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Kinetic and mechanistic studies of the heterogeneous formation of polychlorinated dioxins and furans on incinerator fly ash.

机译:焚烧炉粉煤灰中多氯二恶英和呋喃异质形成的动力学和机理研究。

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Emission problems have hindered the acceptance of incineration as a viable solid waste treatment method, particularly due to releases of polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans (PCDD/F). Experiments in our laboratory suggest that PCDD/F are not formed during combustion, but instead in the lower temperature (250-400{dollar}spcirc{dollar}C) post-combustion zone of the incinerator. Metal species found in incinerator fly ash--the residual material formed from non-combustibles in the waste stream and entrained in the flue gas--appear to be catalyzing PCDD/F formation at these low temperatures.; Two distinct and separable heterogeneous pathways for PCDD/F formation on fly ash were studied in our laboratory: reactions involving native carbon in the fly ash matrix as a precursor, and those involving chemically-similar gas-phase precursors. The first pathway has been referred to as de Novo synthesis, where unlike complexes of elemental carbon, oxygen, chlorine, and hydrogen in fly ash are somehow combined in the presence of gas-phase oxygen to form chlorinated aromatic compounds such as PCDD/F. De Novo synthesis of {dollar}sp{lcub}13{rcub}{dollar}C-labelled PCDD/F was observed when {dollar}sp{lcub}13{rcub}{dollar}C-activated carbon was added to fly ash and reacted with air at 250-350{dollar}spcirc{dollar}C. Optimum temperatures for de Novo synthesis were found to range from 300-325{dollar}spcirc{dollar}C.; The second pathway involves chemically-similar gas-phase precursors, such as chlorophenols, formed initially as products of incomplete combustion (PICs). These precursors appear to react catalytically with elements in the fly ash to produce PCDD molecules. Reactions of chlorophenol precursors--in particular 2,3,4,6-tetrachlorophenol--with fly ash were studied in the laboratory as a function of precursor concentration and temperature. Optimum PCDD formation temperatures ranged from 300-400{dollar}spcirc{dollar}C. Chlorophenols were found to be highly adsorptive on fly ash, while satisfying a Freundlich adsorption isotherm. The catalytic mechanism for chlorophenol conversion to PCDD on fly ash was determined to be consistent with a Langmuir-Hinshelwood mechanism.
机译:排放问题阻碍了将焚烧作为一种可行的固体废物处理方法,尤其是由于释放了多氯二苯并-对-二恶英和多氯二苯并呋喃(PCDD / F)。我们实验室的实验表明,PCDD / F不是在燃烧过程中形成的,而是在焚烧炉较低的燃烧后温度区域(250-400 {sp}}。焚烧炉粉煤灰中发现的金属物质(废料流中由非可燃物形成并夹带在烟道气中的残留物质)似乎在这些低温下催化PCDD / F的形成。在我们的实验室中研究了在粉煤灰上形成PCDD / F的两种不同且可分离的异质途径:涉及粉煤灰基质中的天然碳作为前体的反应,以及涉及化学相似的气相前体的反应。第一条途径被称为从头合成,其中不像粉煤灰中的元素碳,氧,氯和氢的络合物在气相氧存在下以某种方式结合形成氯化芳族化合物,例如PCDD / F。当将{dol} sp {lcub} 13 {rcub} {dollar} C活性炭添加到粉煤灰中时,观察到{dol} sp {lcub} 13 {rcub} {dollar} C标记的PCDD / F的从头合成并与空气在250-350 {sp} {dol} C下反应。发现从头合成的最佳温度为300-325℃。第二种途径涉及化学相似的气相前驱物,例如氯酚,最初形成为不完全燃烧(PIC)的产物。这些前体似乎与粉煤灰中的元素发生催化反应,生成PCDD分子。在实验室中研究了氯酚前体(特别是2,3,4,6-四氯酚)与粉煤灰的反应,该反应是前体浓度和温度的函数。最佳的PCDD形成温度范围为300-400 {。发现氯酚对粉煤灰具有高吸附性,同时满足Freundlich吸附等温线。确定了在粉煤灰上将氯酚转化为PCDD的催化机理与Langmuir-Hinshelwood机理一致。

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