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EC number: 284-366-9 | CAS number: 84852-53-9
- 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:
- (Q)SAR
- Remarks:
- Migrated phrase: estimated by calculation
- Adequacy of study:
- key study
- Study period:
- April 2010
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Estimated performed using software recommended by REACH Guidance.
Data source
Reference
- Reference Type:
- other: software program
- Title:
- EPI v3.20. (February 2007. Estimation Programs Interface. U.S. Environmental Protection Agency Office of Pollution Prevention and Toxic Substances. Syracuse Research Corporation).
- Author:
- anonymous
- Year:
- 2 007
- Bibliographic source:
- U.S. Environmental Protection Agency, Washington, D.C.
Materials and methods
- Model:
- calculation according to Mackay, Level III
- Calculation programme:
- Level III Fugacity Model, EPIwin v3.20
- Release year:
- 2 007
- Media:
- other: air, water, soil, sediment
Test material
- Reference substance name:
- 1,1'-(ethane-1,2-diyl)bis[pentabromobenzene]
- EC Number:
- 284-366-9
- EC Name:
- 1,1'-(ethane-1,2-diyl)bis[pentabromobenzene]
- Cas Number:
- 84852-53-9
- Molecular formula:
- C14H4Br10
- IUPAC Name:
- 1,2,3,4,5-pentabromo-6-[2-(2,3,4,5,6-pentabromophenyl)ethyl]benzene
- Details on test material:
- Modeled on DBDPEthane's chemical structure
Constituent 1
Study design
- Test substance input data:
- Chemical structure was input into EPI.
- Environmental properties:
- Default model parameters
Results and discussion
Percent distribution in media
- Air (%):
- 0.05
- Water (%):
- 0.6
- Soil (%):
- 48.8
- Sediment (%):
- 50.5
- Aerosol (%):
- 0
Any other information on results incl. tables
Predicted Transport and Distribution Between Environmental Compartments
DBDPEthane’s transport and distribution between environmental compartments was modeled using EPI v. 3.20, and based on the chemical’s structure. In the environment, 99.3% of DBDPEthane's releases are predicted to distribute to sediment and soil. DBDPEthane is predicted to partition to sediment (50.5%) and soil (48.8%) with negligible amounts partitioning to water (0.6%) and air (0.05%) (Level III Fugacity Model; Emissions of 1000 kg/hr to each of air, water, soil). It is expected to bind extensively to organic carbon based on estimated Koc values (Table), and therefore to be essentially immobile in soil, sewage sludge, and sediments. It is not expected to volatilize from water (Volatilization half-life in rivers = 7 years, in lakes = 77 years). In air, it is expected to bind to airborne particulates. The fraction sorbed to particulates is estimated to be 1 at 25°C (AEROWIN v1.00). Its characteristic travel distance is expected to be low, which indicates it should not be subject to long-range transport in the atmosphere. Its movement in the atmosphere will be governed by that of the particulates to which it is bound.
Removal in sewage treatment plants is expected (94% total removal) through settling in sludge (60% in primary sludge, 33% in waste sludge) (STP Fugacity Model). Aerobic biodegradation in a sewage treatment plants is not expected. The amount in the final water effluent leaving a treatment plant is estimated at approximately 6% of the influent.
Estimated Properties for DBDPEthane using EPI (v3.20).
Property |
Result |
EPI Module |
Henry’s Law Constant (25ºC) |
6.42 x 10-8atm-m3/mole (Bond) 2.94 x 10-8atm-m3/mole (Group) |
HENRY (v3.10) |
2.94 x 10-8atm-m3/mole 1.20 x 10-6unitless |
HENRYWIN v3.10 |
|
2.09 x 10-1atm-m3/mole |
VP/Wsol Estimate using EPI values |
|
Liquid/Subcooled Vapor Pressure |
9.33 x 10-9Pa 7 x 10-11Hg |
AEROWIN v1.00 |
Log Koa (octanol/air partition coefficient) |
19.221 |
KOAWIN v1.10 |
Log Kaw (air/water partition coefficient) |
-5.581 |
KOAWIN v1.10 |
Particle/gas Partition Coefficient (Kp) (m3/μg) |
321 (Mackay model) 4.08 x106(Koa model) |
AEROWIN v1.00 |
Reaction with Hydroxyl Radicals in the Atmosphere |
Overall OH Rate Constant = 2.395 x10-12cm3/molecule-sec; Half-life = 4.466 days (12-hr d; 1.5x106OH/cm3) |
AOP v1.92 |
Koc |
3.312 x 106 |
PCKOC (v1.66) |
Biomass to water partition coefficient |
8.73 x 1012 |
STP Fugacity Model |
Applicant's summary and conclusion
- Conclusions:
- DBDPE is expected to partition in the environment to sediment and soil (ca. 99%). High binding to particulates in all media is expected. Sewage treatment plants are expected to remove > 95% of that present in the influent. Removal is expected to be via binding to particulates rather than biodegradation. Its characteristic travel distance is expected to be low and long range atmospheric transport is not expected. Its movement in the atmosphere will be governed by the particulates to which it is bound.
- Executive summary:
DBDPE is expected to parition in the environment to sediment and soil (ca. 99%). High binding to particulates in all media is expected. Sewage treatment plants are expected to remove > 95% of that present in the influent. Removal is expected to be via binding to particulates rather than biodegradation. Its characteristic travel distance is expected to be low and long range atmospheric transport is not expected. Its movement in the atmosphere will be governed by the particulates to which it is bound.
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