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Diss Factsheets
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EC number: 247-148-4 | CAS number: 25637-99-4
- 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 water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
Schafer, E. C. and Haberlein, D. (1996). Hexabromocyclododecane (HBCD): Closed Bottle Test. Report no.: 439E-102.
Davis, J. W., Gonsior, S. J., Markham, D. A. and Marty, G. T. (2004a). Investigation of the biodegradation of [14C]Hexabromocyclododecane in sludge, sediment and soil. Report no.: 031178.
Davis, J. W., Gonsior, S. J., Markham, D. A., Friedrich, U., Hunziker, R. W. and Ariano, J. M. (2006). Biodegradation and Product Identification of [14C]Hexabromocyclododecane in Wastewater Sludge and Freshwater Aquatic Sediment. Environ. Sci. Technol. (2006) Vol. 40, pp. 5395-5401.
Gerecke, A. C., Giger, W., Hartmann, P. C., Heeb, N. V., Kohler, H. -P. E., Schmid, P., Zennegg, M. and Kohler, M. (2006). Anaerobic degradation of brominated flame retardants in sewage sludge. Chemosphere (2006), Vol. 64, pp.311-317.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable
Additional information
HBCDD is not readily biodegradable in a 28 day aerobic degradation sewage sludge test (Schafer and Haberlein, 1996). However, inherent biodegradation was observed in aerobic and anaerobic digester sludge (Davis et al., 2004; 2006 (Chemosphere); 2006 (Environ. Sci. Technol.)). Within 28 days HBCDD had decreased to approximately 10% of the starting value while a 50% loss occurred by day 15. Abiotic degradation processes appeared to play an important role. All three diastereomers were degraded. Gerecke et al. (2006) reported a much shorter half-life of 0.66 days in anaerobic sewage sludge. The difference in half-lives (15 days versus 0.66 days) was attributed to the 90-fold higher HBCDD concentration used by Davis et al. At higher concentrations for poorly soluble substances such as HBCDD, biodegradation rates are more dependent on mass transfer limitations than on true biodegradation kinetics. Environmentally relevant concentrations should be used to generate meaningful kinetic data.
Davis et al. (2006) reported three degradants: tetrabromocyclododecane, dibromocyclododecadiene and cyclodecatriene. The authors proposed that HBCDD was sequentially debrominated via dihaloelimination where at each step there is the loss of two bromines from vicinal carbons with the subsequent formation of a double bond between the adjacent carbon atoms. The conclusion was that microorganisms naturally occurring in anaerobic digester sludge mediate complete debromination of HBCDD.
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