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Diss Factsheets
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EC number: 939-464-2 | CAS number: 121617-08-1
- 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
Dermal absorption
Administrative data
- Endpoint:
- dermal absorption in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well documented study report, acceptable for assessment
Data source
Referenceopen allclose all
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 1 988
- Report date:
- 1988
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 1 989
Materials and methods
- Principles of method if other than guideline:
- Triethanolamine uniformly radiolabeled with 14C was administered to C3H/HeJ mice intravenously or dermally to study the skin penetration of the test substance in vitro.
- GLP compliance:
- yes
Test material
- Reference substance name:
- triethanolamine
- IUPAC Name:
- triethanolamine
- Reference substance name:
- 2,2',2''-nitrilotriethanol
- EC Number:
- 203-049-8
- EC Name:
- 2,2',2''-nitrilotriethanol
- Cas Number:
- 102-71-6
- Molecular formula:
- C6H15NO3
- IUPAC Name:
- 2,2',2''-nitrilotriethanol
- Details on test material:
- - Name of test material (as cited in study report): triethanolamine
- Analytical purity: 99.6 %
- Lot/batch No.: 7H-5317
- Radiochemical purity (if radiolabelling): 97-98 % (98.6 % by liquid chromatography reanalysis)
- Specific activity (if radiolabelling): 34.7 mCi/mmol
- Supplier: Amersham Cororation, Arlington Heights, IL, USA (labelled TEA)
- Supplier: Texaco Chemical Company, Austin, Texas, USA (unlabelled TEA)
Constituent 1
Constituent 2
- Radiolabelling:
- yes
- Remarks:
- 14C
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories (Kingston, NY)
- Weight at study initiation: 231 to 247 g
- Fasting period before study: none
- Housing: glass Roth-style metabolism cages
- Individual metabolism cages: yes
- Diet: Purina® Certified Rodent chow #5002 ad libitum
- Water: tap water ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): 40-60
- Air changes (per hr): ca. 12
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Duration of exposure:
- 48 hours
- Doses:
- 1000 mg/kg bw
- No. of animals per group:
- 3
- Control animals:
- no
- Details on study design:
- About 48 hours prior to dosing, indwelling cannulas were surgically implanted into the jugular vein of the rats while they were under methoxyflurane anesthesia using a modification of the method described by Harms and Ojeda, 1974. Approximately, 16 hours prior to dosing, die animals were anesthetized with methoxyflurane and the skin on the back of the rats was shaved using Ivory® soap and a straight razor. The skin was dried and a glass ring (as previously described) was attached to the skin using cyanoacrylate. At the time of dosing, die animals were anesthetized with methoxyflurane and a dosing volume targeted at 200 µl of "neat" 14C-TEA was applied within the ring. The ring was then covered with a round glass cover slip attached with cyanoacrylate to restrict the animals access to the dose site while grooming and to aid in containing this large volume of dose at one site. The dosing volume applied dermally was 96.8 ± 0.3 % (mean ± S.D.) of the target dosing volume. The average amount of radioactivity applied was 4.42 µCi/rat.
Immediately following dosing the animals were placed in glass Roth cages for the separation of urine and feces. Urine and feces were collected at 6, 12, 24 and 48 hours post-dosing. Blood samples (= 0.2 ml) were taken via the indwelling jugular cannulas at 0.5, 1, 2, 4, 6, 12, 24 and 36 hours post-dosing. An additional blood sample was drawn from one animal at 31 hours post-dosing. At 48 hours post-dosing the animals were anesthetized with methoxyflurane and sacrificed by exsanguination via cardiac puncture. Following sacrifice, the skin from the dose site was excised, the remaining skin removed, the liver and kidneys excised, and each Roth cage was washed with a solution of acetone and water. The glass rings used to restrict access to the dosed site were removed from the skin and washed with water to recover any residual radioactivity on thie rings. Radioactivity in excreta, cage wash solution, ring wash solution, liver, kidneys, skin and remaining carcass were determined.
Results and discussion
- Signs and symptoms of toxicity:
- not specified
- Dermal irritation:
- not specified
- Absorption in different matrices:
- Upon dermal application, the dermal absorption of triethanolamine was less extensive and much slower than in mice. Absorption values have not been provided.
- Total recovery:
- The urinary interval excretion data show that the percentage of the administered dose found in the urine per collection interval (0-6, 6-12, 12-24 and 24-48 hrs) was 3% or less.
The level of radioactivity was non-detectable (2x background) in the blood samples taken at 0.5, 1, 2, 4 and 6 hrs post-dosing
- Conversion factor human vs. animal skin:
- No data
Any other information on results incl. tables
As long as the glass ring and coverslip attached to the skin to restrict the animals access to the dosed was intact, the results are as indicated above. Once the integrity of the glass ring or coverslip failed, the dose was leaked to other areas of the skin and ingestion of the dose incidental to grooming could occur. Indeed, the percentage radioactivity found in the urine increased markedly in each as soon as the device for restricting access to the dosed site failed. In the blood, radioactivity was only detectable at sampling times which were after the integrity of the glass ring restricting access to the dosed site had failed. This suggests that most of the blood radioactivity found may have been a result of ingestion incidental to grooming after access to the test material on the skin was obtained. Data were not sufficient to construct a meaningful blood concentration-time profile.
Applicant's summary and conclusion
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