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Diss Factsheets
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EC number: 213-611-4 | CAS number: 994-05-8
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
Additional information
Absorption
Based on the available data, TAME is absorbed efficiently from the rat intestine. Hepatic first-pass metabolism was not observed. TAME is rapidly absorbed from the lungs; in a study with human volunteers, the respiration uptake was approximately 50%. The maximum plasma concentration of humans after 50 ppm TAME exposure for 4 hours was about 13 umol/L.
Distribution and elimination
In rat, TAME is distributed evenly throughout the body and is eliminated via respiration, urine and faeces. Urine represents the main route of elimination while excretion in faeces is only a few percent at most. The elimination from human blood was rapid after the end of inhalation exposure and it occurred in two phases. The blood half-lives were between 1.2 and 6.3 hours with relatively big individual differences between test subjects. The limit of TAME detection was reached after 12 hours. In rat, the removal via respiration increases with higher doses.
The kinetics of excretion of TAME were identical after ingestion and inhalation exposure.
Metabolism
In humans, TAME is metabolised to tert-amyl alcohol (TAA) primarily by cytochrome 2A6 mainly present in liver. The first metabolic step releases tert-amyl alcohol and formaldehyde. The main metabolites in human urine are 2-methyl-2,3-butanediol, 2-hydroxy-2-methylbutyrate and 3-hydroxy-3-methylbutyrate. Free and conjugated TAA and TAME were only minor metabolites in urine. In rats, 2-methyl-2,3-butanediol and its glucuronide were major TAME metabolites recovered in urine.
The metabolic pathway of TAME is identical after ingestion and inhalation exposure.
Information used for DNEL derivation
The inhalation and dermal absorption percentages used for DNEL derivation (in case of applying route-to-route extrapolation) are 50% and 0.4%, respectively.
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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