![]() General chemical structure of octabromodiphenyl ethers, where m + n = 8 | |
Names | |
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Other names Octabromobiphenyl ether; OctaBDE, Octa-BDE; Octabromodiphenyl oxide; OBDPO | |
Identifiers | |
ChemSpider |
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ECHA InfoCard | 100.046.428 |
EC Number |
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UNII | |
CompTox Dashboard (EPA) | |
Properties | |
C12H2Br8O | |
Molar mass | 801.379 g·mol−1 |
Appearance | White solid [1] |
Density | 2.9 g/cm3 [1] |
Melting point | Depends on product composition [1] |
Boiling point | Decomposes [1] |
< 0.1 mg/L [1] | |
Hazards | |
GHS labelling: | |
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Danger | |
H360Df | |
Related compounds | |
Related polybrominated diphenyl ethers | Decabromodiphenyl ether, Pentabromodiphenyl ether |
Related compounds | diphenyl ether |
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa). |
Octabromodiphenyl ether (octaBDE, octa-BDE, OBDE, octa, octabromodiphenyl oxide, OBDPO) is a brominated flame retardant which belongs to the group of polybrominated diphenyl ethers (PBDEs).
Commercial octaBDE (also known as "Octabrom") is a technical mixture of different PBDE congeners having an average of 7.2 to 7.7 bromine atoms per molecule of diphenyl ether. [2] The predominant congeners in commercial octaBDE are those of heptabromodiphenyl ether and octaBDE. [2] [3] The term octaBDE alone refers to isomers of octabromodiphenyl ether (PBDE congener numbers 194–205). [4]
Structure | Congener | Name | Fraction |
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![]() | BDE-153 | 2,2′,4,4′,5,5′-hexa- bromodiphenyl ether | 0.15–8.7% |
![]() | BDE-154 | 2,2′,4,4′,5,6′-hexa- bromodiphenyl ether | 0.04–1.1% |
![]() | BDE-171 | 2,2′,3,3′,4,4′,6-hepta- bromodiphenyl ether | 0.17–1.8% |
![]() | BDE-180 | 2,2′,3,4,4′,5,5′-hepta- bromodiphenyl ether | n.d.–1.7% |
![]() | BDE-183 | 2,2′,3,4,4′,5′,6-hepta- bromodiphenyl ether | 13–42% |
![]() | BDE-196 | 2,2′,3,3′,4,4′,5,6′-octa- bromodiphenyl ether | 3.1–10.5% |
![]() | BDE-197 | 2,2′,3,3′,4,4′,6,6′-octa- bromodiphenyl ether | 11–22% |
![]() | BDE-203 | 2,2′,3,4,4′,5,5′,6-octa- bromodiphenyl ether | 4.4–8.1% |
![]() | BDE-206 | 2,2′,3,3′,4,4′,5,5′,6-nona- bromodiphenyl ether | 1.4–7.7% |
![]() | BDE-207 | 2,2′,3,3′,4,4′,5,6,6′-nona- bromodiphenyl ether | 11–12% |
![]() | BDE-209 | Deca- bromodiphenyl ether | 1.3–50% |
Only congeners with more than 1% listed.
OctaBDE is used in conjunction with antimony trioxide as a flame retardant in the housings of electrical and electronic equipment, mainly in the plastic acrylonitrile butadiene styrene, but also in high impact polystyrene, polybutylene terephthalate and polyamides. [6] Typically 12–15% of the weight of the final product will consist of octaBDE. [6]
The annual demand worldwide was estimated as 3,790 tonnes in 2001, of which Asia accounted for 1,500 tonnes, the Americas 1,500 tonnes, and Europe 610 tonnes. [7] The United Nations Environment Programme reports "Since 2004, it [octaBDE] is no longer produced in the EU, USA and the Pacific Rim and there is no information that indicates it is being produced in developing countries." [3]
OctaBDE is released by different processes into the environment, such as emissions from the manufacture of octaBDE-containing products and from the products themselves. [3] Elevated concentrations can be found in air, water, soil, food, sediment, sludge, and dust. [3] [8] [9]
In the environment, "photolysis, anaerobic degradation and metabolism in biota" can cause debromination of octaBDE, which produces PBDEs with fewer bromine atoms "which may have higher toxicity and bioaccumulation potential." [3]
OctaBDE may enter the body by ingestion or inhalation. [4] It is "stored mainly in body fat" and may stay in the body for years. [4] In an investigation carried out by the WWF, "the brominated flame retardant chemical (PBDE 153), which is a component of the penta- and octa- brominated diphenyl ether flame retardant products" was found in all blood samples of 14 ministers of health and environment of 13 European Union countries. [10]
The chemical has no proven health effects in humans; however, based on animal experiments, octaBDE may have effects on "the liver, thyroid, and neurobehavioral development." [4]
The European Union has carried out a comprehensive risk assessment under the Existing Substances Regulation 793/93/EEC. [6] As a consequence, the EU has banned the use of octaBDE since 2004. [11]
In the United States, as of 2005, "no new manufacture or import of" pentaBDE and octaBDE "can occur... without first being subject to EPA [i.e., United States Environmental Protection Agency ] evaluation." [12] As of mid-2007, a total of eleven states in the U.S. had banned octaBDE. [13]
In May 2009, commercial octaBDE was added to the Stockholm Convention as it meets the criteria for the so-called persistent organic pollutants of persistence, bioaccumulation and toxicity.
Alternatives to octaBDE include tetrabromobisphenol A, 1,2-bis (pentabromophenoxy) ethane, 1,2-bis(tribromophenoxy)ethane, triphenyl phosphate, resorcinol bis(diphenylphosphate), and brominated polystyrene; however, for each of these "the existing data on toxicological and ecotoxicological effects are fewer than for octabromodiphenyl ether." [14]