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SORBENT/COAL INJECTION IN A CERAMIC FILTER TO CONTROL POWERPLANT EMISSIONS - ACID RAIN PRECURSORS

机译:陶瓷过滤器中的吸附剂/煤液注射,控制动力装置排放 - 酸雨前体

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This manuscript provides an update on recent laboratory developments of a high-temperature flue gas filtration technology, in conjunction to sorbent injection. Calcium/sodium-based sorbents are sprayed in the post-combustion zone of a furnace. The sorbent reacts with gaseous forms of sulfur and chlorine (SO_2, H_2, HCl, etc.) in the furnace effluent to form stable salts of calcium. The partially-reacted sorbent is then collected in a high-temperature filter, which is placed downstream of the sorbent injection point, and continues reacting therein for a prolonged period of time. The primary advantage of this technique is that both the likelihood and the duration of contact between the solid sorbent particles and the gaseous pollutants increase, since reaction takes place in the furnace upstream of the filter as well as inside the filter itself. Hence, the sorbent utilization (i.e., the conversion of sorbent CaO to CaSO_4, CaSO_3, CaCl_2, etc.) increases drastically. A preferred filter configuration is a wall-flow honeycomb monolith, made of a high temperature ceramic, such as silicon carbide or cordierite. An additional advantage of the filter is that partially-burned carbon, such as soot, char, tar, etc., is collected therein, where there is sufficient time (several minutes to an hour) for complete combustion of carbon. The filter must be regenerated (cleaned) periodically to remove the collected minerals (ash and spent sorbent). This is accomplished with aerodynamic regeneration, i.e., using bursts of compressed air flowing in the opposite to the flue gas direction. This process is a competitive alternative to existing pollution control methods, such as flue gas desulfurization (FGD) scrubbers, selective catalytic/non-catalytic reduction (SCR/SNCR), baghouses, and electrostatic precipitators. Unlike existing technologies, this technique simultaneously removes SO_2, NO_x, HCl, and particulates.
机译:此手稿结合吸附剂注入,提供了关于高温烟气过滤技术的最近实验室开发的更新。钙/钠的吸附剂喷涂在炉子后燃烧区。吸附剂在炉流出物中以气态形式的硫和氯(SO_2,H_2,HCl等)反应,以形成钙的钙盐。然后将部分反应的吸附剂收集在高温过滤器中,该高温过滤器被置于吸附剂注射点的下游,并继续在其中的时间长时间反应。该技术的主要优点在于,固体吸附剂颗粒与气态污染物之间的偶像和持续时间增加,因为在过滤器上游的炉内以及过滤器本身内部发生反应。因此,吸附剂利用(即,Sorbent Cao转换为Caso_4,Caso_3,CaCl_2等)急剧增加。优选的过滤装置是由高温陶瓷制成的壁流蜂窝整料,例如碳化硅或堇青石。过滤器的另一个优点是其中收集部分燃烧的碳,例如烟灰,焦油,焦油等,其中有足够的时间(几分钟至一小时),以完全燃烧碳。必须定期再生(清洁)过滤器以除去收集的矿物质(灰烬和废吸附剂)。这是通过空气动力学再生完成的,即,使用压缩空气沿与烟道气体的相对流动的压缩空气突发来实现。该方法是对现有的污染控制方法的竞争替代品,例如烟道气脱硫(FGD)洗涤器,选择性催化/非催化还原(SCR / SNCR),巴布孔和静电除尘器。与现有技术不同,该技术同时去除SO_2,NO_X,HCL和微粒。

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