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Effect of phosphorous transformation on the reduction of PM10 formation during co-combustion of coal and sewage sludge

机译:磷转化对煤炭污泥共燃烧过程中PM10形成的影响

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Co-combustion of Municipal Sewage Sludge with coal will become increasingly widely used,regarded as an important incineration method with the high thermal efficiency,low emissions,low investment and operating costs.However, the presence of phosphorus in fine particle has gained increased attention due to its environmental adverse affection and deactivation of SCR DeNOx catalysts. Therefore, the behavior of phosphorus in fine particles during co-combustion of coal and sewage sludge was investigated in a 25 kW quasi one-dimensional down-fired pulverized coal combustor,where PM10 was collected from the furnace centerline in the outlet of flue gas cooler by using a two-stage nitrogen-aspirated,water-cooling isokinetic sampling probe followed a 13-stage electric low pressure impactor. Then the formation mechanism of PM10 was investigated by observing the different fractions of sewage sludge in the coal. Similar to the coal combustion, the particle-sizedistributions (PSD) of PM10 mass concentration by cocombustion of sewage sludge with coal exhibit two distinct modes separated by a fraction of 0.1570.263um,ultrafine mode and intermediate mode.With the sewage sludge blended sludge up to 15% (thermal ratio), the mass concentration of the total fly ash and PM10+ (Dp>10μm) vastly increased from 1088 and 547 mg/Nm3 (during coal combustion) to 5059 and 4403 mg/Nm3.However, the mass concentration of fine particulates,such as PM1,PM2.5 and PM10 was maintained at the emission level of coal combustion.When the fraction of sewage sludge less than 15%, the mass concentration of fine particle is higher than the emission during coal combustion,while the growth rate is only by the 3.6%,7.9% and 4.8% of the total concentration of fly ash (5% thermal). The change of the PSD of mass concentration during cocombustion of sewage sludge and coal,mainly was caused by the interaction between Si、 Al and Ca、Fe、 K、 Na、 Mg,which lowed the fusing temperature of the aluminosilicate and silicate, then readily aggregated to form larger particles.Sulphate and phosphate process during the cooling of flue gas will reduced the mass concentration of fine particle,when the fraction of sewage sludge was 15% (thermal), the phosphate and P2O5 will dominantly increased in the ultrafine mode.
机译:与煤炭的城市污水污泥的共同燃烧将越来越广泛地使用,被视为具有高热效率,低排放量,低投资和运营成本的重要焚烧方法。然而,在微粒中存在磷的存在增加了其环境不良情感和SCR Denox催化剂的失活。因此,在25kW准一体式下燃煤煤燃烧器中研究了煤和污水污泥的共燃烧过程中细颗粒中的磷的行为,其中PM10从烟气冷却器出口的炉子中心线收集通过使用两级氮气吸水,水冷等渗采样探针,然后是13级电动低压冲击器。然后通过观察煤中的污水污泥的不同部分来研究PM10的形成机制。类似于煤燃烧,PM10质量浓度通过污水污泥与煤炭的粒子大小素(PSD)显示出两种不同的模式,分离0.1570.263um,超细模式和中间模式。与污水污泥混合污泥至15%(热比),总粉煤灰和PM10 +(DP>10μm)的质量浓度从1088和547mg / nm3(煤燃烧期间)大大增加至5059和4403mg / nm3.但是质量浓度在煤炭燃烧的排放水平处保持细颗粒,例如PM1,PM2.5和PM10。当污水污泥的级分小于15%时,细粒的质量浓度高于煤燃烧期间的发射增长率仅为粉煤灰总浓度(5%热)的3.6%,7.9%和4.8%。在污水污泥和煤炭中的群众浓度的变化主要是由Si,Al和Ca,Fe,K,Na,Mg之间的相互作用引起的,这降低了硅铝酸盐和硅酸盐的熔合温度聚集以形成较大的颗粒。燃料气体冷却过程中的氧化物和磷酸盐过程将降低细颗粒的质量浓度,当污水污泥的分数为15%(热)时,磷酸盐和P2O5将在超细模式下显着增加。

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