|Abbreviations||TBBPA, TBBP-A, TBBA|
|Jmol-3D images||Image 1|
|Molar mass||543.9 g·mol−1|
|Density||2,12 g·cm−3 (20 °C)|
|Melting point||178 °C (352 °F; 451 K)|
|Boiling point||250 °C (482 °F; 523 K) (decomposition)|
|Solubility in water||insoluble|
|Except where noted otherwise, data are given for materials in their standard state (at 25 °C (77 °F), 100 kPa)|
|(what is: / ?)|
Production and use
TBBPA is produced by the reaction of bromine with bisphenol A. Most commercial TBBPA products consist of a mixture that differ in the degree of bromination with the formula C15H16-xBrxO2 where x = 1 to 4. Its fire-retarding properties correlate with %Br.The annual consumption in Europe has been estimated as 6.200 tons in 2004.
TBBPA is mainly used as a reactive component of polymers, meaning that it is incorporated into the polymer backbone. It is used to prepare fire-resistant polycarbonates by replacing some bisphenol A. A lower grade of TBBPA is used to prepare epoxy resins, used in printed circuit boards.
A study was published by the European Food Safety Authority (EFSA) in December 2011 on the exposure of TBBPA and its derivatives in food. The study, which examined at 344 food samples from the fish and other seafood food group, concluded that “current dietary exposure to TBBPA in the European Union does not raise a health concern.” EFSA also determined that “additional exposure, particularly of young children, to TBBPA from house dust is unlikely to raise a health concern”.
Some studies suggest that TBBPA may be an endocrine disruptor and immunotoxicant. As an endocrine disruptor, TBBPA may interfere with both estrogens and androgens. Further, TBBPA structurally mimics the thyroid hormone thyroxin (T4) and can bind more strongly to the transport protein transthyretin than T4 does, likely interfering with normal T4 activity. TBBPA likely also suppresses immune responses by inhibiting expression of CD25 receptors on T cells, preventing their activation, and by reducing natural killer cell activity.
A 2013 literature review on TBBPA concludes that TBBPA does not produce “adverse effects that might be considered to be related to disturbances in the endocrine system”. Therefore, in accordance with internationally accepted definitions, TBBPA should not be considered an “endocrine disruptor”. Furthermore, TBBPA is rapidly excreted in mammals and therefore does not have a potential for bioaccumulation. Measured concentrations of TBBPA in house dust, human diet and human serum samples are very low. Daily intakes of TBBPA in humans were estimated to not exceed a few ng/kg bw/day. Exposures of the general population are also well below the derived-no-effect-levels (DNELs) derived for endpoints of potential concern in REACH.
TBBPA degrades to bisphenol A and to TBBPA dimethyl ether, and experiments in zebrafish (Danio rerio) suggest that during development, TBBPA may be more toxic than either BPA or TBBPA dimethyl ether.
TBBPA emits can be found in trace concentration in the hydrosphere, soil, and sediments. It also occurs in sewage sludge and house dust. TBBPA has been the subject of an eight year evaluation under the EU Risk Assessment procedure which reviewed over 460 studies. The Risk Assessment was published on the EU Official Journal in June 2008. The conclusions of the Risk Assessment were confirmed by the European Commission SCHER Committee (Scientific Committee on Health and Environmental Risks). TBBPA has been registered under REACH.
- Record of Tetrabromobisphenol A in the GESTIS Substance Database from the IFA, accessed on 2008/2/15
- Dagani, M. J.; Barda, H. J.; Benya, T. J.; Sanders, D. C. (2005), "Bromine Compounds", Ullmann's Encyclopedia of Industrial Chemistry, Weinheim: Wiley-VCH, doi:10.1002/14356007.a04_405
- Draft EU Risk Assessment of 2,2′,6,6′- TETRABROMO-4,4′-ISOPRYOPYLIDENE DIPHENOL, Final Environmental Draft of June 2007
- EFSA Scientific Opinion on Tetrabromobisphenol A (TBBPA) and its derivatives in food (2011) http://www.efsa.europa.eu/en/efsajournal/doc/2477.pdf. See page 1.
- Shaw, S.; Blum, A.; Weber, R.; Kannan, K.; Rich, D.; Lucas, D.; Koshland, C.; Dobraca, D.; Hanson, S.; Birnbaum, L. (2010). "Halogenated flame retardants: do the fire safety benefits justify the risks?". Reviews on Environmental Health 25 (4): 261–305. doi:10.1515/REVEH.2010.25.4.261. PMID 21268442.
- Pullen, S; Boecker R.; Tiegs G (2003). "The flame retardants tetrabromobisphenol A and tetrabromobisphenol A–bisallylether suppress the induction of interleukin-2 receptor α chain (CD25) in murine splenocytes". Toxicology 184 (1): 11–22. doi:10.1016/S0300-483X(02)00442-0.
- Kibakaya, EC; Stephen K; Whalen MM (2009). "Tetrabromobisphenol A has immunosuppressive effects on human natural killer cells". Journal of Immunotoxicology 6 (4): 285–292. doi:10.3109/15476910903258260.
- Thomas Colnot, Sam Kacew, Wolfgang Dekant, Archives of Toxicology, Mammalian toxicology and human exposures to the flame retardant 2,2′,6,6′-tetrabromo-4,4′-isopropylidenediphenol (TBBPA): implications for risk assessment , 2013, http://link.springer.com/article/10.1007/s00204-013-1180-8
- McCormick, J; Paiva MS; Häggblom MM; Cooper KR; White LA (2010). "Embryonic exposure to tetrabromobisphenol A and its metabolites, bisphenol A and tetrabromobisphenol A dimethyl ether disrupts normal zebrafish (Danio rerio) development and matrix metalloproteinase expression". Aquatic Toxicology 100 (3): 255–262. doi:10.1016/j.aquatox.2010.07.019. PMID 20728951.
- Kuch B, Körner W, Hagenmaier H (2001): Monitoring von bromierten Flammschutzmitteln in Fliessgewässern, Abwässern und Klärschlämmen in Baden-Württemberg. Umwelt und Gesundheit, Universität Tübingen.
- TBBPA draft RAR
- European Union Risk Assessment Report on TBBPA (2008) http://echa.europa.eu/documents/10162/32b000fe-b4fe-4828-b3d3-93c24c1cdd51
- TBBPA REACH Registration webpage http://echa.europa.eu/web/guest/information-on-chemicals/registered-substances