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碱性及含硫化合物对十溴联苯醚热降解的影响
Influence of alkaline and sulfur-containing compounds on the thermal degradation of decabromodiphenyl ether
将十溴联苯醚(BDE-209)于400~600℃的温度范围内进行热降解,利用GC、GC/MS对产物种类及含量变化进行分析,讨论了温度、时间、碱性化合物和含硫化合物对BDE-209降解以及对溴代二噁英生成的影响.结果表明.温度和时间均是BDE-209热降解和生成溴代二噁英的重要影响因素;热降解40min时,450℃条件下溴代二噁英生成量最多;产物种类证实碱性化合物通过与BDE-209脱溴形成的HBr反应促进降解,且可抑制二噁英的生成;含硫化合物的添加同样促进BDE-209降解,抑制二噁英的形成,其详细的抑制机理有待进一步确定,BDE-209的降解反应有两种情况,即苯环上的脱溴反应和醚键的断裂反应.
The thermal degradation of decabromodiphenyl ether (BDE-209) was studied at the temperature range of 400~600℃. The types and contents of its degradation products were determined using GC and GC/MS techniques. The effects of temperature, time, and alkaline- and sulfur-containing compounds on the thermal degradation of BDE-209, as well as the formation of brominated dioxins, were discussed in this study. The results showed that both temperature and time were the two key factors for both the thermal degradation of BDE-209 and the formation of brominated dioxins. When BDE-209 was pyrolyzed at 450℃ for 40minutes, the brominated dioxins were generated to the maximum extent. The types of the products confirmed that alkaline compounds promoted the thermal degradation of BDE-209 by reaction with HBr formed from the BDE-209 debromination, and inhibited the formation of dioxins. Similarly, the sulfur compounds also promoted the degradation of BDE-209 and inhibited the formation of dioxins. However, the detailed inhibition mechanism needs to be further investigated in the future study. There are two kinds of degradation reactions for BDE-209, namely, debromination of phenyl rings and cleavage of ether bond. This research may provide a theoretical basis for the safe disposal of BDE-209-contained products and the reduction of secondary pollution.
含硫化合物 / 碱性化合物 / 热降解 / 十溴联苯醚 / 溴代二噁英
alkaline compounds / brominated dioxins / decabromodiphenyl ether (BDE-209) / sulfur-containing compounds / thermal degradation
[1] Huang Y, Zhang D, Yang Y, et al.Distribution and partitioning of polybrominated diphenyl ethers in sediments from the Pearl River Delta and Guiyu, South China [J].Environmental Pollution, 2018,235: 104-112.
[2] English K, Toms L-M L, Gallen C, et al.BDE-209 in the Australian Environment: Desktop review [J].Journal of Hazardous Materials, 2016,320:194-203.
[3] 韦朝海,廖建波,刘浔,等.PBDEs的来源特征、环境分布及污染控制[J].环境科学学报, 2015,35(10):3025-3041. Wei C, Liao J, Liu X, et al.Source, characteristics, environmental distribution and pollution control of PBDEs [J].Acta Scientiae Circumstantiae, 2015,35(10):3025-3041.
[4] 赵金平,何群华,钟英立,等.典型电子垃圾拆解区二噁英污染特征、相分配及暴露风险[J].生态环境学报, 2014,23(8):1338-1343. Zhao J, He Q, Zhong Y, et al.Pollution characteristics, gas/particle partitioning and inhalation risk assessment of dioxin in the typical E-waste dismantling region [J].Ecology and Environmental, Sciences, 2014,23(8):1338-1343.
[5] Zennegg M, Schluep M, Streicher-Porte P, et al.Formation of PBDD/F from PBDE in electronic waste in recycling processes and under simulated extruding conditions Markus [J].Chemosphere, 2014, 116:34-39.
[6] 苍大强,魏汝飞,张玲玲,等.钢铁工业烧结过程二噁英的产生机理与减排研究进展[J].钢铁, 2014,49(8):1-8. Cang D, Wei R, Zhang L, et al.Formation mechanism and emission reduction of PCDD/Fs in iron ore sintering [J].Iron & Steel, 2014,49(8):1-8.
[7] Ebert J, Bahadir M.Formation of PBDD/F from flame-retarded plastic materials under thermal stress [J].Environment International, 2003, 29(6):711-716.
[8] Ortuño N, Lundstedt S, Lundin L.Emissions of PBDD/Fs, PCDD/Fs and PBDEs from ?ame-retarded high-impact polystyrene under thermal stress [J].Chemosphere, 2015,123:64-70.
[9] Brian K, Barbara W, Emanuela G, et al.PCDD/F, PBDD/F, and PBDE Emissions from Open Burning of a Residential Waste Dump [J].Environmental science & technology, 2010,44(1):394-399.
[10] 冯涛,严建华,李晓东,等.典型废弃物焚烧炉飞灰中溴代二噁英和呋喃的分析研究[J].环境污染与防治, 2011,33(5):40-49. Feng T, Yan J, Li X, et al.Analytical research on the PBDD/Fs in typical waste incinerators flyash [J].Environmental Pollution & Control, 2011,33(5):40-49.
[11] Altarawneh M, Dlugogorski B Z.A Mechanistic and Kinetic Study on the Formation of PBDD/Fs from PBDEs [J].Environmental science & technology, 2013,47(10):5118-5127.
[12] Altarawneh M, Saeed A, Al-Harahsheh M, et al.Thermal decomposition of brominated flame retardants (BFRs): Products and mechanisms [J].Progress in Energy and Combustion Science, 2019, 70:212-259.
[13] Mei J, Wang X, Xiao X, et al.Characterization and inventory of PBDD/F emissions from deca-BDE, polyethylene (PE) and metal blends during the pyrolysis process [J].Waste Management, 2017,62: 84-90.
[14] Zhang M, Buekens A, Li X.Brominated flame retardants and the formation of dioxins and furans in fires and combustion [J].Journal of Hazardous Materials, 2016,304:26-39.
[15] 刘芃岩,张雅婧,张彦娜,等.十溴联苯醚的热解及其影响因素研究[J].中国环境科学, 2016,36(4):1099-1105. Liu P, Zhang Y, Zhang Y, et al.Pyrolysis and its influence factors of decabromodiphenyl ether [J].China Environmental Science, 2016, 36(4):1099-1105.
[16] Cai C Y, Yu S Y, Liu Y, et al.PBDE emission from E-wastes during the pyrolytic process: Emission factor, compositional profile, size distribution, and gas-particle partitioning [J].Environmental Pollution, 2018,235:419-428.
[17] Cai C Y, Chen L Y, Huang H J, et al.Effects of temperature on the emission of particulate matter, polycyclic aromatic hydrocarbons, and polybrominated diphenyl ethers from the thermal treatment of printed wiring boards [J].Journal of Hazardous Materials, 2019,380:120849.
[18] Jin Y, Tao L, Chi Y, et al.Conversion of bromine during thermal decomposition of printed circuit boards at high temperature [J].Journal of Hazardous Materials, 2011,186(1):707-712.
[19] Jung S-H, Kim S-J, Kim J-S.Thermal degradation of acrylonitrile-butadiene-styrene (ABS) containing flame retardants using a fluidized bed reactor: The effects of Ca-based additives on halogen removal [J].Fuel Processing Technology, 2012,96:265-270.
[20] Sun J, Wang W, Liu Z, et al.Study of the transference rules for bromine in waste printed circuit boards during microwave-induced pyrolysis [J].Journal of the Air & Waste Management Association [J].2011,61(5):535-542.
[21] Terakado O, Ohhashi R, Hirasawa M.Thermal degradation study of tetrabromobisphenol A under the presence metal oxide: Comparison of bromine fixation ability [J].Journal of Analytical and Applied Pyrolysis 2011,91(2):303-309.
[22] Griffin R D.A new theory of dioxin formation in municipal solid waste combustion [J].Chemosphere, 1986,15(9-12):1987-1990.
[23] Gullett B K, Bruce K R, Beach L O.Effect of sulfur-dioxin on the formation mechanism of poly-chlorinated dibenzodionxin and dibenzofuran in municipal waste combustors [J].Environmental Science & Technology, 1992,26(10):1938-1943.
[24] Raghunathan K, Gullett B K.Role of sulfur in reducing PCDD and PCDF formation [J].Environmental Science & Technology, 1996, 30(6):1827-1834.
[25] Ryan S P, Li X, Gullett B K, et al.Experimental study on the effect of SO2on PCDD/F emissions: determination of the importance of gas-phase versus solid-phase reactions in PCDD/F formation [J].Environmental Science & Technology, 2006,40(22):7040-7047.
国家自然科学基金资助项目(21377033);河北省自然科学基金资助项目(B2018201224);河北省教育厅重点项目(ZD20131046)
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