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EC number: 233-466-0 | CAS number: 10191-41-0
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- 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: Non-GLP near-guideline study, acceptable for assessment.
Data source
Reference
- Reference Type:
- publication
- Title:
- Thirteen-week toxicity study of d-alpha-tocopheryl acetate (Vitamin E) in Fischer 344 rats.
- Author:
- Abdo KM, Rao G, Montgomery A
- Year:
- 1 986
- Bibliographic source:
- Fd Chem Toxic. 24 (10/11): 1043-1050.
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- α-tocopheryl acetate
- EC Number:
- 200-405-4
- EC Name:
- α-tocopheryl acetate
- Cas Number:
- 58-95-7
- Molecular formula:
- C31H52O3
- IUPAC Name:
- 2,5,7,8-tetramethyl-2-(4,8,12-trimethyltridecyl)-3,4-dihydro-2H-chromen-6-yl acetate
- Details on test material:
- Vitamin E acetate (d-alpha-tocopheryl acetate); according to the authors, purity was >99%
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratory, Kingston, NY
- Age at study initiation: 25 days
- Housing: stainless steel cages
- Diet: ad libitum, modified AIN-76 diet
- Water: ad libitum
- Acclimation period: 11 days
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- The vitamin (>99% pure and obtained from Eastman Kodak Company, Rochester, NY) was administered in corn oil by gavage at the rate of 3.5 ml/kg
body weight daily for up to 13 weeks. - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
125, 500, 2000 mg/kg bw/d
Basis:
- No. of animals per sex per dose:
- 10
- Control animals:
- yes
- Details on study design:
- Two control groups (10 rats/sex/group) were either administered corn oil by gavage (vehicle control group) or remained untreated (untreated control group).
Post-exposure period: none - Positive control:
- None
Examinations
- Observations and examinations performed and frequency:
- Individual blood samples (with or without heparin) for haematology and clinical chemistry determinations were collected by terminally bleeding ten males and ten females from each treatment group via the vena cava at days 5, 45 and 90 of dosing treatment.
Haematology determinations, which included mean corpuscular cell volume, haemoglobin, haematocrit, erythrocyte count and total and differential leucocyte counts, were made on a Baker 7000 cell counter (Baker Instruments, Allentown, PA) . Prothrombin time (PT) and activated partial thromboplastin time (APTT) were determined according to the Coag-a Mate operator's manual (General Diagnostics, Division of Warner-Lambert Co, Morris Plains, NJ) . Fibrinogen levels were determined according to the turbidimetric procedure of Exner using the Cetrifichem 400 (Exner, 1979). Serum samples were analysed for chloride, alkaline phosphatase, thyroxine (T4) and γ-glutamyl transpeptidase (GGT) using the Centrifichem 400 according to the procedures specified by the manufacturer (Baker Instruments, Allentown, PA). Triiodothyronine (T3) and thyroid-stimulating hormone (TSH) were determined by radioimmunoassay procedures (Kieffer, 1974) . - Sacrifice and pathology:
- At the end of the treatment period, surviving animals were sacrificed and subjected to complete necropsy.
Organ weights and organ-to-body weight ratios were determined for brain, heart, kidneys, liver, spleen, thyroid and parathyroid (combined), thymus, pituitary gland, ovary, uterus, prostate, epididymis and testes.
In addition to these organs, the spinal cord, eyes, salivary gland, mammary gland, oesophagus, lungs with mainstem bronchi, trachea, stomach, small and large intestine, adrenals, pancreas, urinary bladder, mesenteric lymph node, bone marrow, sternum and sciatic nerve with skeletal muscle were
collected, fixed in 10% buffered formalin, embedded in paraffin, sectioned at 5 ,um and stained with haematoxylin and eosin. All tissues from the control and the high-dose groups were examined microscopically. For the lower-dose groups, only tissues that were designated as targets for vitamin E toxicity were examined (not further specified). - Statistics:
- The significance of differences between Vitamin E-treated and control groups was assessed using the Dunnett's multiple comparison procedure. Dose-response trend was assessed by Jonckheere's test. Results were considered significant when the calculated P value was 0.05 or less.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- not specified
- Details on results:
- Seven out of 10 high dose males died during weeks 9-11.
The test substance had no effect on food consumption or body weights.
The relative liver weight was significantly increased in high dose females.
Administration of 2000 mg/kg bw/d caused hematological changes: prolongation of both prothrombin and activated partial thromboblastin (APTT) times, reticulocytosis and a decrease in hematocrit values and hemoglobin concentrations was observed in males; APTT times were also increased in females. Hemorrhagic diathesis was observed in males and females of the high dose group; and increased medullary erythropoiesis was seen in the spleen of one high dose male.
A compound-related increase was also observed in the plasma levels of thyroid-stimulating hormone. However, without a corresponding increase in T3 and T4, and no evidence for increased energy metabolism ( food consumption and body weights were comparable to control groups), the toxcicological relevance was doubted.
The test substance at all dose levels tested caused interstitial inflammation and adenomatous hyperplasia of the lung. The lung lesions were observed in all vitamin E-treated groups, and the incidence and severity increased in a dose-dependent manner. These lesions were characterized by increased cellularity, vascular congestion, thickened alveolar walls and the presence of foamy macrophages (some of which had undergone cell death and degeneration) in the alveolar spaces. A lipid-like yellow pigmentation was often present within either the macrophages or alveoli.
None of these lesions, however, were considered to reflect systemic toxic effects of the test or reference articles. The changes in the lungs were considered to be a local reaction to the aspiration of a-tocopheryl acetate into the lungs that would not occur under conditions of normal use.
Therefore, for the NOAEL derivation the effects in the lungs were not considered.
Because at 500 mg/kg only the APTT value is increased, but not the PT and fibrinogen values, the NOAEL is set at 500 mg/kg.
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 500 mg/kg bw/day (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
Target system / organ toxicity
- Critical effects observed:
- not specified
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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