Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
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: 214-604-9 | CAS number: 1163-19-5
- 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
Carcinogenicity
Administrative data
Description of key information
Two year studies in rats and mice performed by the U.S. National Toxicology Program on the commercial DecaBDE product at doses of 0, 2.5 and 5% of the diet.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LOAEL
- 6 625 mg/kg bw/day
Justification for classification or non-classification
Classification of DecaBDE as a carcinogen is not justified. The chronic studies with BDE-209 suggest that low-dose exposures (e.g., ≤1.0 mg/kg-day) do not induce non-neoplastic or neoplastic changes in cells; and excessively high-dose exposures (e.g., 6650 mg/kg-day) may induce proliferative lesions in select tissues (e.g., thyroid follicular hyperplasia) that may progress to neoplasia via MOAs that are not relevant to humans. Therefore, doses of BDE-209 that do not produce nonneoplastic changes will be adequately protective against the development of neoplasia. See EURA 20402 EN and Hardy et al. (CRT 2009 39(S3):1 -44) for full discussion.
Additional information
No evidence of a genotoxic effect was detected in the Ames Salmonella, chromosome aberration, mouse lymphoma, or sister-chromatid exchange tests (McGregor et al., 1988; NTP 1986; Wagner & Klug, 1998). No cytogenic changes were observed in the bone marrow of rats (parents and offspring) undergoing a one-generation reproduction test using FR-300 -BA (Norris et al. 1975). The absence of positive genotoxicity findings, along with the absence of tumors in the chronic study by Kociba et al. (1975), and only strain- and sex-specific tumors present in excessively dosed animals in the NTP (1986) study support the following: the commercial BDE-209/BDE-209 is not genotoxic; does not induce tumors via a mutagenic mechanism of action; and that a possible threshold exists for induction of tumors.
Using its evidence of carcinogenicity categories of “clear,” “some,” “equivocal,” and “no,” the NTP (1986) concluded there was some (rats, increased incidence of neoplastic nodules in low-dose males and high-dose animals of both sexes), equivocal (male mice, increased incidence of hepatocellular adenomas or carcinomas [combined] in the low-dose and increased incidence of thyroid follicular cell adenomas or carcinomas [combined] in both dose groups), and no (female mice) evidence of carcinogenicity. Based on the dose levels used, it is remarkable that the responses observed were consistent with rodent- or strain-specific tumors commonly seen in high-dose groups (EPA, 1998f; Goodman et al., 1994). In the NTP (1986) study, the authors considered the increased incidence of neoplastic nodules of the liver in male and female rats to be suggestive evidence of carcinogenicity; however, as noted previously, this terminology has been abandoned and there was no increase in hepatocellular carcinomas, as would be expected if the increased incidence of neoplastic nodules was truly representative of benign neoplasia (Huff et al., 1989). The US NTP does not include BDE-209 in its list of carcinogens (NTP, 2005). Further, BDE-209 is not listed as a carcinogen by the US Occupational Safety and Health Administration (OSHA), and the International Agency for Research on Cancer (IARC) determined it is “ . . . not classifiable as to its carcinogenicity to humans (Group 3)” based on “ . . . limited evidence” in experimental animals (IARC, 1990; OSHA, 2008). In conclusion, the chronic studies with BDE-209 suggest that low-dose exposures (e.g., ≤1.0 mg/kg-day) do not induce non-neoplastic or neoplastic changes in cells; and excessively high-dose exposures (e.g., 6650 mg/kg-day) may induce proliferative lesions in select tissues (e.g., thyroid follicular hyperplasia) that may progress to neoplasia via MOAs that are not relevant to humans. Therefore, doses of BDE-209 that do not produce nonneoplastic changes will be adequately protective against the development of neoplasia. See Hardy et al. (CRT 2009 39(S3):1-44) for full discussion.
Carcinogenicity: via oral route (target organ): glandular: thyroids
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.