Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 201-122-9 | CAS number: 78-51-3
- 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
Key value for chemical safety assessment
Additional information
Genotoxicity in vitro:
The genotoxic potential of TBEP has been investigated in two test systems in vitro. Gene mutation studies have been carried out using bacteria and mammalian cells. Chromosomal aberration has not been investigated in mammalian cells in vitro, but this endpoint is covered by anin vivostudy.
In a reverse gene mutation assay in bacteria (Haworth, 1979), strains TA1535, TA1537, TA1538, TA98 and TA100 of S. typhimurium were exposed to TBEP, in DMSO, at concentration of 0.02, 0.1, 0.5, 1.4 & 2.8 microlitres per plate in the presence and absence of mammalian metabolic activation. The positive controls induced the appropriate responses in the corresponding strains. There was no evidence of induced mutant colonies over background. This key study satisfies the requirement of Test Guideline OECD 471 for in vitro mutagenicity (bacterial reverse gene mutation).
The potential of TBEP for mutagenicity in mammalian cells has been investigated using the Chinese Hamster Ovary HGPRT mammalian cell forward gene mutation assay with and without metabolic activation (Kirby, 1981). Test concentrations were 50, 100, 150, 225 and 300 micrograms per ml with 5% S9; 5, 50, 75, 100 and 130 micrograms per ml in the absence of S9. Cytotoxicity was observed at the highest dose level with a dose-related trend both in presence and absence of S9. There was no evidence of mutagenicity at any dose tested, with or without metabolic activation.
The full study report was not available for assessment, however the data have been peer-reviewed in two reference works (IPCS EHC 218, 2000 and ECETOC JACC report 21, 1992). The data reported in these publications is considered adequate to satisfy the requirements for this endpoint.
Genotoxicity in vivo:
The potential of TBEP for genotoxicityin vivohas been investigated in the micronucleus test (OECD 474). TBEP was administered to male and female mice once by gavage at doses of 0 and 1800 mg/kg. The animals were killed 24, 48 or 72 hours after the administration of the test compound. The number of polychromatic and normochromatic erythrocytes containing micronuclei was not increased. The ratio of polychromatic/normochromatic erythrocytes was not affected by treatment in male or female mice. TBEP was considered not mutagenic in the micronucleus test.
Short description of key
information:
The genotoxic potential of TBEP has been investigated both in vitro
and in vivo. All tests gave negative results, leading to the conclusion
that TBEP is not genotoxic. For in vitro gene mutation studies in
bacteria, a study similar to OECD guideline 471, Haworth (1979), (Rel 2)
has been chosen as the key study. For in vitro mammalian cell gene
mutation, an HGPRT mammalian cell forward gene mutation assay in CHO
cells (Kirby, 1981) performed according to OECD guideline 476 (Rel 2)
has been chosen as key study. No in vitro chromosomal aberration study
in mammalian cells is available, however this endpoint is covered by an
in vivo mouse micronucleus study in bone marrow cells.
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
All in vitro and in vivo studies on TBEP gave a negative (non-genotoxic) result.
TBEP is therefore not classified for genotoxicity according to the criteria of Annex VI Directive 67/748/EECor EU/UN GHS.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.