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EC number: 247-426-5 | CAS number: 26040-51-7
- 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
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- Flash point
- Auto flammability
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- 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
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- Endpoint summary
- Stability
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- 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

Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Scientifically accceptable and well documented
Data source
Reference
- Reference Type:
- publication
- Title:
- In vitro metabolism of the brominated flame retardants 2- ethylhexyl-2,3,4,5-tetrabromobenzoate (TBB) and bis(2-ethylhexyl) 2,3,4,5-tetrabromophthalate (TBPH) in human and rat tissues
- Author:
- Roberts SC, Macaulay LJ, Stapleton HM
- Year:
- 2 012
- Bibliographic source:
- Chem Res Toxicol 2012; 16;25(7): 1435-1441
Materials and methods
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- The in-vitro metabolism of the brominated flame retardant TBPH (bis(2-ethylhexyl) tetrabromophthalate) was examined in human and rat tissues by conducting in vitro experiments with liver and intestinal subcellular fractions.
- GLP compliance:
- no
Test material
- Reference substance name:
- Bis(2-ethylhexyl) tetrabromophthalate
- EC Number:
- 247-426-5
- EC Name:
- Bis(2-ethylhexyl) tetrabromophthalate
- Cas Number:
- 26040-51-7
- Molecular formula:
- C24H34Br4O4
- IUPAC Name:
- 1,2-bis(2-ethylhexyl) 3,4,5,6-tetrabromobenzene-1,2-dicarboxylate
Constituent 1
- Specific details on test material used for the study:
- TBPH (99% purity) were purchased as neat solutions from AccuStandard, Inc. (New Haven, CT, USA).
- Radiolabelling:
- no
Test animals
- Species:
- other: not applicable - in-vitro test
- Strain:
- other: not applicable - in-vitro test
- Sex:
- not specified
Administration / exposure
- Route of administration:
- other: not applicable - in-vitro test
- Vehicle:
- other: not applicable - in-vitro test
- Duration and frequency of treatment / exposure:
- not applicable - in-vitro test
Doses / concentrations
- Remarks:
- Doses / Concentrations:
not applicable - in-vitro test
- No. of animals per sex per dose / concentration:
- not applicable - in-vitro test
- Control animals:
- other: not applicable - in-vitro test
Results and discussion
- Preliminary studies:
- In experiments with human liver microsomes (HLM), a significant loss of TBPH was not observed, and no metabolites were detected by GC/MS analysis of the sample extracts. An LC/MS-MS method was developed to monitor mono(2-ethylhexyl) tetrabromophthalate (TBMEHP), a potential hydrolysis metabolite of TBPH (Figure 1). After a 6-h incubation with HLM, TBMEHP was not detected as a metabolite of TBPH, and no significant loss of TBPH was observed. However, TBPH was slowly metabolized to form TBMEHP in the presence of 0.1mg/mL of porcine hepatic carboxylesterase (PCE). This reaction was monitored at multiple time points up to 6 h and maintained linearity at an approximate rate of 1.08 pmol/min/mg esterase.
In a previous study (Niino, T., Ishibashi, T., Ishiwata, H., Takeda, K., and Onodera, S. (2003) Characterization of human salivary esterase in enzymatic hydrolysis of phthalate esters. J. Health Sci. 49, 76−81.) with PCE, DEHP (50 μM) was metabolized to form MEHP at a rate of 127 pmol/min/mg protein. This rate was approximately 100 times faster than the hydrolysis of TBPH observed in this study (1.08 pmol/min/mg protein).
The prominent difference between the metabolic hydrolysis of DEHP and TBPH may be a result of steric hindrance by the fully brominated phenyl ring of TBPH.
Main ADME results
- Type:
- metabolism
- Results:
- In experiments with human liver microsomes (HLM), a significant loss of TBPH was not observed, and no metabolites were detected by GC/MS analysis of the sample extracts.
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- not applicable - in-vitro test
- Details on distribution in tissues:
- not applicable - in-vitro test
- Details on excretion:
- not applicable - in-vitro test
Metabolite characterisation studies
- Metabolites identified:
- no
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- not applicable - in-vitro test
Any other information on results incl. tables
In experiments with human liver microsomes (HLM), a significant loss of TBPH was not observed, and no metabolites were detected by GC/MS analysis of the sample extracts. An LC/MS-MS method was developed to monitor mono(2-ethylhexyl) tetrabromophthalate (TBMEHP), a potential hydrolysis metabolite of TBPH (Figure 1). After a 6-h incubation with HLM, TBMEHP was not detected as a metabolite of TBPH, and no significant loss of TBPH was observed. However, TBPH was slowly metabolized to form TBMEHP in the presence of 0.1mg/mL of porcine hepatic carboxylesterase (PCE). This reaction was monitored at multiple time points up to 6 h and maintained linearity at an approximate rate of 1.08 pmol/min/mg esterase.
In a previous study (Niino, T., Ishibashi, T., Ishiwata, H., Takeda, K., and Onodera, S. (2003) Characterization of human salivary esterase in enzymatic hydrolysis of phthalate esters. J. Health Sci. 49, 76−81.) with PCE, DEHP (50 μM) was metabolized to form MEHP at a rate of 127 pmol/min/mg protein. This rate was approximately 100 times faster than the hydrolysis of TBPH observed in this study (1.08 pmol/min/mg protein).
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: bioaccumulation potential cannot be judged based on study results
- Executive summary:
The in-vitro metabolism of the brominated flame retardant TBPH was examined.
In experiments with human liver microsomes (HLM), a significant loss of TBPH was not observed, and no metabolites were detected by GC/MS analysis of the sample extracts. An LC/MS-MS method was developed to monitor mono(2-ethylhexyl) tetrabromophthalate (TBMEHP), a potential hydrolysis metabolite of TBPH. After a 6-h incubation with HLM, TBMEHP was not detected as a metabolite of TBPH, and no significant loss of TBPH was observed. However, TBPH was slowly metabolized to form TBMEHP in the presence of 0.1mg/mL of porcine hepatic carboxylesterase (PCE). This reaction was monitored at multiple time points up to 6 h and maintained linearity at an approximate rate of 1.08 pmol/min/mg esterase.
In a previous study with PCE, DEHP (50 μM) was metabolized to form MEHP at a rate of 127 pmol/min/mg protein. This rate was approximately 100 times faster than the hydrolysis of TBPH observed in this study (1.08 pmol/min/mg protein).
The prominent difference between the metabolic hydrolysis of DEHP and TBPH may be a result of steric hindrance by the fully brominated phenyl ring of TBPH.
Overall, no metabolites of TBPH were observed with HLM. From this study there is no indication that TBPH is degradated to TBMEHP in vivo. In an in-vitro experiment the hydrolysis rate of TBPH with PCE is by factor 100 slower compared with DEHP.
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