煤热解过程中多环芳烃的生成与排放特性

Formation and emission characteristics of polycyclic aromatic hydrocarbons during coal pyrolysis

  • 摘要: 燃煤过程中产生的有机污染物对环境造成了严重危害。我国煤炭消费量大,燃煤产生的有机污染物排放不容忽视。以褐煤、无烟煤和高含氯量的天池煤为研究对象,使用傅里叶红外分析方法探究了煤中有机物的赋存形态。在固定床热解平台上探讨了3种煤热解过程中多环芳烃(PAHs)的生成特性及其影响因素,使用气相色谱质谱仪定量分析了16种PAHs的生成量,使用定性分析方法探讨了释放有机污染物的组成。结果表明:烷烃类是煤中主要有机物,占总有机物含量的39%~61%。褐煤中的羟基种类和含量最多,含氧官能团更复杂;无烟煤芳香化程度更高。对原煤中PAHs提取时,12 h为最佳时间,此时无烟煤、天池煤和褐煤原样中PAHs质量分数分别为10.34、15.10、0.75 μg/g。热解时间是影响PAHs生成量的重要因素,30 min时可认为试验中样品已热解完毕,PAHs完全释放。随着热解温度的升高,褐煤和天池煤热解过程中PAHs生成量先增加后减小;在1 000 ℃时最大,排放量分别为3 168.15 µg/g和974.58 µg/g。无烟煤热解过程中PAHs生成量则先升高后减小再升高,在1 100 ℃最大,为853.93 µg/g。挥发分含量对PAHs的排放量有明显影响;随着不同煤中挥发分含量的增加,PAHs生成量不断增加。天池煤中的卤族元素会阻碍苯环的芳构化和缩合反应,影响多环芳烃的生成。褐煤和无烟煤热解气最大毒性当量分别出现在1 000 ℃和1 100 ℃,分别为85.59 µg/g和75.00 µg/g;而天池煤热解气最大毒性当量出现在800 ℃,为24.33 µg/g。

     

    Abstract: The utilization of coal leads to the emission of organic pollutants that cause significant harm to the environmental. The coal consumption in China is particularly high, making the emissions of organic pollutant an issue that cannot be overlooked. In this work, the organic components of raw lignite, anthracite, and Tianchi coal were analyzed using Fourier transform infrared analysis method. The characteristics and influencing factors of polycyclic aromatic hydrocarbons (PAHs) were investigated with a fixed-bed pyrolysis system. The 16 kinds of PAHs were quantitatively determined by gas chromatography-mass spectrometry (GC-MS), while the composition of released organic pollutants was explored through qualitative analysis. The results indicate that alkanes are the primary organic compounds in coals, accounting for 39%−61%. Lignite contains the greatest variety and quantity of hydroxyl groups, along with more complex oxygen-containing functional groups, whereas anthracite exhibits a higher degree of aromatization. The optimal extraction time for PAHs from raw coal is 12 hours. The PAHs content of anthracite, Tianchi coal, and lignite are 10.34, 15.10 and 0.75 μg/g, respectively. The pyrolysis time is found to be a critical factor influencing PAHs formation. At 30 minutes, pyrolysis can be considered complete, with PAHs fully released. With the increase of the pyrolysis temperature, PAHs emission of lignite and Tianchi coal increases and then decreases. The maximum emissions are observed at 1 000 ℃, with the values of 3 168.15 µg/g and 974.58 µg/g, respectively. For anthracite, PAHs emissions followed a different trend-increasing, then decreasing, and finally rising again, with a maximum of 853.93 μg/g at 1 100 ℃. The volatile matter content has a pronounced effect on PAH emissions, and coals with higher volatile content generate more PAHs. Furthermore, halogen elements in Tianchi coal are found to hinder the aromatization and condensation reactions of benzene rings, thereby affecting PAHs formation. The maximum toxic equivalency of lignite and anthracite occur at 1 000 ℃ and 1 100 ℃, with values of 85.59 μg/g and 75.00 μg/g, respectively. For Tianchi coal, the maximum toxic equivalency is observed at 800 ℃, with a value of 24.33 μg/g.

     

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