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Diss Factsheets
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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
Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
The uptake, distribution, and elimination of the commercial BDE-209 product(s) after oral, intravenous (IV), or intraperitoneal administration in rats have been evaluated in several studies (El Dareer et al., 1987; Mörck et al., 2003; Norris et al., 1973, 1974, 1975; NTP, 1986; Riu et al., 2008; Sandholm et al., 2003; Biesemeier et al. 2010). Certain of these studies followed total 14C-radioactivity or total bromine content via neutron activation analysis. Others used methods based on detection of individual BDE congeners. Absorption and metabolism has also been followed in the dairy cow and the seal (Kierkegaard et al., 2007; Thomas et al., 2005). An in vitro study has also been conducted using hepatic microsomes from a marine mammal (Gebbink et al., 2006). Further, an in vitro dermal absorption study has been conducted (Hughes et al., 2001).
The various studies on the commercial product or noncommercial BDE-209 congener indicate poor oral absorption, and essentially no elimination in the urine with typically greater than 90% of an oral dose eliminated in the feces within 72 h as the parent molecule or bound residues. As expected, gavage administration may result in slightly more uptake than administration via the diet. Removal of bromine atoms from the parent molecule to produce lower BDE congeners, if it occurs, represents only a minor fraction of the dose (<3%). At most, it appears that only 1 or 2 bromine atoms may be removed metabolically either in the liver or by gut bacteria. Blood and tissue levels following oral exposure are routinely very low, and represent only a small fraction of the oral dose. After oral dosing, highest concentrations of the parent molecule are typically found in the liver, and are likely related to the venous blood flow from the digestive tract. Direct elimination into the bile, without prior systemic circulation, of a substantial fraction of the absorbed dose likely accounts for the low blood levels. A low uptake from the gut coupled with direct elimination from the liver to the bile results in only a small fraction of an oral dose reaching the systemic circulation and, ultimately, tissues. Skin absorption is negligible. Accumulation after repeated doses is minimal. Blood levels of nonaBDEs, commonly ascribed as metabolites of BDE-209, are typically <0.5% of that of the parent and are indicative of low absorption and/or minimal formation. The designation of nona- and octaBDEs as BDE-209 metabolites is complicated by their presence in test articles. The above findings are relevant for reference value development because they indicate that comparable ADME properties for BDE-209 exist in different species, which supports the use of allometric scaling for addressing interspecies differences in toxicokinetics. See Hardy et al (2009) Critical Reviews in Toxicology 39(S3):1 -44 for a detailed discussion of the BDE-209 ADME studies.
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