examinations (parental animals):
- Females
Macroscopic examinations
Total gross pathological examinations were performed on each animal. Corpora lutea and implantations were counted. Organ weight was determined for the liver, kidneys and thymus. The following organs were fixed in formalin: Liver, kidneys, adrenals, brain, heart, spleen, ovaries, thymus, and other organs with observed pathological changes.
Histopathological examinations
All fixed organs, except thymus, in the control and highest dose group were prepared for histopathological examinations.
Males
Macroscopic examinations
Total macroscopic examinations were performed on each animal.
Organ weight was determined for the following organs: Liver, kidneys, thymus, testis, epididymides. The following organs were fixed in formalin: Liver, kidneys, adrenals, brain, heart, spleen, thymus and organs with pathological changes per indication. Testis and epididymides were fixed in Bouin's solution.
Histopathological examinations
All fixed organs, except thymus, in the control and highest dose group were prepared for histopathological examinations. - Postmortem examinations (offspring):
- Macroscopic examinations
Pups killed on day 5 were weighed and examined for external malformations including the head (especially eyes and cleft palate) and then opened to the abdomen and thoracic cave for study of sex and malformations of the internal organs.
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- not examined
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Other effects:
- no effects observed
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- no effects observed
- Reproductive function: sperm measures:
- no effects observed
- Reproductive performance:
- no effects observed
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Effect level:
- 2 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- not specified
- Mortality / viability:
- not specified
- Body weight and weight changes:
- no effects observed
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings:
- no effects observed
Effect levels (F1)
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 2 000 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- In a study according to OECD test guideline 422, the NOAEL of 1-Octadecanol for reproductive/developmental toxicity was determined to be 2000 mg/kg bw.
- Executive summary:
The reproductive/developmental toxicity of 1-octadecanol was determined in a study according to OECD test guideline 422 under GLP.
The substance was administered to rats in doses of 0, 100, 500, and 2000 mg/kg bw/day via the diet over 14 days.
Reproductive parameters examined were pregancy rate, length of gestation period, findings of corporea luteae, implantations, resorptions and number of fetuses at birth, number of pups per litter, weight, sex distribution, dead foetuses from day 1-5 and macroscopy.
No indication for effects of the test substance on any of these parameters were found. Consequently, the NOAEL of 1-Octadecanol for reproductive/developmental toxicity was determined to be 2000 mg/kg bw.
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