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    某电厂掺烧生物质后脱硫塔内结垢成因分析与对策

    Analysis of the causes and countermeasures of scaling in the desulfurization tower of a power plant after blending with biomass burning

    • 摘要: 随着环保法规的严格执行,燃煤电厂实现超低排放的关键在于维持脱硫系统的安全稳定运行。针对某电厂在掺烧生物质(沙柳)后脱硫塔湍流器内部出现的大面积结垢现象,系统分析了结垢成因及生物质掺烧对垢层特性的影响。通过采集现场垢样并结合实验室分析发现,垢样表面呈现交织结构,质地坚硬。红外光谱分析显示,垢层中存在羟基(O—H)及碳氢键(C—H)吸收峰,表明湍流器表面存在未燃尽的生物质残留。工业分析进一步表明,该电厂掺烧的生物质灰分含量显著高于典型煤种及其他农林生物质,且挥发分较低,导致燃烧效率下降和未完全燃烧物质增多,从而加剧结垢问题。元素分析结果显示,垢样主要成分为 CaSO4·2H2O(石膏),表明结垢类型以石膏垢为主。流场模拟分析表明,湍流层与烟气进口区域存在流场分布不均,形成局部涡流和低流速区,促使脱硫浆液中的石膏过饱和析出并沉积。结合化学动力学分析,生物质掺烧引入的有机成分与石膏晶体生长发生交联作用,进一步加速了垢层的形成与积累。基于上述研究,结垢问题的根本成因可归纳为2方面:其一,生物质掺烧后燃烧不完全导致未燃尽有机物进入脱硫系统,为垢层形成提供异质成核位点;其二,脱硫浆液中石膏过饱和度的升高与流场分布缺陷共同作用,促使石膏晶体在湍流器表面优先沉积。为缓解这一问题,建议采取以下优化措施:改进生物质预处理工艺,提升破碎粒度均匀性及干燥效率,以改善燃烧充分性;优化燃烧参数(如掺烧比例、炉膛温度场分布),减少未燃尽颗粒的产生;调整脱硫系统运行参数(如浆液 pH 值、液气比),控制石膏过饱和度;改造除尘设备以适应生物质掺烧后飞灰特性变化,降低颗粒物携带量;在脱硫塔内增设盐分浓度在线监测装置,实时调控石膏结晶条件;重新设计湍流器布局或引入导流装置,改善流场均匀性,抑制局部沉积。上述综合方案的实施将有效提升脱硫系统运行的稳定性,为燃煤电厂生物质掺烧技术的环保与经济性平衡提供理论依据及工程指导。

       

      Abstract: With the stringent enforcement of environmental regulations, maintaining the safe and stable operation of desulfurization systems has become critical for coal-fired power plants to achieve ultra-low emissions. The large-scale scaling issue observed in the turbulence generator of a desulfurization tower after co-firing biomass (Salix psammophila) at a specific power plant is investigated, and the scaling mechanisms as well as the impact of biomass co-firing on scaling characteristics are analyzed. Field-collected scale samples exhibited an interwoven surface structure with high hardness. Infrared spectroscopy revealed hydroxyl (O—H) and hydrocarbon (C—H) absorption peaks in the scale, indicating the presence of unburned biomass residues on the turbulence generator surface. Industrial analysis further demonstrated that the co-fired biomass had significantly higher ash content and lower volatile matter compared to typical coal and other agricultural biomass, leading to reduced combustion efficiency and increased unburned substances, thereby exacerbating scaling. Elemental analysis identified CaSO4·2H2O (gypsum) as the primary component of the scale, confirming gypsum-dominated scaling. Flow field simulations highlighted uneven distribution between the turbulence layer and flue gas inlet, creating localized vortices and low-velocity zones that promoted supersaturated gypsum crystallization and deposition. Chemical kinetic analysis suggested that organic components introduced by biomass co-firing interacted with gypsum crystal growth through cross-linking effects, accelerating scale formation. The root causes of scaling were attributed to two factors: Incomplete biomass combustion introduced unburned organic matter into the desulfurization system, providing heterogeneous nucleation sites; Elevated gypsum supersaturation in the desulfurization slurry combined with flow field defects facilitated preferential crystal deposition. To address these issues, comprehensive optimization strategies are proposed: Enhance biomass pretreatment (e.g., particle size uniformity and drying efficiency) to improve combustion completeness; Optimize combustion parameters (e.g., co-firing ratio, furnace temperature distribution) to minimize unburned particles; Adjust desulfurization operational parameters (e.g., slurry pH, liquid-to-gas ratio) to control gypsum supersaturation; Upgrade dust removal equipment to adapt to fly ash characteristics post co-firing; Install real-time salinity monitoring in the desulfurization tower for crystallization control; Redesign turbulence generator geometry or install flow guides to homogenize flow distribution. These integrated measures will enhance system stability and provide theoretical and engineering guidance for balancing environmental and economic performance in biomass co-firing applications.

       

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