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UPGRADING OF WHEAT/BARLEY AND MISCANTHUS BIO-OIL OVER A SULPHIDED CATALYST

机译:在硫化催化剂上升级小麦/大麦和MISCANTHUS生物油

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In recent years, the production of biofuels from non-food crops wastes and harvesting residues plays an important role in the improvement of the global environment and in the replacement of declining oil reserves~1. Hydrogenation of lignocellulosic bio-oil is attracting much attention as a suitable way to produce petroleum-refinery compatible feedstock. Primarily, hydrogenation of bio-oil is carried out under severe reaction conditions in two-stage fixed-bed reactors, filled with a noble metal catalyst in the first zone and with a sulphided catalyst in the second zone2. This setup allows producing low-oxygen upgraded bio-oil, however, it is economically unviable and operationally complicated. Here, we present the results from 80 h long hydrogenation experiments of miscanthus and wheat/barley straw bio-oils obtained by one-stage condensation (2-5 °C) or fractional condensation (75 °C) ablative fast pyrolysis (AFP). Bio-oils from fractional condensation, in contrast to those from one-stage condensation, were stable and did not separate into an aqueous and organic phase. In that case, operation with these bio-oils was much easier than with bio-oils from one-stage condensation. Upgrading of bio-oils was performed in a one-stage fixed bed reactor filled with a laboratory-made NiMo/Al_2O_3 catalyst under constant reaction conditions (340 °C, 4 MPa and WHSV 1 h~(-1)), which we identified in our previous research as suitable reaction conditions. Hydrogenated products separated spontaneously into an aqueous phase, formed predominantly by water, and an organic phase. In this work, we used various analytical methods for the determination of physicochemical properties (density, viscosity, elemental analysis etc.) and chemical composition (CAN, Carbonyls by Faix, GC-MS for volatile compounds and hydrocarbons) of the organic products. In addition, we used FTIR in combination with the principle component analysis (PCA) to take a snapshot of the catalyst health and product quality. In all hydrogenated products, we have observed a drop in the quality with the increasing time-on-stream, which may be caused by catalyst deactivation and coke formation, as it shown in Figure 2. Nevertheless, the coke formation and reactor clogging, during the hydrogenation of miscanthus bio-oil, was so high that we were forced to stop the experiment after 36 hours. The observed decrease in Micro Conradson Carbon residues and CAN of the products from wheat/barley straw bio-oil indicated a significant improvement of the product stability. The laboratory-made NiMo/Al_2O_3 catalyst was suitable for the upgrading of straw bio-oil, from one-stage and from fractional condensation AFP, and can be further developed for the upgrading for other feedstocks.
机译:近年来,从非粮食作物废弃物和收获残余物中生产生物燃料在完善全球环境和替代石油储量〜1中发挥着重要作用。木质纤维素生物油的氢化是作为生产石油 - 炼油厂相容原料的合适方式的重视。主要是,生物油的氢化在两阶段固定床反应器中的严重反应条件下进行,在第一区中含有贵金属催化剂并在第二区2中含有硫化催化剂。该设置允许生产低氧升级的生物油,但是,经济不可逃使和运行复杂。在这里,我们介绍了通过单阶段冷凝(2-5℃)或分形缩合(75℃)烧蚀的快速热解(AFP)获得的80 H长氢化实验的结果。与单阶段冷凝相比,来自分数缩合的生物油是稳定的,并且没有分离成水性和有机相。在这种情况下,与这些生物油的操作比来自一级冷凝的生物油更容易。在恒定反应条件下填充有实验室制造的NiMO / Al_2O_3催化剂的单级固定床反应器中进行生物油的升级(340℃,4MPa和WHSV 1 H〜(-1)),我们识别在我们以前的研究中作为合适的反应条件。氢化产物自发地分离成水相,主要由水形成和有机相。在这项工作中,我们使用了各种分析方法来测定有机产品的物理化学性质(密度,粘度,元素分析等)和化学成分(CAN,羰基,用于挥发性化合物和烃类的GC-MS)。此外,我们使用FTIR与原理成分分析(PCA)结合使用催化剂健康和产品质量的快照。在所有氢化产物中,我们已经观察到质量下降,随着催化剂的失活和焦炭形成可能是由催化剂失活和焦炭形成引起的,如图2所示。然而,焦炭形成和反应器堵塞,在此期间Miscanthus生物油的氢化非常高,我们被迫在36小时后停止实验。观察到的微康拉德碳残留物和小麦/大麦秸秆生物油的产品的减少表明产品稳定性的显着提高。实验室制造的NiMO / Al_2O_3催化剂适用于秸秆生物油,从单级和分数缩合AFP升级,并且可以进一步开发用于升级其他原料。

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