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EC number: 244-617-5 | CAS number: 21850-44-2
- 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
Short description of key information on bioaccumulation potential result:
One publication is available: "Absorption, distribution, metabolism, and excretion of intravenously and orally administered tetrabromobisphenol A[2,3-dibromopropyl ether] in male Fischer-344 rats", by Knudsen, G.A., Jacobs, L.M., Kuester, R.K., Sipes, I.G. (Toxicology 237 (2007) 158-167).
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
Additional information
Studies regarding the absorption, distribution, metabolism, and excretion of TBBA-DBPE were conducted. Male Fischer-344 rats were dosed with TBBA-DBPE (20mg/kg) by oral gavage or IV administration. Following a single oral administration of TBBA-DBPE, elimination of [14C] equivalents in feces was extensive and rapid (95% by 96 hours). Following repeated daily oral doses for 5 or 10 days, route and rate of elimination was similar to single administration of TBBA-DBPE. After IV administration, fecal excretion of [14C] equivalents was much slower (27% of dose eliminated by 36h, 71% by 96h). Urinary elimination was minimal (<0.1%) following oral and IV administration. A single peak that co-eluted with the standard of TBBA-DBPE was detected in extracts of whole blood following oral or IV administration. TBBA-DBPE elimination from the blood was slow. Kinetic constants following IV dosing were: t1/2b: 24.8h; CLb: 0.1mL/min. Kinetic constants following oral dosing were: t1/2a: 2.5h:13.9h; CLb :4.6mL/min.
Systemic bioavailability was 2.2%. Liver was the major site of disposition following oral or IV administration. After oral administration, 1% of the dose was eliminated in bile in 24h as metabolites. Inin vitro experiments utilizing hepatocytes or liver microsomal protein, no detectable metabolism of TBBA-DBPE occurred. These data indicate that TBBA-DBPE is poorly absorbed from the gastrointestinal tract. Compound which is absorbed is sequestered in the liver, slowly metabolized, and eliminated in the feces.
The results of these studies show that the likelihood of systemic exposure following ingestion of [14C] TBBA-DBPE is low. Additionally, disposition in liver tissue was minimal, and metabolite formation was slow. Consequently, it was determined that the probability of formation of the carcinogenic moiety DBP was low.
In summary, these data show that TBBA-DBPE was poorly absorbed across the gut lumen following oral administration. However, that which was absorbed was rapidly sequestered in the liver, was slowly metabolized and finally eliminated in the bile for fecal excretion.
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