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EC number: 211-185-4 | CAS number: 632-79-1
- 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
Biodegradation in soil
Administrative data
- Endpoint:
- biodegradation in soil
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- March 27 - August 16, 1979
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study is well-reported, and conducted prior to established guidelines with no information on GLPs.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 979
Materials and methods
- Principles of method if other than guideline:
- Soil was treated with 14C-TBPA. At 0, 1, 2, 4, 7, 14 and 28 d soil was sampled and analyzed. 3 replicates at each dose.
- GLP compliance:
- not specified
- Test type:
- laboratory
Test material
- Reference substance name:
- 14C-tetrabromophthalic anhydride
- IUPAC Name:
- 14C-tetrabromophthalic anhydride
- Details on test material:
- 14C-TBPA: uniformly labeled in aromatic ring. Specific activity: 11.6 mCi/mM; radiochemical purity 98%. Synthesized by Midwest Research Institute.
Constituent 1
- Radiolabelling:
- yes
Study design
- Oxygen conditions:
- aerobic
- Soil classification:
- USDA (US Department of Agriculture)
Soil properties
- Soil no.:
- #1
- Soil type:
- sandy loam
- % Clay:
- 28.4
- % Silt:
- 23.2
- % Sand:
- 48.4
- % Org. C:
- 0.2
- pH:
- 6.3
- CEC:
- 36 meq/100 g soil d.w.
- Bulk density (g/cm³):
- 1.67
Duration of test (contact time)
- Soil No.:
- #1
- Duration:
- 28 d
Initial test substance concentrationopen allclose all
- Soil No.:
- #1
- Initial conc.:
- 1 mg/kg soil d.w.
- Based on:
- test mat.
- Soil No.:
- #1
- Initial conc.:
- 10 mg/kg soil d.w.
- Based on:
- test mat.
Experimental conditions
- Soil No.:
- #1
- Temp.:
- 28 degrees C
- Humidity:
- 70%
Results and discussion
Material (mass) balance
- Soil No.:
- #1
- Remarks on result:
- other: No statistical difference between the 14C-activity at D 0 and 28.
% Degradation
- Soil No.:
- #1
- Parameter:
- other: See text below
Half-life / dissipation time of parent compound
- Soil No.:
- #1
- Remarks on result:
- other: See text below.
- Transformation products:
- yes
Identity of transformation products
- No.:
- #1
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- Tetrabromophthalic acid
- Identifier:
- common name
- Identity:
- Tetrabromophthalic acid
- Evaporation of parent compound:
- no
- Details on results:
- Very slight volatilization (0.038% at the 10 ug/g level). Soil-bound 14C-activity increased in both levels between 0 and 28 d (~24 and 32% of applied 14C at 28 d in the 1 and 10 ug/g doses, respectively). Due to the high amount bound, soil further extracted with NaOH. All of bound 14C-activity soluble in NaOH at both doses at d 0 and 28. At the 10 ug/g level, the 28 d sample contained 94% TBPA-acid and 4% TBPA. Concluded TBPA-acid binds to soil particles.
TLC resulted indicated no evidence of biodegradation. 95% of 14C-activity identified as TBPA-acid at both d 0 and 28. 1% identified as TBPA, and 4% unknown. In summary, there was no difference in the 0 and 28 d samples, indicating little or no biodegradation of TBPA over the 28 d. However, hydrolysis of TBPA to TBPA-acid was observed.
Applicant's summary and conclusion
- Conclusions:
- TBPA rapidly hydrolyzed to TBPA-acid. Little volatilization was observed, and a large proportion (24 -32%) of the 14C-activity became soil-bound after 28 days. The soil-bound radiocarbon was identified as TBPA acid (94.0%) and TBPA (4.0%). Biodegradation was not observed. Hydrolysis to TBPA-acid was observed.
- Executive summary:
When introduced to soil, TBPA rapidly hydrolyzed to TBPA-acid. Little volatilization was observed, and a large proportion (24 -32%) of the 14C-activity became soil-bound after 28 days. The soil-bound radiocarbon was identified as TBPA acid (94.0%) and TBPA (4.0%). Biodegradation was not observed. Hydrolysis to TBPA-acid was observed.
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