College of Water Sciences, Beijing Normal University, Beijing, 100875, PR China; State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing, 100012, PR China.
China National Environmental Monitoring Centre, Beijing, 100012, PR China.
Ecotoxicol Environ Saf. 2020 Apr 1;192:110246. doi: 10.1016/j.ecoenv.2020.110246. Epub 2020 Feb 3.
The thermal processes of cement kilns are sources of polybrominated dibenzofurans and dioxins (PBDD/Fs); however, when co-processing decabromodiphenyl ether (BDE-209) soil in cement kilns, very few reports have investigated the mechanism of PBDD/Fs formation from BDE-209. Therefore, the pathways and factors that influence the formation of PBDD/Fs were investigated using Box-Behnken design (BBD) of the response surface methodology (RSM) at lab-scale. The PBDEs, HBr/Br and PBDD/Fs emissions in flue gas from the simulated thermal process were analyzed using gas chromatography/mass spectroscopy (GC/MS), high-resolution gas chromatography/high-resolution mass spectrometry (HRGC/HRMS), and ion chromatography (IC). Density functional theory (DFT) was also used to further discuss the formation of PBDD/Fs. The major products of BDE-209 thermal decomposition in flue gas were 97.1% HBr/Br (a.v. 26.6%/70.6%) > 2.7% PBDEs >0.2% PBDD/Fs. Formation of precursors were the main pathways for PBDD/Fs, and those precursors were dominated by higher-brominated PBDEs (heptã deca-BDEs); debromination of BDE-209 was also a crucial pathway for the formation of PBDD/Fs throughout the thermal process. Interestingly, it was easier to form HpBDD/Fs from OBDD/Fs than from PBDEs. The O percentage and interaction factors of O percentage, temperature, and CaCO percentage have the largest influence on PBDD/Fs emissions and formation.
水泥窑的热过程是多溴二苯并呋喃和二恶英(PBDD/Fs)的来源;然而,当在水泥窑中协同处理十溴二苯醚(BDE-209)土壤时,很少有报道研究 BDE-209 形成 PBDD/Fs 的机制。因此,使用响应面法(RSM)的 Box-Behnken 设计(BBD)在实验室规模下研究了影响 PBDD/Fs 形成的途径和因素。使用气相色谱/质谱(GC/MS)、高分辨率气相色谱/高分辨率质谱(HRGC/HRMS)和离子色谱(IC)分析模拟热过程中烟道气中的 PBDEs、HBr/Br 和 PBDD/Fs 排放。还使用密度泛函理论(DFT)进一步讨论了 PBDD/Fs 的形成。烟道气中 BDE-209 热分解的主要产物是 97.1% HBr/Br(平均 26.6%/70.6%)>2.7% PBDEs>0.2% PBDD/Fs。前体的形成是 PBDD/Fs 的主要途径,这些前体主要由更高溴化的 PBDEs(七溴十溴)组成;BDE-209 的脱溴也是整个热过程中形成 PBDD/Fs 的关键途径。有趣的是,从 OBDD/Fs 形成 HpBDD/Fs 比从 PBDEs 更容易。O 百分比和 O 百分比、温度和 CaCO 百分比的相互作用因子对 PBDD/Fs 排放和形成的影响最大。