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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
Endpoint summary
Administrative data
Description of key information
Repeated dose information was available for the structural analogues D- and D,L-alpha-tocopheryl acetate (vitamin E acetate). These vitamin E esters will be rapidly hydrolysed to the free alpha-tocopherol forms under physiological conditions. In summary, Vitamin E exerts low toxicity in repeated dose studies. The NOAEL of 500 mg/kg bw/d for D-alpha-tocopheryl acetate was based on a well conducted 90-day study in rat comparable to OECD guideline 408 (Abdo, 1986). In a chronic rat study with doses of 500, 1000 or 2000 mg/kg bw/d D,L-alpha-tocopherol acetate the animals showed at all dose levels spontaneous haemorrhages in several organs which was correctable by administration of Vitamin K3.
The following repeated studies were also part of the assessment for this endpoint:
28-day studies (OECD 407) with D,L-alpha-tocopheryl acetate: gavage study in rats (Pfister, 1999; BASF AG, 1983)
28-day study with D,L-alpha-tocopheryl acetate: feed study in dogs (BASF AG, 1982)
2-year study (OECD 453): feeding study in rats with D,L-alpha-tocopheryl acetate supplemented with Vitamin K (Wheldon, 1978)
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- 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.
- 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
- 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
- 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
- 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
- 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.
- 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. - Dose descriptor:
- NOAEL
- Effect level:
- 500 mg/kg bw/day (nominal)
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
- Critical effects observed:
- not specified
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 500 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
No studies specifically conducted with the free racemic Vitamin E form (D,L-alpha-tocopherol) have been reported. Therefore, experimental data for the Vitamin E esters D- and D,L-alpha-tocopheryl acetate is used which will be rapidly hydrolysed to the free Vitamin E alcohol (D- or D,L-alpha tocopherol) under physiological conditions. Please see read-across justification section 13.
A reliable (GLP, OECD 407) 28 -day study with D,L-alpha tocopheryl acetate in rats is available (Pfister, 1999). The rats were treated by oral gavage at 180, 600 and 2000 mg/kg bw d. As no treatment-related findings were noted, the NOAEL in this study was set at 2000 mg/kg bw/d.
The low toxicity of Vitamin E acetate after repeated administration was supported by further 28 -day feeding studies in rats and dogs (BASF 1983 and 1982). The rats were treated with D,L-alpha tocopheryl acetate at dose levels ca. 139, 278, 556 and 1111 mg/kg bw/d and the dogs at dose levels of ca. 45, 90, 180, 360 mg/kg bw/d in the diet. There were no significant, substance-related differences between the groups with regard to body weight, food consumption, and clinical-chemical, hematological, and urine parameters. The NOAELs can be set at >= 1111 mg/kg bw/d in the rat study and >= 360 mg/kg bw/d in the dog study.
A 90-day repeated dose (oral gavage) study is available for D-alpha-tocopheryl acetate (Abdo et al. 1986). In this study, the rats were dosed at 125, 500 and 2000 mg/kg bw/d D-alpha tocopheryl acetate. The relative liver weight was significantly increased in high dose females. Administration of 2000 mg/kg bw/d caused hematological changes: prolongation of prothrombin and activated partial thromboblastin (APTT) times and an increase in fibrinogen value, 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.
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. These effects were attributed to local aspiration of the test substance (as in the other oral gavage 90-day study this was not observed), which would not occur under normal circumstances. Furthermore, these effects were not seen in the chronic feed study (Wheldon, 1978). Therefore, for the NOAEL derivation the effects in the lungs were not considered. Because at 500 mg/kg only APTT values were increased in absence of an increase in PT and fibrinogen value, the NOAEL is set at 500 mg/kg bw/d.
In a long-term toxicity study rats were fed D,L-alpha-tocopheryl acetate at dietary concentrations providing dosages of 0, 500, 1000 and 2000 mg/kg bw/d for 104 weeks (Wheldon et al., 1983). Vitamin K supplementation suppressed the induced hypoprothrombinemia. Growth rate and survival were unaltered by treatment. The observation of agglomerations of vacuolated macrophages in the hepatic centriacini in all treatment groups, alongside changes in serum liver enzyme activity, suggested a limited hepatic response to vitamin E overload. A NOAEL could not be established, since hemorrhage effects were treated by supplementing Vitamin K after 26 weeks.
For the DNEL-derivation, a NOAEL of 500 mg/kg bw /d derived from the 90 -day repeated dose with D-alpha-tocopheryl acetate (Abdo,1986) study will be used.
Justification for selection of repeated dose toxicity via oral
route - systemic effects endpoint:
Reliable study which followed current guideline requirements
Repeated dose toxicity: via oral route - systemic effects (target
organ) cardiovascular / hematological: blood coagulation
Justification for classification or non-classification
According to EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008 classification is not warranted.
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