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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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
The following information is available for this endpoint:
Graves, W. C. and Swigert, J. P (1997). Hexabromocyclododecane (HBCD): 48-hour flow-through acute toxicity test with the Cladoceran (Daphnia magna). Report no.: 439A-102. Report date: 1997-05-21.
Priestly, S. L. (2008a). EPS - Styropor F 215-N, Lot 39-2704: Acute toxicity to Daphnia magna. Report no.: 2631/0001.Report date: 2008-10-27.
Priestly, S. L. (2008b). XPS - Styrodur 2800C 40mm, Lot 286 985 75LO: Acute Toxicity to Daphnia magna. Report no.: 2631/0003. Report date: 2008-10-27.
Graves and Swigert (1997) was selected as the key study as it was considered to be the most reliable and relevant study available.
Key value for chemical safety assessment
Additional information
The commercial HBCDD product was not acutely toxic to Daphnia magna. HBCDD’s 48 hour EC50, no mortality/immobility concentration, and NOEC (6.8 µg/L nominal) in Daphnia magna were all greater than gamma HBCDD’s water solubility (3.4 µg/L measured). The highest nominal dose tested was twice gamma HBCDD’s water solubility. Nominal test concentrations were 0, 1.5, 2.2, 3.2, 4.6 and 6.8 µg/L which corresponded to mean measured concentrations (HPLC with UV/VIS detector) of 0, 2.4, 1.8, 2.1, 2.3 and 3.2 µg/L, respectively (Graves and Swigert, 1997). A composite of three manufacturers' commercial products was used as test article in the above study. The dose levels in the study were based on the water solubility of HBCDD (approxiamtely 3.4 µg/L) determined via quantiation on the gamma diastereomer. The alpha and beta diastereomers were not quantifiable at a gamma concentration of 3.4 µg/L due to their low concentrations in the test article. Correcting for gamma diasteromer content in the test article, the 48 hour NOEC was > 8.5 µg/L of the commercial product in water.
The lack of acute toxicity in daphnia was also observed in the Daphnia 21 day study, using the commercial HBCDD product as test article. No mortality was observed at 48 hour at nominal concentrations up to 13.6 µg/L (11 µg/L, measured, based on gamma diasteromer). Correcting for the content of the gamma diastereomer, the nominal concentration was 17.2 µg/L. Thus, the 48 hour EC50 in daphnia of the HBCDD commercial product is > 17.2 ug/L.
The HBCDD commercial product has not been tested in Daphnia at higher doses.
The 48 hour effective loading rate 50 (EL50) of XPS or EPS foam boards flame retarded with HBCDD was > 100 mg board/L.
Thus, HBCDD was not acutely toxic to daphnia when tested up to and five times the limit of solubility of the gamma diastereomer, or when the commercial product was incorporated into XPS or EPS foamInformation 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.
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