Registration Dossier
Registration Dossier
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: 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

Distribution modelling
Administrative data
- Endpoint:
- distribution modelling
- Type of information:
- calculation (if not (Q)SAR)
- Remarks:
- Migrated phrase: estimated by calculation
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Estimated using software recommended by REACH Guidance.
Data source
Reference
- Reference Type:
- other: software program
- Title:
- Estimation Programs Interface (EPI) Suite™ v3.20 for Microsoft® Windows
- Author:
- anonymous
- Year:
- 2 009
- Bibliographic source:
- U.S. Environmental Protection Agency, Washington, DC, U.S.A.
Materials and methods
- Model:
- calculation according to Mackay, Level III
- Calculation programme:
- LEVEL III Fugacity Modelm EPI v 3.20
- Release year:
- 2 007
- Media:
- other: air, water, soil
Test material
- Reference substance name:
- tetrabromophthalic anydride
- IUPAC Name:
- tetrabromophthalic anydride
- Details on test material:
- The hydrolysis product of TBPA was modeled, e.g. tetrabromphthalic acid (TBPA_acid).
Constituent 1
Study design
- Test substance input data:
- chemical structure
Results and discussion
Percent distribution in media
- Air (%):
- 5
- Water (%):
- 7.4
- Soil (%):
- 82.8
- Sediment (%):
- 9.4
Any other information on results incl. tables
Tetrabromophthalic anhydride is expected to rapidly hydrolyze to tetrabromophthalic acid in the environment. TBPA acid's properties are modeled below.
Environmental Fate Parameters for Tetrabromophthalic Acid using EPI Suite, v3.20.
Parameter |
Estimation Program |
Result |
Stability |
||
Photodegradation in Air |
AOP v1.92 |
Overall OH rate constant: 1.0464 E-012 cm3/molecule-sec Half-life: 10.222 days (12-hr day; 1.5E6 OH/cm3) |
Hydrolysis |
HYDROWIN v1.67 |
Program cannot estimate for this structure. |
Photodegradation in Water |
No Estimate |
---- |
Photodegradation in Soil |
No Estimate |
---- |
Biodegradation |
||
Water |
LEVEL III Fugacity Model using Biowin Ulitmate, AOPwin |
Half-life: 1440 hours |
Water and Sediment |
LEVEL III Fugacity Model using Biowin Ulitmate, AOPwin |
Half-life in sediment: 1.296E+004 hours |
Soil |
LEVEL III Fugacity Model using Biowin Ulitmate, AOPwin |
Half-life: 2880 hours |
Mode of Degradation in Actual Use |
STP Fugacity Model BIOWIN (v4.10) |
Primary sludge: 37.88%, Waste Sludge 24.21%, Total Biodegradation 0.57%, Total Removal 62.65%, Final Water Effluent 37.35% Linear Model: Does Not Biodegrade Fast Non-Linear Model: Does Not Biodegrade Fast Ultimate Biodegradation Timeframe: Months Primary Biodegradation Timeframe: Weeks-Months MITI Liner Model: Biodegrades Fast MITI Non-Linear Model: Does Not Biodegrade Fast Anaerobic Model: Biodegrades Fast Ready Biodegradation Prediction: NO |
Bioaccumulation |
||
Aquatic/Sediment Organisms |
BCF v2.17 |
Estimated Log BCF=0.500 BCF=3.162 |
Terrestrial Organisms |
No Estimate |
---- |
Transport and Distribution |
||
Adsorption/ Desorption |
PCKOCWIN v1.66 |
557.3 Koc may vary with pH |
Henry’s Law Constant, 25°C |
HENRY v3.10 |
1.17E-014 atm-m3/mole 4.79E-013 unitless |
Distribution Modeling |
LEVEL III Fugacity Model |
Emissions of 1000 kg/hr to air, water and soil Air: 5.34E-007%, half-life 245 hr Water: 7.362%, half-life 1.44E+03 hr Soil: 82.8%, half-life 2.88E+03 hr Sediment: 9.381%, half-life 1.3E+04 |
Other Distribution Data |
KOAWIN v1.10 AEROWINv1.00 Volatilization from Water |
Log Koa (octanol/air): 16.278 Koa (octanol/air): 1.897E+016 Sorption to aerosols at25°C: Kp (particle/gas partition coef.) 0.183 m3/ug (Mackay model); 4.66E+003m3/ug (Octanol/air model); Fraction sorbed to airborne particulates (phi): 0.869 Junge-Pankow, 0.936 Mackay, and 1 Octanol/air models. Half life: 1.253x10+007 years (River); 1.367x10+008 years (Lake) |
Applicant's summary and conclusion
- Conclusions:
- The primary environmental compartment for TBPA-acid, the hydrolysis product of TBPA, is expected to be soil (82.8%). Sediment and water are the next largest expected compartments (9.38% and 7.36%, repectively). Negligible amounts are expected to partition to air.
- Executive summary:
The primary environmental compartment for TBPA-acid, the hydrolysis product of TBPA, is expected to be soil (82.8%). Sediment and water are the next largest expected compartments (9.38% and 7.36%, repectively). Negligible amounts are expected to partition to air.
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.