污泥掺烧对燃煤电站污染物控制装置的影响

Impact of sludge blending on the air pollutant control devices in a coal-fired power plant

  • 摘要: 利用燃煤电站进行污泥掺烧既可以实现污泥的高效消纳,又可以利用燃煤电站现有的污染物控制装置控制污泥燃烧生成的污染物。然而,燃煤电站的实际运行经验表明污泥掺烧后会影响污染物控制装置的稳定运行。文中在功率为660 MWe的超低排放燃煤机组上进行了污泥掺烧试验并开展现场测试,探究污泥掺烧对痕量元素分布、灰渣特性的影响机制,并评估污泥掺烧对选择性催化还原(SCR)脱硝、静电除尘及烟气湿法脱硫系统的潜在影响。试验所用的市政和印染污泥混合物中含有较高浓度的Ni、Cu、Zn和Mn等元素,但在湿污泥掺烧质量比为5%的工况下,并未改变重金属元素在系统中的分布情况,除了Hg以外的绝大部分重金属元素仍然分布在颗粒相中,仅有少量的Pb、Cr和Ni元素出现在脱硫石膏中;试验所用污泥的Cl元素质量浓度要远高于原煤,在SCR反应器入口采用EPA Method 26A方法采样并测试烟气中HCl和Cl2的体积分数。结果表明:燃烧时,燃料中75%以上的Cl元素都以HCl的形式释放到烟气中,使得脱硫浆液中含有较高质量浓度的Cl离子;掺烧污泥后,PM1~PM10的超微米颗粒的生成量则要低于未掺烧工况,且污泥飞灰中较高质量浓度的Fe2O3、P2O5降低了飞灰比电阻,有利于提高混燃后静电除尘器的效率;污泥掺烧后部分细颗粒进入脱硫浆液,造成脱硫石膏脱水困难,而浆液中Cl质量浓度的增加,进一步导致脱硫石膏含水率的升高。

     

    Abstract: Using coal-fired power plants for co-firing can achieve efficient consumption of sludge, and the existing Air Pollutant Control Devices (APCDs) in coal-fired power plants can effectively control the pollutants generated by sludge combustion. However, the experience of power plants also indicates that sludge co-firing may have adverse effects on the stable operation of APCDs. This study conducted sludge co-firing experiments and field tests on a 660 MWe power unit, investigated the impact mechanism of sludge co-firing on trace element distribution, ash characteristics, and evaluated the potential influence of sludge blending on SCR de-NOx, Electrostatic Precipitator (ESP) and wet Flue Gas Desulfurization (FGD) systems. The mixture of municipal and printing/dyeing sludge used in the experiment contained higher concentrations of Ni, Cu, Zn and Mn elements, but the distribution of heavy metal elements in the system did not change at a 5% sludge blending ratio. Except for Hg, most of the heavy metal elements were still distributed in the particle phase, with only a small amount of Pb, Cr and Ni elements appear in desulfurization gypsum. Cl element content in the sludge used in the experiment is much higher than that of the raw coal. HCl and Cl2 concentrations in the flue gas were sampled and tested at the entrance of the SCR reactor using EPA Method 26A. The results showed that more than 75% of Cl element in the fuel was released into the flue gas in the form of HCl during the combustion process, causing a high concentration of Cl ions in the desulfurization slurry. The generation of PM1 to PM10 ultrafine particles after co-firing is lower than that under non co-firing conditions, and the higher concentrations of Fe2O3 and P2O5 in the sludge ash reduced its resistivity, which is beneficial for improving the efficiency of ESP after co-firing. More fine particles enter the desulfurization slurry after co-firing, making it difficult to dehydrate the gypsum. And the increase in Cl concentration in the slurry further leads to an increase in gypsum moisture content.

     

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