Degradation pathways of decabromodiphenyl ether during hydrothermal treatment.
The hydrothermal degradation pathways of decabromodiphenyl ether during hydrothermal treatment were investigated. After an initial "Heating time", the reaction runs were carried out at constant temperature (heating to 300 degrees C and keeping temperature) and pressure (8MPa) in a SUS316 stainless steel micro autoclave filled with water. Some decomposition of decabromodiphenyl ether was observed over 200 degrees C, and it was decomposed by more than 99% after 10 min at 300 degrees C. The reactivities of bromine on para and meta substituents were relatively high, while its reactivity on ortho bromine was extremely low. The formations of polybrominated dibenzo-p-dioxins and furans (PBDD/DFs) were observed in the early stages of the reactions at around 300 degrees C. The TCDD toxicity equivalency (TCDD-EQs) of the by-products was determined based on relative potencies (REPs EC(5TCDD)) with the Dioxin-Responsive-Chemical Activated Luciferase gene eXpression (DR-CALUX) bioassays technology. These results indicated that the risk of formation of PBDD/DFs in the hydrothermal degradation of deca-BDE was low, and it would be possible to reduce the TCDD-EQs value by adding some catalyst or alkali, or extending processing time.
Nose
Kazutoshi
K
National Institute for Environmental Studies, 16-2 Onogawa, Tsukuba, Ibaraki 305-8506, Japan. nose.kazutoshi@nies.go.jp
Hashimoto
Shunji
S
Takahashi
Shin
S
Noma
Yukio
Y
Sakai
Shin-ichi
S
D001681:Biological Assay; D005411:Flame Retardants; D055768:Halogenated Diphenyl Ethers; D006358:Hot Temperature; D010647:Phenyl Ethers / Q000737:chemistry* / Q000633:toxicity; D011075:Polybrominated Biphenyls / Q000737:chemistry* / Q000633:toxicity; D011312:Pressure; D018508:Water Purification / Q000295:instrumentation / Q000379:methods*
D005411:Flame Retardants; D055768:Halogenated Diphenyl Ethers; D010647:Phenyl Ethers; D011075:Polybrominated Biphenyls; C010902:decabromobiphenyl ether